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Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program L384-AW-REP-10005 Prepared for INPEX August 2013 Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program L384-AW-REP-10005

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Subtidal Benthos Monitoring Baseline Report

Ichthys Nearshore Environmental Monitoring Program L384-AW-REP-10005

Prepared for INPEX August 2013

Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program L384-AW-REP-10005

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Document Information Prepared for INPEX Project Name Ichthys Nearshore Environmental Monitoring Program File Reference L384-AW-REP-10005_1_Subtidal Benthos Baseline Report.docm Job Reference L384-AW-REP-10005 Date August 2013

Contact Information Cardno (NSW/ACT) Pty Ltd Cardno (WA) Pty Ltd Cardno (NT) Pty Ltd

Level 9, The Forum 11 Harvest Terrace Level 6, 93 Mitchell Street 203 Pacific Highway West Perth WA 6005 Darwin NT 0800 St Leonards NSW 2065 Telephone: 02 9496 7700 Telephone: 08 9273 3888 Telephone: 08 8942 8200 Facsimile: 02 9499 3902 Facsimile: 08 9486 8664 Facsimile: 08 8942 8211 International: +61 2 9496 7700 International: +61 8 9273 3888 International: +61 8 8942 8211 www.cardno.com.au www.cardno.com.au www.cardno.com.au

Document Control Version Date Author Author

Initials Reviewer Reviewer

Initials

A 11/11/2012 Kate Reeds KR Peggy O’Donnell POD

B 21/11/2012 Kate Reeds KR Peggy O’Donnell POD

0 26/11/2012 Kate Reeds KR Peggy O’Donnell POD

0A 02/08/2013 Kate Reeds KR Joanna Lamb JL

1 19/08/2013 Kate Reeds KR Joanna Lamb JL

This document is produced by Cardno solely for the benefit and use by the client in accordance with the terms of the engagement for the performance of the Services. Cardno does not and shall not assume any responsibility or liability whatsoever to any third party arising out of any use or reliance by any third party on the content of this document.

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Executive Summary This Baseline Phase report outlines the initial findings of the Subtidal Benthos Monitoring Program undertaken between May 2012 and July 2012 as per the methodology outlined in the Ichthys Project Nearshore Environmental Monitoring Plan (NEMP) (Cardno 2012a). As part of the NEMP, sampling was undertaken to characterise the baseline (pre-dredging) conditions of the infaunal assemblages and physical parameters associated with the subtidal soft sediment habitats in Darwin Harbour Inner and Darwin Offshore.

The key objectives of the informative Subtidal Benthos Monitoring Program are to:

> Investigate the potential effects of dredging and dredge spoil disposal on the abundance and diversity of soft-bottom infauna and epifaunal communities;

> Determine whether there are significant changes in sediment characteristics (sediment particle size distrubution (PSD), oxidation-reduction potential (ORP) and pH) before dredging/spoil disposal compared to during and after and how this affects abundance and diversity of soft bottom communities; and

> Follow the subsequent recovery of any infauna and epifauna that may be impacted and relate this to depth of sedimentation, nature of sediment and ORP.

Specific objectives of the Baseline Phase are to:

> Assess the abundance and diversity of infauna and epifaunal assemblages;

> Sample seabed sediment to determine PSD in the predicted Impact and Control locations;

> Assess the ORPand pH of the sediments; and

> Investigate the relationship between the physico-chemical characteristics of the sediment (ORP and pH) and the composition of infaunal and epibenthic assemblages.

The Baseline Phase included an inshore (Darwin Harbour Inner) and offshore (Darwin Offshore) component and was carried out in four consecutive field trips between May 2012 and July 2012, during the Darwin dry season (May to October) and prior to any dredging and spoil disposal activities. Epifauna (animals living mainly on the surface of the seabed), were sampled remotely using a high-definition underwater video drop camera and frame. Sediment samples were also collected with a Ponar grab for abundance and diversity counts of benthic infauna (animals living within the sediment), PSD, pH and ORP.

The overall percentage cover of epifauna was sparse, with ascidians, sponges, hydroids, anemones, bryozoans, macroalgae and filamentous algae collectively accounting for less than 1% of the total mean cover in both the Darwin Harbour Inner and Darwin Offshore surveys. These results suggest that areas likely to be directly affected by dredging activities within the harbour and offshore spoil disposal do not provide any unique or significant habitat for subtidal soft sediment epifauna.

The Darwin Harbour Inner and Darwin Offshore infaunal assemblages sampled were diverse, including several types of crustaceans (amphipods, isopods, tanaids, cumaceans, penaeids, copepods, ostracods, shrimp, hermit crabs, ghost shrimp and brachyuran crabs), polychaete worms (from a variety of families), molluscs (gastropods, bivalves and opisthobranchs), echinoderms (ophiuroids, echinoids, holothurians and seastars) and other worm taxa such as nematodes, nemerteans, oligochaetes, phoronids, platyhelminthes and sipunculids. Other taxa recorded but identified to broader groups included anemones, bryozoans, hydrozoans, sponges, and pycnogonids (sea spiders). A total of 15,487 individual animals comprised of 155 taxa were recorded from the Darwin Harbour Inner survey and 10,295 individual animals comprised of 150 taxa recorded from the Darwin Offshore survey. Darwin Harbour Inner infaunal assemblages did not vary significantly among Control and Impact locations but did vary among sites. Darwin Offshore assemblages varied between Control and Impact locations and among sites within locations.

Darwin Harbour Inner sediments generally had higher proportions of clay and silt with varying proportions of sand and gravel. Darwin Offshore sediments consisted predominantly of sand and gravel with the exception of Control location 2, which contained high percentages of clay and silt. Sediment pH was relatively consistent, varying between 7.3 to 8.0 for Darwin Harbour Inner sites and 6.9 to 8.1 for Darwin Offshore

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sites. Mean ORP ranged between -200 mV to 322 mV, for Darwin Harbour Inner sites and -108 mV to 185 mV for Darwin Offshore sites, with strongly reducing conditions typically associated with clay and silty sediment types.

No clear relationships between any physical parameters investigated and the infaunal assemblages observed were evident, suggesting that other hydrographic, physico-chemical or biotic factors drive site and location level distribution patterns.

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Glossary

Term or Acronym Definition

Benthic Living on or in the seabed

Benthos The collection of organisms attached to or resting on the bottom sediments (i.e. epifauna) and those which burrow into the sediments (i.e. infauna)

Bioturbation The stirring or mixing of sediment or soil by organisms, especially by burrowing or boring

Bray-curtis dissimilarity matrices Matrices of dissimilarity between samples in the types and relative abundance of species/substrata type

COC Chain of Custody

CPCe Coral Point Count with Excel extensions

DSDMP Dredging and Spoil Disposal Management Plan – East Arm

Epifauna Animals that live on the surface of the seabed

Filter Feeder Animal which obtains its nutrtion by filtering suspended particles from the water column

GEP Gas Export Pipeline

GPS Global Positionining System

Infauna Aquatic animals living within the sediment

Intertidal The portion of shoreline between low and high tide marks, that is intermittently submerged

Invasive marine pest Organisms (usually transported by humans) which successfully establish themselves and then overcome otherwise intact, pre-existing native ecosystems

Macrofauna Organisms associated with sediment and retained in a sieve of 0.5 to 1.0 mm

Macrotidal Applied to coastal areas where the tidal range is in excess of 4 m. Tidal currents dominate the processes active in macrotidal areas

MOF Module Offloading Facility

Morpho-species A species distinguished from others only by its morphology

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Term or Acronym Definition

NATA National Association of Testing Authorities Australia

Non-Selective Deposit Feeder Animal which obtains its nutrition from the indescriminant ingestion of organic matter from fine sediments

NEMP Nearshore Environmental Monitoring Plan

ORP (mV) Oxidation Reduction Potential (ORP) is a measure of a water systems capacity to release or gain electrons in chemical reactions

PCoA, PCA Principle Coordinates Analysis; Principal Components Analysis

pH pH gives an indication of the acidity or alkalinity of a solution by its ability to gain or lose hydrogen ions

PSD Particle Size Distribution

SE Standard Error

Selective Deposit Feeder Animal which selects organic material from fine sediments prior to ingestion or which selects sediment of a particular size range for ingestion

SQL Search Query Language

Subtidal Waters below the low-tide mark

Taxon (plural taxa) The named taxonomic unit to which individuals, or sets of species, are assigned (e.g. genus, species, family etc.)

Turbidity Turbidity gives an indication of water clarity

WDL Waste Discharge Licence

ZoI Zone of Influence

ZoMI Zone of Moderate Impact

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Table of Contents Executive Summary iii

Glossary v

1 Introduction 1 1.1 Overview 1 1.2 Background 1 1.3 Aims and Objectives 2

2 Methodology 3 2.1 Sampling Locations 3

2.1.1 Darwin Harbour Inner 3 2.1.2 Darwin Offshore 3

2.2 Sampling Design 3 2.3 Field Methodology 7

2.3.1 Epibenthic Habitats 7 2.3.2 Benthic Infauna 7 2.3.3 Particle Size Distribution (PSD) 7 2.3.4 pH 7 2.3.5 Oxidation Reduction Potential 7

2.4 Laboratory Methodology 9 2.4.1 Epibenthic Habitats 9 2.4.2 Benthic Infauna 11 2.4.3 Particle Size Distribution (PSD) 11

2.5 Statistical and Analytical Methodology 11 2.5.1 General Findings 11 2.5.2 Multivariate Analyses 11 2.5.3 Univariate Analyses 12 2.5.4 Relating Physical and Biological Variables 12

2.6 Quality Control Procedures 12 2.6.1 Field 12 2.6.2 Laboratory 13 2.6.3 Data Processing 13

3 Results 14 3.1 Darwin Harbour Inner 14

3.1.1 Epibenthic Habitats 14 3.1.2 Infauna 16 3.1.3 Particle Size Distribution 22 3.1.4 pH and ORP 26 3.1.5 Relationship of Physical and Biological Variables 28

3.2 Darwin Offshore 29 3.2.1 Epibenthic Habitats 29 3.2.2 Infauna 31 3.2.3 Particle Size Distribution 39 3.2.4 pH and ORP 43 3.2.5 Relationship of Physical and Biological Variables 45

4 Discussion 46

5 Acknowledgements 48

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6 References 49

Tables Table 2-1 Design for the Subtidal Benthos Baseline Phase 4 Table 2-2 List of the categories and codes of fixed transects 10 Table 3-1 Sampling dates and locations for the subtidal benthos Baseline Phase 14 Table 3-2 Abundance and taxon richness of subtidal infauna assemblages collected from Darwin Harbour

Inner during the Baseline Phase, May 2012 to July 2012 16 Table 3-3 Percentage contribution, median grain size and sediment descriptions for Darwin Harbour Inner

locations 24 Table 3-4 Mean pH and ORP values for Darwin Harbour Inner locations (+/- SE) sampled during the

Baseline Phase, May 2012 to July 2012 26 Table 3-5 Abundance and taxon richness of subtidal infauna assemblages collected from Darwin Offshore

during the Baseline Phase, May 2012 to July 2012 31 Table 3-6 Percentage contribution, median grain size and sediment descriptions for Darwin Offshore

locations 41 Table 3-7 Mean pH and ORP values for Darwin Offshore locations (+/- SE) sampled during the Baseline

Phase, May 2012 to July 2012 43

Figures Darwin Harbour Inner sampling sites, including the Zones of Moderate Impact, Zones of Figure 2-1

Influence and Control locations 5 Darwin Offshore sampling locations, including sites in the spoil disposal area and Control Figure 2-2

locations 6 Images of: a) remote drop camera frame and housing; b) Ponar grab sampler; and c) pH and Figure 2-3

ORP measurement probes 8 Screenshot of the CPCe photoquadrat analyses frame with a virtual 64 point grid overlayed 9 Figure 2-4 Principle Coordinates Analyses (PCoA) of epibenthic assemblages sampled from Darwin Figure 3-1

Harbour Inner during the Baseline Phase, May 2012 to July 2012 15 Percentage contribution of abundance and taxa richness for major taxonomic groups collected Figure 3-2

from Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012 (n=5) 17 Photomicrographs of numerically abundant taxa identified from the Darwin Harbour Inner Figure 3-3

subtidal benthos Baseline Phase, May 2012 to July 2012 18 Photomicrographs of other representative taxa identified from the Darwin Harbour Inner Figure 3-4

Baseline Phase, May 2012 to July 2012 19 Mean abundance and mean taxon richness (+/- S.E.) for subtidal benthos samples collected Figure 3-5

from Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012 (n=5) 20 Principal Coordinates Analyses (PCoA) of subtidal infaunal assemblages sampled from Darwin Figure 3-6

Harbour Inner during the Baseline Phase, May 2012 to July 2012 21 Mean PSD of sediment samples collected from Darwin Harbour Inner during the Baseline Figure 3-7

Phase, May 2012 to July 2012 (n=2) 23 Mean pH (+/- SE) for Darwin Harbour Inner locations (n=7) 27 Figure 3-8 Mean ORP values for Darwin Harbour Inner locations (n=7) 27 Figure 3-9 dbRDA (distance based redundancy analysis) ordination of Darwin Harbour Inner infauna Figure 3-10assemblage data versus median grain size, pH and ORP for the Baseline Phase, May 2012 to July 2012 28

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Principal Coordinates Analyses (PCoA) of epibenthic assemblages sampled from Darwin Figure 3-11Offshore during the Baseline Phase, May 2012 to July 2012 30

Percentage contribution of abundance and taxon richness for major taxonomic groups collected Figure 3-12from Darwin Offshore during the Baseline Phase, May 2012 to July 2012 (n=5) 32

Photomicrographs of representative taxa identified from Darwin Offshore during the Baseline Figure 3-13Phase, May 2012 to July 2012 33

Mean abundance and mean taxon richness (+/- S.E.) for samples collected from Darwin Figure 3-14Offshore during the Baseline Phase, May 2012 to July 2012 (n=5). N.B. no data available for Control 1 (site 6) 34

Principal Coordinates Analyses (PCoA) of subtidal infaunal assemblages sampled from Darwin Figure 3-15Offshore during the Baseline Phase, May 2012 to July 2012 35

Mean abundance of families (Apseudidae, Aoridae/Isaeidae/Photidae) contributing to Figure 3-16approximately 5% or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012 36

Mean abundance of polychaete families (Ampeliscidae/Spionidae/Capitellidae) contributing to Figure 3-17approximately 5 % or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012 37

Mean abundance of polychaete families (Maldanidae and Ampharetidae) contributing to Figure 3-18approximately 5 % or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012 38

Particle Size Distribution of samples collected from Darwin Offshore during the Baseline Phase, Figure 3-19May 2012 to July 2012 (n=2) 40

Mean pH (+/- SE) for Darwin Offshore locations (n=7) (N.B. no data available for Control 1 (site Figure 3-206)) 44

Mean ORP (+/- SE) for Darwin Harbour Inner locations (n=7) (N.B. no data available for Control Figure 3-211 (site 6)) 44

dbRDA (distance based redundancy analysis) ordination of Darwin Offshore infauna Figure 3-22assemblage data versus median grain size, pH and ORP for the Baseline Phase, May 2012 to July 2012 45

Appendices

Appendix A: Field Data

Appendix B: CPCe Habitat Descriptions

Appendix C: CPCe Summary Data

Appendix D: CPCe Summary Graphs

Appendix E: PERMANOVA Results

Appendix F: Pair Wise Test Results

Appendix G: SIMPER Results

Appendix H: PERMDISP Results

Appendix I: Infauna Raw Data

Appendix J: PSD Raw Data

Appendix K: DIST LM Results

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1 Introduction

1.1 Overview

INPEX is the operator of the Ichthys Gas Field Development Project (the Project). The Project comprises the development of offshore production facilities at the Ichthys Field in the Browse Basin, some 820 km west-south-west of Darwin, an 889 km long subsea gas export pipeline (GEP) and an onshore processing facility and product loading jetty at Blaydin Point on Middle Arm Peninsula in Darwin Harbour. To support the nearshore infrastructure at Blaydin Point, dredging works will be carried out to extend safe shipping access from near East Arm Wharf to the new product loading facilities at Blaydin Point which will be supported by piles driven into the sediment. A trench will also be dredged to seat and protect the GEP for the Darwin Harbour portion of its total length. Dredged material will be disposed at the spoil ground located approximately 12 km north-west of Lee Point. A detailed description of the dredging and spoil disposal methodology is provided in Section 2 of the Dredging and Spoil Disposal Management Plan – East Arm (DSDMP) (INPEX 2012).

1.2 Background

The Baseline Phase monitoring program investigated benthic assemblages of infauna (aquatic animals that live within the soft sediments of the seabed) and epifauna (animals that live on the surface of the seabed), within the subtidal benthic habitats in Darwin Harbour and the nearshore coastal environment. The infaunal component focused on macrofauna which are classified as animals that are retained on a 0.5 mm mesh sieve. This group comprises the vast majority of biomass found in benthic soft sediments (Schwinghamer 1981). In tropical macrotidal estuaries such as Darwin Harbour, infaunal assemblages generally contain burrowing organisms such as polychaete worms, amphipod crustaceans, bivalve and gastropod molluscs and other worm-like phyla such as nemerteans and nematodes (which are often abundant). These animals are generally found within the upper 30 cm of the sediment. As well as being a source of food for organisms higher up the food chain, such as fish and large invertebrates, they also drive nutrient cycling through reworking of the sediments (bioturbation), altering physical and chemical processes, excreting nutrient-rich wastes and feeding on phytoplankton (Pennifold and Davis 2001). The activity of benthic assemblages in nearshore sediments is linked to pelagic processes and thus affects exchange processes between coastal and offshore systems (Eyre and Ferguson 2005; Connell and Gillanders 2007).

The composition of infaunal assemblages is expected to vary both annually and seasonally in relation to the intensity of the wet season and recruitment success (Metcalfe and Glasby 2008). Fluctuations may also occur at shorter time scales (e.g. days to weeks) due to diurnal activity patterns or migrations (Wildsmith et al. 2005). Infaunal assemblages also vary depending on sediment type (Brown and McLachlan 2006). Changes to sediment particle size distribution (PSD) or physico-chemical properties of the sediments are therefore likely to affect the composition of assemblages that are found there. Physical parameters measured as part of the Monitoring Program included sediment PSD, pH and Oxidation Reduction Potential (ORP), which are useful indicators of change, potentially related to dredging/spoil disposal activity.

Epifauna can generally be classed as either sessile (i.e. attached to the seabed) or mobile. Sessile organisms are often attached to hard structure such as reef or gravel, although some sponges, hydroids, ascidians, burrowing anemones and tube building polychaetes can also establish within soft sediments, although epifaunal biota found in association with soft sediments is comparatively sparse compared to that of hard bottom or coral reef substrata. Mobile epifauna associated with subtidal soft sediments often include echinoderms (e.g. seastars, echinoids and holothurians), gastropod molluscs, nemerteans and sipunculid worms among others.

Infaunal and epifaunal assemblages within Darwin Harbour Inner and the spoil disposal area have potential to be affected by dredging activities via three main mechanisms:

> Direct removal from within the dredge footprint;

> Direct smothering via placement of dredged material within the offshore spoil disposal area; and

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> Indirect changes to their habitat from the physical changes of the sediment (e.g. through re-suspension and deposition of finer sediment particles released during dredging and spoil disposal activities).

Dredging will remove most of the associated infaunal and epifaunal invertebrates occurring within the dredge footprint. Impacts on subtidal benthic assemblages are likely to be localised and relatively short-term, persisting until re-colonisation occurs. Dispersion of the sediment plume may also have affects beyond the vicinity of the dredge footprint by clogging of respiratory and feeding appendages.

Recolonisation of dredged areas by benthos is likely to occur relatively quickly, occurring within a few months of the cessation of dredging, due to the colonisation of opportunistic species (Sarda et al. 2000; van Dalfsen et al. 2000; Newell et al. 2004). Recovery of benthic assemblages to comparable pre-dredging conditions may, however, take much longer. The rate of recovery of infaunal assemblages will depend on local hydrodynamic conditions, the degree of changes in sediment composition caused by dredging (van Dalfsen et al. 2000) and the successful recruitment of larvae and immigration of mobile species. Recovery may result in assemblages that are quite different in structure from that originally present due to changes in sediment composition and changed water depth. As the material to be mobilised by dredging is not contaminated or vastly different in composition from that at the spoil disposal area, it is unlikely to prevent subsequent recolonisation of disturbed areas (URS 2009).

1.3 Aims and Objectives

The aim of the Baseline Phase is to collect baseline data within Darwin Harbour and offshore spoil ground on the soft-bottom benthos around the predicted Impact and Control locations prior to the start of any dredging and spoil disposal activities.

The objectives of the Subtidal Benthos Monitoring Program are to:

> Investigate the potential effects of dredging and dredge spoil disposal on the abundance and diversity of soft-bottom infauna and epifaunal communities;

> Determine whether there are significant changes in sediment characteristics (sediment grain size, ORP and pH) before dredging/spoil disposal compared to during and after and how this affects abundance and diversity of soft bottom communities; and

> Follow the subsequent recovery of any infauna and epifauna that may be impacted and relate this to depth of sedimentation, nature of sediment and ORP.

Specific objectives of the Baseline Phase are to:

> Assess the abundance and diversity of infauna and epifaunal assemblages;

> Sample seabed sediment to determine PSD in the predicted Impact and Control locations;

> Assess the ORP and pH of the sediments; and

> Investigate the relationship between the physico-chemical characteristics of the sediment (ORP and pH) and the composition of infaunal and epibenthic assemblages.

This report outlines the findings of the Subtidal Benthos Monitoring Program undertaken during the baseline (pre-dredging phase) as per the methodology outlined in the NEMP (Cardno 2012a). The report includes results and analyses of sampling that has been carried out to date, an outline of the methods and Quality Control (QC) procedures that were adopted and a discussion of the outcomes of the Baseline Phase. The Baseline Phase monitoring was carried out during the Darwin dry season in four consecutive trips over neap tide cycles between 30 May 2012 and 17 July 2012.

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2 Methodology

2.1 Sampling Locations

2.1.1 Darwin Harbour Inner

Sampling locations within Darwin Harbour (hereafter referred to as Darwin Harbour Inner sampling locations) were selected on the basis of the dredging areas and predicted areas for sediment deposition and turbidity plumes indicated within Section 6.5 of the DSDMP. The sampling design included four locations (ZoMI, ZoI, Control 1 and Control 2), with six sites randomly selected within each location, yielding a total of 24 sites (Figure 2-1). Habitat maps provided in the DSDMP were used to identify sites with similar sediment characteristics.

2.1.2 Darwin Offshore

Darwin Offshore sampling locations were selected to investigate the impacts of the spoil disposal area located approximately 12 km northwest of Lee Point (Figure 2-2). Previous surveys have described the spoil disposal area as a flat seabed with depths ranging from 15 m in the south-west end to 20 m in the northeast end, comprised of a relatively featureless seafloor with sand/silt and very sparse epibenthic fauna (URS 2009).

In additional to the spoil disposal area, two sampling locations were included to the east of the spoil disposal area: Zone of Impact (Near) and Zone of Impact (Far). Based on model predictions, these are located in the zone of sediment suspension and deposition from the dredge spoil disposal area.

Two Control locations (Control 1 and Control 2) were situated approximately 20 km west of the spoil ground and away from the proposed pipeline location, north-west of Charles Point, following a similar 10 m to 14 m depth contour as the Impact locations (Figure 2-2). These locations were chosen as they were expected to have similar depth and bottom type to that previously observed at the spoil disposal area. Six sites within each location were selected at random within each location.

Locations for the Darwin Offshore survey were similar in size as the dredge spoil disposal area (i.e. 5 km x 2.5 km). Sites within locations were also standardised to an area of ~200 m x 200 m.

2.2 Sampling Design

The proposed sampling design is consistent with the ‘beyond BACI’ (Before, After, Control, Impact) sampling approach, which makes use of multiple controls in space and time (Underwood 1991, 1992; Long et al. 1996). This allows changes at a potential impact location to be evaluated against variation measured at multiple control locations. The design requires that sampling be carried out in at least two external control locations in addition to the potential impact locations. Monitoring was undertaken at Darwin Harbour Inner and Darwin Offshore sampling locations in relation to the dredge area and spoil disposal areas. As the Baseline Phase survey was carried out during the Darwin dry season (May to October), further surveys during and after dredging will be carried out at the same time of year to allow comparison.

The monitoring program would be conducted in four phases:

> Phase 1: Baseline sampling;

> Phase 2: During dredging (the most intensive phase);

> Phase 3: Post dredging (at the end of dredging); and

> Phase 4: Post dredging (one year post-dredging).

The sampling design for each area is outlined below (Table 2-1).

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Table 2-1 Design for the Subtidal Benthos Baseline Phase

Area Locations Sites Transects Replicates Total Samples (per survey)

Dredge Area Infauna

x 4 Zone of Moderate Impact Zone of Influence Control 1 Control 2

x 6 within each location, resulting in a total of 24 sites

N/A

x 5 benthic samples and x 2 PSD samples per site

120 benthic samples 48 PSD samples

Dredge Area Epifauna

x 4 Zone of Moderate Impact Zone of Influence Control 1 Control 2

x 6 within each location, resulting in a total of 24 sites

x 2 per site (A and B)

x 15 photoquadrats per transect

720 samples

Dredge Spoil Disposal Area Infauna

x 5 Spoil disposal area, Zone of Influence (Near) Zone of Influence (Far) Control 1 Control 2

x 6 sites per location; N/A

x 5 benthos samples x 2 PSD samples per site

150 benthos samples 60 PSD samples

Dredge Spoil Disposal Area Epifauna

x 5 Spoil disposal area, Zone of Influence (Near) Zone of Influence (Far) Control 1 Control 2

x 6 per location

x 2 per site (A and B)

x 15 photoquadrats per transect

900 samples

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Darwin Harbour Inner sampling sites, including the Zones of Moderate Impact, Zones of Influence and Control locations Figure 2-1

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Darwin Offshore sampling locations, including sites in the spoil disposal area and Control locations Figure 2-2

1= Spoil Disposal Area, 2= Zone of Impact (Near), 3= Zone of Impact (Far)

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2.3 Field Methodology

2.3.1 Epibenthic Habitats

Epifauna was photographed using a high-definition underwater video drop camera and frame (Figure 2-3). The drop camera yields high quality photographs in low light and low visibility conditions and produces images suitable for photoquadrat analysis. The drop camera consisted of a Sony HDR- CX700 (1080i) digital video camera, fitted with a 0.6 wide angle conversion lens video camera, pointing downwards, mounted within a watertight housing and frame and deployed from the survey vessel. The camera automatically adjusts focus and exposure to suit conditions on the seafloor. The frame was built from solid aluminium and consisted of four padded legs and a cradle to hold and secure the housed video camera. The unit was deployed with 1.35 kg of lead weight attached to each leg as ballast to provide stability in surge or current. A length of silver rope was attached to each corner of the frame for deployment and retrieval of the unit. The camera was lowered to the seabed at the start of each transect and raised and lowered to approximately 50 cm above the substratum as the vessel drifted with the current (between 0.5 and 1 km/hr) until the end of the transect. The camera sat approximately 50 cm above the seabed providing a quadrat size of ~ 40 cm x 65 cm. Fifteen replicate quadrats were taken per transect. Darwin Harbour Inner transects were approximately 50 m in length and Darwin Offshore transects approximately 100 m in length. Upon completion of each transect (A and B) at a site, the video camera was retrieved and video footage was downloaded onto a laptop computer and external hard drive as a back-up.

GPS positions of each site were recorded so the exact same positions could be revisited in future surveys. Vessel movements throughout the course of the day were also tracked and downloaded.

2.3.2 Benthic Infauna

Sediment samples to be analysed for benthic infauna, PSD, pH and ORP were collected using a stainless steel Ponar benthic grab deployed by winch to the seabed at each site. The Ponar grab can collect up to 4.5 L of sediment, with a bite depth of 90 mm and was fitted with stainless steel mesh flaps to retain surface biota greater than 0.5 mm in size. Sample volume, water depth, time and GPS position of each grab sample were recorded. Infauna samples were sieved on board the vessel through a 0.5 mm mesh sieve, with retained sediment and biota transferred to a labelled bag. The sieve was examined after removal of retained sediment and any animals trapped in the mesh added to the sample, rinsing with water to avoid any cross-contamination. The sample was then preserved on board the vessel in a solution of 40% formalin and seawater with Rose Bengal dye. Formalin stored on board the vessel was bunded within a plastic container to ensure no leakage onto the deck. Sample bags were labelled internally and externally with project details, time, date, location, site and replicate number and placed in a sealed labelled poly-drum.

2.3.3 Particle Size Distribution (PSD)

Sediment samples collected for PSD analysis were sealed into labelled bags and placed in a cooler to be stored below 4°C until transfer to a freezer on land. They were later dispatched to a National Association of Testing Authorities (NATA) accredited laboratory (ALS Laboratories Darwin), accompanied by a Chain of Custody (COC) document for external laboratory analyses.

2.3.4 pH

Immediately after sample collection and prior to sieving, pH measurements were recorded using an Oakton Instruments waterproof pH tester pen (Figure 2-3). The probe was inserted 4 to 5 cm into the sediment sample and left until the value on the instrument remained stable. Values were recorded on the field data sheet. Tester pens were calibrated prior to each field trip and rinsed in a bucket of fresh water between measurements.

2.3.5 Oxidation Reduction Potential

Immediately after sample collection and prior to sieving, ORP measurements were recorded using an Oakton Instruments waterproof ORP tester pen (Figure 2-3). The probe was inserted 4 to 5 cm into the sediment sample and left until the value on the instrument remained stable or after 30 seconds (whichever was sooner). Measurements were then recorded on the field data sheet. Tester pens were calibrated prior to each field trip and rinsed in a bucket of fresh water between measurements.

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Images of: a) remote drop camera frame and housing; b) Ponar grab sampler; and c) pH Figure 2-3

and ORP measurement probes

a)

b) c)

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2.4 Laboratory Methodology

2.4.1 Epibenthic Habitats

Still images of each camera drop were captured using VLC Media Player. Each captured still was colour corrected using Adobe Photoshop to allow for better quality images and aid in the processing of photoquadrats. Each video transect was reviewed and a general habitat description recorded. Photoquadrats were processed using the Coral Point Count with Excel extensions (CPCe) program (Kohler and Gill 2006). The analysis involved digitally overlaying a virtual photoquadrat (scaled to approximately 40 cm x 65 cm) with 64 points in a random stratified grid on each captured video frame (Figure 2-4). Each point was then assigned a category as indicated in Table 2-2. This provided an estimate of the percentage cover of each habitat category (including biotic and abiotic categories).

Screenshot of the CPCe photoquadrat analyses frame with a virtual 64 point grid Figure 2-4

overlayed

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Table 2-2 List of the categories and codes of fixed transects

Category Sub Category Code

CNIDARIA

Anemone (AMNE)

Hard Coral (HD COR)

Hydroid (HYD)

Sea Fan (SEA FN)

Sea Whip (SEA WP)

ALGAE

Algal Mat on Sand (ALG MAT)

Filamentous Algae (ALG FIL)

Macroalgae (ALG MAC)

Wrack (ALG WRCK)

SUBSTRATUM

Burrow (BRW)

Gravel (GVL)

Organic Debris (ORG)

Rubble (RUB)

Sand (SND)

Shell Grit (SHL GRT)

Bioturbated Sand (Spare Category 3) (SC3)

Algal Mat on Shell Grit (Spare Category 4) (SC4)

SPONGE

Sponge (SPNG)

ECHINODERM

Echinoid (ECND)

Ophiuroid (OPHI)

MOLLUSC

Bivalve (BIV)

Gastropod (GAST)

BRYOZOAN

Bryozoan (BRYZ)

ASCIDIAN

Ascidian (ASCI)

QUALITY

Poor Quality (PR QUAL)

OTHER

Soft Coral (Other 1) (OTHR 1)

Worm like Phyla (Other Biota) OTHER

INDETERMINATE

Indeterminate (IND)

FISH MOBILE

Fish Mobile FSH MOB

TAPE, WAND, SHADOW

Shadow (SHAD)

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2.4.2 Benthic Infauna

Samples for analyses of infaunal assemblages were sent via road freight to Cardno’s in-house laboratory. Excess formalin in samples was initially drained from each sample over a 0.5 mm mesh sieve and appropriately disposed of. Samples were then rinsed under tap water and transferred to an alcohol solution for preservation and further processing. Large sandy samples (greater than 0.5 L) were elutriated to separate animals from the substrate and improve sorting efficiency. The coarse fraction settled out from the elutriation was then sorted in a tray to remove any larger invertebrates (such as bivalves) which may have not been extracted during the elutriation. Animals were then removed from the sediment and elutriate fractions under a binocular microscope using forceps and stored according to their taxonomic group with the Project details and sample information. Animals were identified to Family level with each taxon separated into an individually labelled vial. For groups where further identification would require a large expenditure of time (e.g. oligochaetes and nematodes) or where taxonomic status in Australia was insufficient to achieve a finer level of identification (e.g. anemones), identification was to a lower resolution such as Class or Sub Order.

2.4.3 Particle Size Distribution (PSD)

Samples collected for analysis of PSD were dispatched to ALS Laboratories, Darwin, a NATA accredited laboratory, accompanied with COC documentation. The distribution of particles sizes greater than 0.001 mm and median grain size were determined using the dry sieve (AS 1289.3.6.1) and hydrometer (AS1289.3.6.3) methods.

2.5 Statistical and Analytical Methodology

2.5.1 General Findings

General findings for infaunal assemblages are presented as total numbers of individuals and total number of taxa (taxon richness) occurring among sampling sites. General findings for physical parameters (PSD, pH and ORP) are presented as averages and standard errors (SE) of the mean for all sampling sites.

2.5.2 Multivariate Analyses

Statistical analysis of infauna data was done using PERMANOVA+ (based on Bray-Curtis dissimilarity matrices) in PRIMER v6. This is a permutational approach to analysis of variance (ANOVA) that is superior to traditional methods (Anderson et al. 2008) in that there is no assumption of normality in the data and designs can be unbalanced (e.g. different numbers of replicate samples at different places or times) if necessary. The approach yields exact tests for each level of an experimental design and is robust to differences among variances. Post–hoc permutational t-tests or ‘pair-wise’ tests using PERMANOVA+ were performed to examine significant interactions of main effects. Prior to analyses, any samples with greater than 50% poor quality/shadow or indeterminate categories were removed.

As transformation of data to achieve normality was unnecessary, abundance data were not transformed. In order to help discriminate between groups of interest (in this case locations/treatments and sites), multivariate data were represented graphically using Principle Coordinates Analysis (PCoA), a generalised form of Principal Components Analysis (PCA), which complements the permutational ANOVA procedure (Anderson et al. 2008). Samples were projected onto linear axes based on their dissimilarities in a way that best describes the patterns among them using as few dimensions as possible (Clarke and Gorley 2006).

Similarity Percentage Analysis (SIMPER) was used to identify those taxa, or groups of taxa contributing most to dissimilarities between assemblages where appropriate.

Differences in the dispersion of data between surveys were examined using the PERMDISP routine in PERMANOVA+. This routine was used to separate the effects of differences in dispersion of points within clusters from differences in the relative positions of the clusters (Anderson et al. 2008).

The design for the statistical analyses for each component of the baseline survey was as follows:

1. Darwin Harbour Inner Drop Camera

> Location: 4 levels (ZoMI, ZoI, Control 1, Control 2), fixed;

> Sites: 24 levels, random, nested in treatment;

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> Transects: 2 levels (A and B), random, nested in site; and

> Replicates: x 15.

2. Darwin Harbour Inner Grab Sampling

The design for the statistical analyses (Darwin Offshore) was:

> Location: 4 levels (ZoMI, ZoI, Control 1, Control 2), fixed;

> Sites: 24 levels, random, nested in treatment; and

> Replicates: x 5.

3. Darwin Offshore Drop Camera

> Location: 5 levels (spoil disposal area, Zone of Impact (Near), Zone of Impact (Far), Control 1, Control 2), fixed;

> Sites: 6 levels (sites 1 -6), random, nested in treatment;

> Transects: 2 levels (A and B), random, nested in site; and

> Replicates: x 15.

4. Darwin Offshore Grab Sampling

> Location: 5 levels (spoil disposal area, Zone of Impact (Near), Zone of Impact (Far), Control 1, Control 2), fixed;

> Sites: 6 levels (sites 1 - 6), random, nested in treatment; and

> Replicates: x 5.

2.5.3 Univariate Analyses

Where appropriate, univariate analyses were done to investigate differences in taxon richness, taxon abundance and individual taxa contributing the most to the spatial and temporal variability among samples. PERMANOVA+ (based on Euclidian distance) was used to perform permutational analyses of variance as this approach does not require that the data come from a normal distribution or that variances are homogeneous, as is the case with traditional ANOVA. After calculating a Euclidean distance matrix of all possible pairs of samples of the variable of interest, the underlying distribution of the data was determined by repeated randomisation of the samples in the matrix, enabling exact tests for all levels of the experimental design (Anderson et al. 2008).

2.5.4 Relating Physical and Biological Variables

To examine the relationship between the physical variables of PSD, pH and ORP with the biotic data, a sub-program within the PRIMER package called Distance Based Linear Models (DIST-LM) was used. DIST-LM models the relationship between a multivariate data cloud (as described by a resemblance matrix) and one or more predictor variables that were measured from the same set of samples. P-values for testing the null hypothesis of no relationship are obtained using permutation methods rather than traditional tables.

2.6 Quality Control Procedures

2.6.1 Field

As per the requirements of INPEX’s Waste Discharge Licence (WDL) and EPA 8 permit conditions on reporting, for all replicate samples collected, a unique sample code, a record of the GPS position, time, date, depth, name of the sampler, sediment type and weather conditions were recorded on waterproof field sheets. All data were then transcribed into the master project database linked to each unique sample code. GPS positions were downloaded into excel format then imported into the master database. A photographic record was also archived for each PSD grab sample collected. Sediment samples were transferred into polyurethane bags and labelled internally and on the outside of the bag. Hard copies of all original datasheets were scanned and stored electronically within the master database.

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COC documentation accompanied all consignments of samples being transported from one party to another. Field quality assurance included the collection and analysis of a duplicate sample at a randomly selected site. External laboratory quality assurance included the use of blind replicate environmental samples.

2.6.2 Laboratory

All samples were logged upon receipt from the field on a laboratory management sheet. In the laboratory, a sample sign-in/sign out system was used to track sample status and time required to process each sample. For each sample, the sediment remaining after removal of all biota was checked by a second experienced person to recover any missed organisms. Verification of identifications and counts were completed by a second experienced scientist on all samples. A voucher collection was retained for future comparison and identification. External laboratory quality assurance included the use of blind replicate environmental samples.

2.6.3 Data Processing

Personnel involved in sampling photographs using CPCe were required to demonstrate proficiency before being authorised to begin sampling of photoquadrats. Proficiency was acquired through training by an experienced scorer available to assist CPCe analysts full time throughout processing. All photos were checked by a senior staff member for consistency and accuracy. Once these checks were completed, the Scope Leader or Data Manager approved the images for release within Vault for exporting to the SQL database. Before exporting data to Excel, the CPCe files were examined to ensure that all the points of each quadrat (i.e. 64 points) were scored and check that there was a CPCe file (‘.cpc’) for every photograph allocated. If a file was missing, it was analysed prior to the CPCe data being exported to the SQL database.

Prior to use in statistical analyses, data files were locked to avoid corruption or accidental over-write. The video analysis and all field data was error checked before undertaking further analysis or presentation using a two-scientist, digital and hard copy procedure. This involved one person entering the data and two scientists then checking the digital and hardcopies against each other.

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3 Results

Sampling dates, times and locations for the subtidal benthos Baseline Phase survey are presented in Table

3-1. Field notes and GPS positions of all sampling points are presented in Appendix A.

Table 3-1 Sampling dates and locations for the subtidal benthos Baseline Phase

Field Trip Sampling Dates Sampling Method Location

1a 30 May 2012 – 1 June 2012 Drop Camera Darwin Harbour Inner

1b 13 June 2012 – 16 June 2012 Grab Sampling Darwin Harbour Inner

1c 27 June 2012 – 1 July 2012 Drop Camera Darwin Offshore

1d 12 July 2012 – 17 July 2012 Grab Sampling/Drop Camera Darwin Offshore

*No data were retrieved with the grab sampler for site 6 within Control location 1 (Darwin Offshore). This was due to coarse sediment type and hard (reef) substratum, which was unsuitable for sampling with a benthic grab

3.1 Darwin Harbour Inner

3.1.1 Epibenthic Habitats

3.1.1.1 General findings

General habitat descriptions for each site are provided in Appendix B. Video stills representative of the epibenthic environment have also been provided to assist in the interpretation of habitat descriptions. In general, seabed consisted of relatively flat bare, bioturbated fine sand with silty clay and coarser sand/shell grit. Epifauna was minimal, limited to the rare occurrence of bryozoans, hydroids and sea whips. CPCe summary data for each transect (A and B) within sites 1-24 are presented in Appendix C. Overall, sand (including fine sand and silt) was the most abundant category across the Darwin Harbour Inner survey, accounting for approximately 70% of mean coverage. Shell grit accounted for 9.6% of cover followed by algal mat on sand (5.4%), bioturbated sand (2.5%) and burrows (1.3%). The overall percentage cover of epifauna was very sparse, with ascidians, sponges, hydroids, anemones, bryozoans, macroalgae and filamentous algae collectively accounting for less than 1% of the total cover sampled. The remaining coverage (approximately 10%) was either indeterminate, obscured by shadow or visibility was too poor to accurately assign a data point. The greatest percentage cover of epifauna was recorded at sites 2, 11, 18, 16 and 19. The percentage contribution of each category for each site is presented graphically in Appendix

D.

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3.1.1.2 Analyses of Assemblages

Epifaunal assemblages varied at the scale of locations (several kilometres), sites (hundreds of metres) and transects (metres) within Darwin Harbour. Percentage cover of epibenthic categories sampled from the ZoMI, ZoI, Control 1 and Control 2 varied significantly (Appendix E), with pairwise tests indicating that this was due to Control location 1 being significantly different in composition from all other locations (Appendix

F). This is illustrated in the PCoA plot (Figure 3-1), which shows that 84% of the total variation can be explained by differences among samples. SIMPER analyses indicated that differences between Control location 1 and other locations were due to a smaller percentage cover of sand and greater percentage cover of shell grit (Appendix G) at Control location 1. Samples from Control location 1 were also more variable than at other locations as indicated from the results of the pairwise PERMDISP analyses (Appendix H). When biotic categories were analysed separately from the abiotic categories, the epibenthic assemblages were found to differ at the level of sites but not among locations (Appendix E).

Principle Coordinates Analyses (PCoA) of epibenthic assemblages sampled from Darwin Figure 3-1

Harbour Inner during the Baseline Phase, May 2012 to July 2012

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3.1.2 Infauna

3.1.2.1 General Findings

A total of 15,487 individual animals comprised of 155 taxa were recorded from the Darwin Harbour Inner subtidal benthos survey. A diverse range of taxa were collected, including numerous types of crustaceans (amphipods, isopods, tanaids, cumaceans, penaeids, copepods, ostracods, shrimp, hermit crabs, ghost shrimp and brachyuran crabs), polychaete worms (from a variety of families and feeding guilds), molluscs (gastropods, bivalves and opisthobranchs), echinoderms (ophiuroids, echinoids, holothurians and seastars) and other worm taxa such as nematodes, nemerteans, oligochaetes, phoronids, platyhelminthes and sipunculids. Other taxa recorded but identified to broader groups included anemones, bryozoans, hydrozoans, sponges, pycnogonids (sea spiders) and juvenile fish. Raw sample data are presented in Appendix I.

Crustaceans were the most numerically abundant of the major taxonomic groups, followed by polychaetes, other worm phyla (e.g. nemerteans, nematodes, phoronids and sipunculids), molluscs, other phyla and echinoderms. Crustaceans were also the most diverse in terms of taxon richness followed by polychaete worms, molluscs, other phyla, other worm phyla and echinoderms (Table 3-2, Figure 3-2).

The most numerically abundant taxa throughout the Darwin Harbour Inner survey were tanaid crustaceans from the family Apseudidae (contributing to 17.3% of the total abundance), followed by amphipod crustaceans from the family group Aoridae/Isaeidae and Photidae (12%), polychaete worms from the families Spionidae (5.8%), Ampharetidae (5.4%) and Capitellidae (2.9%), nematodes (2.8%), nemerteans (2.8%), and polychaetes from the families Maldanidae (2.7%), Cirratulidae (2.0%) and Syllidae (1.9 %) (Figure 3-3). Representative taxa from other phyla and family groups are presented in Figure 3-4.

Mean abundance and taxon richness did not vary significantly among locations (ZoMI, ZoI, Control 1 and Control 2) but did vary among sites within locations. Abundance was greatest at site 6 (within East Arm) and lowest at sites 8 (main channel), 18 (main channel) and 24 (West Arm). Taxon richness was greatest at sites 1, 13 and 15 (all within the main channel) and lowest at site 3 (within the proposed dredge footprint), site 8 (main channel) and Site 24 (West Arm) (Figure 3-5).

Table 3-2 Abundance and taxon richness of subtidal infauna assemblages collected from Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012

Major Taxonomic Group Total Abundance Taxon Richness

Polychaeta 6,152 42

Crustacea 6,805 60

Mollusca 977 33

Echinodermata 232 4

Other Worm Phyla 1,040 7

Other Phlya 281 9

Baseline Phase Total 15,487 155

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Percentage contribution of abundance and taxa richness for major taxonomic groups Figure 3-2

collected from Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012 (n=5)

Total Abundance (Darwin Harbour Inner)

Total Taxa (Darwin Harbour Inner)

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Photomicrographs of numerically abundant taxa identified from the Darwin Harbour Inner Figure 3-3subtidal benthos Baseline Phase, May 2012 to July 2012

Crustaceans: a) Apseudidae b) Aoridae; Polychaetes: c) Spionidae; d) Ampharetidae;

e) Capitellidae; Worm Phyla: f) Nematode; g) Nemertean and Polychaete: h) Maldanidae

a) b)

c) d)

e) f)

g) h)

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Photomicrographs of other representative taxa identified from the Darwin Harbour Inner Figure 3-4Baseline Phase, May 2012 to July 2012 Crustaceans: a) Cumacean (Bododridae); b) Caprellidae; c) Ampeliscidae; Polychaete: d) Cirratulidae; Molluscs: e) Nuculanidae; f) Iravadiidae; Echinoderms: g) Echinoid; and h) Ophiuroid

a) b)

c) d)

e) f)

g) h)

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Mean abundance and mean taxon richness (+/- S.E.) for subtidal benthos samples collected from Darwin Harbour Inner during the Figure 3-5

Baseline Phase, May 2012 to July 2012 (n=5)

Mean Abundance (Darwin Harbour Inner)

Mean Taxon Richness (Darwin Harbour Inner)

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3.1.2.2 Analyses of Assemblages

Infaunal assemblages did not vary significantly among locations, but did vary among sites within locations (Appendix E) as shown by pairwise tests (Appendix F). This is illustrated in the PCoA plot (Figure 3-6), although this shows that only 25% of the total variation can be explained by differences among samples represented by the two axes. Various taxa including polychaetes, tanaids, amphipods, bivalves and anemones were responsible for significant variation among sites as indicated in the results of the SIMPER analyses.

Principal Coordinates Analyses (PCoA) of subtidal infaunal assemblages sampled from Figure 3-6Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012

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3.1.3 Particle Size Distribution

Sediment samples collected from Darwin Harbour contained sand with varying proportions of clay, silt and gravel. Sites located to the far west of Darwin Harbour Inner had a high clay and silt content, whereas samples collected from the central channel tended to contain higher proportions of gravel than elsewhere. Samples collected from within the East Arm were mostly sandy with smaller proportions of clay and silt (Figure 3-7). Mean particle size data are summarised in (Table 3-3). Raw PSD data for Darwin Harbour Inner sampling sites are presented in Appendix J.

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Mean PSD of sediment samples collected from Darwin Harbour Inner during the Baseline Phase, May 2012 to July 2012 (n=2)Figure 3-7

Subtidal

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Table 3-3 Percentage contribution, median grain size and sediment descriptions for Darwin Harbour Inner locations

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 19.5 25.5 3.5 9.5 13.5 25.0 Silt (2-60 µm) 28.0 29.5 0.0 19.0 10.0 28.5 Sand (0.06-2.00 mm) 36.0 40.0 90.5 30.5 75.0 44.0 Gravel (>2mm) 16.5 5.0 6.0 41.0 1.5 2.5Median Grain Size (mm) 0.070 0.058 0.188 1.180 0.150 0.064

Sediment DescriptionSilty clay, medium fine

sand and shellSilty clay and medium

fine sand SandSand/Shell, sand and

silty clay Sand and silty clayMedium fine sand and

silty clay

Zone of Moderate Impact

LocationSite 7 8 9 10 11 12

Clay (<2 µm) 9.0 1.5 12.0 18.5 8.5 13.5 Silt (2-60 µm) 8.5 0.5 8.5 18.5 3.5 15.5 Sand (0.06-2.00 mm) 82.5 67.5 60.5 61.5 75.0 56.0 Gravel (>2mm) 0.0 30.5 19.0 1.5 13.0 15.0Median Grain Size (mm) 0.075 0.890 0.225 0.075 0.300 0.075

Sediment DescriptionMedium fine sand and

silty clayMedium coarse sand

and shellSand, shell and silty

clay Sand and silty clayMedium coarse sand

and shellSand, silty clay and

shell

Zone of Influence

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LocationSite 13 14 15 16 17 18

Clay (<2 µm) 20.5 10.0 9.0 12.0 8.5 9.5 Silt (2-60 µm) 18.5 4.5 15.0 8.5 17.5 7.0 Sand (0.06-2.00 mm) 45.0 81.5 26.5 63.0 34.0 61.5 Gravel (>2mm) 16.0 4.0 49.5 16.5 40.0 22.0Median Grain Size (mm) 0.113 0.288 1.770 0.394 0.745 0.150

Sediment DescriptionSand, silty clay and

shell

Sand and silty clay/Medium coarse

sand

Shell, sand and silty clay

Sand, silty clay and shell

Sand, shell and silty clay

Sand, shell and silty clay

Control 1

LocationSite 19 20 21 22 23 24

Clay (<2 µm) 11.5 35.5 33.5 13.5 38.0 41.0 Silt (2-60 µm) 11.5 31.0 27.5 6.5 30.0 36.5 Sand (0.06-2.00 mm) 53.0 33.5 39.0 78.0 32.0 22.5 Gravel (>2mm) 24.0 0.0 0.0 2.0 0.0 0.0Median Grain Size (mm) 0.438 0.043 0.052 0.188 0.037 0.008

Sediment DescriptionSand, shell and silty

clay Silty clay and fine sand Silty clay and fine sand Sand and silty clay Silty clay and fine sand Silty clay and fine sand

Control 2

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3.1.4 pH and ORP

Mean pH and ORP values for Darwin Harbour Inner locations are presented in Table 3-4, Figure 3-8 and

Figure 3-9. pH values ranged between 7.3 at site 7 to 8.0 at site 6. ORP values ranged from -200 mV at site 12 to 322 mV at site 1.

Table 3-4 Mean pH and ORP values for Darwin Harbour Inner locations (+/- SE) sampled during the Baseline Phase, May 2012 to July 2012

pH -log [H+] ORP (mV)

Treatment Site Mean S.E Mean S.E

Zone of Moderate Impact

1 7.50 0.01 147 104.0

2 7.72 0.06 -150 15.3

3 7.95 0.02 128 1.9

4 7.64 0.03 -67 28.3

5 7.67 0.02 13 11.3

6 7.65 0.02 -110 20.7

Zone of Influence

7 7.44 0.10 75 3.3

8 8.06 0.01 53 1.6

9 7.66 0.04 2 21.2

10 7.64 0.03 -131 16.1

11 7.75 0.03 -60 27.9

12 7.61 0.03 -177 11.1

Control 1

13 7.64 0.05 -144 19.0

14 7.69 0.06 -79 34.4

15 7.57 0.04 -135 15.1

16 7.72 0.05 -133 26.3

17 7.75 0.08 -98 23.4

18 7.86 0.07 -61 41.8

Control 2

19 7.53 0.02 1 11.4

20 7.50 0.11 -90 9.8

21 7.35 0.00 -18 14.7

22 7.71 0.06 36 23.3

23 7.59 0.07 -49 17.0

24 7.38 0.07 -121 14.4

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Mean pH (+/- SE) for Darwin Harbour Inner locations (n=7) Figure 3-8

Mean ORP values for Darwin Harbour Inner locations (n=7) Figure 3-9

6.80

7.00

7.20

7.40

7.60

7.80

8.00

8.20

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24

pH

-lo

g[H

+]

Site

pH -log [H+]

-250-200-150-100

-500

50100150200250300

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24OR

P (

mV

)

Site

ORP (mV)

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3.1.5 Relationship of Physical and Biological Variables

Examination of the distance based linear model indicated that very little of the variation of the Darwin Harbour Inner infaunal assemblage could be attributed to the physical variables measured (median grain size, pH and ORP). Cumulatively these variables explained less than 10% of the total variation (R2 for each individual variable against the infaunal data cloud = <0.04). This is illustrated in the distance based redundancy analyses ordination (dbRDA) (Figure 3-10). Statistical results are presented in Appendix K.

dbRDA (distance based redundancy analysis) ordination of Darwin Harbour Inner infauna Figure 3-10assemblage data versus median grain size, pH and ORP for the Baseline Phase, May 2012 to July 2012

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3.2 Darwin Offshore

3.2.1 Epibenthic Habitats

3.2.1.1 General findings

General habitat descriptions are provided in Appendix B. Video stills representative of the epibenthic environment have also been provided to assist in the interpretation of habitat descriptions. In general, seabed consisted of relatively flat, bare, bioturbated fine sand with silty clay and coarser sand/shell grit. Epifauna was limited to the occasional occurrence of sponges, bryozoans, hydroids, macroalgae and sea whips. Hard coral fragments were also present, but rare within the spoil disposal area and at Control location 1.

CPCe summary data for each transect (A and B) within the Darwin Offshore monitoring locations is presented in Appendix C. Overall, sand (including fine sand and silt) was the most abundant category across the Darwin Offshore survey accounting for approximately 71% of mean coverage. Shell grit accounted for 4% of cover followed by bioturbated sand (2%), algal mat (1.1%) and rubble (0.6%). The overall percentage cover of epifauna was very sparse, with ascidians, sponges, hydroids, anemones, bryozoans, macroalgae and filamentous algae collectively accounting for less than 1% of the total mean cover. The remaining coverage (approximately 20%) was either indeterminate, obscured by shadow or visibility was too poor to accurately assign a data point. The greatest percentage cover of epifauna was recorded at the Zone of Impact (Far) (sites 3 and 1), followed by Control location 1 (sites 3 and 4). The percentage contribution of each category for each location and site is presented graphically in Appendix D.

3.2.1.2 Analyses of Assemblages

In Darwin Offshore, epifaunal assemblages varied at the scale of locations (several kilometres), sites (hundreds of metres) and transects (metres). Percentage cover of epibenthic categories sampled from the Spoil Disposal Area, Zone of Impact (Near), Zone of Impact (Far), Control location 1 and Control location 2 varied significantly (Appendix E). Pairwise tests indicated that this was due to significant differences between the Spoil Disposal Area and Zone of Impact (Far)/Control location 1, and differences between Control locations 1 and 2 and the Zone of Impact (Near) and Zone of Impact (Far) (Appendix F). This is illustrated in the PCoA plot (Figure 3-11) which shows that 64% of the total variation can be explained by differences among samples. SIMPER analyses indicated that differences among locations were mainly due to varying percentages of sand, shell grit, bioturbated sand, rubble and to a much lesser extent, sponge (Appendix G). Samples from within the Spoil Disposal Area and Zone of Impact (Near) were generally less variable than at other locations as indicated from the results of the pair-wise PERMDISP analyses (Appendix H).

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Principal Coordinates Analyses (PCoA) of epibenthic assemblages sampled from Darwin Figure 3-11Offshore during the Baseline Phase, May 2012 to July 2012

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3.2.2 Infauna

3.2.2.1 General Findings

A total of 10,295 individual animals comprised of 150 taxa were recorded from the Darwin Offshore subtidal survey. A diverse range of taxa similar to that recorded for the Darwin Harbour Inner survey were collected, including numerous types of crustaceans (amphipods, isopods, tanaids, cumaceans, penaeids, squat lobsters, copepods, ostracods, shrimp, hermit crabs and brachyuran crabs), polychaete worms (from a variety of families and feeding guilds), molluscs (bivalves, opisthobranchs, nudibranchs and microgastropods), echinoderms (ophiuroids, echinoids, holothurians and crinoids) and other worm like taxa such as nematodes, nemerteans, oligochaetes, phoronids, platyhelminthes and sipunculids. Other taxa recorded but identified to broader groups included anemones, bryozoans, hydrozoans, sponges, pycnogonids (sea spiders), branchiostomes (small eel-like invertebrates) and juvenile fish. Raw sample data are presented in Appendix I.

Polychaete worms and crustaceans accounted for the greatest abundance and taxon diversity throughout the Darwin Offshore Baseline Phase survey, with polychaetes being the most numerically abundant of the major taxonomic groups. Crustacea was the next most numerically abundant group, followed by Mollusca, other worm phyla (e.g. nemerteans, nematodes, phoronids and sipunculids), Echinodermata and other phyla (e.g. anemones, hydroids, sponges and sea spiders). Crustaceans were the most diverse of the major taxonomic groups, followed by polychaetes, molluscs, other phyla, other worm phyla and echinoderms (Table 3-5, Figure 3-12).

The most numerically abundant taxa throughout the Darwin Offshore survey were amphipod crustaceans from the family group Aoridae/Isaeidae/Photidae (contributing 15.7% of the total abundance), followed by tanaid crustaceans from the family Apseudidae (7.2%), polychaete worms from the families Spionidae (4.9%), Capitellidae (4.7%), Maldanidae (4.2%), Ampharetidae (3.9%) and Nephtyidae (3.2%), amphipod crustaceans from the family Ampeliscidae (3.2%), tanaid crustaceans from the family Leptochelidae (2.9%) and nemerteans (2.4%). Examples of the most numerically abundant taxa (from the Darwin Harbour Inner survey) are shown in Figure 3-3. Representative phyla collected during the Darwin Offshore survey are also presented in Figure 3-13.

Mean abundance did not vary significantly among locations (Spoil Disposal Area, Zone of Impact (Near), Zone of Impact (Far), Control 1 and Control 2) but did vary among sites within locations. Abundance was greatest at Control location 2 (site 3) and Control location 1 (site 1), although the fewest numbers of individuals were also found in samples collected from both Control locations. Taxon richness was significantly different among locations due to differences between Control location 2 and the Spoil Disposal Area/Zone of Impact (Near). The greatest diversity of taxa was found at Control location 1 (site 1) and the Spoil Disposal Area (site 5) (Figure 3-14).

Table 3-5 Abundance and taxon richness of subtidal infauna assemblages collected from Darwin Offshore during the Baseline Phase, May 2012 to July 2012

Major Taxonomic Group Total Abundance Taxon Richness

Polychaeta 4,831 41

Crustacea 4,036 56

Mollusca 567 32

Echinodermata 222 4

Other Worm Phyla 513 8

Other Phyla 126 9

Baseline Total 10,295 150

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Percentage contribution of abundance and taxon richness for major taxonomic groups Figure 3-12collected from Darwin Offshore during the Baseline Phase, May 2012 to July 2012 (n=5)

Total Abundance (Darwin Offshore)

Taxon Richness (Darwin Offshore)

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Photomicrographs of representative taxa identified from Darwin Offshore during the Figure 3-13Baseline Phase, May 2012 to July 2012

Polychaetes: a) Eunicidae; b) Glyceridae; Crustaceans: c) Arcturidae; d) Squillidae

(mantis shrimp); Molluscs: e) Glaucidae f) Laevidentaliidae; Other: g) feather star

(Crinoidea) and h) sea spider (Pycnogonida)

a) b)

c) d)

e) f)

g) h)

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Mean abundance and mean taxon richness (+/- S.E.) for samples collected from Darwin Offshore during the Baseline Phase, May 2012 to Figure 3-14July 2012 (n=5). N.B. no data available for Control 1 (site 6)

Mean Abundance (Darwin Offshore)

Mean Taxon Richness (Darwin Offshore)

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3.2.2.2 Analyses of Assemblages

Infaunal assemblages varied significantly among locations and sites within locations (Appendix E). Pairwise tests (Appendix F) showed that these location-scale differences were explained by differences between the two Control locations and the three Impact sites, but also between the Zone of Impact (Far) and the Zone of Impact (Near)/Spoil Disposal Area. Locational differences were also due to variation in the dispersion of samples (i.e. variability among samples within each location) (Appendix H). This is illustrated in the PCoA plot (Figure 3-15), although this shows that only 24% of the total variation can be explained by differences among samples represented by the two axes.

Taxa driving these locational differences were tanaids (Apseudidae and Leptochelidae), amphipods from the families Aoridae/Isaeidae/Photidae and Ampeliscisdae and polychaetes from the families Spionidae, Capitellidae, Maldanidae and Ampharetidae (Figure 3-16, Figure 3-17, Figure 3-18, Appendix G).

Principal Coordinates Analyses (PCoA) of subtidal infaunal assemblages sampled from Figure 3-15Darwin Offshore during the Baseline Phase, May 2012 to July 2012

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Mean abundance of families (Apseudidae, Aoridae/Isaeidae/Photidae) contributing to Figure 3-16approximately 5% or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012

N.B. no data available for Control 1 (site 6)

0.00

5.00

10.00

15.00

20.00

25.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Apseudidae

0.0010.0020.0030.0040.0050.0060.0070.0080.0090.00

100.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Aoridae/Isaeidae/Photidae

0.002.004.006.008.00

10.0012.0014.0016.0018.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Leptochelidae

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Mean abundance of polychaete families (Ampeliscidae/Spionidae/Capitellidae) Figure 3-17contributing to approximately 5 % or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012

N.B. no data available for Control 1 (site 6)

0.002.004.006.008.00

10.0012.0014.0016.0018.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Ampeliscidae

0.00

2.00

4.00

6.00

8.00

10.00

12.00

14.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Spionidae

0.00

2.00

4.00

6.00

8.00

10.00

12.00

14.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Capitellidae

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Mean abundance of polychaete families (Maldanidae and Ampharetidae) contributing to Figure 3-18approximately 5 % or more to dissimilarities among Darwin Offshore locations during the Baseline Phase, May 2012 to July 2012

N.B. no data available for Control 1 (site 6)

0.002.004.006.008.00

10.0012.0014.0016.0018.0020.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Maldanidae

0.00

2.00

4.00

6.00

8.00

10.00

12.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6Mean

Ab

un

dan

ce +

/-S

.E.

(n=

5)

Site

Mean Abundance - Ampharetidae

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3.2.3 Particle Size Distribution

Sediment samples collected from the spoil disposal area contained a large proportion of sand with smaller proportions of gravel, clay and silt. This distribution was fairly uniform across the six sites sampled within the Spoil Disposal Area and the Zones of Impact (Near and Far). The proportion of gravel recorded from Control location 2 was notably smaller than at the other four locations (Figure 3-19). Mean particle size data are summarised in Table 3-6. Raw PSD data for Darwin Harbour Inner sampling sites are presented in Appendix J.

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Particle Size Distribution of samples collected from Darwin Offshore during the Baseline Phase, May 2012 to July 2012 (n=2) Figure 3-19

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Table 3-6 Percentage contribution, median grain size and sediment descriptions for Darwin Offshore locations

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 13.0 17.5 17.0 22.0 11.0 10.5 Silt (2-60 µm) 4.0 7.5 12.0 11.5 8.5 6.0 Sand (0.06-2.00 mm) 65.0 63.0 50.5 55.0 60.0 61.5 Gravel (>2mm) 18.0 12.0 20.5 11.5 20.5 22.0Median Grain Size (mm) 0.394 0.325 0.257 0.188 0.595 0.450

Sediment Description Sand, shell and clay Sand, shell and claySand, shell and silty

claySand, silty clay and

shellSand, shell and silty

claySand, shell and silty

clay

Spoil Disposal Area

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 15.0 14.5 17.5 24.0 16.5 18.0 Silt (2-60 µm) 11.0 7.0 15.5 13.5 9.5 7.5 Sand (0.06-2.00 mm) 54.5 59.0 47.0 54.0 55.0 60.0 Gravel (>2mm) 19.5 19.5 20.0 8.5 19.0 14.5Median Grain Size (mm) 0.332 0.394 0.188 0.150 0.394 0.300

Sediment DescriptionSand, silty clay and

shell Sand, shell and claySand, silty clay and

shell Sand and silty claySand, silty clay and

shell Sand, shell and clay

Zone of Impact (Near)

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N.B. no data available for Control 1 (site 6)

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 26.0 18.0 18.0 15.5 12.5 11.0 Silt (2-60 µm) 12.0 4.0 10.5 9.0 2.5 1.5 Sand (0.06-2.00 mm) 58.0 69.5 65.0 51.5 66.0 79.5 Gravel (>2mm) 4.0 8.5 6.5 24.0 19.0 8.0Median Grain Size (mm) 0.113 0.332 0.219 0.332 0.469 0.332

Sediment Description Sand and silty clay Sand, clay and shell Sand and silty claySand, silty clay and

shell Sand, shell and clay Sand and clay

Zone of Impact (Far)

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 25.0 21.5 9.0 12.0 15.0 no data Silt (2-60 µm) 14.0 12.0 6.0 5.5 17.5 no data Sand (0.06-2.00 mm) 49.0 66.5 46.0 63.0 42.0 no data Gravel (>2mm) 12.0 0.0 39.0 19.5 25.5 no data Median Grain Size (mm) 0.094 0.075 1.180 0.513 0.357 no data

Sediment DescriptionSand, silty clay and

shellFine sand and silty

clay Sand, shell and clay Sand, shell and claySand, shell and silty

clay no data

Control 1

LocationSite 1 2 3 4 5 6

Clay (<2 µm) 34.5 53.0 24.0 9.5 16.5 25.0 Silt (2-60 µm) 32.0 38.0 11.5 3.0 11.5 10.5 Sand (0.06-2.00 mm) 33.5 9.0 64.0 87.5 40.0 63.0 Gravel (>2mm) 0.0 0.0 0.5 0.0 32.0 1.5Median Grain Size (mm) 0.030 0.001 0.094 0.225 0.665 0.075

Sediment Description Silty clay and fine sand Silty clayMedium fine sand and

silty clay

Medium fine sand/medium sand and

clay

Sand, silty clay and shell

Medium fine sand and silty clay

Control 2

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3.2.4 pH and ORP

Mean pH and ORP values for Darwin Offshore locations are presented in Table 3-7, Figure 3-20 and Figure

3-21. pH values ranged between 6.9 at Control 2 (site 2) to 8.1 at Control 2, (site 4). ORP values ranged from -108 mV at Control 1 (site 3) to 185 mV at the spoil disposal area (site 6).

Table 3-7 Mean pH and ORP values for Darwin Offshore locations (+/- SE) sampled during the Baseline Phase, May 2012 to July 2012

pH -log [H+] ORP (mV)

Location Site Mean S.E Mean S.E

Spoil Disposal Area

1 7.78 0.06 -43 7.6

2 7.60 0.03 9 23.7

3 7.70 0.04 70 8.4

4 7.66 0.03 144 7.8

5 7.76 0.04 175 2.4

6 7.87 0.06 164 7.4

Zone of Impact (Near)

1 7.67 0.06 85 13.9

2 7.64 0.05 78 10.1

3 7.66 0.06 114 8.1

4 7.62 0.04 21 2.2

5 7.61 0.04 42 17.7

6 7.65 0.04 44 9.7

Zone of Impact (Far)

1 7.50 0.01 69 11.7

2 7.63 0.06 53 17.2

3 7.61 0.06 38 18.8

4 7.66 0.09 129 6.2

5 7.69 0.04 66 15.8

6 7.81 0.06 83 21.1

Control 1

1 8.10 0.10 -125 23.1

2 7.91 0.11 61 15.1

3 8.00 0.03 -134 10.4

4 7.63 0.05 29 12.6

5 7.53 0.04 61 15.1

6 - - - -

Control 2

1 7.13 0.06 -73 7.00

2 7.08 0.08 -92 5.61

3 7.71 0.03 -60 14.86

4 7.89 0.06 -21 15.78

5 7.56 0.04 51 14.61

6 7.69 0.03 -13 13.38

N.B. no data available for Control 1 (site 6)

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Mean pH (+/- SE) for Darwin Offshore locations (n=7) (N.B. no data available for Control 1 (site 6)) Figure 3-20

Mean ORP (+/- SE) for Darwin Harbour Inner locations (n=7) (N.B. no data available for Control 1 (site 6)) Figure 3-21

0.001.002.003.004.005.006.007.008.009.00

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6

pH

-lo

g[H

+]

Site

pH -log [H+]

-200

-150

-100

-50

0

50

100

150

200

1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6 1 2 3 4 5 6

OR

P (

mV

)

Site

ORP (mV)

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3.2.5 Relationship of Physical and Biological Variables

Examination of the distance based linear model indicated that very little of the variation of the Darwin Offshore infaunal assemblage could be attributed to the physical variables measured (median grain size, pH and ORP). Cumulatively these variables explained less than 10% of the total variation (R2 for each individual variable against the infaunal data cloud = <0.05). This is illustrated in the distance based redundancy analyses ordination (dbRDA) (Figure 3-22). Statistical results are presented in Appendix K.

dbRDA (distance based redundancy analysis) ordination of Darwin Offshore infauna Figure 3-22assemblage data versus median grain size, pH and ORP for the Baseline Phase, May 2012 to July 2012

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4 Discussion

The overall percentage cover of epifauna sampled within Darwin Harbour Inner was sparse, with ascidians, sponges, hydroids, anemones, bryozoans, macroalgae and filamentous algae collectively accounting for less than 1% of the total area sampled. This would be expected given the predominantly sandy substratum and the fact that many sessile invertebrates require a hard surface to form a stable attachment to the seabed. The epifauna observed in the drop camera survey may have been limited to those groups that are able to burrow a holdfast into the sediment or that have settled on an occasional clump of rubble or gravel (such as some species of anemones, sponges and sea whips). Very few examples of mobile epifauna were observed in photoquadrats, although tracks of small gastropod molluscs and the occasional demersal fish were noted. Large burrows were commonly observed suggesting the presence of crabs or other mobile crustaceans. Visibility was particularly poor at some of the Darwin Harbour Inner Control locations at the time of sampling therefore the percentage cover of epifauna observed at these locations is likely to have been conservative. Although a relatively small proportion of epifauna was observed in terms of the area sampled, at the scale of the harbour, this epifauna may provide important structure or refuge in an otherwise sparse subtidal seabed. No significant epifauna was observed within the dredge footprint or ZoMI.

The epifaunal assemblage at the Darwin Offshore sampling locations was similar to that of the Darwin Harbour Inner survey, with less than 1% of epifaunal cover. Results suggest that the Darwin Offshore spoil ground does not provide any unique or significant habitat. This is consistent with the findings of drop camera surveys of the spoil disposal ground carried out as part of the Ichthys Gas Field Development Project Environmental Impact Statement (EIS) (URS 2009).

Darwin Harbour Inner and Darwin Offshore subtidal benthic assemblages were diverse, with 155 and 150 taxa recorded from the Darwin Harbour Inner and Darwin offshore surveys respectively and approximately 169 taxa across the two surveys combined. The number of actual ‘species’ occurring in Darwin Harbour Inner and Darwin Offshore is likely to be significantly more than the number of taxa identified to family level (or higher), as more than one morpho-species were noted for several families during the identification process. Similar taxa were numerically abundant in both the Darwin Harbour Inner and Darwin Offshore surveys, including tanaid and amphipod crustaceans, several polychaete families, nematodes and nemerteans, although several species not recorded in the Darwin Offshore survey were present in the Darwin Harbour Inner survey and vice versa. All of the numerically abundant species recorded in the Darwin Harbour Inner and Darwin Offshore surveys are ubiquitous to most marine habitats and commonly found to occur in large numbers.

In Darwin Harbour Inner, variability was occurring at the site level but not at the broader (locational) scale for the infauna assemblages sampled. This was not the case in the Darwin Offshore infauna survey, where both locational and site level variation was evident. Variation at the locational scale may have been a result of smaller sample sizes at the Darwin Offshore Control locations (due to limited soft sediment habitat) which may have caused the lower abundances and taxon richness evident at these locations.

Multiple biotic and abiotic factors are reported to affect the distributional patterns of shallow water benthic infauna (Currie and Small 2006), with one of the major physical influences being PSD (Brown and McLachlan 2006; Sundberg and Kennedy1993; Butman and Grassle 1992). However, results of the distance based linear model did not indicate any clear relationship between median grain size and the infaunal subtidal assemblage data for the Darwin Harbour Inner or Darwin Offshore surveys. This is not due to inadequacies of the model (which captures around 80% of the fitted variation in both Darwin Harbour Inner and Darwin Offshore data), but suggests that other hydrographic, physico-chemical or biotic factors drive site and location level distribution patterns. Co-variance with parameters may also misrepresent causal mechanisms between organisms and particle size (Aller et al. 2001).

Mean sediment pH and ORP was within the ranges that would be considered normal for similar marine systems. Sites containing a high proportion of clay and silt were generally reducing, whereas those containing a high proportion of sand were generally oxidising. High proportions of clay and silt in samples limits water circulation and hence oxygenation potential, generally resulting in strongly reducing conditions. No relationship between pH, ORP and the infaunal subtidal assemblage data for the Darwin Harbour Inner or Darwin Offshore surveys was observed.

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General conclusions may be drawn from comparison of the Subtidal Benthos Baseline Phase Monitoring Survey and the Intertidal Benthos Baseline Phase Monitoring Survey which were carried out concurrently as part of the NEMP during the period from June 2012 to August 2012. That is, taxon richness and abundance was greater for the subtidal habitats (Darwin Harbour Inner and Darwin Offshore) than the intertidal habitats (Cardno 2012b), which is consistent with studies reporting macrofaunal abundance and species richness to be relatively low on beaches, higher in intertidal sand and mud flats and increasing in the shallow subtidal habitats of estuaries and towards the shelf (Metcalfe and Glasby 2008; Connell and Gillanders 2007; Smit 2003). The percentage contribution of major taxonomic groups was also distinctly different between intertidal and subtidal assemblages, with the intertidal assemblages characterised by a high proportion of polychaete families whereas a greater number of crustacean taxa were represented in the subtidal surveys (Cardno 2012b). Direct quantitative comparisons cannot be made due to differences in the sampling effort between the two monitoring programs.

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5 Acknowledgements

This report was written and compiled by Kate Reeds and reviewed by Dr Peggy O’Donnell. Field work was carried out by Kate Reeds, Brendan Alderson, Oliver Silver, Ivon Sebastian, Dan Aveling and Jonathon Syron. Laboratory work was carried out by Rick Johnson, Dr Rad Nair, Belinda Parkes, Molly Scott, Sean Smith, Greig Campbell, Caroline Bathje, Sarah Fitzsimmons, Kelly Davis, Ben Muscat, Yesmin Chikhani, Christina Chiu, Belinda Cook, Valeriya Komyakova and Andrea Nicastro. Thanks to Work Boats Northern Australia for providing crew and vessel.

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6 References Aller, J, Y., Woodin, S. A. and Aller, R.C. (2001). Organism-Sediment Relationships. University of South Carolina, Columbia.

Anderson, M. J., Gorley, R. N. and Clarke, K. R. (2008). PERMANOVA+ for PRIMER: Guide to Software and Statistical Methods. PRIMER-E: Plymouth, UK.

Butman, C. A. and Grassle J. P. (1992). Active habitat selection by Capitella sp. I larvae. I. Two-choice experiments in still water and flume flows. Journal of Marine Research 50: 669–715.

Brown, A. C. and McLachlan, A. (2006). The Ecology of Sandy Shores. Academic Press, Burlington, Massachusetts.

Cardno (2012a). Ichthys Project: Nearshore Environmental Monitoring Plan (NEMP). Prepared for INPEX, August 2012.

Cardno (2012b). Intertidal Benthos Monitoring Baseline Report. Ichthys Nearshore Environmental Monitoring Program. Report for INPEX, Cardno (NSW/ACT) Pty Ltd, Sydney.

Clarke K. R. and Gorley R. N. (2006). Primer V6: User Manual/Tutorial. Primer-E, Plymouth. Kohler, K. E. and Gill, S. M. (2006). Coral Point Count with excel extensions (CPCe): A visual basic program for the determination of coral and substrate coverage using random point count methodology. Comparative Geoscience. 32: 1259-1269.

Connell, S. D and Gillanders, B. M. (2007). Marine Ecology. Oxford University Press. Melbourne, Victoria.

Currie, D.R. and Small, K. J. (2006). The influence of dry-season conditions on the bottom dwelling fauna of an east Australian sub-tropical estuary. Hydrobiologia, 560: 345–361.

Eyre, B.D. and Ferguson, A. J. P. (2005). Benthic metabolism and b=nitrogen cycling in a subtropical east Australian estuary (Brunswick): Temporal variability and controlling factors. Limnology and Oceanography 50:81-96.

INPEX (2012). Dredging and Spoil Disposal Management Plan - East Arm (DSDMP). INPEX Operations Australia Pty Ltd.

Long, B. G., Dennis, D. M., Skewes, T. D., Poiner, I. R. (1996). Detecting an environmental impact of dredging on seagrass beds with a BACI sampling design. Aquatic Botany 53: 235-243.

Metcalfe K, and Glasby, C. (2008). Diversity of Polychaeta (Annelida) and other worm taxa in mangrove habitats of Darwin Harbour, northern Australia. Journal of Sea Research 59: 70-82.

Newell, R. C., Seiderer, L. J., Simpson, N. M. and Robinson, J. E (2004). Impacts of marine aggregate dredging on benthic macrofauna off the south coast of the United Kingdom. Journal of Coastal Research 20: 115–125.

Pennifold, M., Davis, J., (2001), Macrofauna and nutrient cycling in the Swan River Estuary, Western Australia: experimental results. Hydrological Processes, Vol 12 (13) pp. 2537-2553.

Sarda, R., Pinedo, S., Gremare, A. and Taboada, S. (2000). Changes in the dynamics of shallow sandy-bottom assemblages due to sand extraction in the Catalan Western Mediterranean Sea. ICES Journal of Marine Science 57: 1446–1453.

Schwinghamer, P. (1981). Characteristic size distributions of integral benthic communities. Canadian Journal of Fish and Aquatic Sciences. 38: 1255-1263.

Smit, N. (2003). Marine vertebrate life in the Darwin Harbour region and management implications. Proceedings of the Darwin Harbour Public Presentation – February 2003. Department of Infrastructure, Planning and Environment, PO BOX 496, Palmerston NT.

Sundberg, K. and Kennedy, V. S. (1993). Larval settlement of the Atlantic regia, Rangia cuneata (Bivalvia: Mactridae). Estuaries 16: 223–228.

Underwood, A. J. (1991). Beyond BACI: experimental designs for detecting human environmental impacts on temporal variations in natural populations. Australian Journal of Marine and Freshwater Research 42: 569-587.

Underwood, A. J. (1992). Beyond BACI: the detection of environmental impacts on populations in the real, but variable, world. Journal of Experimental Marine Biology and Ecology 161: 145-178.

URS Australia Pty. Ltd. (2009). Ichthys Gas Field Development Project: Nearshore Marine Ecology and Benthic Assemblages Study. Report prepared for INPEX Browse Ltd., Perth, Western Australia.

van Dalfsen, J. A., Essink, K., Toxvig Madsen, H., Birklund, J., Romero, J. and Manzanera, M. (2000). Differential response of macrozoobenthos to marine sand extraction in the North Sea and Western Mediterranean. ICES Journal of Marine Science 57: 1439–1445.

Wildsmith, M.D., Potter, I.C., Valesini, F.J., Platell, M.E. (2005). Do the assemblages of benthic macroinvertebrates in nearshore waters of Western Australia vary among habitat types, zones and seasons? Journal of the Marine Biological Association of the United Kingdom, 85: 217-232.

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APPENDIX A FIELD DATA

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1. Field data collected at inshore (harbour) grab sampling locations during the baseline sampling phase May - July 2012. GPS coordinates are in WGS84.

Location Site Rep Waypoint Lat Long Time Depth (m) Sample Vol (l) Comments

1 107 -12.47600597 130.852318 10:43 23.8 3 Silty mud (Shell grit)

2 108 -12.47617101 130.851458 11:00 23.4 1.5 Silty mud (Shell grit)

3 109 -12.47655499 130.850667 11:05 24.2 2 Silty mud (Shell grit)

4 110 -12.47648198 130.850693 11:10 24 4 Silty mud (Shell grit)

5 111 -12.47644803 130.850692 11:15 24.5 4 Silty mud (Shell grit)

1 244 -12.51002803 130.891388 14:14 10.2 2 Muddy with shell grit (-186)

2 245 -12.51011998 130.891296 14:16 10.2 2 Muddy with shell grit (-150)

3 246 -12.51025502 130.891294 14:17 10.2 3 Muddy with shell grit (-197)

4 247 -12.51017396 130.891062 14:18 10.2 3 Muddy with shell grit (-172)

5 248 -12.51015703 130.891085 14:20 10.3 3.5 Muddy with shell grit (-149)

1 251 -12.50614403 130.904991 14:39 7.8 1 Clean, sand/shell grit (122)

2 252 -12.50616901 130.905024 14:42 7.8 1 Clean, sand/shell grit (125)

3 254 -12.50601101 130.904862 14:43 7 1 Clean, sand/shell grit (123)

4 255 -12.50607303 130.90485 14:44 7.4 1 Clean, sand/shell grit (127)

5 256 -12.50611897 130.904834 14:45 7.4 1 Clean, sand/shell grit (129)

1 259 -12.50613397 130.904851 9:40 26.4 1.5 Fine sand + Silt + some gravel + shell grit (-75)

2 260 -12.47489898 130.846368 9:47 26 1.5 some macro algae? Sponge? (-89)

3 261 -12.47500199 130.846358 9:50 26 2 -12

4 262 -12.47492496 130.845878 9:52 26 3 -60

5 278 -12.475033 130.84655 12:48 27.1 3.5 54

Zone

of M

oder

ate

Impa

ct

1

2

3

4

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 264 -12.49774201 130.912103 10:30 5.7 4 Fine Sand, silt + fine gravel + shell grit (-45)

2 265 -12.49769499 130.911693 10:33 6 4 1

3 266 -12.49792398 130.911534 10:35 6 4 33

4 267 -12.49811601 130.912148 10:36 6 4 Nemertean? Flatworm (39)

5 268 -12.49805499 130.911932 10:40 6 4 6

1 271 -12.491471 130.915012 11:19 3.3 3 Mantis Shrimp, fine sand + silt + shell grit (-173)

2 272 -12.49170301 130.914775 11:22 3.3 3 -141

3 273 -12.49171701 130.914764 11:23 3.3 4 -99

4 274 -12.49173503 130.914756 11:24 3.9 4 -115

5 275 -12.49143898 130.914898 11:29 3.9 1.5 2

1 114 -12.43673198 130.817652 11:46 6.4 4 Sandy Silt

2 115 -12.43660298 130.817681 11:49 6.5 2.5 Sandy Silt

3 116 -12.43645504 130.817512 11:55 6.5 2.5 Sandy Silt

4 117 -12.43647901 130.817537 11:56 6.5 3 Sandy Silt

5 118 -12.43649402 130.817555 11:59 6.5 3 Sandy Silt

1 223 -12.48552497 130.827617 12:01 17.3 1 Clean coarse sand + shell grit (46)

2 224 -12.48545799 130.827366 12:03 17 1 Clean coarse sand + shell grit (57)

3 225 -12.48496003 130.827276 12:07 18.5 1 Clean coarse sand + shell grit (55)

4 226 -12.48490797 130.827258 12:09 18 1 Clean coarse sand + shell grit (54)

5 227 -12.48536202 130.827045 12:11 17.9 1 Clean coarse sand + shell grit (48)

Zone

of M

oder

ate

Impa

ctZo

ne o

f Inf

luen

ce

5

6

7

8

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 193 + 194 -12.53092001 130.848283 9:37 16 3 Sandy + Shell grit 17,18,19

2 195 -12.53097902 130.848267 9:39 15.2 3 35,41

3 196 -12.53091498 130.848211 9:43 15 2.5 51

4 197 -12.53104599 130.848465 9:45 15 3.5 22

5 198 -12.53104499 130.848512 9:47 15.8 2 -99

1 201 -12.52905898 130.856164 10:04 12.3 3 Fine sand, some mud + shell grit (-137)

2 202 -12.529048 130.856212 10:05 12.3 3 -138

3 203 -12.52901397 130.856247 10:07 12.2 1.5 -129

4 204 -12.52910701 130.856179 10:08 12 2.5 -173

5 205 -12.52912201 130.856179 10:09 12.1 1.5 -49,-52,-50

1 230 -12.50100399 130.86558 13:19 3.1 3 Sand/fine gravel, muddysediment

2 231 -12.50087801 130.865571 13:21 3.1 3 Stalked ascidians attached to seabed + seagrass halophila?

3 232 -12.50087701 130.865571 13:22 3.1 2

4 233 -12.50079897 130.865484 13:23 3.1 3

5 234 -12.50079403 130.865467 13:24 3.1 3

1 237 -12.51351197 130.873035 13:46 3.1 3.5 Muddy with shell grit (-170)

2 238 -12.51383803 130.873057 13:48 3.1 4 Muddy with shell grit (-196)

3 239 -12.513833 130.873114 13:49 3.1 3 Muddy with shell grit (-200)

4 240 -12.51383199 130.873153 13:51 3.1 1.5 Muddy with shell grit (-180)

5 241 -12.51367198 130.873357 13:54 3.2 3 Muddy with shell grit (-116)

Zone

of I

nflu

ence

9

10

11

12

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 172 -12.52019604 130.804377 13:02 22 2.5 -38

2 173 -12.52024499 130.80445 13:05 22 2.5 Muddy + Fine Gravel (-155)

3 174 -12.52008297 130.804332 13:09 22.9 2 -131

4 175 -12.52022102 130.804296 13:11 22 1.5 -173

5 176 -12.51999403 130.804187 13:15 23.1 4 -185

1 179 -12.51314099 130.802483 13:32 20.4 2.5 Coarse (no mud) -192

2 180 -12.513215 130.802492 13:33 20.4 1.5 -164

3 181 -12.51337099 130.80256 13:39 23 1.5 70

4 182 -12.51334299 130.802498 13:43 20 3 -22

5 183 -12.513402 130.802477 13:46 20 2 -59

1 165 -12.52717104 130.80117 11:45 21.8 4 Fine sand, some silt + fine gravelly worm (-115)

2 166 -12.52722502 130.801239 11:49 21.8 3 -75,-76,-78

3 167 -12.527107 130.801257 11:52 21.8 2.5 -95

4 168 -12.52739098 130.801022 11:55 21.3 3 -159, -159,-159

5 169 -12.52699502 130.801145 12:01 21.5 3 -146

1 215 + 216 -12.49117797 130.813194 11:25 17.3 1.5 Sandy gravel + Shell grit (-130)

2 217 -12.49101603 130.813239 11:27 17 1 Sandy gravel + Shell grit (-185)

3 218 -12.49091897 130.813307 11:28 18 1.5 Sandy gravel + Shell grit + Some mud (-147,-150,-151)

4 219 -12.49089902 130.813336 11:30 18 1.5 Sandy gravel + Shell grit (-140)

5 220 -12.49087798 130.813433 11:32 17.5 1 Sandy gravel + Shell grit (17)

Con

trol 1

13

14

15

16

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 208 -12.49234398 130.817395 10:47 17.6 1 Sand, fine gravel + shell grit + worm tubes (-166)

2 209 -12.49236996 130.816922 10:51 17.6 1 19

3 210 -12.49246703 130.816726 10:53 17.8 1 -72

4 211 -12.49274497 130.81728 10:56 17.8 2 -133,-134,-140

5 212 -12.49221004 130.817101 11:02 17.3 2 -145

1 186 -12.49435597 130.812899 14:08 17.5 1 Coarse sand (some mud) 98

2 187 -12.49447701 130.812981 14:10 17 1 Coarse sand (some mud) -43,44

3 188 -12.494447 130.812626 14:18 16.9 1 Coarse sand (some mud) 80

4 189 -12.49450802 130.812596 14:20 16.9 1.5 Coarse sand (some mud) -98

5 190 -12.49458002 130.812591 14:25 16 2.5 Coarse sand (some mud) -170

1 135 -12.501466 130.788356 13:30 10.5 2.5 Sandy/ Shell grit

2 136 -12.501465 130.788111 13:50 10.2 2.5 Sandy/ Shell grit

3 137 -12.50142904 130.788212 13:52 9.9 4 Sandy/ Shell grit (some fine gravel)

4 138 -12.50149098 130.7882 13:54 9.9 2.5 Sandy/ Shell grit

5 139 -12.501868 130.787996 13:56 9.1 2.5 Sandy/ Shell grit

1 128 -12.49565399 130.782699 13:06 9.6 4 Muddy Sand

2 129 -12.49569003 130.78272 13:07 9.5 3.5 Muddy Sand

3 130 -12.49582901 130.782841 13:13 9.6 3.5 Muddy Sand

4 131 -12.495871 130.782933 13:17 10.5 4 Muddy Sand

5 132 -12.49584904 130.783004 13:19 10.8 4 Muddy Sand

Con

trol 1

Con

trol 2

17

18

19

20

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 121 -12.48784298 130.780801 12:40 7 3 Silty Mud

2 122 -12.48792504 130.780897 12:44 7.3 4 Silty Mud

3 123 -12.48803803 130.780863 12:45 7.5 3.5 Silty Mud

4 124 -12.48806904 130.780874 12:48 7.5 3.5 Silty Mud

5 125 -12.48810701 130.780936 12:50 7.5 3.5 Silty Mud

1 143 -12.55052403 130.779928 10:05 5.6 3 Sandy, Fine Gravel + Worm tubes (25,26,27)

2 144 -12.55056904 130.779913 10:08 5.5 3 88,89,90

3 145 -12.55058697 130.779698 10:09 5.6 2.5 50,50,50

4 146 -12.55067197 130.779611 10:12 5.7 2.5 -98,97,92

5 147 -12.55012597 130.779804 10:20 5 3 -66,67,68

1 150 -12.54208596 130.782902 10:38 6.3 2.5 Muddy/Clay, Hydroids + Worm tubes (-85,-84,-83)

2 151 -12.54217297 130.782699 10:41 6.3 2.5 Muddy/Clay, Hydroids + Worm tubes (-49)

3 153 -12.54300797 130.782204 10:49 7.8 2 Muddy/Clay, Hydroids + Worm tubes (-78,-79,-85)

4 154 -12.54248997 130.782637 10:50 7.8 3 Muddy/Clay, Hydroids + Worm tubes (35,35,25)

5 155 -12.54268602 130.782724 10:53 9.1 3 Muddy/Clay, Hydroids + Worm tubes (-90,-92,-93)

1 158 -12.53533501 130.786668 11:13 9.7 2 Muddy/Clay (-95,-94,95)

2 159 -12.53532898 130.786568 11:15 9.1 2 Muddy/Clay (-142,-153,-154)

3 160 -12.53550299 130.786466 11:17 9.5 3 Muddy/Clay (-134,134,-135)

4 161 -12.53555001 130.786442 11:20 9.5 3 Muddy/Clay (-144)

5 162 -12.53562897 130.786388 11:21 9.5 4 Muddy/Clay (-130)

Con

trol 2

23

24

21

22

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2. Field data collected at offshore (spoil ground) grab sampling locations during the baseline sampling phase May - August 2012. GPS coordinates are in WGS84.

Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 455 -12.25550802 130.797796 10:58 20 1.5 Fine sediment + coarse sand (-10)

2 456 -12.25536302 130.798147 10:59 20 1.5 Gravel with shell grit + whole dead shells (-32)

3 457 -12.25524701 130.798408 11:00 20 1.5 -35

4 458 -12.25518197 130.798583 11:03 20 1.5 -37

5 459 -12.25583903 130.79747 11:08 20 1.5 -64

1 462 -12.24931497 130.80874 11:31 20.1 1.5 Same as SD1 + Large dead coral fragments (83)

2 463 -12.24923702 130.808333 11:33 20.1 1 Same as SD1 + Large dead coral fragments (80)

3 464 -12.25024603 130.807186 11:36 20.1 2 Same as SD1 + Large dead coral fragments (-80)

4 465 -12.25024897 130.807286 11:40 20.7 1.5 Same as SD1 + Large dead coral fragments (-47)

5 466 -12.25021603 130.80753 11:41 20.7 1.5 Same as SD1 + Large dead coral fragments (47)

1 469 -12.24579499 130.800301 12:13 20.5 2 Same as SD2 (98)

2 470 -12.24579901 130.800366 12:14 20.5 1.5 Same as SD2 (87)

3 471 -12.24578904 130.800431 12:15 20.5 2 Same as SD2 (41)

4 472 -12.245783 130.800476 12:17 20.5 1.5 Same as SD2 (50)

5 473 -12.245797 130.800607 12:19 20.5 1.5 Same as SD2 (56)

1 475 -12.24059503 130.810697 12:37 20.9 1.5 Fine sediment + a lot of dead coral + shell grit (154)

2 476 -12.240389 130.810554 12:38 20.9 1.5 Difficult to get good samples (155)

3 476 -12.24137999 130.808855 12:47 20.9 ~1 152

4 477 -12.24117698 130.809489 12:50 20.9 ~1 136

5 478 -12.24085797 130.810268 12:56 20.9 ~1 156

Spo

il D

ispo

sal A

rea

1

2

3

4

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 481 -12.23188698 130.809645 13:13 21.1 1.5 Same as SD4 (175)

2 482 -12.23147099 130.810267 13:20 21.1 1.5 Same as SD4 (174)

3 483 -12.23048301 130.81119 13:25 21.1 ~1 Same as SD4 (169)

4 484 -12.23256801 130.809209 13:30 21.1 3 Same as SD4 (180)

5 485 -12.23250397 130.809338 13:35 21.1 1.5 Same as SD4 (183)

1 487 -12.23533999 130.817743 13:50 21.5 ~1 Same as SD4 (174)

2 488 -12.23514201 130.818687 13:51 21.5 2.5 Same as SD4 (175)

3 489 -12.23505199 130.818992 13:52 21.5 1.5 Same as SD4 (175)

4 491 -12.23480799 130.819516 13:58 21.5 2 Same as SD4 (163)

5 492 -12.23472501 130.818778 14:05 21.5 2.5 Same as SD4 (128)

1 528 -12.24569701 130.84157 9:41 18.3 ~1 Same As ZI Near 2 ( poor sample volumes) -89

2 529 -12.24557396 130.841472 9:43 18.3 1.5 Same As ZI Near 2 ( poor sample volumes) -104

3 530 -12.24540297 130.841264 9:47 18.3 ~1 Same As ZI Near 2 ( poor sample volumes) - 74

4 531 -12.24537397 130.841138 9:48 18.4 ~1 Same As ZI Near 2 ( poor sample volumes) - 10

5 532 -12.24540104 130.841241 10:12 18.4 1.5 Same As ZI Near 2 ( poor sample volumes) - 116

1 521 -12.25660798 130.838584 9:06 16.9 3.5 Coarse sand, grey mud, shell grit + fragments (stalked ascidians) - 104

2 522 -12.25659801 130.838405 9:07 16.9 ~1 Coarse sand, grey mud, shell grit + fragments (stalked ascidians) - 94

3 523 -12.25657596 130.838317 9:08 16.9 2 Coarse sand, grey mud, shell grit + fragments (stalked ascidians) - 113

4 524 -12.25647002 130.837995 9:15 16.9 ~1 Coarse sand, grey mud, shell grit + fragments (stalked ascidians) - 80

5 525 -12.25649801 130.838424 9:24 16.9 ~1 Coarse sand, grey mud, shell grit + fragments (stalked ascidians) - 56

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 535 -12.25042298 130.847929 10:29 17.5 1.5 127

2 536 -12.25047201 130.847836 10:31 17.5 1.5 126

3 537 -12.25047704 130.847678 10:33 17.5 1.5 133

4 538 -12.25045902 130.847624 10:34 17.5 2 133

5 539 -12.25046698 130.847382 10:38 17.5 ~1 105

1 542 -12.24170697 130.850392 10:51 18.9 2 Coarse sand/grey mud + shells. Some large pebble fragments (28)

2 543 -12.24166104 130.85035 10:53 18.9 2.5 Coarse sand/grey mud + shells. Some large pebble fragments (20)

3 544 -12.24164201 130.850324 10:54 18.9 2 Coarse sand/grey mud + shells. Some large pebble fragments (16)

4 545 -12.24163204 130.850284 10:56 18.9 2.5 Coarse sand/grey mud + shells. Some large pebble fragments (23)

5 546 -12.24163396 130.850241 10:57 18.9 1.5 Coarse sand/grey mud + shells. Some large pebble fragments (15)

1 557 -12.23227104 130.850358 11:38 20.4 1.5 Same as S4 (107)

2 558 -12.23230097 130.850288 11:41 20.4 2 Same as S4 (32)

3 559 -12.23230801 130.850225 11:43 20.4 2 Same as S4 (6)

4 560 -12.23233298 130.850137 11:45 20.4 ~1 Same as S4 (-28)

5 561 -12.23234204 130.850099 11:48 20.4 2 Same as S4 (25)

1 549 -12.23579203 130.859104 11:10 19.1 3 Same as S4 (10)

2 550 -12.23576998 130.859113 11:10 19.1 2 Same as S4 (64)

3 551 x 552 -12.23541199 130.859435 11:16 19.1 1.5 Same as S4 (20)

4 553 -12.23589404 130.85886 11:20 19.1 2 Same as S4 (74)

5 554 -12.23547603 130.859365 11:23 19.1 2 Same as S4 (23)

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 535 -12.25042298 130.847929 10:29 17.5 1.5 127

2 536 -12.25047201 130.847836 10:31 17.5 1.5 126

3 537 -12.25047704 130.847678 10:33 17.5 1.5 133

4 538 -12.25045902 130.847624 10:34 17.5 2 133

5 539 -12.25046698 130.847382 10:38 17.5 ~1 105

1 542 -12.24170697 130.850392 10:51 18.9 2 Coarse sand/grey mud + shells. Some large pebble fragments (28)

2 543 -12.24166104 130.85035 10:53 18.9 2.5 Coarse sand/grey mud + shells. Some large pebble fragments (20)

3 544 -12.24164201 130.850324 10:54 18.9 2 Coarse sand/grey mud + shells. Some large pebble fragments (16)

4 545 -12.24163204 130.850284 10:56 18.9 2.5 Coarse sand/grey mud + shells. Some large pebble fragments (23)

5 546 -12.24163396 130.850241 10:57 18.9 1.5 Coarse sand/grey mud + shells. Some large pebble fragments (15)

1 557 -12.23227104 130.850358 11:38 20.4 1.5 Same as S4 (107)

2 558 -12.23230097 130.850288 11:41 20.4 2 Same as S4 (32)

3 559 -12.23230801 130.850225 11:43 20.4 2 Same as S4 (6)

4 560 -12.23233298 130.850137 11:45 20.4 ~1 Same as S4 (-28)

5 561 -12.23234204 130.850099 11:48 20.4 2 Same as S4 (25)

1 549 -12.23579203 130.859104 11:10 19.1 3 Same as S4 (10)

2 550 -12.23576998 130.859113 11:10 19.1 2 Same as S4 (64)

3 551 x 552 -12.23541199 130.859435 11:16 19.1 1.5 Same as S4 (20)

4 553 -12.23589404 130.85886 11:20 19.1 2 Same as S4 (74)

5 554 -12.23547603 130.859365 11:23 19.1 2 Same as S4 (23)

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 592 -12.23392404 130.890694 11:42 17.6 1 Coarse orange sand + shells/grey mud (110)

2 593 -12.23380602 130.890019 11:44 17.6 2 Coarse orange sand + shells/grey mud (32)

3 594 -12.23393502 130.889967 11:45 17.6 1.5 Coarse orange sand + shells/grey mud (-10)

4 595 -12.23400098 130.889888 11:47 17.6 1 Coarse orange sand + shells/grey mud (87)

5 596 -12.23409402 130.889643 11:49 17.6 2 Coarse orange sand + shells/grey mud (74)

1 600 -12.23700204 130.89999 12:18 16.9 1 Same as S5 (115)

2 601 -12.23695602 130.899529 12:21 16.9 1 Same as S5 (70)

3 602 -12.23635999 130.899663 12:29 16.9 1 Same as S5 (124)

4 603 -12.23636904 130.899659 12:30 16.9 1.5 Same as S5 (82)

5 604 -12.23639896 130.899146 12:33 16.9 1.5 Same as S5 (95)

1 344 -12.33215198 130.532446 12:00 20 1.5 Clay and coral and gravel (-165)

2 345 -12.33225499 130.533398 12:00 23 1.5 Clay and coral and gravel (9)

3 345 -12.33225499 130.533398 12:00 23 1.5 Clay and coral and gravel (-150)

4 346 -12.33256596 130.534466 12:00 23 2 Clay and coral and gravel (-149)

5 346 -12.33256596 130.534466 12:00 23 3 Clay and coral and gravel (-146)

1 347 -12.343963 130.520477 13:30 19.8 3 Grey fine sand/clay (-118)

2 348 -12.34401396 130.520571 13:32 19 3 Grey fine sand/clay (-117)

3 349 -12.34415604 130.520734 13:38 19.6 1.5 Grey fine sand/clay (-46)

4 350 -12.34427297 130.520861 13:38 19.6 1.5 Grey fine sand/clay (-162)

5 351 -12.34437103 130.52096 13:38 19.6 1.5 Grey fine sand/clay (-140)

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 355 -12.34372898 130.539619 14:15 18.5 1.5 Very reefy with clay/silt + gravel + shell grit (-142)

2 356 -12.34372596 130.539623 14:16 18 1.5 Fine and soft coral (-143)

3 358 -12.34384096 130.53977 14:17 18 1.5 -132

4 359 -12.34387902 130.539821 14:18 18 1.5 -137

5 360 -12.34409502 130.54003 14:19 18 1.5 -163

1 613 -12.33978102 130.554616 11:31 17 2.5 Grey Mud + shells + coarse sand (36)

2 614 -12.33971598 130.554385 11:32 17 1.5 Grey Mud + shells + coarse sand (-4)

3 615 -12.33972704 130.554208 11:33 17 1.5 Grey Mud + shells + coarse sand (37)

4 616 -12.33974196 130.553374 11:37 17 2 Grey Mud + shells + coarse sand (25)

5 617 -12.33962202 130.554004 11:44 17 2 Grey Mud + shells + coarse sand (51)

1 606 -12.33495003 130.544779 10:29 22.4 1 Grey soft sediment (mud) + shell grit (145)

2 607 -12.33497702 130.543396 10:33 20.3 1 Grey soft sediment (mud) + shell grit (20)

3 608 -12.33497098 130.54258 10:36 20.3 1 Grey soft sediment (mud) + shell grit (35)

4 609 -12.33488901 130.541874 10:38 20.3 1 Grey soft sediment (mud) + shell grit (56)

5 610 -12.33480804 130.540539 10:42 20.3 1 Grey soft sediment (mud) + shell grit (52)

1 No Data No Data No Data No Data No Data No Data SITE TOO HARD AND REEFY TO SAMPLE

2 No Data No Data No Data No Data No Data No Data SITE TOO HARD AND REEFY TO SAMPLE

3 No Data No Data No Data No Data No Data No Data SITE TOO HARD AND REEFY TO SAMPLE

4 No Data No Data No Data No Data No Data No Data SITE TOO HARD AND REEFY TO SAMPLE

5 No Data No Data No Data No Data No Data No Data SITE TOO HARD AND REEFY TO SAMPLE

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 408 -12.33263402 130.572444 11:45 21.5 1 Fine silty grey sand (-63)

2 409 -12.33252296 130.572567 11:49 21.5 3 -41

3 410 -12.33236304 130.572654 11:51 21.5 4 -72

4 411 -12.33185501 130.573053 11:53 21.5 4 -68

5 414 -12.33279697 130.572788 11:58 21.5 4 -94

1 418 -12.335434 130.583526 12:25 21.1 2.5 Fine silty grey sand (-105)

2 419 -12.33526904 130.583661 12:29 21.1 3.5 Fine silty grey sand (-62)

3 420 -12.335175 130.583738 12:31 21.1 3.5 Fine silty grey sand (-92)

4 421 -12.33509998 130.584009 12:32 21.1 3 Fine silty grey sand (-85)

5 422 -12.33591897 130.584097 12:35 21.1 3 Fine silty grey sand (-97)

1 432 -12.33075899 130.591023 13:28 19.5 2 Fine silty sand (-48)

2 433 -12.33071901 130.591129 13:29 19.5 2 Fine silty sand (-75)

3 434 -12.330689 130.591152 13:33 19.5 2 Fine silty sand (-108)

4 437 -12.33123802 130.591336 13:37 19.5 2.5 Fine silty sand (-59)

5 438 -12.33101103 130.591296 13:39 19.8 3 Fine silty sand (-40)

1 425 -12.32767998 130.582043 12:54 21.4 3 Orange - Medium/Coarse sand (1.0)

2 426 -12.32760002 130.582041 12:56 21.4 3 finer sediments (silty sand) 31.0

3 427 -12.327467 130.58202 12:57 21.4 3 13

4 428 -12.32794099 130.582817 13:02 21.4 3.5 -6.5

5 429 -12.32780202 130.582834 13:04 21.4 1 2

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Location Site Rep Waypoint Time Depth (m) Sample Vol (l) Comments

1 408 -12.33263402 130.572444 11:45 21.5 1 Fine silty grey sand (-63)

2 409 -12.33252296 130.572567 11:49 21.5 3 -41

3 410 -12.33236304 130.572654 11:51 21.5 4 -72

4 411 -12.33185501 130.573053 11:53 21.5 4 -68

5 414 -12.33279697 130.572788 11:58 21.5 4 -94

1 418 -12.335434 130.583526 12:25 21.1 2.5 Fine silty grey sand (-105)

2 419 -12.33526904 130.583661 12:29 21.1 3.5 Fine silty grey sand (-62)

3 420 -12.335175 130.583738 12:31 21.1 3.5 Fine silty grey sand (-92)

4 421 -12.33509998 130.584009 12:32 21.1 3 Fine silty grey sand (-85)

5 422 -12.33591897 130.584097 12:35 21.1 3 Fine silty grey sand (-97)

1 432 -12.33075899 130.591023 13:28 19.5 2 Fine silty sand (-48)

2 433 -12.33071901 130.591129 13:29 19.5 2 Fine silty sand (-75)

3 434 -12.330689 130.591152 13:33 19.5 2 Fine silty sand (-108)

4 437 -12.33123802 130.591336 13:37 19.5 2.5 Fine silty sand (-59)

5 438 -12.33101103 130.591296 13:39 19.8 3 Fine silty sand (-40)

1 425 -12.32767998 130.582043 12:54 21.4 3 Orange - Medium/Coarse sand (1.0)

2 426 -12.32760002 130.582041 12:56 21.4 3 finer sediments (silty sand) 31.0

3 427 -12.327467 130.58202 12:57 21.4 3 13

4 428 -12.32794099 130.582817 13:02 21.4 3.5 -6.5

5 429 -12.32780202 130.582834 13:04 21.4 1 2

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3. Field data collected at inshore (harbour) grab sampling locations during the baseline sampling phase May- July 2012.

Site 1 Zone Transect A Start Finish Comments

Time on Bottom: 11:20 Time on Deck: 11:25 305 deleteLat: Long Lat: Long 945 delete-12.47641199 130.850885 -12.476168 130.850883001 002 120 keepDepth: 24.4 Depth: 24

Transect B Start Finish CommentsTime on Bottom: 11:26 Time on Deck:Lat: Long Lat: Long-12.47646798 130.850853 -12.47641903 130.850883003 004 Camera 2 Depth: 24.5 Depth: 24.5

Site 2Transect A Start Finish Comments

Time on Bottom: 13:25 Time on Deck: 13:30Lat: Long Lat: Long-12.51013801 130.891126 -12.51009601 130.891072013 014Depth: 10.2 Depth: 10.2

Transect B Start Finish CommentsTime on Bottom: 13:33 Time on Deck: 13:35Lat: Long Lat: Long-12.51023197 130.891148 -12.51027999 130.891132015 016 Camera 5Depth: 7.9 Depth: 5.5

Site 3Transect A Start Finish Comments

Time on Bottom: 13:55 Time on Deck: 13:57Lat: Long Lat: Long Missed fix-12.50620999 130.905089 -12.50626699 130.905097018 019 Camera 2 Depth: 8.1 Depth:

Transect B Start Finish CommentsTime on Bottom: 14:00 Time on Deck: 14:05Lat: Long Lat: Long-12.50626699 130.905097 -12.50646497 130.904502019 020 Camera 2 Depth: 7.9 Depth: 7.6

Site 4Transect A Start Finish Comments

Time on Bottom: 12:22 Time on Deck: 12:35Lat: Long Lat: Long-12.47498103 130.846313 -12.47493301 130.846273005 006Depth: 29.5 Depth:

Transect B Start Finish CommentsTime on Bottom: 12:40 Time on Deck: 12:45Lat: Long Lat: Long-12.47489998 130.846305 -12.47486796 130.846286007 008 Camera 2 Depth: 29.3 Depth: 28.5

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Site 5Transect A Start Finish Comments

Time on Bottom: 14:15 Time on Deck: 14:253-4 dolphins spotted, cruising and diviing

Lat: Long Lat: Long-12.49799296 130.912005 -12.49803797 130.911714021 022Depth: 7.6 Depth:

Transect B Start Finish CommentsTime on Bottom: 14:30 Time on Deck: 14:35Lat: Long Lat: Long-12.49801501 130.911954 -12.49788702 130.911407023 024Depth: 7.5 Depth: 8.1

Site 6 SiltTransect A Start Finish Comments

Time on Bottom: 14:40 Time on Deck: 14:45Lat: Long Lat: Long-12.491628 130.914876 -12.49161601 130.914682025 026Depth: 4.8 Depth: 4.6

Transect B Start Finish CommentsTime on Bottom: 14:50 Time on Deck: 14:55Lat: Long Lat: Long-12.49160402 130.914823 -12.49148198 130.914012027 028Depth: 4.6 Depth: 4.6

Site 7Transect A Start Finish Comments

Time on Bottom: 14:15 Time on Deck: 14:20Lat: Long Lat: Long-12.436505 130.817554 -12.43651598 130.817661069 070Depth: 6.7 Depth: 6.7

Transect B Start Finish CommentsTime on Bottom: 14:25 Time on Deck: 14:30Lat: Long Lat: Long-12.43648798 130.817426 -12.43648396 130.817459071 072Depth: 6.6 Depth: 6.7

Site 8Transect A Start Finish Comments

Time on Bottom: 14:50 Time on Deck: 14:55Lat: Long Lat: Long-12.48542598 130.827683 -12.4853 130.827726073 074Depth: 15.8 Depth: 18

Transect B Start Finish CommentsTime on Bottom: 14:56 Time on Deck: 15:00Lat: Long Lat: Long-12.48541902 130.82768 -12.48537501 130.827668075 076Depth: 16.2 Depth: 17.6

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Site 9Transect A Start Finish Comments

Time on Bottom: 10:15 Time on Deck: 10:20Lat: Long Lat: Long-12.53114498 130.848495 -12.53111104 130.848466038 039Depth: 16.2 Depth: 16.2

Transect B Start Finish CommentsTime on Bottom: 10:21 Time on Deck: 10:25Lat: Long Lat: Long-12.53109704 130.848465 -12.53112 130.848518040 041Depth: 16.4 Depth: 15.8

Site 10Transect A Start Finish Comments

Time on Bottom: 10:40 Time on Deck: 10:45Lat: Long Lat: Long-12.52909804 130.856131 -12.529164 130.85595042 043Depth: 13 Depth: 12.2

Transect B Start Finish CommentsTime on Bottom: 10:47 Time on Deck: 10:50Lat: Long Lat: Long-12.52911304 130.856204 -12.52914296 130.856244044 045Depth: 13.1 Depth: 12.5

Site 11Transect A Start Finish Comments

Time on Bottom: 12:10 Time on Deck: 12:15 SandyLat: Long Lat: Long-12.50090802 130.865518 -12.50092302 130.865336100 101Depth: 2.7 Depth: 2.6

Transect B Start Finish CommentsTime on Bottom: 12:17 Time on Deck: 12:22 Epifauna (hydroids)?Lat: Long Lat: Long Ascidians?-12.50098899 130.865445 -12.50086804 130.86546102 103Depth: 2.6 Depth: 3

Site 12Transect A Start Finish Comments

Time on Bottom: 12:40 Time on Deck: 12:50Lat: Long Lat: Long-12.51349404 130.873131 -12.51361004 130.873105104 105Depth: 3.2 Depth: 3.1

Transect B Start Finish CommentsTime on Bottom: 12:52 Time on Deck: 12:55Lat: Long Lat: Long-12.51356302 130.873059 -12.51352396 130.873021106 107Depth: 3.1 Depth: 3.1

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Site 13Transect A Start Finish Comments

Time on Bottom: 11:50 Time on Deck: 11:55 Quite SiltyLat: Long Lat: Long-12.520104 130.804331 -12.52019101 130.804343050 051Depth: 23 Depth: 23.5

Transect B Start Finish CommentsTime on Bottom: 11:00 Time on Deck: 12:00Lat: Long Lat: Long-12.52008397 130.804218 -12.52017198 130.804258052 053Depth: 23.1 Depth: 22.9

Site 14Transect A Start Finish Comments

Time on Bottom: 11:25 Time on Deck: 11:30Lat: Long Lat: Long-12.51325599 130.802365 -12.51332003 130.802414046 047Depth: 20 Depth: 20.7

Transect B Start Finish CommentsTime on Bottom: 11:35 Time on Deck: 11:40Lat: Long Lat: Long-12.51315398 130.802379 -12.51312196 130.802497048 049Depth: 20.2 Depth: 21.3

Site 15Transect A Start Finish Comments

Time on Bottom: 12:10 Time on Deck: 12:20Lat: Long Lat: Long-12.52691296 130.801351 -12.52704397 130.801232054 055Depth: 22 Depth: 21.8

Transect B Start Finish CommentsTime on Bottom: 12:25 Time on Deck:Lat: Long Lat: Long-12.52698898 130.801293 -12.52702896 130.801318056 057Depth: 22.2 Depth: 22.4

Site 16Transect A Start Finish Comments

Time on Bottom: 13:40 Time on Deck: 13:45 Sandy (not silty)Lat: Long Lat: Long-12.491068 130.813281 -12.49097303 130.813364065 066Depth: 19.5 Depth: 19.5

Transect B Start Finish CommentsTime on Bottom: 13:50 Time on Deck: 13:55 (a bit further out than it Lat: Long Lat: Long should have been) so -12.491054 130.813307 -12.489342 130.813584067 068 shorten transectDepth: 19.7 Depth: 20

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Site 17Transect A Start Finish Comments

Time on Bottom: 13:15 Time on Deck: 13:20 Sandy (not silty)Lat: Long Lat: Long-12.49289903 130.817264 -12.49275402 130.817209061 062Depth: 19.6 Depth: 18.7

Transect B Start Finish CommentsTime on Bottom: 13:26 Time on Deck: 13:30Lat: Long Lat: Long-12.49293499 130.817331 -12.49285502 130.817391063 064Depth: 19.5 Depth: 19.5

Site 18Transect A Start Finish Comments

Time on Bottom: 12:50 Time on Deck: 12:55 Sandy (not silty)Lat: Long Lat: Long-12.49459301 130.81304 -12.494649 130.813106058 059Depth: 18.1 Depth: 17

Transect B Start Finish CommentsTime on Bottom: 13:00 Time on Deck: 13:05 missed point at start of BLat: Long Lat: Long-12.494649 130.813106 -12.49464699 130.81322approx 059? 060Depth: 17 Depth: 17.7

Site 19Transect A Start Finish Comments

Time on Bottom: 8:15 Time on Deck: 8:20 SandyLat: Long Lat: Long-12.50181603 130.788398 -12.50152803 130.788235077 078Depth: 8.5 Depth: 8.3

Transect B Start Finish CommentsTime on Bottom: 8:21 Time on Deck: 8:25Lat: Long Lat: Long-12.50147296 130.788212 -12.50140398 130.788098079 080Depth: 8.3 Depth: 7.7

Site 20Transect A Start Finish Comments

Time on Bottom: 8:40 Time on Deck: 8:45 Finer/Sandy siltLat: Long Lat: Long-12.49565902 130.782887 -12.49563698 130.782786081 082Depth: 8.1 Depth: 7.5

Transect B Start Finish CommentsTime on Bottom: 8:46 Time on Deck: 8:50Lat: Long Lat: Long-12.49556003 130.782857 -12.49551603 130.782674083 084Depth: 7.5 Depth: 7.4

Con

trol 2

Con

trol 2

Con

trol 1

Con

trol 1

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Site 21Transect A Start Finish Comments

Time on Bottom: 8:55 Time on Deck: 9:05Lat: Long Lat: Long-12.48812998 130.781167 -12.48795999 130.780966085 086Depth: 6.2 Depth: 6.8

Transect B Start Finish CommentsTime on Bottom: 9:10 Time on Deck: 9:15Lat: Long Lat: Long-12.48790098 130.781127 -12.48786301 130.780938087 088Depth: 5.6 Depth: 4.1

Site 22Transect A Start Finish Comments

Time on Bottom: 10:05 Time on Deck: 10:10 Silty sand in west arm channelLat: Long Lat: Long Poor visibility-12.55041397 130.779904 -12.55043803 130.779595089 090Depth: 7.5 Depth: 7.5

Transect B Start Finish CommentsTime on Bottom: 10:15 Time on Deck: 10:20Lat: Long Lat: Long-12.55041397 130.779904 -12.55051397 130.779906089 092Depth: 7.5 Depth: 8.9

Site 23Transect A Start Finish Comments

Time on Bottom: 10:30 Time on Deck: 10:35Lat: Long Lat: Long Silty sand in channel-12.54256197 130.782662 -12.542969 130.782534093 094 Poor visibilityDepth: 6.5 Depth: 7.8

Transect B Start Finish CommentsTime on Bottom: 10:40 Time on Deck: 10:45Lat: Long Lat: Long-12.542969 130.782534 -12.54289197 130.782636094 095Depth: 7.5 Depth:

Site 24Transect A Start Finish Comments

Time on Bottom: 11:00 Time on Deck: 11:10Lat: Long Lat: Long Silty sediment-12.53543098 130.786503 -12.53559502 130.786393096 097 Poor visibilityDepth: 10.1 Depth: 9

Transect B Start Finish CommentsTime on Bottom: 11:15 Time on Deck: 11:20Lat: Long Lat: Long-12.53536502 130.786396 -12.53575101 130.786145098 099Depth: 8 Depth: 8.1

Con

trol 2

Con

trol 2

Con

trol 2

Con

trol 2

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4. Field data collected at offshore (spoil ground) grab sampling locations during the baseline sampling phaseMay - July 2012

Date Site 1 Zone Transect A Start Finish Comments

Time on Bottom: 9:05 Time on Deck: 9:10 Excellent VisibilityLat: Long Lat: Long-12.25580097 130.797123 -12.25569997 130.795902362 363 Bioturbated flat sand bottomDepth: 18 Depth: 18

Transect B Start Finish CommentsTime on Bottom: 9:14 Time on Deck: 9:20Lat: Long Lat: Long-12.25543301 130.797538 -12.255547 130.796039364 365Depth: 18 Depth: 18

Site 2Transect A Start Finish Comments

Time on Bottom: 9:35 Time on Deck: 9:43 Excellent VisibilityLat: Long Lat: Long-12.24954003 130.807775 -12.24937901 130.806034366 367Depth: 19.3 Depth: 19.3

Transect B Start Finish CommentsTime on Bottom: 9:45 Time on Deck: 9:50Lat: Long Lat: Long-12.24920701 130.808069 -12.24907097 130.806625368 369Depth: 19.1 Depth: 19.3

Site 3Transect A Start Finish Comments

Time on Bottom: 10:00 Time on Deck: 10:08Lat: Long Lat: Long-12.24506903 130.800275 -12.24492302 130.798931370 371Depth: 19.1 Depth: 19.1

Transect B Start Finish CommentsTime on Bottom: 10:10 Time on Deck: 10:15Lat: Long Lat: Long-12.24526299 130.8008 -12.24536902 130.799602372 373Depth: 19.1 Depth: 19.1

Site 4Transect A Start Finish Comments

Time on Bottom: 10:30 Time on Deck: 10:35Lat: Long Lat: Long-12.24115896 130.809818 -12.24111898 130.8095374 375Depth: 19.5 Depth: 19.5

Transect B Start Finish CommentsTime on Bottom: 10:40 Time on Deck: 10:45Lat: Long Lat: Long-12.24104622 130.809531 -12.24086601 130.809175SD-S4(WP) 375? 376Depth: 19.4 Depth: 19.4

Spo

il D

ispo

sal A

rea

Spo

il D

ispo

sal A

rea

Spo

il D

ispo

sal A

rea

Spo

il D

ispo

sal A

rea

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Site 5Transect A Start Finish Comments

Time on Bottom: 10:55 Time on Deck: 11:00Lat: Long Lat: Long Short Transect ~50m-12.23167601 130.809289 -12.23143998 130.809174377 378Depth: 20 Depth: 19.9

Transect B Start Finish CommentsTime on Bottom: 11:05 Time on Deck: 11:15Lat: Long Lat: Long Flat bottom-12.23199 130.809569 -12.23226802 130.808443379 380Depth: 20.1 Depth: 20

Site 6Transect A Start Finish Comments

Time on Bottom: 11:25 Time on Deck: 11:30Lat: Long Lat: Long Short Transect-12.23494696 130.818642 -12.23501704 130.818157381 382Depth: 19.9 Depth: 19.9

Transect B Start Finish CommentsTime on Bottom: 11:35 Time on Deck: 11:40Lat: Long Lat: Long-12.234938 130.81881 -12.23561802 130.818162383 384Depth: 19.8 Depth: 19.8

Site 1Transect A Start Finish Comments

Time on Bottom: 11:55 Time on Deck: 12:05Lat: Long Lat: Long-12.24554496 130.84116 -12.24534798 130.841105385 386Depth: 18.7 Depth: 18.7

Transect B Start Finish CommentsTime on Bottom: 12:06 Time on Deck: 12:10Lat: Long Lat: Long-12.24584503 130.841376 -12.24631098 130.841012387 388Depth: 18.5 Depth: 18.5

Site 2Transect A Start Finish Comments

Time on Bottom: 12:20 Time on Deck: 12:30Lat: Long Lat: Long-12.25618101 130.838063 -12.25663296 130.837869389 390Depth: 17.5 Depth: 17.6

Transect B Start Finish CommentsTime on Bottom: 12:31 Time on Deck: 12:35Lat: Long Lat: Long-12.255792 130.83804 -12.25643397 130.837768391 392Depth: 17.6 Depth: 17.6

Spo

il D

ispo

sal A

rea

Spo

il D

ispo

sal A

rea

Zone

of I

mpa

ct (N

ear)

Zone

of I

mpa

ct (N

ear)

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Site 3Transect A Start Finish Comments

Time on Bottom: 12:50 Time on Deck: 12:55Lat: Long Lat: Long-12.24988301 130.848468 -12.249248 130.848325393 394Depth: 18.5 Depth: 18.5

Transect B Start Finish CommentsTime on Bottom: 12:56 Time on Deck: 13:01Lat: Long Lat: Long-12.25018602 130.848563 -12.25018099 130.848193395 396Depth: 18.5 Depth: 18.5

Site 4Transect A Start Finish Comments

Time on Bottom: 13:10 Time on Deck: 13:20Lat: Long Lat: Long-12.24123398 130.85029 -12.24125803 130.850224397 398Depth: 20.8 Depth: 19.8

Transect B Start Finish CommentsTime on Bottom: 13:21 Time on Deck: 13:25Lat: Long Lat: Long-12.24164402 130.850769 -12.24169096 130.850637399 400Depth: 20.8 Depth: 20

Site 5Transect A Start Finish Comments

Time on Bottom: 13:35 Time on Deck: 13:40Lat: Long Lat: Long-12.232063 130.850275 -12.23145104 130.850319401 402Depth: 21.5 Depth: 21.9

Transect B Start Finish CommentsTime on Bottom: 13:45 Time on Deck: 13:50Lat: Long Lat: Long-12.23145104 130.850319 -12.23196301 130.850252403 404Depth: 21.6 Depth: 21.8

Site 6Transect A Start Finish Comments

Time on Bottom: 14:00 Time on Deck: 14:05Lat: Long Lat: Long-12.23527 130.859396 -12.23441002 130.859849405 406Depth: 21.1 Depth: 21.1

Transect B Start Finish CommentsTime on Bottom: 14:07 Time on Deck: 14:15Lat: Long Lat: Long-12.235644 130.859242 -12.235427 130.859336407 20.9 408Depth: Depth: 21.3

Zone

of I

mpa

ct (N

ear)

Zone

of I

mpa

ct (N

ear)

Zone

of I

mpa

ct (N

ear)

Zone

of I

mpa

ct (N

ear)

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Site 1Transect A Start Finish Comments

Time on Bottom: 9:30 Time on Deck: 9:35Lat: Long Lat: Long

495 494Depth: 16.9 Depth:

Transect B Start Finish CommentsTime on Bottom: 9:40 Time on Deck: 9:45Lat: Long Lat: Long-12.257992 130.878742 -12.25749303 130.87832495 496Depth: 16.9 Depth: 17.1

Site 2Transect A Start Finish Comments

Time on Bottom: 10:38 Time on Deck: 10:46Lat: Long Lat: Long-12.24668096 130.882692 -12.24648901 130.881627500 501Depth: 17.6 Depth: 17.7

Transect B Start Finish CommentsTime on Bottom: 10:48 Time on Deck: 10:58Lat: Long Lat: Long-12.24648901 130.881627 -12.24688003 130.884951501 502 Camera 5Depth: 17.7 Depth: 17.5

Site 3Transect A Start Finish Comments

Time on Bottom: 10:03 Time on Deck: 10:12Lat: Long Lat: Long-12.25161798 130.887492 -12.25210003 130.890043497 498 Camera 2Depth: 16.7 Depth: 16.5

Transect B Start Finish CommentsTime on Bottom: 10:15 Time on Deck: 10:23Lat: Long Lat: Long-12.25210003 130.890043 -12.24966802 130.889436498 499Depth: 16.9 Depth: 16.9

Site 4Transect A Start Finish Comments

Time on Bottom: 11:09 Time on Deck: 11:15Lat: Long Lat: Long

-12.24199899 130.890719missed 503Depth: 17.5 Depth: 17.5

Transect B Start Finish CommentsTime on Bottom: Time on Deck: 11:23Lat: Long Lat: Long-12.24210897 130.890213 -12.24334203 130.891046504 505 Camera 2Depth: 17.5 Depth: 17.5

Zone

of I

mpa

ct (F

ar)

Zone

of I

mpa

ct (F

ar)

Zone

of I

mpa

ct (F

ar)

Zone

of I

mpa

ct (F

ar)

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Site 5Transect A Start Finish Comments

Time on Bottom: 11:35 Time on Deck: 11:43Lat: Long Lat: Long-12.23423802 130.891657 -12.23254496 130.892302506 507Depth: 18.8 Depth: 18.9

Transect B Start Finish CommentsTime on Bottom: 11:48 Time on Deck: 11:54Lat: Long Lat: Long-12.23327301 130.88984 -12.23329699 130.891195508 509 Camera 5Depth: 18.7 Depth: 18.9

Site 6Transect A Start Finish Comments

Time on Bottom: 12:08 Time on Deck: 12:14Lat: Long Lat: Long-12.23612403 130.898 -12.23612898 130.898296510 511 Camera 2Depth: 18 Depth: 17.8

Transect B Start Finish CommentsTime on Bottom: 12:16 Time on Deck: 12:22Lat: Long Lat: Long-12.23661697 130.898235 -12.23596302 130.899769512 513Depth: 17.8 Depth: 18.4

Site 1Transect A Start Finish Comments

Time on Bottom: 9:45 Time on Deck: 9:50 Visibility improvedLat: Long Lat: Long-12.33813398 130.533264 -12.33809902 130.533341296 297Depth: 19.7 Depth:

Transect B Start Finish CommentsTime on Bottom: 9:55 Time on Deck: 10:00Lat: Long Lat: Long-12.33850203 130.532637 -12.33834101 130.533052298 299Depth: 20.1 Depth: 19.5

Site 2Transect A Start Finish Comments

Time on Bottom: 10:10 Time on Deck: 10:15Lat: Long Lat: Long-12.34325096 130.52321 -12.34227003 130.524659300 301Depth: 19.7 Depth: 19.8

Transect B Start Finish CommentsTime on Bottom: 10:20 Time on Deck:Lat: Long Lat: Long-12.34335699 130.522643 -12.341216 130.542999302 303? travelled ~200mDepth: 19.8 Depth: 19.8

Zone

of I

mpa

ct (F

ar)

Zone

of I

mpa

ct (F

ar)

Con

trol 1

Con

trol 1

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Site 3Transect A Start Finish Comments

Time on Bottom: 10:45 Time on Deck: 10:55Lat: Long Lat: Long-12.341216 130.542999 -12.34109698 130.543497303 304Depth: 18.9 Depth: 18.9

Transect B Start Finish CommentsTime on Bottom: 10:56 Time on Deck: 11:00 Some reefy sectionsLat: Long Lat: Long Waypoint caught on reef-12.3416159 130.5418387 -12.34129898 130.542683CL-3(WP) 305Depth: 19.5 Depth: 19.5

Site 4Transect A Start Finish Comments

Time on Bottom: 11:20 Time on Deck: 11:30Lat: Long Lat: Long-12.34391246 130.5526208 -12.34331299 130.554094CL-4 306Depth: 18.4 Depth: 18.7

Transect B Start Finish CommentsTime on Bottom: 11:35 Time on Deck: 11:40 Reefy in placesLat: Long Lat: Long-12.34385001 130.552387 -12.34278803 130.553631307 308Depth: 18.2 Depth: 18.5

Site 5Transect A Start Finish Comments

Time on Bottom: 11:50 Time on Deck: 11:55Lat: Long Lat: Long-12.335248 130.548787 -12.33439598 130.54986309 310Depth: 20.4 Depth: 21.3

Transect B Start Finish CommentsTime on Bottom: 12:00 Time on Deck: 12:05Lat: Long Lat: Long-12.33529997 130.548123 -12.33415199 130.549394311 312Depth: 20.7 Depth: 21.5

Site 6Transect A Start Finish Comments

Time on Bottom: 12:20 Time on Deck: 12:30 Some reefy bitsLat: Long Lat: Long-12.346177 130.534318 -12.345387 130.534919313 314Depth: 19.3 Depth: 19.6

Transect B Start Finish CommentsTime on Bottom: 12:35 Time on Deck: 12:40Lat: Long Lat: Long-12.34663901 130.533977 -12.34589696 130.534439315 316Depth: 18.4 Depth: 19.8

Con

trol 1

Con

trol 1

Con

trol 1

Con

trol 1

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Site 3Transect A Start Finish Comments

Time on Bottom: 10:45 Time on Deck: 10:55Lat: Long Lat: Long-12.341216 130.542999 -12.34109698 130.543497303 304Depth: 18.9 Depth: 18.9

Transect B Start Finish CommentsTime on Bottom: 10:56 Time on Deck: 11:00 Some reefy sectionsLat: Long Lat: Long Waypoint caught on reef-12.3416159 130.5418387 -12.34129898 130.542683CL-3(WP) 305Depth: 19.5 Depth: 19.5

Site 4Transect A Start Finish Comments

Time on Bottom: 11:20 Time on Deck: 11:30Lat: Long Lat: Long-12.34391246 130.5526208 -12.34331299 130.554094CL-4 306Depth: 18.4 Depth: 18.7

Transect B Start Finish CommentsTime on Bottom: 11:35 Time on Deck: 11:40 Reefy in placesLat: Long Lat: Long-12.34385001 130.552387 -12.34278803 130.553631307 308Depth: 18.2 Depth: 18.5

Site 5Transect A Start Finish Comments

Time on Bottom: 11:50 Time on Deck: 11:55Lat: Long Lat: Long-12.335248 130.548787 -12.33439598 130.54986309 310Depth: 20.4 Depth: 21.3

Transect B Start Finish CommentsTime on Bottom: 12:00 Time on Deck: 12:05Lat: Long Lat: Long-12.33529997 130.548123 -12.33415199 130.549394311 312Depth: 20.7 Depth: 21.5

Site 6Transect A Start Finish Comments

Time on Bottom: 12:20 Time on Deck: 12:30 Some reefy bitsLat: Long Lat: Long-12.346177 130.534318 -12.345387 130.534919313 314Depth: 19.3 Depth: 19.6

Transect B Start Finish CommentsTime on Bottom: 12:35 Time on Deck: 12:40Lat: Long Lat: Long-12.34663901 130.533977 -12.34589696 130.534439315 316Depth: 18.4 Depth: 19.8

Con

trol 1

Con

trol 1

Con

trol 1

Con

trol 1

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Site 5Transect A Start Finish Comments

Time on Bottom: 10:05 Time on Deck: 10:15 Wrong date on slate.Lat: Long Lat: Long Poor visibility-12.33296704 130.60259 -12.33207403 130.603988336 337Depth: 19.6 Depth: 19.3

Transect B Start Finish CommentsTime on Bottom: Time on Deck: 10:25Lat: Long Lat: Long Poor visibility-12.3330382 130.6024493 -12.3330382 130.6024493CON2-5 338Depth: Depth: 19.5

Site 6Transect A Start Finish Comments

Time on Bottom: 14:18 Time on Deck: 14:22Lat: Long Lat: Long-12.324289 130.597745 -12.32365097 130.598964518 519Depth: 20.5 Depth: 20.5

Transect B Start Finish CommentsTime on Bottom: 14:20 Time on Deck: 14:31Lat: Long Lat: Long-12.32365097 130.598964 -12.32429101 130.598938519 520Depth: 20 Depth: 20

Con

trol 2

Con

trol 2

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APPENDIX B EPIBENTHIC HABITAT DESCRIPTIONS

Ichthys Nearshore Environmental

Monitoring Program

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1. Epibenthic habitat descriptions for Darwin Harbour (inshore) locations sampled during the baseline phase

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Location Site7

8

9

10

11

12

Habitat DescriptionZone of Influence

Bare bioturbated sand.

Bare coarse sand and shell grit.

Bare bioturbated fine sand (some rubble*).

Bare bioturbated fine sand and organic detritus including leaves.

Bioturbated sand, turfing algae and occasional sponge.

Bioturbated sand, turfing algae and occasional sponge.

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Location Site13

14

15

16

17

18

Control 1 Bare biotubated sand.

Bare sand.

Habitat Description

Bioturbated bare sand, occasional sea whip.

Bare. bioturbated sand.

Bioturbated sand, occasional bryozoan.

Bare clean sand.

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Location Site19

20

21

22

23

24

Control 2 Bare sand and macroalgae.

Bare bioturbated sand.

Bare bioturbated sand.

Bare bioturbated sand and occasional hydroids.

Habitat Description

Bare bioturbated sand and occasional hydroids.

Bare bioturbated sand and occasional hydroids.

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2. Epibenthic habitat descriptions for offshore locations sampled during the baseline phase

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Location Site1

2

3

4

5

6

Zone of Impact (Far)

Bare bioturbated sand and shell grit. Bryozoans common. Sponges and stalked ascidians occasional.

Bare bioturbated sand and shell grit. Sponges, bryozoans, hydroids and stalked ascidians occasional.

Bare bioturbated sand and shell grit and coral rubble. Hydroids and bryozoans occasional.

Bioturbated sand and shell grit with coral rubble and occasional bryozoans.

Habitat Description

Bare, coarse clean sand. Sponge present but rare.

Bare, bioturbated sand and shell grit and coral rubble. Occasional bryozoans and hydroids.

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Location Site1

2

3

4

5

6

Control 1Habitat Description

Poor Visibility. Bare flat sandy seabed with occasional patches of epifauna, including bryozoans, macroalge, sea whips and sea fans.

Bare bioturbated fine sand/silt. Occasional bryozoans, macroalgae and ascidians.

Poor Visibility. Bare flat sandy seabed with occasional patches of epifauna, including bryozoans, macroalge, sea whips and sea fans.

Poor Visibility. Bare flat bioturbated, sandy seabed with occasional patches of epifauna, including bryozoans, macroalge, sea whips and sea fans.

Poor Visibility. Bare flat sandy seabed with occasional patches of epifauna, including bryozoans, macroalge, sea whips and sea fans.

Poor Visibility. Bare flat sandy seabed with occasional patches of epifauna, including bryozoans, macroalge, sea whips and sea fans.

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Location Site1

2

3

4

5

6

Control 2

Bare, bioturbated sand

Bare, bioturbated sand/silt

Bare, bioturbated sand

Poor visibility. Bare, bioturbated sand

Bare, sandy seabed and invertebrate tracks.

Poor visibility. Bare, bioturbated sand with occasional epifauna.

Habitat Description

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APPENDIX C CPCE SUMMARY DATA

Ichthys Nearshore Environmental

Monitoring Program

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1. CPCe summary data collected from within Darwin Harbour (inshore) during the baseline sampling phase(May to July 2012).

Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 2.43 0.70 1.15 0.49 0.00 0.00 0.00 0.00 32.71 6.16 27.71 3.13Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 3.46 1.31 1.35 0.48 0.00 0.00 0.10 0.10SUBSTRATUM Burrow 9.15 6.82 5.26 1.45 2.46 0.77 4.69 0.98 0.21 0.14 0.31 0.23Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 2.29 1.68 0.21 0.21Organic Debris 0.12 0.12 0.00 0.00 0.00 0.00 0.31 0.17 0.00 0.00 1.35 0.64Rubble 0.00 0.00 1.48 1.48 0.00 0.00 0.00 0.00 0.10 0.10 0.10 0.10Shell Grit 0.12 0.12 0.53 0.26 1.80 0.66 5.52 1.61 6.56 2.55 10.83 1.45Sand 83.70 7.01 82.93 6.06 91.16 1.77 81.88 2.60 57.29 5.15 59.27 2.89Bioturbated Sand 4.48 0.87 8.54 3.49 1.12 0.89 6.15 1.84 0.83 0.83 0.10 0.10Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOWShadow 0.60 0.28 6.67 5.67 0.22 0.15 0.00 0.00 0.00 0.00 0.00 0.00

Zone of Moderate ImpactSite 1A Site 1B Site 2A Site 2B Site 3A Site 3B

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.42 0.42 0.11 0.11 0.31 0.31 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.33 0.24 0.00 0.00 1.08 0.96 11.61 2.17Filamentous Algae 0.00 0.00 0.31 0.31 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00 0.12 0.12 0.67 0.67Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.10 0.10 0.73 0.43 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.21 0.21 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.83 0.26 3.54 0.56 1.45 0.45 1.04 0.47 3.37 0.75 1.23 0.37Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00Organic Debris 0.00 0.00 0.10 0.10 0.00 0.00 0.10 0.10 0.00 0.00 0.45 0.45Rubble 0.00 0.00 0.31 0.23 0.33 0.24 0.10 0.10 0.00 0.00 0.00 0.00Shell Grit 0.00 0.00 0.94 0.30 1.67 0.55 1.25 0.38 0.00 0.00 0.11 0.11Sand 90.52 1.87 83.02 1.37 86.94 1.38 85.63 2.44 88.58 5.90 71.21 2.63Bioturbated Sand 6.98 1.73 9.58 1.00 7.59 1.08 11.25 2.29 0.96 0.60 1.12 0.34Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 1.25 1.25 0.42 0.32 1.34 0.61 0.00 0.00 5.65 5.52 13.62 1.65OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.21 0.21 0.42 0.42 0.11 0.11 0.21 0.21 0.24 0.16 0.00 0.00TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Zone of Moderate ImpactSite 6BSite 4A Site 4B Site 5A Site 5B Site 6A

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.42 0.42 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.24 0.24Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 5.80 1.75 6.58 3.24 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.24 0.24BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.12 0.12SUBSTRATUM Burrow 0.78 0.32 0.00 0.00 0.11 0.11 0.00 0.00 2.46 0.69 3.85 0.91Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.00 0.00 0.11 0.11 0.10 0.10 0.00 0.00 0.00 0.00Shell Grit 0.11 0.11 0.22 0.22 36.01 9.19 26.35 8.23 2.69 0.83 3.97 1.25Sand 90.07 2.08 92.30 3.14 63.21 9.05 72.71 8.27 74.90 1.85 86.06 2.51Bioturbated Sand 3.13 0.93 0.89 0.58 0.00 0.00 0.00 0.00 15.79 2.49 2.40 1.04Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.34 0.34 0.00 0.00QUALITY Poor Quality 0.11 0.11 0.00 0.00 0.56 0.21 0.31 0.17 3.71 1.99 3.13 2.87OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.33 0.24 0.00 0.00 0.33 0.18 0.00 0.00

Zone of InfluenceSite 7A Site 7B Site 8A Site 8B Site 9A Site 9B

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.21 0.21 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 51.88 6.71 43.02 3.70 34.38 2.39 36.25 1.67Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.33 0.24 0.00 0.00 1.04 0.52 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.42 0.42 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 3.33 3.22 0.31 0.17 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00 0.21 0.21SUBSTRATUM Burrow 0.24 0.24 0.78 0.32 0.00 0.00 0.31 0.17 1.56 0.34 0.42 0.18Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.72 0.60 0.22 0.22 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.22 0.15 0.10 0.10 0.31 0.23 0.00 0.00 0.10 0.10Shell Grit 0.24 0.16 0.11 0.11 5.21 1.53 7.50 2.01 0.21 0.14 1.04 0.42Sand 98.20 0.77 97.10 0.91 35.31 6.13 46.15 4.08 63.23 2.38 61.77 1.89Bioturbated Sand 0.36 0.36 1.23 0.50 1.04 0.83 0.21 0.14 0.21 0.14 0.00 0.00Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 0.12 0.12 0.00 0.00 2.40 1.04 1.04 0.45 0.10 0.10 0.10 0.10OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.12 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.31 0.23 0.10 0.10TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Zone of InfluenceSite 12BSite 10A Site 10B Site 11A Site 11B Site 12A

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.11 0.11 0.10 0.10 0.00 0.00 0.10 0.10 0.00 0.00 0.52 0.36Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.42 0.42 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.83 0.50 0.00 0.00 0.00 0.00 0.00 0.00 0.31 0.31Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 1.15 0.60 0.00 0.00 0.63 0.63Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.33 0.33 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 1.00 0.35 0.52 0.20 0.22 0.15 0.83 0.43 2.08 0.52 1.88 0.41Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.31 0.31 0.00 0.00Rubble 0.00 0.00 0.00 0.00 0.00 0.00 0.21 0.14 0.00 0.00 0.00 0.00Shell Grit 8.59 2.81 9.17 2.53 51.79 6.79 14.48 1.91 1.35 0.53 3.44 1.28Sand 83.37 3.38 53.75 7.26 27.79 7.34 80.10 2.04 91.67 1.25 61.56 8.91Bioturbated Sand 1.79 0.36 0.21 0.14 0.67 0.27 1.35 0.53 1.98 0.42 1.46 0.47Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 10.04 6.46 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 4.69 2.03 35.42 7.80 9.38 4.55 1.67 0.67 2.08 0.90 30.10 9.75OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.10 0.10 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 1Site 13A Site 13B Site 14A Site 14B Site 15A Site 15B

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.91 0.62 0.00 0.00 0.36 0.26 0.00 0.00 0.11 0.11Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.24 0.16 1.69 0.85 0.11 0.11 0.36 0.26 0.00 0.00 2.12 1.02Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.26 0.18 0.00 0.00 0.00 0.00 0.22 0.22 0.00 0.00BRYOZOABryozoan 0.12 0.12 0.13 0.13 0.33 0.33 0.24 0.24 0.00 0.00 0.22 0.15ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00 0.45 0.34SUBSTRATUM Burrow 0.48 0.27 0.91 0.30 4.13 0.53 0.60 0.28 1.00 0.42 0.11 0.11Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.24 0.16 1.04 0.44 0.11 0.11 0.60 0.33 0.22 0.15 1.23 1.00Shell Grit 23.08 2.42 22.53 3.72 28.91 3.81 12.74 3.04 93.75 3.16 43.75 11.43Sand 72.96 2.13 64.97 2.86 62.72 3.43 80.05 3.74 4.24 2.76 50.56 10.78Bioturbated Sand 1.56 0.64 6.12 1.94 3.35 0.77 4.93 1.00 0.22 0.22 0.45 0.26Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.12 0.12 0.00 0.00 0.00 0.00QUALITY Poor Quality 1.32 0.39 1.43 0.30 0.00 0.00 0.00 0.00 0.33 0.18 0.67 0.32OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00 0.33 0.24TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 1Site 18BSite 16A Site 16B Site 17A Site 17B Site 18A

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.56 0.45 1.00 1.00 0.00 0.00 3.85 3.74 0.00 0.00 1.04 0.71Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 1.12 0.76 0.56 0.56 0.00 0.00 0.21 0.21 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.33 0.33 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 2.90 0.75 1.67 0.58 0.78 0.22 0.73 0.43 0.13 0.13 1.35 0.40Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.13 0.13 0.00 0.00Rubble 0.22 0.15 0.11 0.11 0.00 0.00 0.31 0.31 0.00 0.00 0.10 0.10Shell Grit 13.50 1.55 23.44 8.80 0.00 0.00 0.00 0.00 0.26 0.26 0.63 0.37Sand 77.79 1.93 60.71 10.78 51.56 10.13 92.71 3.78 98.57 0.45 91.77 2.96Bioturbated Sand 2.57 0.63 5.58 1.45 11.05 2.90 1.88 0.49 0.91 0.36 2.81 0.70Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 0.56 0.21 6.92 6.23 36.61 12.26 0.10 0.10 0.00 0.00 2.29 2.29OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.33 0.18 0.00 0.00 0.00 0.00 0.21 0.21 0.00 0.00 0.00 0.00TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 2Site 19A Site 19B Site 20A Site 20B Site 21A Site 21B

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Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.

CNIDARIAAnemone 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.52 0.52 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.42 0.32 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.63 0.43 0.52 0.25 0.31 0.23 0.10 0.10 0.00 0.00 0.00 0.00Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Organic Debris 0.21 0.14 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.21 0.14 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00Shell Grit 0.21 0.14 0.73 0.34 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sand 93.44 2.01 97.50 0.74 90.52 6.50 82.92 7.62 0.00 0.00 6.67 6.67Bioturbated Sand 4.38 1.77 0.83 0.45 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Algal Mat on Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 0.31 0.31 0.00 0.00 9.06 6.52 16.98 7.63 100.00 0.00 93.33 6.67OTHER Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOWShadow 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00

Control 2Site 24BSite 22A Site 22B Site 23A Site 23B Site 24A

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2. CPCe summary data collected from offshore of Darwin Harbour during the baseline sampling phase (May to July 2012).

Category

Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.42 0.42 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.33 0.18 0.22 0.15 0.43 0.17 0.00 0.00 0.42 0.32 0.20 0.14Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.22 0.15 0.11 0.11 0.17 0.12 0.22 0.15 0.31 0.23 0.68 0.32Sand 91.85 1.73 96.09 1.19 92.97 1.41 96.54 0.88 96.15 1.82 94.32 1.20Shell Grit 0.45 0.34 2.12 0.99 0.69 0.38 0.45 0.26 0.21 0.14 2.45 0.74Bioturbated Sand 6.25 1.52 1.23 0.50 1.82 0.34 1.23 0.57 1.56 1.09 2.06 0.68PORIFERASponge 0.00 0.00 0.00 0.00 1.39 1.39 0.78 0.78 0.94 0.74 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.20 0.20ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00QUALITY Poor Quality 0.89 0.61 0.11 0.11 2.43 0.76 0.67 0.27 0.00 0.00 0.00 0.00OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.09 0.09 0.00 0.00 0.00 0.00 0.10 0.10FISH MOBILE Fish Mobile 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.20 0.20

Site 1A Site 1B Site 2A Site 2B Site 3A Site 3BSpoil Disposal Area

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.24 0.16 0.24 0.17 0.26 0.18 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.26 0.26 0.28 0.28 0.78 0.78 0.00 0.00Sea Fan 0.00 0.00 0.98 0.98 0.26 0.26 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.12 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.36 0.36 0.00 0.00 0.00 0.00 0.09 0.09 0.22 0.22 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.24 0.16 0.00 0.00 0.13 0.13 0.92 0.27 0.22 0.15 0.39 0.23Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.33 0.24 0.00 0.00Rubble 2.40 1.48 0.36 0.19 3.52 2.03 1.01 0.30 1.79 0.56 2.15 0.70Sand 87.50 2.17 94.83 2.40 87.63 4.15 84.93 2.18 88.84 1.65 87.11 1.78Shell Grit 4.81 1.34 0.00 0.00 6.25 1.94 3.22 0.70 4.02 1.02 5.66 1.26Bioturbated Sand 1.80 0.66 2.11 1.29 0.91 0.41 4.87 0.82 1.67 0.42 3.61 1.02PORIFERASponge 0.24 0.24 0.12 0.12 0.00 0.00 0.09 0.09 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.24 0.24 0.12 0.12 0.13 0.13 0.55 0.40 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.12 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00QUALITY Poor Quality 1.80 0.46 0.00 0.00 0.39 0.28 2.67 1.02 2.01 0.42 0.88 0.43OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.12 0.12 1.23 0.71 0.26 0.26 1.38 0.67 0.00 0.00 0.20 0.13FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 2.28 0.46 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Site 4A Site 4BSpoil Disposal Area

Site 5A Site 5B Site 6A Site 6B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.12 0.12 0.78 0.61 0.00 0.00 0.00 0.00 0.00 0.00 0.61 0.51Sea Fan 0.12 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.78 0.78 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.12 0.12 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.36 0.26 0.49 0.24 0.63 0.30 0.00 0.00 0.00 0.00 0.10 0.10Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.20 0.20Rubble 2.04 1.08 1.37 0.68 0.52 0.20 1.56 0.61 1.23 0.68 1.13 0.44Sand 87.86 2.36 79.79 2.47 86.88 2.44 84.51 1.57 85.27 2.00 95.59 1.13Shell Grit 0.60 0.33 11.43 1.65 8.44 2.25 9.38 1.15 5.92 1.28 0.40 0.23Bioturbated Sand 4.69 1.52 4.00 1.10 2.81 0.55 1.82 0.46 4.80 1.23 1.46 0.78PORIFERASponge 0.24 0.16 0.00 0.00 0.10 0.10 0.00 0.00 0.22 0.22 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00QUALITY Poor Quality 0.12 0.12 0.98 0.35 0.52 0.33 2.47 0.62 2.46 0.42 0.00 0.00OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 3.73 1.23 0.39 0.27 0.00 0.00 0.26 0.26 0.00 0.00 0.51 0.33FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 4.59 0.48

Zone of Impact (Near)Site 1A Site 1B Site 2A Site 2B Site 3A Site 3B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.12 0.12 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.20 0.20 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10Macroalgae 0.29 0.16 0.00 0.00 0.00 0.00 0.29 0.29 0.00 0.00 0.10 0.10Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.39 0.30SUBSTRATUM Burrow 0.39 0.30 0.29 0.16 0.21 0.14 0.20 0.14 0.97 0.33 0.88 0.28Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.20 0.13Rubble 1.27 0.54 0.49 0.31 0.31 0.23 1.09 0.70 0.24 0.16 1.07 0.49Sand 87.79 1.61 82.71 1.95 91.77 1.04 95.62 1.42 94.90 1.33 74.22 2.50Shell Grit 6.15 1.13 6.05 1.28 3.23 0.60 0.50 0.24 0.60 0.33 14.26 2.16Bioturbated Sand 2.44 0.71 9.67 1.65 3.02 0.83 0.10 0.10 2.08 1.01 8.20 1.26PORIFERASponge 0.68 0.51 0.00 0.00 0.00 0.00 0.30 0.30 0.24 0.16 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.20 0.20 0.00 0.00 0.00 0.00 0.24 0.24 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.20 0.20 0.00 0.00 0.10 0.10QUALITY Poor Quality 0.59 0.40 0.39 0.39 1.25 0.41 0.40 0.27 0.00 0.00 0.39 0.30OTHER Soft Coral 0.00 0.00 0.00 0.00 0.10 0.10 0.10 0.10 0.00 0.00 0.10 0.10Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.10 0.10 0.20 0.20 0.10 0.10 0.91 0.33 0.61 0.38 0.00 0.00FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 2.34 0.43 1.20 0.51 0.00 0.00

Zone of Impact (Near)Site 4BSite 4A Site 5A Site 5B Site 6A Site 6B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.89 0.89 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 1.74 1.31 0.33 0.33 0.00 0.00 0.00 0.00 1.01 0.38 1.19 0.43Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.29 0.29 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.78 0.29 0.22 0.15 0.20 0.13 0.59 0.20 0.28 0.15 0.28 0.15Gravel 0.35 0.35 0.00 0.00 0.29 0.16 0.68 0.59 0.00 0.00 0.00 0.00Rubble 0.17 0.12 0.22 0.22 0.39 0.39 0.78 0.38 0.28 0.20 0.37 0.29Sand 77.24 3.47 80.69 2.74 82.52 3.12 70.41 7.38 77.57 3.64 77.30 6.37Shell Grit 12.07 3.42 10.16 2.26 11.91 2.85 22.46 7.60 9.38 2.39 14.98 6.47Bioturbated Sand 5.56 1.71 4.91 1.20 2.64 1.17 3.32 0.93 8.82 2.00 5.15 1.24PORIFERASponge 0.09 0.09 0.00 0.00 0.00 0.00 0.00 0.00 0.09 0.09 0.00 0.00BRYOZOABryozoan 0.17 0.12 0.11 0.11 0.49 0.34 0.20 0.13 1.01 0.60 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.10 0.10 0.10 0.10 0.28 0.15 0.37 0.17QUALITY Poor Quality 1.83 0.70 2.46 0.80 1.46 0.42 1.17 0.33 1.29 1.19 0.18 0.18OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.18 0.13FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.09 0.09 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Site 1A Site 1B Site 2A Site 2B Site 3A Site 3BZone of Impact (Far)

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.22 0.22 0.00 0.00Hydroid 0.21 0.14 0.00 0.00 0.39 0.23 0.00 0.00 0.00 0.00 0.31 0.31Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.67 0.56 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.21 0.21 0.11 0.11 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 1.15 0.52 0.73 0.30 0.39 0.17 1.05 0.43 1.46 0.58 0.00 0.00Gravel 1.35 0.82 1.46 1.14 1.27 0.67 5.52 2.52 1.57 0.73 1.77 1.26Rubble 0.42 0.18 0.94 0.30 1.07 0.68 2.09 0.76 1.67 1.00 1.35 0.48Sand 83.44 2.20 88.85 1.70 92.29 2.08 80.05 3.38 80.98 3.52 74.27 5.84Shell Grit 10.00 1.93 5.83 1.58 2.25 0.87 7.21 1.48 11.63 3.79 21.35 6.07Bioturbated Sand 2.60 0.71 1.46 0.39 0.39 0.23 1.26 0.49 0.67 0.39 0.73 0.30PORIFERASponge 0.10 0.10 0.31 0.31 0.00 0.00 0.53 0.37 0.45 0.34 0.21 0.21BRYOZOABryozoan 0.00 0.00 0.21 0.21 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.21 0.14 0.00 0.00 0.32 0.23 0.11 0.11 0.00 0.00QUALITY Poor Quality 0.21 0.21 0.00 0.00 1.95 0.39 1.46 0.58 0.11 0.11 0.00 0.00OTHER Soft Coral 0.31 0.23 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.21 0.14 0.00 0.00 0.00 0.00 0.32 0.32 0.34 0.18 0.00 0.00FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 0.21 0.14 0.45 0.26 0.00 0.00

Zone of Impact (Far)Site 4BSite 4A Site 5A Site 5B Site 6A Site 6B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.89 0.89 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.45 0.31 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.94 0.94 0.49 0.49 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.10 0.10 0.00 0.00 0.00 0.00 0.00 0.00 0.07 0.07 0.00 0.00Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sand 89.68 6.55 95.56 2.36 0.00 0.00 0.00 0.00 54.32 10.56 38.33 11.88Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Bioturbated Sand 1.36 0.53 1.23 0.42 0.00 0.00 0.00 0.00 0.74 0.33 0.31 0.17PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.60 0.45 1.35 1.07BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 6.98 6.65 0.74 0.45 100.00 0.00 100.00 0.00 39.58 10.23 46.15 11.51OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.94 0.94 1.97 1.97 0.00 0.00 0.00 0.00 3.35 1.47 13.85 4.98FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.21 0.21 0.16 0.11 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 1Site 1A Site 1B Site 2A Site 2B Site 3A Site 3B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.10 0.10ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 2.50 2.50 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sand 31.41 13.58 7.14 5.30 21.56 9.66 0.00 0.00 7.21 7.21 0.00 0.00Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Bioturbated Sand 0.00 0.00 0.00 0.00 0.10 0.10 0.00 0.00 0.48 0.48 0.00 0.00PORIFERASponge 0.00 0.00 0.67 0.67 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 63.28 15.25 82.81 6.89 66.88 10.72 96.99 1.15 85.82 9.23 96.15 2.38OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 2.81 1.93 9.38 3.26 11.46 4.58 3.01 1.15 6.49 5.85 3.65 2.31FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 1Site 4A Site 5A Site 5B Site 6A Site 6BSite 4B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 23.66 9.38 5.94 4.05Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.31 0.31 0.11 0.11 0.11 0.11 0.00 0.00 0.00 0.00Sand 93.01 1.23 96.04 1.38 95.76 1.67 95.87 1.68 24.67 10.07 30.73 10.46Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Bioturbated Sand 1.01 0.40 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 5.88 1.34 2.60 1.41 3.79 1.59 3.91 1.55 51.67 13.50 63.33 12.12OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.11 0.11 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.09 0.09 1.04 0.54 0.22 0.22 0.00 0.00 0.00 0.00 0.00 0.00FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 2Site 3A Site 3BSite 1A Site 1B Site 2A Site 2B

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Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E. Mean S.E.CNIDARIAHard Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Hydroid 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Fan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sea Whip 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ALGAEAlgal Mat on Sand 19.89 6.96 14.58 5.65 0.00 0.00 0.00 0.00 0.20 0.20 0.00 0.00Filamentous Algae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Macroalgae 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wrack 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00SUBSTRATUM Burrow 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Gravel 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Rubble 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Sand 70.17 9.52 83.27 5.38 22.24 11.73 0.00 0.00 98.05 0.42 96.67 0.79Shell Grit 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Bioturbated Sand 0.85 0.85 0.00 0.00 0.00 0.00 0.00 0.00 1.17 0.33 0.73 0.53PORIFERASponge 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00BRYOZOABryozoan 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00ASCIDIACEAAscidian 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00QUALITY Poor Quality 9.09 9.09 2.15 1.02 77.04 11.94 100.00 0.00 0.49 0.24 2.60 0.62OTHER Soft Coral 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00Wormlike Phyla 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00INDETERMINATE Indeterminate 0.00 0.00 0.00 0.00 0.72 0.38 0.00 0.00 0.10 0.10 0.00 0.00FISH MOBILE Fish Mobile 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00TAPE, WAND, SHADOW Shadow 0.00 0.00 0.49 0.19 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Control 2Site 6A Site 6BSite 4A Site 4B Site 5A Site 5B

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APPENDIX D CPCE SUMMARY GRAPHS

Ichthys Nearshore Environmental

Monitoring Program

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1. CPCe summary graphs for inshore sites sampled during the baseline sampling phase (May to July 2012).

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2. CPCe summary graphs for offshore sites sampled during the baseline sampling phase (May to July 2012).

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APPENDIX E PERMANOVA RESULTS

Ichthys Nearshore Environmental

Monitoring Program

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Appendix E. Permutational Analysis of Variance of CPCe percent cover/infaunal assemblages sampled during the baseline sampling phase (May to July 2012). P-values highlighted in bold are significant. RED = Redundant term. A term becomes redundant if a lower order interaction including that term is significant. Res = Residual. This term is a measure of the variation in the data not explained by the variation attributed to the main factors in the experimental model (i.e. location, site, transect). 1. CPCe (inshore)

Source df SS MS Pseudo-F P(perm) Location 3 90771 30257 2.6052 0.0152 Site(Lo) 19 2.22E+05 11662 4.6983 0.0002 Transect(Si(Lo)) 23 57105 2482.8 6.8389 0.0002 Res 602 2.19E+05 363.05 Total 647 5.90E+05

2. Infauna (inshore)

Source df SS MS Pseudo-F P(perm) Location 3 19141 6380.5 1.0667 0.3202 Site(Lo) 20 1.20E+05 5981.4 3.1036 0.0002 Res 96 1.85E+05 1927.3 Total 119 3.24E+05

3. CPCe (offshore)

Source df SS MS Pseudo-F P(perm) Location 4 24471 6117.8 4.9581 0.0002 Site(Lo) 24 35735 1489 1.829 0.0126 Tra(Si(Lo)) 27 23222 860.07 4.1601 0.0002 Res 686 1.42E+05 206.74 Total 741 2.29E+05

4. Infauna (offshore)

Source df SS MS Pseudo-F P(perm) Location 4 36634 9158.4 2.6605 0.0002 Site(Location) 24 82616 3442.4 1.757 0.0002 Res 116 2.27E+05 1959.2 Total 144 3.47E+05

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APPENDIX F PAIR WISE TEST RESULTS

Ichthys Nearshore Environmental

Monitoring Program

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Appendix F. Pairwise tests of epifaunal and infaunal assemblages for significant terms. Significant results in bold. 1. CPCe inshore (for significant term ‘location’) Groups t P(perm) ZoMI, ZoI 0.9028 0.403 ZoMI, Control 1 2.2195 0.0078 ZoMi, Control 2 0.85053 0.683 ZoI, Control 1 1.6197 0.0596 ZoI, Control 2 1.249 0.3154 Control 1, Control 2 2.1322 0.0332

2. Infauna inshore (for significant term ‘site’) Within level 'Zone of Moderate Impact' of factor 'Location'

Groups t P(perm) 1, 2 1.4994 0.0066 1, 3 2.2542 0.0092 1, 4 1.7181 0.031 1, 5 1.798 0.0082 1, 6 2.5742 0.0084 2, 3 1.8811 0.009 2, 4 1.5788 0.0254 2, 5 1.3768 0.0774 2, 6 2.2631 0.0064 3, 4 2.3922 0.0096 3, 5 2.608 0.0092 3, 6 2.7115 0.0076 4, 5 1.2675 0.0828 4, 6 2.3307 0.0084 5, 6 2.3835 0.0072

Within level 'Zone of Influence' of factor 'Location'

Groups t P(perm) 7, 8 1.9212 0.0086 7, 9 2.065 0.0072 7, 10 2.1358 0.0086 7, 11 2.5159 0.009 7, 12 2.2786 0.006 8, 9 1.8634 0.0058 8, 10 1.5534 0.0166 8, 11 2.1543 0.007 8, 12 1.9378 0.008 9, 10 1.7663 0.0072 9, 11 2.1601 0.0092 9, 12 2.0117 0.0096 10, 11 2.4925 0.0064 10, 12 1.9187 0.0172 11, 12 1.5488 0.0204

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Within level 'Control 1' of factor 'Location'

Groups t P(perm) 13, 14 1.3487 0.0532 13, 15 1.0175 0.3746 13, 16 1.4359 0.0418 13, 17 1.5324 0.0272 13, 18 1.6078 0.018 14, 15 1.322 0.063 14, 16 0.99581 0.51 14, 17 1.3063 0.048 14, 18 1.0149 0.358 15, 16 1.6523 0.0074 15, 17 1.8042 0.0072 15, 18 1.7435 0.0192 16, 17 0.80152 0.8668 16, 18 1.1453 0.1704 17, 18 1.1358 0.2128

Within level 'Control 2' of factor 'Location'

Groups t P(perm) 19, 20 1.4479 0.008 19, 21 1.7405 0.0098 19, 22 1.2803 0.0616 19, 23 1.7529 0.0088 19, 24 2.1058 0.0088 20, 21 1.4636 0.0074 20, 22 1.065 0.2548 20, 23 1.1686 0.1624 20, 24 1.9902 0.0094 21, 22 1.387 0.0372 21, 23 1.4849 0.011 21, 24 1.6411 0.0088 22, 23 1.0796 0.2262 22, 24 1.7806 0.0088 23, 24 1.8692 0.0084

3. CPCe offshore (for significant ‘location’) Groups t P(perm) Spoil Disposal Area, ZoI (Near) 1.8959 0.0754 Spoil Disposal Area, ZoI (Far) 3.6987 0.0036 Spoil Disposal Area, Control 1 2.9039 0.0074 Spoil Disposal Area, Control 2 1.8553 0.0608 ZoI (Near), ZoI (Far) 2.2842 0.0224 ZoI (Near), Control 1 2.9286 0.0024 ZoI (Near), Control 2 2.2088 0.01 ZoI (Far), Control 1 2.7481 0.0028 ZoI (Far), Control 2 2.7875 0.0002 Control 1, Control 2 1.6288 0.0862

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4. Infauna offshore (for significant term ‘location’) Groups t P(perm) Control 1, Control 2 1.1266 0.2218 Control 1, ZoI (Far) 1.8185 0.0064 Control 1, ZoI (Near) 1.5079 0.0086 Control 1, Spoil Disposal Area 1.28 0.0864 Control 2, ZoI (Far) 2.1492 0.002 Control 2, ZoI (Near) 2.0261 0.0024 Control 2, Spoil Disposal Area 1.6097 0.0158 ZoI (Far), ZoI (Near) 1.4635 0.0182 ZoI (Far), Spoil Disposal Area 1.6603 0.0018 ZoI (Near), Spoil Disposal Area 1.168 0.1602

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APPENDIX G SIMPER RESULTS

Ichthys Nearshore Environmental

Monitoring Program

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Appendix G. Results of SIMPER analyses of epifauna and infauna assemblages sampled during the baseline sampling phase (May to July 2012). Cut off for percentage contribution is 90 %. Only SIMPER results for significant terms are presented.

1. CPCe inshore (for the significant term ‘location’)

Groups ZoMI & Control 1Average dissimilarity = 38.11

Group ZoMI Group Control 1Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 79.99 61.91 15.8 1 41.45 41.45Shell Grit 2.52 26.13 12.94 0.86 33.94 75.39Algal Mat on Sand 6.57 0.21 3.51 0.48 9.21 84.6Bioturbated Sand 4.97 1.95 2.64 0.76 6.92 91.52

Groups ZoI & Control 1Average dissimilarity = 42.73

Group ZoI Group Control 1Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 72.68 61.91 17 1.13 39.79 39.79Shell Grit 7.06 26.13 13.63 0.9 31.89 71.68Algal Mat on Sand 15.53 0.21 8.17 0.71 19.12 90.81

Groups Control 1 & Control 2Average dissimilarity = 36.62

Group Control 1 Group Control 2Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 61.91 87.51 18.46 1.05 50.42 50.42Shell Grit 26.13 3.94 13.62 0.88 37.2 87.62Bioturbated Sand 1.95 3.1 1.95 0.69 5.33 92.95

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2. CPCe offshore (for the significant term ‘location’)

Groups Spoil Disposal Area & Control 1Average dissimilarity = 16.49

Group Spoil Disposal Area Group Control 1 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 91.54 85.19 11.34 0.54 68.74 68.74Bioturbated Sand 2.48 1.07 1.44 0.78 8.73 77.47Shell Grit 2.48 0 1.36 0.62 8.28 85.74Sponge 0.32 0.63 0.61 0.3 3.7 89.44Rubble 1.03 0 0.57 0.37 3.43 92.87

Groups ZoI (Near) & Control 1Average dissimilarity = 19.49

Group ZoI (Near) Group Control 1 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 87.16 85.19 12.03 0.62 61.71 61.71Shell Grit 5.66 0 3.1 0.83 15.93 77.64Bioturbated Sand 3.81 1.07 2.06 0.82 10.56 88.2Rubble 1.02 0 0.56 0.46 2.87 91.07

Groups ZoI (Far) & Control 1Average dissimilarity = 25.22

Group ZoI (Far) Group Control 1 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 80.37 85.19 13.85 0.74 54.92 54.92Shell Grit 11.64 0 6.39 0.68 25.33 80.25Bioturbated Sand 3.23 1.07 1.83 0.69 7.26 87.51Gravel 1.15 0 0.63 0.29 2.49 90

Groups ZoI (Near) & Control 2Average dissimilarity = 16.64

Group ZoI (Near) Group Control 2 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 87.16 89.65 7.37 0.96 44.29 44.29Algal Mat on Sand 0.09 6.58 3.38 0.37 20.34 64.63Shell Grit 5.66 0 2.89 0.86 17.38 82.01Bioturbated Sand 3.81 0.42 1.95 0.83 11.7 93.72

Groups ZoI (Far) & Control 2Average dissimilarity = 22.64

Group ZoI (Far) Group Control 2 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Sand 80.37 89.65 9.76 1.02 43.11 43.11Shell Grit 11.64 0 5.95 0.7 26.3 69.42Algal Mat on Sand 0.05 6.58 3.37 0.37 14.87 84.29Bioturbated Sand 3.23 0.42 1.69 0.67 7.45 91.74

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3. Infauna offshore (for the significant term ‘location’)

Groups Control 1 & Control 2Average dissimilarity = 75.66

Group Control 1 Group Control 2 Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 8.32 23.2 13.98 1.19 18.48 18.48Spionidae 4.8 2.57 4.36 0.82 5.77 24.25Maldanidae 5 1.87 3.83 0.99 5.06 29.31Apseudidae 3.4 4.37 3.38 1.16 4.47 33.78Capitellidae 3.56 2.27 3.32 0.98 4.39 38.17Nephtyidae 2.32 1.57 2.17 0.92 2.87 41.03Ampharetidae 1.68 2.2 2.14 1.03 2.83 43.87Copepoda 1.2 1.97 2.12 0.75 2.81 46.67Nemertea 1.92 1.23 1.85 0.95 2.45 49.12Nuculanidae 1 1.47 1.68 0.8 2.23 51.35Sabellariidae 1 0.83 1.63 0.45 2.15 53.5Onuphidae 1.44 1.73 1.62 0.99 2.14 55.64Tellinidae 0.92 1.23 1.54 0.52 2.04 57.67Ophiuroidea 1.16 1.43 1.47 0.93 1.94 59.61Terebellidae 1.76 0.57 1.41 0.76 1.87 61.48Glyceridae 0.92 0.8 1.19 0.68 1.57 63.05Cirratulidae 1.08 1.03 1.18 0.85 1.55 64.6Galeommatidae 0.48 0.97 1.08 0.72 1.43 66.03Opheliidae 0.52 0.77 0.95 0.51 1.25 67.28Cypridinidae/Rutidermatidae 0.6 0.97 0.94 0.64 1.24 68.53Ampeliscidae 0.44 1.2 0.9 0.77 1.2 69.72Nereididae 0.4 0.7 0.9 0.61 1.2 70.92Magelonidae 0.8 0.67 0.9 0.72 1.19 72.1Pisionidae 0.64 0.8 0.82 0.63 1.09 73.19Phyllodocidae 0.92 0.2 0.79 0.54 1.05 74.24Sipuncula 0.68 0.6 0.76 0.79 1.01 75.25Eunicidae 0.92 0.33 0.72 0.81 0.95 76.19Trichobranchidae 1.04 0.23 0.71 0.62 0.94 77.13Veneridae 0.16 1.03 0.68 0.43 0.89 78.02Syllidae 1.08 0.23 0.66 0.65 0.88 78.9Anthuridae 0.68 0.23 0.66 0.48 0.87 79.77Orbiniidae 0.72 0.23 0.64 0.59 0.84 80.62Lumbrineridae 0.56 0.27 0.52 0.66 0.69 81.3Bryozoa 0.44 0.17 0.51 0.61 0.68 81.98Pectinariidae 0.4 0.4 0.5 0.6 0.66 82.64Bodotriidae 0.4 0.23 0.49 0.56 0.65 83.29Poecilochaetidae 0.24 0.37 0.48 0.5 0.63 83.93Platyischnopidae 0 0.47 0.47 0.27 0.62 84.54Paraonidae 0.28 0.4 0.41 0.61 0.54 85.08Oenonidae 0.36 0.27 0.38 0.6 0.5 85.58Nematoda 0.24 0.3 0.36 0.41 0.47 86.05Podoceridae 0.32 0.3 0.35 0.45 0.46 86.51Liljeborgiidae 0.36 0.17 0.35 0.51 0.46 86.96Scalibregmatidae 0.12 0.13 0.33 0.23 0.43 87.39Balanidae 0.12 0.2 0.32 0.33 0.42 87.82Iravadiidae 0.12 0.1 0.32 0.3 0.42 88.23Leptocheliidae 0.4 0.1 0.3 0.5 0.39 88.63Chaetognatha 0.08 0.23 0.3 0.33 0.39 89.02Cylindroleberidae 0.12 0.27 0.29 0.33 0.39 89.41Melitidae 0.2 0.13 0.27 0.37 0.36 89.76Phoxocephalidae 0.16 0.27 0.27 0.52 0.35 90.12

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Groups Control 1 & ZoI (Far)Average dissimilarity = 73.14

Group Control 1 Group ZoI (Far) Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Apseudidae 3.4 8.23 5.91 0.88 8.08 8.08Aoridae/Isaeidae/Photidae 8.32 6.83 5.6 1.17 7.66 15.74Leptocheliidae 0.4 7.4 5.57 1.02 7.61 23.35Spionidae 4.8 2.6 3.44 0.9 4.7 28.05Capitellidae 3.56 4.37 3.12 1.22 4.27 32.32Maldanidae 5 1.8 3.06 1 4.18 36.51Ampeliscidae 0.44 3.13 2.29 1.08 3.13 39.64Ampharetidae 1.68 3.17 2.27 1.04 3.1 42.73Syllidae 1.08 2.33 1.88 1.04 2.57 45.3Nephtyidae 2.32 1.67 1.83 0.97 2.5 47.8Nemertea 1.92 1.4 1.63 0.99 2.23 50.03Sabellidae 0.2 1.97 1.5 0.97 2.05 52.07Terebellidae 1.76 1.43 1.42 0.96 1.95 54.02Eunicidae 0.92 1.7 1.39 0.9 1.9 55.92Nereididae 0.4 1.9 1.38 0.64 1.89 57.81Cirratulidae 1.08 1.63 1.29 0.92 1.76 59.57Magelonidae 0.8 1.07 1.14 0.72 1.56 61.13Ophiuroidea 1.16 0.93 1.12 0.92 1.54 62.66Lumbrineridae 0.56 1.37 1.07 0.91 1.47 64.13Copepoda 1.2 0.77 1.06 0.8 1.45 65.59Nuculanidae 1 0.6 1.06 0.76 1.45 67.04Onuphidae 1.44 0.63 1.06 0.85 1.44 68.48Sabellariidae 1 0.2 0.98 0.4 1.34 69.82Glyceridae 0.92 1.03 0.91 1.04 1.24 71.07Tellinidae 0.92 0.3 0.87 0.48 1.19 72.25Galeommatidae 0.48 0.8 0.86 0.67 1.18 73.43Phyllodocidae 0.92 0.37 0.75 0.65 1.03 74.46Trichobranchidae 1.04 0.37 0.72 0.7 0.98 75.44Cypridinidae/Rutidermatidae 0.6 0.67 0.69 0.53 0.95 76.39Pisionidae 0.64 0.47 0.68 0.63 0.93 77.32Anthuridae 0.68 0.53 0.68 0.65 0.93 78.25Sipuncula 0.68 0.6 0.67 0.86 0.91 79.17Orbiniidae 0.72 0.43 0.63 0.74 0.87 80.03Paraonidae 0.28 0.67 0.63 0.78 0.87 80.9Liljeborgiidae 0.36 0.67 0.63 0.68 0.86 81.76Nematoda 0.24 0.67 0.54 0.69 0.74 82.5Oligochaeta 0.24 0.37 0.48 0.48 0.65 83.15Bodotriidae 0.4 0.33 0.47 0.66 0.64 83.8Goniadidae 0.36 0.5 0.46 0.51 0.63 84.43Tanaidae 0 0.67 0.43 0.67 0.59 85.02Poecilochaetidae 0.24 0.37 0.4 0.61 0.55 85.57Bryozoa 0.44 0.27 0.4 0.76 0.54 86.11Hesionidae 0.24 0.4 0.37 0.6 0.5 86.61Opheliidae 0.52 0.1 0.37 0.55 0.5 87.11Oenonidae 0.36 0.23 0.34 0.61 0.46 87.57Serolidae 0 0.33 0.33 0.18 0.45 88.02Veneridae 0.16 0.37 0.3 0.43 0.42 88.44Melitidae 0.2 0.2 0.29 0.3 0.4 88.84Carditidae 0.04 0.33 0.29 0.55 0.39 89.24Caprellidae 0.12 0.3 0.29 0.51 0.39 89.63Sigalionidae 0.16 0.27 0.28 0.5 0.39 90.01

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Groups Control 2 & ZoI (Far)Average dissimilarity = 76.79

Group Control 2 Group ZoI (Far) Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 23.2 6.83 11.55 1.07 15.05 15.05Apseudidae 4.37 8.23 6.01 0.85 7.83 22.87Leptocheliidae 0.1 7.4 5.6 1.01 7.29 30.16Capitellidae 2.27 4.37 3.07 1.1 4 34.16Ampeliscidae 1.2 3.13 2.4 1.06 3.13 37.29Ampharetidae 2.2 3.17 2.4 1.07 3.13 40.42Spionidae 2.57 2.6 2.13 1.12 2.77 43.19Syllidae 0.23 2.33 1.8 0.92 2.34 45.53Maldanidae 1.87 1.8 1.77 0.95 2.31 47.84Nephtyidae 1.57 1.67 1.54 1 2.01 49.85Copepoda 1.97 0.77 1.54 0.74 2 51.85Sabellidae 0.07 1.97 1.51 0.95 1.97 53.82Nereididae 0.7 1.9 1.47 0.69 1.92 55.74Nemertea 1.23 1.4 1.35 0.91 1.76 57.5Eunicidae 0.33 1.7 1.29 0.79 1.69 59.18Cirratulidae 1.03 1.63 1.25 0.89 1.63 60.82Nuculanidae 1.47 0.6 1.16 0.87 1.51 62.33Lumbrineridae 0.27 1.37 1.1 0.85 1.44 63.76Ophiuroidea 1.43 0.93 1.1 0.9 1.43 65.19Terebellidae 0.57 1.43 1.08 1.02 1.4 66.6Onuphidae 1.73 0.63 1.04 1.01 1.35 67.95Glyceridae 0.8 1.03 1.03 0.74 1.34 69.29Galeommatidae 0.97 0.8 1.02 0.69 1.33 70.62Magelonidae 0.67 1.07 1.02 0.64 1.33 71.94Cypridinidae/Rutidermatidae 0.97 0.67 0.94 0.59 1.22 73.17Tellinidae 1.23 0.3 0.87 0.65 1.14 74.3Veneridae 1.03 0.37 0.73 0.51 0.95 75.25Paraonidae 0.4 0.67 0.67 0.77 0.88 76.13Opheliidae 0.77 0.1 0.65 0.44 0.85 76.97Sipuncula 0.6 0.6 0.63 0.78 0.82 77.8Sabellariidae 0.83 0.2 0.62 0.47 0.81 78.61Pisionidae 0.8 0.47 0.62 0.64 0.81 79.42Nematoda 0.3 0.67 0.57 0.61 0.74 80.16Liljeborgiidae 0.17 0.67 0.54 0.57 0.7 80.87Tanaidae 0.07 0.67 0.45 0.68 0.59 81.45Oligochaeta 0.13 0.37 0.43 0.4 0.55 82Bodotriidae 0.23 0.33 0.42 0.52 0.55 82.55Orbiniidae 0.23 0.43 0.42 0.62 0.54 83.1Poecilochaetidae 0.37 0.37 0.41 0.55 0.54 83.63Anthuridae 0.23 0.53 0.41 0.78 0.53 84.17Trichobranchidae 0.23 0.37 0.4 0.53 0.51 84.68Platyischnopidae 0.47 0 0.39 0.27 0.5 85.19Phyllodocidae 0.2 0.37 0.34 0.7 0.45 85.64Serolidae 0.03 0.33 0.34 0.18 0.44 86.07Hesionidae 0.13 0.4 0.33 0.57 0.43 86.51Goniadidae 0.07 0.5 0.33 0.48 0.43 86.93Bryozoa 0.17 0.27 0.3 0.56 0.39 87.32Phoxocephalidae 0.27 0.23 0.29 0.58 0.38 87.7Sternaspidae 0.2 0.23 0.29 0.55 0.37 88.07Melitidae 0.13 0.2 0.27 0.28 0.36 88.43Lysianassidae 0.17 0.23 0.27 0.52 0.36 88.78Cylindroleberidae 0.27 0.13 0.27 0.37 0.36 89.14Carditidae 0 0.33 0.27 0.51 0.35 89.49Oenonidae 0.27 0.23 0.27 0.54 0.35 89.84Sigalionidae 0.17 0.27 0.27 0.48 0.35 90.19

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Groups Control 1 & ZoI (Near)Average dissimilarity = 69.10

Group Control 1 Group ZoI (Near) Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 8.32 6.43 5.82 1.33 8.42 8.42Spionidae 4.8 3.33 3.58 1.02 5.17 13.59Maldanidae 5 3.13 3.46 1.14 5.01 18.61Apseudidae 3.4 4.47 3.37 1.4 4.87 23.48Ampeliscidae 0.44 3.23 2.74 0.59 3.97 27.44Capitellidae 3.56 3.13 2.61 1.31 3.78 31.22Nephtyidae 2.32 2.2 2.2 1.01 3.18 34.4Terebellidae 1.76 2.17 2.17 1.03 3.14 37.54Ampharetidae 1.68 2.57 2.1 1.21 3.03 40.57Nemertea 1.92 2.03 1.9 1.06 2.75 43.32Eunicidae 0.92 1.83 1.71 0.92 2.48 45.8Ophiuroidea 1.16 1.77 1.62 1.01 2.35 48.15Syllidae 1.08 1.67 1.53 1 2.21 50.36Leptocheliidae 0.4 1.7 1.43 1 2.07 52.43Nereididae 0.4 1.73 1.42 1.07 2.06 54.5Sabellidae 0.2 1.6 1.35 0.99 1.95 56.45Onuphidae 1.44 0.93 1.25 0.92 1.81 58.26Magelonidae 0.8 1.43 1.21 0.97 1.76 60.02Cirratulidae 1.08 1.27 1.18 1.08 1.71 61.73Sabellariidae 1 0.5 1.14 0.47 1.66 63.39Copepoda 1.2 0.73 1.11 0.8 1.61 65Nuculanidae 1 0.5 1.09 0.78 1.58 66.57Anthuridae 0.68 0.97 1.07 0.75 1.54 68.12Phyllodocidae 0.92 0.5 0.95 0.71 1.38 69.5Glyceridae 0.92 0.83 0.9 1.03 1.3 70.8Tellinidae 0.92 0.27 0.87 0.46 1.26 72.05Lumbrineridae 0.56 1 0.86 0.97 1.24 73.29Sipuncula 0.68 0.83 0.83 0.86 1.2 74.49Cypridinidae/Rutidermatidae 0.6 0.67 0.76 0.79 1.1 75.58Trichobranchidae 1.04 0.4 0.75 0.72 1.09 76.67Galeommatidae 0.48 0.5 0.75 0.68 1.08 77.75Pisionidae 0.64 0.33 0.62 0.63 0.9 78.65Orbiniidae 0.72 0.27 0.59 0.67 0.85 79.5Podoceridae 0.32 0.6 0.58 0.51 0.84 80.34Paraonidae 0.28 0.5 0.56 0.48 0.82 81.15Nematoda 0.24 0.5 0.54 0.72 0.79 81.94Caprellidae 0.12 0.57 0.54 0.76 0.79 82.73Liljeborgiidae 0.36 0.43 0.49 0.67 0.71 83.44Bryozoa 0.44 0.4 0.49 0.8 0.71 84.15Bodotriidae 0.4 0.23 0.41 0.7 0.6 84.75Opheliidae 0.52 0.13 0.4 0.62 0.58 85.32Poecilochaetidae 0.24 0.27 0.37 0.64 0.53 85.86Pectinariidae 0.4 0.13 0.35 0.57 0.51 86.37Goniadidae 0.36 0.17 0.35 0.43 0.51 86.88Pasiphaeidae 0.12 0.3 0.33 0.57 0.47 87.35Veneridae 0.16 0.3 0.31 0.35 0.44 87.79Oedicerotidae 0.12 0.27 0.29 0.48 0.42 88.21Cylindroleberidae 0.12 0.37 0.29 0.59 0.42 88.63Oenonidae 0.36 0.1 0.29 0.58 0.42 89.05Sarsiellidae 0 0.33 0.27 0.34 0.4 89.44Goneplacidae 0.2 0.13 0.27 0.43 0.39 89.84Sternaspidae 0.16 0.27 0.27 0.48 0.39 90.23

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Groups C2 & ZoI (Near)Average dissimilarity = 73.73

Group Control 2 Group ZoI (Near) Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 23.2 6.43 11.87 1.1 16.1 16.1Apseudidae 4.37 4.47 3.47 1.24 4.71 20.81Ampeliscidae 1.2 3.23 2.81 0.59 3.81 24.62Maldanidae 1.87 3.13 2.6 1.12 3.53 28.15Spionidae 2.57 3.33 2.52 1.35 3.42 31.58Capitellidae 2.27 3.13 2.49 1.11 3.37 34.95Ampharetidae 2.2 2.57 2.22 1.18 3.01 37.95Nephtyidae 1.57 2.2 1.92 0.97 2.6 40.56Terebellidae 0.57 2.17 1.83 0.85 2.49 43.04Eunicidae 0.33 1.83 1.66 0.82 2.25 45.29Copepoda 1.97 0.73 1.62 0.75 2.2 47.5Nemertea 1.23 2.03 1.62 0.95 2.2 49.7Ophiuroidea 1.43 1.77 1.57 0.96 2.13 51.82Leptocheliidae 0.1 1.7 1.48 0.97 2.01 53.83Nereididae 0.7 1.73 1.44 1.05 1.96 55.79Syllidae 0.23 1.67 1.4 0.87 1.9 57.69Sabellidae 0.07 1.6 1.39 0.96 1.89 59.57Onuphidae 1.73 0.93 1.23 1.02 1.67 61.24Nuculanidae 1.47 0.5 1.2 0.88 1.63 62.87Cirratulidae 1.03 1.27 1.16 1.04 1.58 64.44Magelonidae 0.67 1.43 1.09 0.93 1.48 65.92Cypridinidae/Rutidermatidae 0.97 0.67 0.98 0.74 1.33 67.26Glyceridae 0.8 0.83 0.98 0.68 1.33 68.58Galeommatidae 0.97 0.5 0.95 0.7 1.29 69.87Lumbrineridae 0.27 1 0.89 0.9 1.21 71.08Tellinidae 1.23 0.27 0.88 0.64 1.19 72.27Anthuridae 0.23 0.97 0.87 0.67 1.18 73.45Sabellariidae 0.83 0.5 0.87 0.64 1.17 74.62Sipuncula 0.6 0.83 0.79 0.79 1.07 75.7Veneridae 1.03 0.3 0.75 0.49 1.02 76.72Opheliidae 0.77 0.13 0.69 0.46 0.94 77.66Paraonidae 0.4 0.5 0.62 0.49 0.84 78.49Podoceridae 0.3 0.6 0.59 0.47 0.8 79.29Nematoda 0.3 0.5 0.58 0.63 0.79 80.08Phyllodocidae 0.2 0.5 0.57 0.56 0.78 80.86Pisionidae 0.8 0.33 0.56 0.67 0.76 81.62Caprellidae 0.13 0.57 0.51 0.72 0.69 82.31Trichobranchidae 0.23 0.4 0.43 0.53 0.58 82.89Bryozoa 0.17 0.4 0.42 0.68 0.57 83.46Platyischnopidae 0.47 0 0.41 0.27 0.55 84.02Cylindroleberidae 0.27 0.37 0.4 0.49 0.54 84.56Poecilochaetidae 0.37 0.27 0.39 0.57 0.53 85.08Liljeborgiidae 0.17 0.43 0.37 0.53 0.5 85.58Bodotriidae 0.23 0.23 0.35 0.52 0.48 86.06Orbiniidae 0.23 0.27 0.33 0.53 0.45 86.51Pasiphaeidae 0.1 0.3 0.33 0.55 0.44 86.95Pectinariidae 0.4 0.13 0.31 0.53 0.42 87.37Cirolanidae 0.17 0.23 0.31 0.53 0.42 87.79Sternaspidae 0.2 0.27 0.31 0.52 0.42 88.21Sarsiellidae 0.03 0.33 0.29 0.36 0.4 88.61Phoxocephalidae 0.27 0.17 0.29 0.49 0.39 89Oedicerotidae 0.17 0.27 0.29 0.47 0.39 89.39Laevidentaliidae 0.3 0.1 0.29 0.45 0.39 89.77Anthozoa: Actinaria 0.1 0.13 0.23 0.34 0.31 90.09

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Groups ZoI (Far) & ZoI (Near)Average dissimilarity = 63.11

Group ZoI (Far) Group ZoI (Near) Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Leptocheliidae 7.4 1.7 4.53 1.01 7.18 7.18Apseudidae 8.23 4.47 4.5 0.87 7.13 14.31Aoridae/Isaeidae/Photidae 6.83 6.43 4.35 1.14 6.9 21.21Ampeliscidae 3.13 3.23 2.6 0.73 4.12 25.33Capitellidae 4.37 3.13 2.54 1.13 4.03 29.36Ampharetidae 3.17 2.57 2.05 1.12 3.25 32.61Maldanidae 1.8 3.13 1.98 1.17 3.14 35.74Spionidae 2.6 3.33 1.82 1.18 2.88 38.63Syllidae 2.33 1.67 1.67 1.13 2.65 41.28Terebellidae 1.43 2.17 1.63 1.06 2.59 43.86Nereididae 1.9 1.73 1.62 0.9 2.57 46.43Eunicidae 1.7 1.83 1.58 1.02 2.5 48.93Nephtyidae 1.67 2.2 1.54 0.93 2.44 51.37Nemertea 1.4 2.03 1.52 1.04 2.41 53.79Sabellidae 1.97 1.6 1.35 1.07 2.14 55.93Ophiuroidea 0.93 1.77 1.26 1.04 1.99 57.92Cirratulidae 1.63 1.27 1.19 0.97 1.88 59.81Magelonidae 1.07 1.43 1.17 0.91 1.86 61.66Lumbrineridae 1.37 1 1.02 1.09 1.61 63.28Glyceridae 1.03 0.83 0.8 1.09 1.26 64.54Anthuridae 0.53 0.97 0.78 0.79 1.24 65.78Galeommatidae 0.8 0.5 0.77 0.6 1.22 67Cypridinidae/Rutidermatidae 0.67 0.67 0.74 0.63 1.17 68.17Onuphidae 0.63 0.93 0.73 0.84 1.16 69.33Copepoda 0.77 0.73 0.71 0.95 1.13 70.46Sipuncula 0.6 0.83 0.69 0.82 1.1 71.56Paraonidae 0.67 0.5 0.68 0.71 1.09 72.64Liljeborgiidae 0.67 0.43 0.61 0.73 0.97 73.61Nuculanidae 0.6 0.5 0.6 0.71 0.96 74.57Nematoda 0.67 0.5 0.59 0.82 0.93 75.5Phyllodocidae 0.37 0.5 0.53 0.76 0.85 76.35Caprellidae 0.3 0.57 0.49 0.84 0.78 77.13Trichobranchidae 0.37 0.4 0.47 0.63 0.75 77.88Pisionidae 0.47 0.33 0.47 0.61 0.74 78.62Podoceridae 0.1 0.6 0.45 0.45 0.71 79.33Tanaidae 0.67 0.07 0.42 0.72 0.67 80Orbiniidae 0.43 0.27 0.4 0.67 0.64 80.63Veneridae 0.37 0.3 0.4 0.44 0.63 81.27Sabellariidae 0.2 0.5 0.4 0.76 0.63 81.89Goniadidae 0.5 0.17 0.39 0.58 0.62 82.51Oligochaeta 0.37 0.13 0.37 0.51 0.59 83.11Sarsiellidae 0.27 0.33 0.36 0.53 0.57 83.68Bodotriidae 0.33 0.23 0.36 0.61 0.57 84.25Bryozoa 0.27 0.4 0.35 0.79 0.56 84.81Pasiphaeidae 0.23 0.3 0.35 0.61 0.55 85.36Tellinidae 0.3 0.27 0.34 0.6 0.55 85.91Poecilochaetidae 0.37 0.27 0.34 0.67 0.54 86.45Carditidae 0.33 0.2 0.32 0.67 0.5 86.95Sternaspidae 0.23 0.27 0.31 0.6 0.49 87.45Serolidae 0.33 0 0.29 0.18 0.46 87.9Hesionidae 0.4 0.07 0.28 0.56 0.44 88.35Sigalionidae 0.27 0.13 0.28 0.53 0.44 88.79Cylindroleberidae 0.13 0.37 0.27 0.61 0.43 89.22Phoxocephalidae 0.23 0.17 0.26 0.54 0.4 89.62Hydrozoa 0.2 0.2 0.24 0.63 0.37 90Cirolanidae 0.13 0.23 0.24 0.55 0.37 90.37

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Groups Control 1 & Spoil Disposal AreaAverage dissimilarity = 70.52

Group Control 1 Group Spoil Disposal Area Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 8.32 10.53 7.17 1.31 10.16 10.16Spionidae 4.8 4.43 3.77 1.02 5.34 15.5Maldanidae 5 3.7 3.59 1.1 5.09 20.59Apseudidae 3.4 4.83 3.31 1.18 4.69 25.28Ampharetidae 1.68 4.2 2.92 1.19 4.13 29.42Capitellidae 3.56 3.4 2.65 1.15 3.76 33.18Nephtyidae 2.32 3.57 2.58 0.93 3.66 36.84Ampeliscidae 0.44 2.93 1.96 1.07 2.78 39.62Nemertea 1.92 1.9 1.67 1.05 2.37 41.99Cirratulidae 1.08 2.33 1.65 1.07 2.33 44.32Ophiuroidea 1.16 2.07 1.58 0.93 2.24 46.57Magelonidae 0.8 1.73 1.53 0.77 2.17 48.73Terebellidae 1.76 1.5 1.51 0.99 2.14 50.87Onuphidae 1.44 1.23 1.27 0.83 1.8 52.67Sabellidae 0.2 1.77 1.17 1.01 1.66 54.33Syllidae 1.08 1.37 1.17 0.87 1.65 55.98Eunicidae 0.92 1.23 1.14 0.88 1.62 57.6Sipuncula 0.68 1.5 1.14 0.88 1.62 59.22Nuculanidae 1 0.87 1.14 0.77 1.61 60.83Sabellariidae 1 0.4 1.05 0.41 1.49 62.32Tellinidae 0.92 0.67 1.03 0.53 1.47 63.79Anthuridae 0.68 1.1 1 0.78 1.42 65.21Copepoda 1.2 0.4 0.99 0.67 1.41 66.62Phyllodocidae 0.92 0.83 0.97 0.72 1.38 68Glyceridae 0.92 1.03 0.91 1.04 1.3 69.3Lumbrineridae 0.56 1.23 0.91 0.95 1.29 70.59Nematoda 0.24 1.17 0.9 0.67 1.27 71.86Caprellidae 0.12 1.2 0.87 0.74 1.23 73.09Paraonidae 0.28 1 0.78 0.73 1.1 74.2Pisionidae 0.64 0.7 0.78 0.69 1.1 75.3Nereididae 0.4 1.07 0.77 0.96 1.09 76.39Trichobranchidae 1.04 0.47 0.75 0.71 1.07 77.46Orbiniidae 0.72 0.4 0.64 0.67 0.91 78.37Galeommatidae 0.48 0.5 0.61 0.73 0.87 79.24Liljeborgiidae 0.36 0.57 0.57 0.67 0.81 80.04Cypridinidae/Rutidermatidae 0.6 0.63 0.57 0.77 0.81 80.85Leptocheliidae 0.4 0.57 0.52 0.75 0.74 81.59Poecilochaetidae 0.24 0.6 0.49 0.68 0.69 82.28Bryozoa 0.44 0.47 0.48 0.81 0.68 82.96Pectinariidae 0.4 0.33 0.47 0.68 0.66 83.62Oenonidae 0.36 0.3 0.39 0.63 0.56 84.18Carditidae 0.04 0.47 0.39 0.32 0.55 84.73Hesionidae 0.24 0.37 0.37 0.45 0.53 85.25Veneridae 0.16 0.57 0.35 0.54 0.5 85.75Goniadidae 0.36 0.2 0.35 0.35 0.5 86.25Oligochaeta 0.24 0.23 0.35 0.5 0.49 86.74Scalibregmatidae 0.12 0.3 0.34 0.35 0.48 87.23Bodotriidae 0.4 0.17 0.33 0.58 0.47 87.7Callianassidae 0.12 0.3 0.33 0.52 0.47 88.17Opheliidae 0.52 0.03 0.32 0.52 0.45 88.62Cylindroleberidae 0.12 0.4 0.32 0.48 0.45 89.07Sarsiellidae 0 0.43 0.31 0.67 0.45 89.51Hydrozoa 0 0.33 0.27 0.59 0.38 89.9Podoceridae 0.32 0.23 0.26 0.51 0.37 90.27

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Groups C2 & SDAAverage dissimilarity = 73.54

Group Control 2 Group Spoil Disposal Area Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 23.2 10.53 12.09 1.15 16.44 16.44Apseudidae 4.37 4.83 3.38 1.1 4.6 21.03Ampharetidae 2.2 4.2 2.85 1.07 3.88 24.91Spionidae 2.57 4.43 2.84 1.28 3.86 28.77Maldanidae 1.87 3.7 2.71 0.99 3.69 32.46Capitellidae 2.27 3.4 2.5 1.11 3.39 35.85Nephtyidae 1.57 3.57 2.29 0.87 3.12 38.97Ampeliscidae 1.2 2.93 2.08 1.08 2.83 41.79Cirratulidae 1.03 2.33 1.62 1.02 2.2 44Ophiuroidea 1.43 2.07 1.54 0.92 2.09 46.09Copepoda 1.97 0.4 1.53 0.67 2.09 48.18Magelonidae 0.67 1.73 1.45 0.7 1.97 50.14Nemertea 1.23 1.9 1.38 0.97 1.88 52.02Onuphidae 1.73 1.23 1.25 0.78 1.7 53.72Nuculanidae 1.47 0.87 1.23 0.87 1.68 55.4Sabellidae 0.07 1.77 1.18 0.96 1.6 57.01Terebellidae 0.57 1.5 1.17 0.95 1.59 58.6Sipuncula 0.6 1.5 1.11 0.83 1.51 60.11Tellinidae 1.23 0.67 1.01 0.72 1.38 61.49Glyceridae 0.8 1.03 1 0.69 1.35 62.85Eunicidae 0.33 1.23 0.97 0.71 1.33 64.17Lumbrineridae 0.27 1.23 0.96 0.9 1.3 65.47Nereididae 0.7 1.07 0.93 0.83 1.26 66.74Nematoda 0.3 1.17 0.92 0.63 1.26 67.99Syllidae 0.23 1.37 0.9 0.68 1.22 69.22Caprellidae 0.13 1.2 0.83 0.7 1.13 70.35Galeommatidae 0.97 0.5 0.83 0.69 1.13 71.48Cypridinidae/Rutidermatidae 0.97 0.63 0.83 0.67 1.12 72.6Paraonidae 0.4 1 0.8 0.73 1.09 73.7Anthuridae 0.23 1.1 0.79 0.73 1.07 74.77Veneridae 1.03 0.57 0.76 0.54 1.03 75.8Pisionidae 0.8 0.7 0.72 0.7 0.98 76.78Sabellariidae 0.83 0.4 0.69 0.5 0.93 77.71Opheliidae 0.77 0.03 0.62 0.4 0.84 78.55Phyllodocidae 0.2 0.83 0.61 0.61 0.83 79.38Poecilochaetidae 0.37 0.6 0.49 0.61 0.66 80.05Liljeborgiidae 0.17 0.57 0.48 0.58 0.66 80.71Bryozoa 0.17 0.47 0.43 0.69 0.59 81.3Pectinariidae 0.4 0.33 0.43 0.63 0.59 81.88Trichobranchidae 0.23 0.47 0.43 0.53 0.58 82.46Cylindroleberidae 0.27 0.4 0.42 0.46 0.57 83.04Leptocheliidae 0.1 0.57 0.41 0.61 0.56 83.6Orbiniidae 0.23 0.4 0.41 0.52 0.56 84.15Platyischnopidae 0.47 0 0.39 0.27 0.53 84.68Carditidae 0 0.47 0.36 0.3 0.49 85.18Hesionidae 0.13 0.37 0.35 0.4 0.47 85.65Oenonidae 0.27 0.3 0.34 0.55 0.46 86.1Callianassidae 0.1 0.3 0.33 0.46 0.46 86.56Sarsiellidae 0.03 0.43 0.32 0.65 0.44 87Diastylidae/Gynodiastylidae 0.17 0.37 0.28 0.58 0.39 87.38Phoxocephalidae 0.27 0.3 0.28 0.48 0.39 87.77Oligochaeta 0.13 0.23 0.28 0.44 0.38 88.15Hydrozoa 0.03 0.33 0.27 0.57 0.37 88.52Scalibregmatidae 0.13 0.3 0.26 0.46 0.36 88.88Podoceridae 0.3 0.23 0.26 0.37 0.36 89.24Bodotriidae 0.23 0.17 0.24 0.38 0.33 89.57Cirolanidae 0.17 0.1 0.23 0.41 0.32 89.88Sternaspidae 0.2 0.17 0.23 0.52 0.31 90.2

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Groups ZoI (Far) & Spoil Disposal AreaAverage dissimilarity = 66.65

Group ZoI (Far) Group Spoil Disposal Area Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 6.83 10.53 5.64 1.16 8.47 8.47Apseudidae 8.23 4.83 4.76 0.88 7.15 15.62Leptocheliidae 7.4 0.57 4.71 0.99 7.06 22.68Capitellidae 4.37 3.4 2.56 1.12 3.84 26.52Ampharetidae 3.17 4.2 2.55 1.23 3.83 30.34Spionidae 2.6 4.43 2.2 1.19 3.3 33.64Maldanidae 1.8 3.7 2.17 1.03 3.25 36.89Ampeliscidae 3.13 2.93 1.99 1.17 2.98 39.87Nephtyidae 1.67 3.57 1.98 0.86 2.98 42.85Syllidae 2.33 1.37 1.66 1.05 2.49 45.34Cirratulidae 1.63 2.33 1.51 1.04 2.26 47.6Magelonidae 1.07 1.73 1.37 0.83 2.06 49.66Sabellidae 1.97 1.77 1.36 1.08 2.04 51.7Eunicidae 1.7 1.23 1.32 0.95 1.98 53.68Nemertea 1.4 1.9 1.31 0.99 1.97 55.65Nereididae 1.9 1.07 1.27 0.7 1.91 57.56Ophiuroidea 0.93 2.07 1.27 0.98 1.9 59.46Terebellidae 1.43 1.5 1.05 1.1 1.57 61.04Lumbrineridae 1.37 1.23 1.03 1.07 1.55 62.58Sipuncula 0.6 1.5 0.98 0.87 1.47 64.05Nematoda 0.67 1.17 0.85 0.77 1.27 65.32Onuphidae 0.63 1.23 0.81 0.75 1.22 66.54Glyceridae 1.03 1.03 0.81 1.1 1.21 67.75Paraonidae 0.67 1 0.79 0.91 1.19 68.94Caprellidae 0.3 1.2 0.76 0.78 1.15 70.09Anthuridae 0.53 1.1 0.75 0.85 1.12 71.21Nuculanidae 0.6 0.87 0.73 0.78 1.09 72.3Galeommatidae 0.8 0.5 0.67 0.6 1 73.3Liljeborgiidae 0.67 0.57 0.64 0.74 0.97 74.26Cypridinidae/Rutidermatidae 0.67 0.63 0.62 0.56 0.93 75.2Pisionidae 0.47 0.7 0.61 0.67 0.91 76.11Copepoda 0.77 0.4 0.59 0.82 0.88 77Phyllodocidae 0.37 0.83 0.58 0.74 0.87 77.87Tellinidae 0.3 0.67 0.53 0.7 0.8 78.67Trichobranchidae 0.37 0.47 0.48 0.59 0.71 79.38Carditidae 0.33 0.47 0.46 0.47 0.69 80.08Orbiniidae 0.43 0.4 0.45 0.68 0.68 80.75Poecilochaetidae 0.37 0.6 0.45 0.71 0.67 81.42Veneridae 0.37 0.57 0.44 0.58 0.66 82.08Hesionidae 0.4 0.37 0.41 0.59 0.62 82.7Oligochaeta 0.37 0.23 0.41 0.54 0.61 83.31Goniadidae 0.5 0.2 0.4 0.48 0.6 83.91Tanaidae 0.67 0 0.38 0.67 0.57 84.48Bryozoa 0.27 0.47 0.36 0.83 0.54 85.02Sarsiellidae 0.27 0.43 0.34 0.8 0.5 85.53Serolidae 0.33 0.07 0.31 0.2 0.47 85.99Oenonidae 0.23 0.3 0.3 0.57 0.44 86.44Cylindroleberidae 0.13 0.4 0.29 0.5 0.44 86.88Bodotriidae 0.33 0.17 0.29 0.49 0.44 87.32Sigalionidae 0.27 0.23 0.29 0.51 0.43 87.75Hydrozoa 0.2 0.33 0.28 0.71 0.42 88.17Kalliapseudidae 0.23 0.3 0.28 0.41 0.42 88.59Callianassidae 0.17 0.3 0.28 0.59 0.42 89.01Sabellariidae 0.2 0.4 0.27 0.64 0.4 89.42Pasiphaeidae 0.23 0.23 0.27 0.56 0.4 89.82Phoxocephalidae 0.23 0.3 0.27 0.51 0.4 90.22

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Groups ZoI (Near) & Spoil Disposal AreaAverage dissimilarity = 62.88

Group ZoI (Near) Group Spoil Disposal Area Species Av. Abund Av.Abund Av.Diss Diss/SD Contrib% Cum.%Aoridae/Isaeidae/Photidae 6.43 10.53 5.72 1.25 9.1 9.1Apseudidae 4.47 4.83 2.84 1.2 4.51 13.61Ampeliscidae 3.23 2.93 2.59 0.7 4.11 17.73Maldanidae 3.13 3.7 2.5 1.15 3.98 21.7Ampharetidae 2.57 4.2 2.3 1.26 3.66 25.36Nephtyidae 2.2 3.57 2.29 0.91 3.64 29Spionidae 3.33 4.43 2.14 1.29 3.41 32.41Capitellidae 3.13 3.4 2.1 1.12 3.34 35.75Terebellidae 2.17 1.5 1.66 1.07 2.63 38.38Ophiuroidea 1.77 2.07 1.58 1.06 2.51 40.89Eunicidae 1.83 1.23 1.52 0.98 2.42 43.31Nemertea 2.03 1.9 1.5 1.03 2.38 45.69Cirratulidae 1.27 2.33 1.46 1.13 2.32 48.01Syllidae 1.67 1.37 1.43 1.03 2.28 50.29Magelonidae 1.43 1.73 1.39 0.89 2.21 52.5Sabellidae 1.6 1.77 1.27 1.16 2.02 54.52Nereididae 1.73 1.07 1.19 1.12 1.89 56.41Leptocheliidae 1.7 0.57 1.16 0.95 1.85 58.26Sipuncula 0.83 1.5 1.1 0.92 1.75 60.02Anthuridae 0.97 1.1 1.01 0.9 1.61 61.62Onuphidae 0.93 1.23 0.94 0.81 1.5 63.12Lumbrineridae 1 1.23 0.9 1.06 1.43 64.55Caprellidae 0.57 1.2 0.84 0.88 1.33 65.88Paraonidae 0.5 1 0.84 0.73 1.33 67.21Nematoda 0.5 1.17 0.83 0.76 1.32 68.53Glyceridae 0.83 1.03 0.79 1.09 1.26 69.79Nuculanidae 0.5 0.87 0.74 0.77 1.17 70.96Phyllodocidae 0.5 0.83 0.74 0.79 1.17 72.13Cypridinidae/Rutidermatidae 0.67 0.63 0.64 0.83 1.02 73.15Copepoda 0.73 0.4 0.59 0.82 0.94 74.1Pisionidae 0.33 0.7 0.56 0.68 0.9 74.99Galeommatidae 0.5 0.5 0.56 0.63 0.9 75.89Liljeborgiidae 0.43 0.57 0.56 0.71 0.89 76.78Tellinidae 0.27 0.67 0.53 0.68 0.84 77.63Trichobranchidae 0.4 0.47 0.51 0.62 0.8 78.43Podoceridae 0.6 0.23 0.48 0.47 0.77 79.2Sabellariidae 0.5 0.4 0.46 0.8 0.74 79.93Veneridae 0.3 0.57 0.45 0.5 0.71 80.65Sarsiellidae 0.33 0.43 0.44 0.63 0.69 81.34Poecilochaetidae 0.27 0.6 0.42 0.75 0.67 82.02Carditidae 0.2 0.47 0.42 0.42 0.67 82.68Cylindroleberidae 0.37 0.4 0.4 0.61 0.64 83.32Bryozoa 0.4 0.47 0.4 0.83 0.63 83.95Orbiniidae 0.27 0.4 0.39 0.59 0.63 84.58Pasiphaeidae 0.3 0.23 0.33 0.66 0.52 85.1Hydrozoa 0.2 0.33 0.3 0.71 0.48 85.57Pectinariidae 0.13 0.33 0.3 0.62 0.47 86.04Goniadidae 0.17 0.2 0.29 0.39 0.46 86.51Hesionidae 0.07 0.37 0.27 0.42 0.43 86.94Oligochaeta 0.13 0.23 0.27 0.5 0.43 87.37Sternaspidae 0.27 0.17 0.27 0.54 0.42 87.79Diastylidae/Gynodiastylidae 0.1 0.37 0.26 0.6 0.42 88.21Callianassidae 0.03 0.3 0.26 0.54 0.41 88.62Phoxocephalidae 0.17 0.3 0.26 0.45 0.41 89.03Oenonidae 0.1 0.3 0.25 0.53 0.4 89.44Scalibregmatidae 0.13 0.3 0.25 0.54 0.39 89.83Chrysopetalidae 0.13 0.37 0.25 0.65 0.39 90.22

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APPENDIX H PERMDISP RESULTS

Ichthys Nearshore Environmental

Monitoring Program

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Appendix H. Distance based test for homogeneity of multivariate dispersion. Significant results in bold 1. CPCe inshore (for the significant term ‘location’) DEVIATIONS FROM CENTROID F: 30.771 df1: 3 df2: 644 P(perm): 0.0005

MEANS AND STANDARD ERRORS Group Size Average SE Moderate Impact 173 16.844 1.0316 Influence 171 25.845 1.1689 Con 1 166 28.462 1.6018 Con 2 138 12.901 1.3459

PAIRWISE COMPARISONS Groups t P(perm) (Moderate Impact,Influence) 5.7779 1.00E-03 (Moderate Impact,Con 1) 6.1482 1.00E-03 (Moderate Impact,Con 2) 2.3652 7.50E-02 (Influence,Con 1) 1.3254 0.337 (Influence,Con 2) 7.2876 1.00E-03 (Con 1,Con 2) 7.2608 1.00E-03

2. CPCe offshore (for the significant term ‘location’) DEVIATIONS FROM CENTROID F: 12.127 df1: 4 df2: 737 P(perm): 0.0005

MEANS AND STANDARD ERRORS Group Size Average SE Spoil Disposal Area 176 7.1039 0.39532 ZoI (Near) 178 9.4577 0.40898 ZoI (Far) 188 14.3 0.98163 Control 1 67 15.685 2.6586 Control 2 133 12.036 1.2438

PAIRWISE COMPARISONS Groups t P(perm) (Spoil Disposal Area,ZoI (Near)) 4.1372 2.00E-03 (Spoil Disposal Area,ZoI (Far)) 6.6361 1.00E-03 (Spoil Disposal Area,Control 1) 4.8863 1.00E-03 (Spoil Disposal Area,Control 2) 4.2064 4.00E-03 (ZoI (Near),ZoI (Far)) 4.4645 1.00E-03 (ZoI (Near),Control 1) 3.5439 6.00E-03 (ZoI (Near),Control 2) 2.1959 0.117 (ZoI (Far),Control 1) 0.6069 0.641 (ZoI (Far),Control 2) 1.4442 0.27 (Control 1,Control 2) 1.418 3.65E-01

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3. Infauna offshore (for the significant term ‘location’) DEVIATIONS FROM CENTROID F: 9.2453 df1: 4 df2: 140 P(perm): 0.001

PAIRWISE COMPARISONS Groups t P(perm) (Control 1,Control 2) 0.75019 0.504 (Control 1,ZoI (Far)) 2.9206 1.50E-02 (Control 1,ZoI (Near)) 4.4857 2.00E-03 (Control 1,Spoil Disposal Area) 2.4372 3.70E-02 (Control 2,ZoI (Far)) 3.7556 1.00E-03 (Control 2,ZoI (Near)) 5.3485 1.00E-03 (Control 2,Spoil Disposal Area) 3.287 7.00E-03 (ZoI FAR,ZoI (Near)) 1.0189 0.354 (ZoI (Far),Spoil Disposal Area) 0.72679 0.526 (ZoI (Far),Spoil Disposal Area) 1.985 8.60E-02

MEANS AND STANDARD ERRORS Group Size Average SE Control 1 25 49.168 1.5807 Control 2 30 50.828 1.5315 ZoI (Far) 30 42.821 1.4832 ZoI (Near) 30 40.987 1.0198 Spoil Disposal Area 30 44.249 1.2886

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APPENDIX I INFAUNA RAW DATA

Ichthys Nearshore Environmental

Monitoring Program

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Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012 Location 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6Sieve Size: 0.5 mm Rep 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1

POLYCHAETES Class PolychaetaAmpharetidae 2 9 18 3 5 9 1 1 5 1 1 32 40 68 34 5 27 4 9 14 3

Amphinomidae 1 2 2 1Aphroditidae

Capitellidae 4 5 5 4 6 2 5 4 9 1 2 2 7 11 13 1 14 4 17 6 14 4 19Chaetopteridae 1 1 2 1 1 1 2 1 3 2

Chrysopetalidae 1 2 1 1 1 1Cirratulidae 2 3 3 1 1 4 6 4 7 2 2 3 5 3 8 1 4 9 5 8 6 3Cossuridae

Dorvilleidae 1 1 1 1 1 1Eunicidae 2 2 1 1 2 1 3 1 1

Flabelligeridae 4 1 1 1 2 1 1Glyceridae 2 1 5 1 3 1 1 2 2 1 1 2 2 1 1

Goniadidae 1Hesionidae 7 1 1 3 2 14 2 3 5 1

Lumbrineridae 2 1 1 1 1 3 3 3 2 4Magelonidae 3 4 4 2 2 1 1 1 2 1 5 4 3 2 3 2

Maldanidae 13 17 7 6 1 2 2 4 1 16 15 8 8 3 9 2 2 6 6Nephtyidae 10 3 2 2 3 1 2 3 3 8 5 4 8Nereididae 2 1 1 2 1 1 2 3 1 1 3 1 4 5Oenonidae 2 2 3 1 1 2 1 1 2 2 5 1Onuphidae 2 2 2 6 3Opheliidae 1 3 1 1 4 2 2 3 2 2Orbiniidae 1 3 3 1 1 1 2 3 2 4 2 2Oweniidae

Paraonidae 4 1 3 4 1 2 1 3 2 4 2 4 2Pectinariidae 1 1 2

Phyllodocidae 2 1 2 1 1 1 1 1Pilargidae 2 2 2 3 3 4 2 3 6 3 1 7 1 3Pisionidae 2

Poecilochaetidae 2 1 2Polynoidae 1 1 2 1 2 1

Sabellariidae 3 1 1 1 1 3 7Sabellidae 1 1 1 2 1 9 1 4 1 1 1 3 1

Scalibregmatidae

Serpulidae 1 1 1 1 2Sigalionidae 1 4 1 1 2

Sphaerodoridae

Spionidae 4 6 2 2 3 7 1 2 8 22 3 6 4 4 8 6 15 8 4 4 8 2 16 7 10Sternaspidae 2 1 5 5 1 5 1 2 6 1 1 64

Syllidae 7 1 2 1 10 2 2 12 25 2 3 1 1 3Terebellidae 2 4 1 1 2 3 3 1 3 1 6 12 1 1 1

Trichobranchidae 1 1 3 1 2

CRUSTACEANS Order: Leptostraca Nebaliidae

Order: Stomatopoda Squillidae 1Order: Mysidacea Mysidae 1 1 1Order: Amphipoda Ampeliscidae 12 3 6 6 2 2 5 8 1 2 2 4 3 4 1 1 6

Aoridae/Isaeidae/Photidae 12 19 14 6 14 3 52 14 7 13 8 5 3 1 10 21 21 19 23 24 52 26 22 12 125Caprellidae 2 1 1 1 1 1 8 1 1

Corophiidae 1Iciliidae 3

Ischyroceridae 1 1 3Leucothoidae 2 2 1 8Liljeborgiidae 1 1 1 2 2 1 2 2

Lysianassidae

Melitidae 6 1 1 1 1 1 1 5Melphidippidae 3Oedicerotidae 1 1 1 1 3 3 6 5 1 2

Pachynus GroupPhoxocephalidae 1 1 2 1 3 3 4 1 1 3 1 2Platyischnopidae 30 2 19 4 14

Podoceridae 5 3 3 3 2 1Synopiidae 1 1

Urohaustoriidae 2 2 4 2 1 2Order: Isopoda Anthuridae 1 1 3 1 1 2 4 2 1 6 2 1 1 4 2 5 8

Arcturidae 1Arcturididae

Austrarcturellidae 1Cirolanidae 3 1 1Gnathiidae 2

Janiridae 1Leptanthuridae 2

Serolidae 1Sphaeromatidae 1 1 2 1 1 1

Order: Tanaidacea Apseudidae 3 18 4 2 9 1 35 12 4 23 26 32 38 11 34 23 39 29 18 36 146Leptocheliidae 4 11 1 1 2 1 2 1 2 11 1Paratanaidae 1 3

Tanaidae

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Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012 Location 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6Sieve Size: 0.5 mm Rep 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1

Order: Cumacea Bodotriidae 1 4 5 1 1 3 1 2 2 2 1 2 1Diastylidae/Gynodiastylidae 2 6 1 1 1 1 1 1

Nannastacidae

Order: Decapoda IOrder Penaeidea Luciferidae 1 1Penaeidae 1

IOrder Caridea Crangonidae 1 1Palaemonidae 1Pasiphaeidae 1 1 1 2

IOrder Thalassinidea Callianassidae 2 1 1 1 2IOrder Anomura Diogenidae

Superfamily PaguroideaPorcellanidae 1

IOrder Brachyura Goneplacidae 2 1 1Grapsidae 1 1 1

Hymenosomatidae 1Leucosiidae 1Portunidae

Crab Larvae (megalopa, zoea) 1Subclass Cirripedia Balanidae 2SubClass Copepoda Copepoda 1 2 2 2 2 1 1 1 1 3 5 4 55SubClass Ostracoda Order:

Myodocopida Cylindroleberidae 2 2 3 2 2 2 1 1 2 1 2Cypridinidae/Rutidermatidae 1 1 2 1 3 1 8 2 1 1 1 1 4 4 1 5 1 2 1

Philomedidae 1Sarsiellidae 2 1 1 1 1 1 6 1 1 2 2

Order: Podocopida Podocopida 5 1 5 3MOLLUSCS Class Scaphopoda Laevidentaliidae 1 2

unidentified ScaphopodaClass Polyplacophora PolyplacophoraClass Gastropoda Anabathronidae 1

Columbellidae 2Conidae

Epigridae

Iravadiidae 5 1 1Lottiidae

Marginellidae 1Nassariidae

Skeneidae 3Trochidae

Turridae

Volutomitridae

SubClass Opisthobranchia Order:

Cephalaspidea Haminoeidae 1 1 1 1Onchidiidae 1

PhilinidaeClass Bivalva Cardiidae 2 3

Carditidae 1 4 2 2 1 1Condylocardiidae 1

Cuspidariidae 2 1 1Galeommatidae 24 2 1 1 1 5 1

Lucinidae 2 1 2Myochamidae

Mytilidae 1 1Nuculanidae 32 13 4 6 4 2 5 3 1 4 1 1 2

Nuculidae 3 1 3 2 1Pectinidae 1

Solemyidae

Tellinidae 9 4 3 2 5 1 1 1 1 1 7 4 5 3 1Ungulinidae

Veneridae 5 2 1 3 1 5 4 1 5 1 7 2 7ECHINODERMS Asteroidea

EchinoideaHolothuroidea

Ophiuroidea 3 13 3 3 6 3 1 1 5 1 2 1 11 4 5 2 1 2OTHER WORM PHYLA Chaetognatha 1 1

Nematoda 9 12 1 1 1 1 8 2 4 4 20 3 3 5 4 3 5 1 11Nemertea 2 7 4 4 2 4 3 2 3 6 10 2 1 10 3 12 2 10 2 6 6 6 9 8

Oligochaeta 2 1 2 4 2 1 1Phoronida 3 1 1 1 1 1

Platyhelminthes 1 1 1 1 1Sipuncula 1 1 3 1 2

OTHER PHYLA Anthozoa: Actinaria 1 1 4 1Anthozoa: Alcyonacea 1 1

Ascidiacea 1 2 1Bryozoa 1 1 1 1 1 1 1

Hydrozoa 1 1 1Porifera 1 2 3

Pycnogonida 2 4 2 2 1Fish: Gobiidae 1

Fish: juvenile or unidentified 1 1 3 1 1 1 1

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Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Amphinomidae

Aphroditidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Sphaerodoridae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order: Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/PhotidaeCaprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Melitidae

Melphidippidae

Oedicerotidae

Pachynus GroupPhoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

UrohaustoriidaeOrder: Isopoda Anthuridae

Arcturidae

Arcturididae

Austrarcturellidae

Cirolanidae

Gnathiidae

Janiridae

Leptanthuridae

Serolidae

SphaeromatidaeOrder: Tanaidacea Apseudidae

Leptocheliidae

Paratanaidae

Tanaidae

6 6 6 6 7 7 7 7 7 8 8 8 8 8 9 9 9 9 9 10 10 10 10 10 11 11 112 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3

1 1 1 3 8 2 4 26 13 9 14 2 2 7 3 22 1

6 3 2 9 4 3 3 2 1 2 9 5 9 3 13 14 91 6 1 1 4 1

1 5 1 1 3 14 5 1 2 7 4 1 1 2 2 1 2 2 1 4 6 2

11 3 1 1

2 1 3 2 1 3 2 1 31 1 2

1 1 20 10 18 17 8 3 1 2 2 9 4 6 32

1 1 2 3 1 1 1 1 9 71 3 2 10 2 7 6 4 3 1 4 2 1 1 2 1 3

1 1 8 1 3 2 6 17 131 5 5 3 1 4 1 3 2 8 3 5 2 2 7 15 64 1 2 2 16 6 6 16 9 5 3 2 2 4 1 1 2 3

7 3 2 4 2 1 2 1 3 1 1 4 3 5 20 71 1 3 3 2 14 1 5 3 1 2 1 2

1 3 1 2 1 1 1 1 1 13 1 3 4 1 2 1 1 2

11 1 1 1 3 2 2 2 1 2 3 5 2

1 1 1 1 1 11 4 1 1 7 1

2 1 5 5 2 1 1 4 3 22

1 1 1 11

3 14 2 1 1 2 1 2 3 5 1

16 3 2 7 2 1

13 8 1 2 2 2 9 9 11 1 4 8 22 5 7 6 1 1 1 5 42 28 151 1 1 1 1 2 3 1

2 7 3 5 2 1 2 1 9 13 9 1 8 3 1 3 7 3 72 1 4 2 1 1 1 5 3 4 1 21 1 1 1

1 1

1 13 1 2 4 7 4 5 1 1 6 2 1 1

47 231 43 44 10 1 6 11 1 1 3 4 1 5 10 4 5 11 4 9 6 6 9 16 11 1 1 3 1 5 1 2

5 1

12 3

8 1 4 1 3 1 1 1 11 2

2 2 3 15 4 2 4 1 1 6 1 1

1 5 12 2 11

4 1 2 2 1 2 1 2

3 16 2 14 1

23 29 2 2 3 1 1 1 8 2 6 2 4 3 1 1 2 1

1 1 1 1 1 12

5 41 4 3 3

58 409 406 141 13 11 5 42 3 1 1 1 88 14 23 8 17 14 14 8 11 35 23 4 81 2 3 2 1 2 5 8 5 1 9 1 4 2 1

Page 153: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder Penaeidea Luciferidae

PenaeidaeIOrder Caridea Crangonidae

PalaemonidaePasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Diogenidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Crab Larvae (megalopa, zoea)Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

PhilomedidaeSarsiellidae

Order: Podocopida PodocopidaMOLLUSCS Class Scaphopoda Laevidentaliidae

unidentified ScaphopodaClass Polyplacophora PolyplacophoraClass Gastropoda Anabathronidae

Columbellidae

Conidae

Epigridae

Iravadiidae

Lottiidae

Marginellidae

Nassariidae

Skeneidae

Trochidae

Turridae

Volutomitridae

SubClass Opisthobranchia Order:

Cephalaspidea Haminoeidae

Onchidiidae

PhilinidaeClass Bivalva Cardiidae

Carditidae

CondylocardiidaeCuspidariidae

Galeommatidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Solemyidae

Tellinidae

UngulinidaeVeneridae

ECHINODERMS AsteroideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaNematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

AscidiaceaBryozoa

HydrozoaPorifera

PycnogonidaFish: Gobiidae

Fish: juvenile or unidentified

6 6 6 6 7 7 7 7 7 8 8 8 8 8 9 9 9 9 9 10 10 10 10 10 11 11 112 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3

4 1 1 1 1 1 1 71 4 4 8 2 2 1 1 2

1 6 2 1

21 3 2

8 11 1 1 3

3 1 1 31

1 1

11 1 1 2

1

1 2 2 11 1 1 1 8 2 1 1 1 3 1

1 2 2 2 1 1 3 1 6 2 12 3 11 4 3 3 1 3 1 1 11 2 1

1 2 1 2 1 2 2 1 7 3 61

1 1 11

2 11 1 1

2

6

2 1

1

1

9 22 3 7 1 1 1 2 1 1

3 1 1 1 121

16 1 1 5 2 2 1 13 3 6 6 1 3

1 5 5 8 1 3 1 1 1 1 1 12

1 4 31 17 9 6 1 21

2 21

1 1 2 7 6 3 9 2 1 2 7 3 3 2 1 1 11 1 1 1

4 6 3 3 2 5 1 2 3 1 6 5 1 105 2 2 1 1 1 9 1 1 2 4 11 4 1 2 1 2 2 3 6 8

1 1 3 2 1 21 1 2 1 4 4

1 1 1 1 1 11 1 1 1 1 6

1 1 1 82 196

1 11 1 11

1 2

1

Page 154: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Amphinomidae

Aphroditidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Sphaerodoridae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order: Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/PhotidaeCaprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Melitidae

Melphidippidae

Oedicerotidae

Pachynus GroupPhoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

UrohaustoriidaeOrder: Isopoda Anthuridae

Arcturidae

Arcturididae

Austrarcturellidae

Cirolanidae

Gnathiidae

Janiridae

Leptanthuridae

Serolidae

SphaeromatidaeOrder: Tanaidacea Apseudidae

Leptocheliidae

Paratanaidae

Tanaidae

11 11 12 12 12 12 12 13 13 13 13 13 14 14 14 14 14 15 15 15 15 15 16 16 16 16 164 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5

5 28 5 4 32 19 1 27 12 7 3 8 2 13 14 16 8 23 2 4 12 1 1 1 1 1 1 2

8 17 6 1 9 3 1 15 2 1 5 6 5 1 2 1 5 1 3 2 1 31 7 1 3 1 3 1 1 1

1 2 1 1 3 17 5 5 13 6 6 5 2 5 2 1 2 7 1 2 7 2 4 1 6 3 1

7 2 2 1 16 2 1 1 3

1 1 37 3 11 4 5 1 3 1 3 4 2 2 2 1 2 1

11 5 2 3 1 2 1 1 1 11 2 9 3 3 1 3 1 1 1 1 3 3 3 7 1 1 3

19 35 13 9 12 7 5 9 3 2 2 2 4 3 4 12 8 2 1 15 7 2 4 5 3 17 7 2 21 5 1 6 1 6 6 3 6 10 1 5 13 8 1 5 4 2 4 1 5 3 4 3 2 6 2 1 5 1 1 1

29 46 23 8 15 10 2 4 2 6 1 12 1 1 4 3 1 1 3 2 1

3 1 22 1 2 1 2 1

2 1 1 1 2 1 5 2 2 2 1

2 1 6 18 4 5 5 1 1 1 5 1 1 1 2 11 1 2 1

1 8 2 1 1 1 1 2 1 21 4 4 1 3 3 1 2 1 5 1

9 62 1 1 1 2

2 1 11 4 1 1 1 1 4 4 1

1 1 3 1 6 11 1 1 1 1 5 1

1 13 1 1 3

146 41 15 56 37 38 22 27 1 9 4 7 1 11 3 12 3 1 2 6 5 6 9 4 1

11 10 4 1 1 2 3 2 1 1 1 3 1 13 6 3 1 1 7 16 2 2 1 6 1 2 5 6 2 4 4 2 5 15 10 1 2 2 4 2 1 3 2 2 1 4 1 7 2

2 2 1 1

1 1 1 12 3 1 1 3 3 2 4 2 2 28 7 6 6 29 13 51 12 4 21 22 8 17 1 20 4 18 37 12 44 15 9 7 4 7 2

1 13 2 1 8 1 22

1 2 11 2 1 1 1 1 4

1 1 1 1 2 1 3 1 2 1 1 52 2

7 16 4 7 1 1 1 2 1

5 1 3 2

4 1 1 1 1 3

1 3 2 8 11 2

1 32 1 2 15 4 4 1 5 3 1 2 1 3 2 6 10 2 1 1 4 1

1 11

1 1 1 1 1 1 1

5 1 1 3 2 17 21 19 39 21 15 9 24 13 8 5 8 12 18 14 9 16 33 12 18 24 3 5 11 12 52 20 11 4 19 3 2

1 3

Page 155: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder Penaeidea Luciferidae

PenaeidaeIOrder Caridea Crangonidae

PalaemonidaePasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Diogenidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Crab Larvae (megalopa, zoea)Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

PhilomedidaeSarsiellidae

Order: Podocopida PodocopidaMOLLUSCS Class Scaphopoda Laevidentaliidae

unidentified ScaphopodaClass Polyplacophora PolyplacophoraClass Gastropoda Anabathronidae

Columbellidae

Conidae

Epigridae

Iravadiidae

Lottiidae

Marginellidae

Nassariidae

Skeneidae

Trochidae

Turridae

Volutomitridae

SubClass Opisthobranchia Order:

Cephalaspidea Haminoeidae

Onchidiidae

PhilinidaeClass Bivalva Cardiidae

Carditidae

CondylocardiidaeCuspidariidae

Galeommatidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Solemyidae

Tellinidae

UngulinidaeVeneridae

ECHINODERMS AsteroideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaNematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

AscidiaceaBryozoa

HydrozoaPorifera

PycnogonidaFish: Gobiidae

Fish: juvenile or unidentified

11 11 12 12 12 12 12 13 13 13 13 13 14 14 14 14 14 15 15 15 15 15 16 16 16 16 164 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5

7 1 3 1 1 3 1 11 1 5 2 1 1 1 1 1 1 1 1 2

1 1 1

11 1

1 51 1 5 1 1 2 2

1 4 2

1 1

1 11 1 3 1

1

3 1 4 1 1 22 1 1 1 4 2 1 3 1 1 1 2 1

2 3 2 11 1 1 3 2 4 31 1 6 10 2 5 4 7 1 7 1 3 1 11 3 1 2 4

2 1 1 1 5 1 1 2 13 7 1 10 4 1 4 2 2 2 1 2 1 1 2 1

1 18

1 1

3 12 7

11

21

1

2 2 2 2

7 11 10 1 2 1 2 4 7 12 1 1 1 1 2

11 1

1 2 2 6 2 3 1 1 1 1 3 3 12 1 3

17 2 1 1 8 1 2 1 5 2 3 6 1 6 6 2 3 1

1 14 2 2 1 1 2 4 2 3 11

12 1 1 2 2 5 1 1 5 1 1 1 3 5 3 1 5 1 1 5

18 6 8 2 1 1 21 3 1 3 13 1 1 5 12 8 8 3 13 7 1 2 1 17 8 3 13 2 4 17 4 4 4 6 1 1 3 9 5 19 8 4 1 2 6

4 4 1 2 1 1 1 1 1 1

1 21 1 1 1

26 21 1 1 1 1

1 1 11

1 11 1 1 1

1 1

1

Page 156: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Amphinomidae

Aphroditidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Sphaerodoridae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order: Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/PhotidaeCaprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Melitidae

Melphidippidae

Oedicerotidae

Pachynus GroupPhoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

UrohaustoriidaeOrder: Isopoda Anthuridae

Arcturidae

Arcturididae

Austrarcturellidae

Cirolanidae

Gnathiidae

Janiridae

Leptanthuridae

Serolidae

SphaeromatidaeOrder: Tanaidacea Apseudidae

Leptocheliidae

Paratanaidae

Tanaidae

17 17 17 17 17 18 18 18 18 18 25 25 25 25 25 26 26 26 26 26 27 27 27 27 27 28 281 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2

3 18 2 17 3 1 13 28 6 3 16 21 14 13 1 7 1 2 5 31 1 2 1 1

11 1 6 3 5 7 3 1 2 10 6 2 7 2 1 1 4 8

2 1 1 21 1 2 2 1 2 1 1 1

1 5 1 1 12 5 3 3 4 9 1 3 1 2 1 2 51

1 1 1 1 1 11 2 4 1 4

1 1 1 4 11 1 2 1 2 1 3 4 1 1 1 1 1 1 1 3 6

1 11 1 2 1 1 1 3 1 4 8 1 2 41 1 1 4 1 2 2 1 2 1 1 1 1

1 2 2 2 32 1 4 4 4 1 2 10 2 1 31 5 4 2 2 2 4 8 7 4 6 4 2 7 1 2 1 2 1 8

5 2 4 1 11 1 7 1 6 4 1 3 3 1 1 1 2 1 11 5 1 6 11 4 2 2 1 3

1 3 6 1 3 3 1 12 1 1 2

3 1 1 1 12 1 1 1 1 5 1 2 2

11 2 2 3 2 2 1 1 2

1 1 11 1 1 2 1

1 4 1 3 2 2 16 1 1

1 2 5 1 11

1 1 1 11 2 1 1 2 1 1 2 3 2 2 1 2 31

12 3 1 1 1 1

1 2 1 8 5 2 1 1 3 9 17 14 2 6 21 6 3 4 4 6 2 2 4 1 31 1 1 3 1 1 5 1 3 1 2 1 2 2

1 1 1 1 1 2 2 4 2 4 4 1 5 1 12 1 25 1 2 2 1 7 1 1 3 9 1 2 3 2 4

1 1

1 1 1 1 1 12 1 2 2 16 5

5 5 4 10 6 3 1 3 11 12 7 7 8 14 23 30 10 7 38 6 9 3 7 1 15 111 1 6 1 2 3 2 2

11 3

1 1

5 2 1 1 2

2 2 2 1 1 10 1

2 1 1 1

2 2 1 2 1

3 11 1 1 11 1 1

1 1 11 1 3 2 2 1 1 2 3 2 2 2 1 1 2 6 1

1

12 1

3 6 2 4 4 3 1 10 7 4 7 16 9 12 10 7 8 12 8 1 8 5 2 27 132 1 3 1

1 1

Page 157: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder Penaeidea Luciferidae

PenaeidaeIOrder Caridea Crangonidae

PalaemonidaePasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Diogenidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Crab Larvae (megalopa, zoea)Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

PhilomedidaeSarsiellidae

Order: Podocopida PodocopidaMOLLUSCS Class Scaphopoda Laevidentaliidae

unidentified ScaphopodaClass Polyplacophora PolyplacophoraClass Gastropoda Anabathronidae

Columbellidae

Conidae

Epigridae

Iravadiidae

Lottiidae

Marginellidae

Nassariidae

Skeneidae

Trochidae

Turridae

Volutomitridae

SubClass Opisthobranchia Order:

Cephalaspidea Haminoeidae

Onchidiidae

PhilinidaeClass Bivalva Cardiidae

Carditidae

CondylocardiidaeCuspidariidae

Galeommatidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Solemyidae

Tellinidae

UngulinidaeVeneridae

ECHINODERMS AsteroideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaNematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

AscidiaceaBryozoa

HydrozoaPorifera

PycnogonidaFish: Gobiidae

Fish: juvenile or unidentified

17 17 17 17 17 18 18 18 18 18 25 25 25 25 25 26 26 26 26 26 27 27 27 27 27 28 281 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2

2 2 3 1 1 1 1 11 2 1 2

1

1 1 11

1 11 2 2 1 1 1 1 1

1 1

11

1 1 2 1 11 2

1

3 11 1 1 1 1 2 1 1 1 2 2 1

1 1 1 7 2 5 6 1 93 2 3 2 1 1 2 1 1 2 1 1 7 2

1 1 1 15 1 2 1 1 2 1 2 1 8 1

2 1

3

1 1 1 1

1 1

1

1

1 1 2 3 1 2 1

2 21 1 7 1 3 1 3 5 3 12

2 1 7 2 11 1

1 11 1 1 1 2 4 2 3

3 1 1 1

1 2 5 4 1 1 6 1 5 6

2 2 3 1 6 1 2 5 7 6 5 1

21 4 1 2 4 1 2 1 3 1 3 1 3 2 1 5 4 3 1 7 1

1 1 1 11 2 2 6 7 17 6 6 3 8 6 5 2 8 6 3 1 12 42 7 1 4 1 2 1 7 4 8 10 1 6 7 1 3 4 1 2 1 1 6 1 4

2 8 1 5 1 1 4 3 1 61 1 2 2

1 2 11 1 2 1 3 1 2 1

1 11

1 1 1 1 1 1 11 1 1 1 1 1

1 1 1 11 1 1 1

1 11

Page 158: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Amphinomidae

Aphroditidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Sphaerodoridae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order: Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/PhotidaeCaprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Melitidae

Melphidippidae

Oedicerotidae

Pachynus GroupPhoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

UrohaustoriidaeOrder: Isopoda Anthuridae

Arcturidae

Arcturididae

Austrarcturellidae

Cirolanidae

Gnathiidae

Janiridae

Leptanthuridae

Serolidae

SphaeromatidaeOrder: Tanaidacea Apseudidae

Leptocheliidae

Paratanaidae

Tanaidae

28 28 28 29 29 29 29 29 30 30 30 30 303 4 5 1 2 3 4 5 1 2 3 4 5

2 4 15 7 5 1 6 1 1

7 10 1 4 2 1 2 11 2 3 1 2

18 4 3 1 1

1 2 15 1 1

3 6 1 1 2 1

2 2 1 1 11 2 2 1 11 2 2 1 1 1 11 2 8 1 1 2 3

10 4 1 2 1 1 31 2 1 2

1 3 12 2 1

1 1 23 4 1

2 1

1 1 1 11 3

4

1 11

1 2 2

13 5 2 1 2

13 7 3 3 1 2 1 33 2 5 2 5 4 112 2 1

4 4 4 1 1 42 1

11 3 1 1 3 14 32 35 13 38 11 9 53

1 11

11 2 6

181 5 11

1 1

3 1 2 3

3 2 21

1 1

12 1

5 20 40 18 72 9 5 37 1

Page 159: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - Inshore pest species

Job No: EL12047061Trip 1b - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class PolychaetaAmpharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder Penaeidea Luciferidae

PenaeidaeIOrder Caridea Crangonidae

PalaemonidaePasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Diogenidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Crab Larvae (megalopa, zoea)Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

PhilomedidaeSarsiellidae

Order: Podocopida PodocopidaMOLLUSCS Class Scaphopoda Laevidentaliidae

unidentified ScaphopodaClass Polyplacophora PolyplacophoraClass Gastropoda Anabathronidae

Columbellidae

Conidae

Epigridae

Iravadiidae

Lottiidae

Marginellidae

Nassariidae

Skeneidae

Trochidae

Turridae

Volutomitridae

SubClass Opisthobranchia Order:

Cephalaspidea Haminoeidae

Onchidiidae

PhilinidaeClass Bivalva Cardiidae

Carditidae

CondylocardiidaeCuspidariidae

Galeommatidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Solemyidae

Tellinidae

UngulinidaeVeneridae

ECHINODERMS AsteroideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaNematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

AscidiaceaBryozoa

HydrozoaPorifera

PycnogonidaFish: Gobiidae

Fish: juvenile or unidentified

28 28 28 29 29 29 29 29 30 30 30 30 303 4 5 1 2 3 4 5 1 2 3 4 5

2 1 1

1 1 1 1

12 2

22

1 1 1

31 5 2 1

1 1 11 1 1

1

1 11

414 3 2 1

1 13 3 1 1 4 1 1

2 11

31 7 1 1

1 2

1 8 2 2

2 12 3 1 1 1

2 1 2 1

11 3 1 14 8 5 1 16 8 1 4

14 3 4 21 1 31 1

1 12 1 1

2 11

Page 160: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012 Location C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C2 C2Sieve Size: 0.5 mm Site 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 1 1

Rep 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2

POLYCHAETES Class

Polychaeta Ampharetidae 13 7 1 3 3 1 3 2 2 1 2 2 1 1Amphinomidae 3 1

Capitellidae 11 6 14 6 5 6 4 1 2 4 6 3 2 5 1 5 3 4 1Chaetopteridae

Chrysopetalidae 1Cirratulidae 1 3 5 1 6 1 3 2 1 2 1 1Cossuridae 1Dorvilleidae

Eunicidae 3 3 3 6 1 1 2 1 2 1Flabelligeridae 1 1 1

Glyceridae 1 3 4 1 2 1 2 2 2 1 1 1 1 1Goniadidae 7 1 1Hesionidae 4 1 1

Lumbrineridae 1 2 2 1 3 1 1 1 1 1Magelonidae 4 1 2 1 2 1 4 1 1 1 2 1Maldanidae 6 3 25 23 10 2 2 2 3 5 2 3 3 5 9 11 1 2 8Nephtyidae 2 2 2 9 10 9 1 2 1 2 4 1 8 3 1 1Nereididae 1 1 3 3 1 1 2Oenonidae 1 4 1 1 1 1Onuphidae 2 2 5 2 3 1 1 1 2 3 1 7 3 1 2Opheliidae 6 1 2 1 1 2Orbiniidae 1 3 6 2 3 1 1 1Oweniidae 1 1 1

Paraonidae 1 1 3 1 1Pectinariidae 3 2 2 1 2

Phyllodocidae 4 1 1 3 1 1 7 2 2 1Pilargidae 1 1 1Pisionidae 4 7 3 1 1

Poecilochaetidae 1 1 1 2 1Polynoidae 4 2Questidae

Sabellariidae 1 2 1 10 2 4 1 1 1 2Sabellidae 1 1 1 1 1

Scalibregmatidae 3Serpulidae 1

Sigalionidae 2 1 1Spionidae 5 2 14 7 8 20 11 7 10 3 1 4 1 2 2 6 3 12 1 1

Sternaspidae 3 1Syllidae 2 2 4 3 12 1 1 1 1

Terebellidae 2 1 7 14 1 2 9 2 1 2 1 1 1Trichobranchidae 2 7 11 1 1 1 1 2 1

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae 1 1 1 1 1 1 1 3 1Aoridae/Isaeidae/Photidae 25 4 34 23 42 1 1 1 2 4 1 4 8 10 8 12 10 4 6 3 1 4 3 1

Caprellidae 1 2Corophiidae 1

Iciliidae 1Ischyroceridae 1Leucothoidae

Liljeborgiidae 3 1 2 1 1 1Lysianassidae 1

Megaluropidae

Melitidae 3 1 1Oedicerotidae 1 2

Phoxocephalidae 1 1 1 1Platyischnopidae

Podoceridae 2 1 3 1 1Synopiidae 1

Urohaustoriidae 1Order: Isopoda Anthuridae 4 2 1 1 1 1 1 1 5

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae 1 1Leptanthuridae

Serolidae

Sphaeromatidae 1Order: Tanaidacea Apseudidae 11 9 12 3 16 1 1 1 3 2 1 7 6 4 2 2 3 1

Kalliapseudidae

Leptocheliidae 1 3 3 1 1 1Tanaidae

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012 Location C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C1 C2 C2Sieve Size: 0.5 mm Site 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 1 1

Rep 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2

Order: Cumacea Bodotriidae 1 2 2 1 1 2 1Diastylidae/Gynodiastylidae 1 1

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae 1 1 1IOrder Thalassinidea Callianassidae 2 1

IOrder Anomura Galatheidae 1Superfamily Paguroidea 1

Porcellanidae 1IOrder Brachyura Goneplacidae 1 1 2 1

Grapsidae 1Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae 3SubClass Copepoda Copepoda 1 3 1 2 3 4 2 5 2 1 1 2 1 1 1 1SubClass Ostracoda Order:

Myodocopida Cylindroleberidae 1 1 1Cypridinidae/Rutidermatidae 1 1 8 1 1 1 2

Philomedidae 1 1 1Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae 1 2Marginellidae

Muricidae

Nassariidae 1 1Olividae 1

Rissoidae

Skeneidae 1Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae 1Cuspidariidae 1

Galeommatidae 1 1 2 1 2 1 1 1 2Laternulidae

Lucinidae

Myochamidae

Mytilidae 1Nuculanidae 4 1 1 1 1 2 1 1 1 4 1 3 4 2

Nuculidae 2Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae 8 2 4 1 2 6 1Trigonidae

UngulinidaeVeneridae 1 2 1

ECHINODERMS Crinoidea 1Echinoidea

HolothuroideaOphiuroidea 7 4 1 1 3 1 1 1 1 1 2 1 4 1

OTHER WORM PHYLA Chaetognatha 1 1Hirudinea

Nematoda 2 1 1 2Nemertea 2 2 1 1 8 1 6 1 1 4 3 2 3 4 6 1 2 1 2

Oligochaeta 1 1 1 3Phoronida 1

Platyhelminthes 1 1 1Sipuncula 2 3 1 4 1 1 3 1 1

OTHER PHYLA Anthozoa: Actinaria 1 2Anthozoa: Alcyonacea 1 1 1

Bryozoa 1 1 1 1 1 1 2 1 1 1Foraminifera

HydrozoaPorifera 1 1 1 1

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Amphinomidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Questidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/Photidae

Caprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Megaluropidae

Melitidae

Oedicerotidae

Phoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

Urohaustoriidae

Order: Isopoda Anthuridae

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae

Leptanthuridae

Serolidae

Sphaeromatidae

Order: Tanaidacea Apseudidae

Kalliapseudidae

Leptocheliidae

Tanaidae

C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C21 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6 6 6 6 63 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5

1 7 4 1 1 7 6 2 6 6 1 6 4 4 2 1 2 52

2 1 3 10 3 3 19 1 1 1 5 3 5 1 4 2 1 31

1 12 1 4 1 2 7 1 3 3 1 3 1 2

1 2 2 1 1 1 1 11 1 1

1 1 1 1 3 10 1 1 3 1 11 1

1 1 1 11 2 3 2

1 1 2 1 3 4 1 1 1 1 2 15 5 2 2 16 4 3 7 4 1 2 1 1 3

2 1 2 7 2 4 5 3 1 5 2 8 2 1 24 4 3 1 1 1 1 2 1 1

1 1 1 3 1 11 1 1 1 2 6 2 6 9 1 1 4 1 3 1 1 4 5 2

1 1 3 2 1 7 3 3 1 11 1 2 2 1

4 11 4 2 3 1 11 2 3 1 1 4

1 1 1 1 1 11 1

2 1 4 9 5 1 22 3 1 3 1 1

1 1

1 1 1 9 7 3 32

1 1 21 1

1 1 1 1 11 2 1 1 6 5 7 6 13 2 4 1 1 3 2 8 1 1 4 82 1 1 1 1

1 1 2 1 23 1 3 2 1 3 1 2 1

2 2 1 1

11

1 12 3 1 2 5 10 6 1 1 5

27 32 23 1 38 2 7 5 21 58 116 109 75 3 1 10 4 35 5 7 9 8 9 46 13 11 171 2 1

11 1

3 1 12 1 1 1

11 2 1

1 41 1 1 1 1 3

6 1 73 1 1 4

2 11 3 1

1 2 1 1 1 1

1 1 1 1 11

1

1 2 2 1 1 1 9 22 31 16 1 1 2 2 9 3 4 1 1 4 7 4 4 2

2 12

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Galatheidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

Philomedidae

Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae

Marginellidae

Muricidae

Nassariidae

Olividae

Rissoidae

Skeneidae

Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae

Cuspidariidae

Galeommatidae

Laternulidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae

Trigonidae

UngulinidaeVeneridae

ECHINODERMS CrinoideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaHirudinea

NematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

BryozoaForaminifera

HydrozoaPorifera

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C2 C21 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6 6 6 6 63 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5

3 1 1 21 1 1 2

11

11 1 1

2 1

1

11 3 2

8 6 3 1 1 1 2 2 1 1 10 7 1 6 1 2 1 2 1 1

1 1 4 21 3 3 1 1 3 2 8 3 1 1 1 1

1 1 11

1 1 4 2 11

1 1 1

12

1 1 2

1

2 12 2 1 1 7 5 4 2 1 4

1

22 1 3 4 5 1 4 1 1 1 2 2 3 2 6 41 1 1 1 2 1

12

2 101

2 2 4 8 1 1 4 10 1 3

4 10 3 2 8 4

31 1

2 2 3 2 2 3 5 1 1 1 1 8 2 2 1 2 1 3 11 1 5

12 1 5 1

4 2 1 3 2 1 3 3 2 1 2 1 2 3 1 31 1 1 1

11 1 3

1 1 1 6 1 1 1 1 2 31

11 1 1 1 1

11 1

1 1

1 1 1 2

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Amphinomidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Questidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/Photidae

Caprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Megaluropidae

Melitidae

Oedicerotidae

Phoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

Urohaustoriidae

Order: Isopoda Anthuridae

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae

Leptanthuridae

Serolidae

Sphaeromatidae

Order: Tanaidacea Apseudidae

Kalliapseudidae

Leptocheliidae

Tanaidae

ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6 6 61 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3

9 2 3 2 3 1 3 2 4 1 18 5 4 7 6 2 12 3 3 11

1 4 2 2 9 1 8 8 5 3 13 10 13 9 8 3 5 2 2 2 2 4 7 3 1 21 2 1

24 2 2 1 2 1 1 3 1 3 1 12 2 2 1 1 1 2 3 4

16 7 3 3 2 2 1 4 2 3 1 4 4 2 1 1 1 1 3

21 1 1 2 3 1 2 2 1 3 1 1 2 4 1 1

5 2 2 1 2 2 11 2 1 3 2 1 1 1

1 4 3 3 5 1 1 2 1 1 1 1 4 2 1 6 21 4 3 5 1 2 1 1 1 1 1 7 2 13 6 1 1 3 2 2 3 6 1 1 4 2 1 1 7 4 2 21 2 2 3 5 1 8 2 1 2 1 4 3 1 3 3 1 1 1 2

1 8 2 4 1 3 18 2 4 1 2 5 1 1 1 12 1 1 1 2

1 1 1 1 1 2 1 3 2 1 1 1 1 21 2

2 1 1 3 1 1 1 1 1 1

2 1 1 3 1 2 1 1 1 1 2 2 1

1 1 1 1 1 1 1 1 1 1 11 1

5 1 1 1 1 1 2 21 4 1 1 2 1 1

1 1 1

1 1 1 1 1 11 2 2 1 1 2 1 6 3 2 1 2 2 3 1 9 3 3 3 3 4 4

1 1

2 1 1 1 1 21 1 2 7 3 2 8 1 2 6 1 3 6 2 3 5 4 3 4 1 4 1 21 1 1 1 2 11 1 1 3 6 1 5 7 4 1 4 2 3 2 1 5 3 4 3 2 71 3 2 4 1 2 1 1 1 2 4 7 1 2 1 2 1 2 2 1

3 2 2 1 1 2

2 3 4 3 9 1 1 3 3 7 3 2 1 5 3 4 5 4 1 11 1 3 1 4 11 9 8 4 1 15 4 3 2 12 4 4 6 3 4 31 18 5 8 1 32 5 4 5 4 5

3 1 1 1 2 11

4 1

1 1 12 1 4 3 2 1 2 1

1 1 1 1 2 1

1

1 1 2 1 1 1

1 21 1

1 1 12 2 1 2 1 1 1 1 1 1 1 2

1 2 1

1 1 1 13

2 1 1 112 5 14 5 2 27 5 4 10 5 5 6 5 1 14 14 32 7 4 1 9 3 6 13 4 24 3

1 2 1 2 16 4 3 8 28 8 11 24 11 16 6 16 5 10 15 14 3 3 7 1 11 2 3 4 1 1

2 1 1 1 1 3 1 2 1 4 2 1

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Galatheidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

Philomedidae

Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae

Marginellidae

Muricidae

Nassariidae

Olividae

Rissoidae

Skeneidae

Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae

Cuspidariidae

Galeommatidae

Laternulidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae

Trigonidae

UngulinidaeVeneridae

ECHINODERMS CrinoideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaHirudinea

NematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

BryozoaForaminifera

HydrozoaPorifera

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR ZI FAR1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 6 6 61 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3

1 1 1 3 1 1 21 2 1

1

1

23 1 1 2

1 1 1 1 1

11

1

1 2 1 1 1 1 4 3 2 1 1 1 1

1 1 1 11 1 1 1 1 1 1 8 1 3 1

11 1 1 1 1 1 2

1 1

1 1 1

12

2 1

1 1

1 1 1 11

13 1 1 1 1 1 1

1 3 4 1 3 5 71

11 1 1

2 5 2 1 2 1 1 22 1 1

11 11 1 1 1 1 2

5 1 1 3 1

1

2 2 2 4 1 2 1 2 2 1 1 2 2 1

1 1 1 1 1 4 1 1 1 2 4 21 1 1 1 6 3 4 1 1 1 2 1 4 4 2 4 1

2 2 1 1 1 1 1 21

2 1 1 1 2 2 1 1 1 1 1 3 1

1 1 1 1 1 1 1 1

1 1 1 1 1 11 1 1 1 1 1

1 1 1 11

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Amphinomidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Questidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/Photidae

Caprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Megaluropidae

Melitidae

Oedicerotidae

Phoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

Urohaustoriidae

Order: Isopoda Anthuridae

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae

Leptanthuridae

Serolidae

Sphaeromatidae

Order: Tanaidacea Apseudidae

Kalliapseudidae

Leptocheliidae

Tanaidae

ZI FAR ZI FAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR6 6 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 64 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1

2 2 1 4 6 2 1 5 5 1 1 2 2 1 1 2 2 7 3 4 3 2 4 4 2 21 1 21 1 1 3 2 3 1 2 4 2 2 5 2 1 5 6 5 2 8 3 3 13 7 2 1 4

1 1 1 1 11 1 1 1

2 2 1 1 1 2 1 1 4 1 3 2 7 1 3 1 1 1 3

1 16 2 3 2 1 1 1 4 3 5 2 1 3 4 1 4

1 12 2 1 1 2 2 2 1 2 3 1 1 4 1 1 1

1 11 1

2 1 4 2 1 1 3 2 2 1 2 1 2 1 1 2 11 1 1 3 1 2 4 1 4 1 1 5 5 1 1 2 2 1 1 12 1 6 4 1 5 2 1 1 3 3 5 2 1 6 3 8 5 10 5 9 3 3

2 1 1 2 3 3 1 1 1 1 1 1 4 1 6 7 1 15 4 5 1 32 2 2 2 2 2 5 2 2 5 3 2 3 5 2 3 1

1 11 1 5 1 1 1 5 2 1 1 2 2 1 1 1

1 1 11 1 3 1 1 12 1

1 1 1 2 1 1 1 1 2 51 1 1 1

1 1 3 2 1 2 21 1 1

1 1 3 1 31 1 1 1 1 1 1

1 1 1 11

2 1 1 1 1 1 1 1 2 1 13 1 1 1 3 1 3 2 1 7 3 2 2 3 3 1 2 3 2

1 21 1 2

1 1 12 4 4 4 5 1 3 2 3 2 2 4 8 2 2 7 2 2 7 2 6 8 2 1 5 1 2 1

2 2 24 4 1 2 6 2 1 7 2 1 3 1 1 5 2 2 2 2

1 1 3 1 1 3 8 4 7 2 4 8 5 3 3 3 61 1 1 1 3 2

11

2 7 2 6 24 1 4 3 1 4 4 3 2 1 3 7 2 6 2 4 63 4 2 13 2 2 4 3 4 8 2 11 5 2 13 1 12 5 11 9 4 20 20 7 6 1

1 1 2 1 1 1 1 2 1 1 2 11

1 11

1 2 1 13 1 2 2 1 1 4 2

2

5 31 2 1 1 1

1 1 2 1

1 1 3 2 3 1

1 1 3 4 1 2 3 1 4 1 1 1 1 2 12

1 1 11

110

3 4 4 4 3 3 2 7 8 4 2 2 6 5 3 8 2 2 11 11 11 3 4 2 4 1 2

1 2 1 1 1 1 3 6 1 2 1 2 3 4 1 1 2 1 1 1 41 1

Page 167: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Galatheidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

Philomedidae

Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae

Marginellidae

Muricidae

Nassariidae

Olividae

Rissoidae

Skeneidae

Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae

Cuspidariidae

Galeommatidae

Laternulidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae

Trigonidae

UngulinidaeVeneridae

ECHINODERMS CrinoideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaHirudinea

NematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

BryozoaForaminifera

HydrozoaPorifera

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

ZI FAR ZI FAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR ZI NEAR6 6 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 5 5 64 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1

1 1 2 11 1

11 1 1

1 1 1 2 1 11

1 21

1

2 1 1 1 1 1 3 2 1 1 1 2 2 2 1

1 1 2 3 2 1 11 1 1 1 2 2 1 1 1 1 2

3 1 1 4

1

1

1

1 1 1 1 1 1 11

1 1 4 1 1 1 3

1

1 12 3 2 1 1 1 2

1

1 12 2 2 2 1

2

1 1 1

2 1 2 7 1 4 3 3 3 1 2 5 1 1 1 3 5 31

1 1 1 1 1 1 2 1 1 2 14 1 3 7 1 3 2 4 1 1 7 3 2 1 5 6 2 1 1 2 2 2

1 1

1 11 1 3 1 1 2 2 2 7 1 1 1

1 1 1 1

1 1 1 1 1 1 1 1 1 1

1 1 1 1 11 1 1 1

11

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POLYCHAETES Class

Polychaeta Ampharetidae

Amphinomidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Questidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/Photidae

Caprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Megaluropidae

Melitidae

Oedicerotidae

Phoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

Urohaustoriidae

Order: Isopoda Anthuridae

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae

Leptanthuridae

Serolidae

Sphaeromatidae

Order: Tanaidacea Apseudidae

Kalliapseudidae

Leptocheliidae

Tanaidae

ZI NEAR ZI NEAR ZI NEAR ZI NEAR SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA6 6 6 6 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 52 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4

7 3 1 4 8 5 3 1 6 4 6 5 5 12 6 5 2 1 1 6 1 9 13 41 1 1

2 3 1 1 7 3 4 3 5 1 2 4 8 5 4 1 7 2 1 1 5 2 15 3 41 1 11 1 2 1 3

1 7 1 1 1 3 2 3 8 2 3 3 5 3 2 2 2 6

1 1 16 3 3 4 4 1 2 1 5 1 2 2 5 2 4

2 1 1 11 1 1 1 1 2 3 1 1 2 1 2 2 22 1 1 4

2 1 22 1 2 1 1 2 1 3 2 1 3 1 3 1 3 11 4 1 2 3 4 1 3 1 1 5 2 2 4 2 1 8 2 3 4

2 1 4 8 2 1 3 1 1 2 1 13 5 4 3 13 1 3 3 5 1 12 72 2 11 2 3 1 1 3 9 3 4 1 1 1 3 5 26 4

2 4 3 1 1 1 2 1 2 1 1 1 2 3 1 5 31 1 1 2 2 2 12 4 1 1 1 1 1 1 1 6 1 1 3 1 1 1 1 1 1 3

11 1 2 4 1

1 5 11 2 4 2 3 3 1 2 1 1 4

1 1 1 1 1 2 11 2 1 1 2 1 1 7 41 1 11 1 2 3 3 1 5 5

1 2 1 1 3 1 2 2 41 2 2 1 1

2 1 1 1 1 2 22 1 1 2 2 1 2 2 5 4 1 1 4 4 1 3 4 41 1 1 3 21 3

1 1 44 5 2 1 1 3 2 2 2 1 2 1 1 5 8 5 7 15 5 4 3 4 3 12 3 7 10 1

1 1 1 1 1 14 1 1 5 7 3 2 2 1 3 2 3 1 8

1 3 2 4 2 2 3 2 5 3 1 1 2 1 1 3 71 2 2 1 3 5

1 11

5 7 1 1 3 2 1 2 4 6 2 3 1 1 4 4 9 5 7 8 88 6 2 10 5 2 6 10 1 8 7 34 10 2 18 24 6 3 1 5 4 18 8 27 16 12 1 1 4 2 1 4 1 1 1 7 5 1

1 1 11

21

1 2 1 1 1 1 1 21

12 2

1 1 5 1

7 1

12 1 1 2 2 2 5 1 3 2 1 9 2

11

1 1 2 1 1 11 3 1

11

4 11 2 3 1 4 2 5 2 1 2 1 1 1 2 9 7 3 7 4 2 1 17 1 6 20 52 1

6 4 1 1 3 1 1 1 1 2 1 2 1 1

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POLYCHAETES Class

Polychaeta Ampharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Galatheidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

Philomedidae

Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae

Marginellidae

Muricidae

Nassariidae

Olividae

Rissoidae

Skeneidae

Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae

Cuspidariidae

Galeommatidae

Laternulidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae

Trigonidae

UngulinidaeVeneridae

ECHINODERMS CrinoideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaHirudinea

NematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

BryozoaForaminifera

HydrozoaPorifera

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

ZI NEAR ZI NEAR ZI NEAR ZI NEAR SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA SDA6 6 6 6 1 1 1 1 1 2 2 2 2 2 3 3 3 3 3 4 4 4 4 4 5 5 5 52 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4 5 1 2 3 4

1 1 1 41 1 1 1 2 2 1

1 22

2 1 1 1 1 1 1 11 1 1 1 1

13 1

1 11

11

2 1 1 2 1 1 1 2 1

1 1 1 51 1 4 1 1 1 4 1 1 2 1

1 1 1 2 1 1 1 1 11

12 1

1 11 2

1 1 1 1 1 1

3 1 1 1 2 2 3 1

11

1 1 22 1 2 2 1 1 1 1 2 1

11

1 21

1 3 2 3 1 4 2 1

16 1 2 1 1 1

2 3 1 2 1 1 3 6 1 6 2 6 1 2 2 1 5 1 1 1 8 21

1 1 1 1 1 3 1 2 1 1 5 4 1 3 22 2 1 1 1 1 2 1 2 1 1 2 2 6 1 1 1 2 12 22 1 1 1 2 1 1

11 1

1 1 1 4 2 2 1 1 3 8 3 2 1 2 2 61 1

1 1 1 1 1 1 1 1 1 1 1 13

1 1 1 1 1 1 1 1 11 1

11

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Amphinomidae

Capitellidae

Chaetopteridae

Chrysopetalidae

Cirratulidae

Cossuridae

Dorvilleidae

Eunicidae

Flabelligeridae

Glyceridae

Goniadidae

Hesionidae

Lumbrineridae

Magelonidae

Maldanidae

Nephtyidae

Nereididae

Oenonidae

Onuphidae

Opheliidae

Orbiniidae

Oweniidae

Paraonidae

Pectinariidae

Phyllodocidae

Pilargidae

Pisionidae

Poecilochaetidae

Polynoidae

Questidae

Sabellariidae

Sabellidae

Scalibregmatidae

Serpulidae

Sigalionidae

Spionidae

Sternaspidae

Syllidae

TerebellidaeTrichobranchidae

CRUSTACEANS Order:

Leptostraca Nebaliidae

Order: Stomatopoda Squillidae

Order: Mysidacea Mysidae

Order: Amphipoda Ampeliscidae

Aoridae/Isaeidae/Photidae

Caprellidae

Corophiidae

Iciliidae

Ischyroceridae

Leucothoidae

Liljeborgiidae

Lysianassidae

Megaluropidae

Melitidae

Oedicerotidae

Phoxocephalidae

Platyischnopidae

Podoceridae

Synopiidae

Urohaustoriidae

Order: Isopoda Anthuridae

Arcturidae

Austrarcturellidae

Cirolanidae

Gnathiidae

Leptanthuridae

Serolidae

Sphaeromatidae

Order: Tanaidacea Apseudidae

Kalliapseudidae

Leptocheliidae

Tanaidae

SDA SDA SDA SDA SDA SDA5 6 6 6 6 65 1 2 3 4 5

3 4 3 8

5 1 5 2 21 1

1 1 11 4 7 3

13 1

1 11 5 1 5

15 1

1 1 2 7 13

1 1 7 3 101 4 1 20 3

3 2 2

1 1 1 31

1 2

2 2 22

2 4 1 12

11 1

41 1 6 2 31 1

1 114 3 7 21

3 11 1 1 1 2

2 1

2

2 1 5 1 78 5 32 7 20 281 3 2 1

1

11 1 1 5

1

5 11

22 1

1

8 2 4 2 9 1681 2

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Job: INPEX Subtidal Benthos - OffshoreJob No: EL12047061Trip 1d - June 2012Sieve Size: 0.5 mm

POLYCHAETES Class

Polychaeta Ampharetidae

Order: Cumacea Bodotriidae

Diastylidae/Gynodiastylidae

Nannastacidae

Order: Decapoda IOrder

Penaeidea Luciferidae

Penaeidae

IOrder Caridea Crangonidae

Palaemonidae

Pasiphaeidae

IOrder Thalassinidea Callianassidae

IOrder Anomura Galatheidae

Superfamily PaguroideaPorcellanidae

IOrder Brachyura Goneplacidae

Grapsidae

Hymenosomatidae

Leucosiidae

Portunidae

Subclass Cirripedia Balanidae

SubClass Copepoda CopepodaSubClass Ostracoda Order:

Myodocopida Cylindroleberidae

Cypridinidae/Rutidermatidae

Philomedidae

Sarsiellidae

Order: Podocopida Podocopida

MOLLUSCS Class AplacophoraPruvotinidae

Class Scaphopoda Laevidentaliidae

Columbellidae

Iravadiidae

Marginellidae

Muricidae

Nassariidae

Olividae

Rissoidae

Skeneidae

Trochidae

SubClass Opisthobranchia

Order: Cephalaspidea Haminoeidae

Onchidiidae

Order: Nudibranchia Glaucidae

Class Bivalva Cardiidae

Carditidae

Cuspidariidae

Galeommatidae

Laternulidae

Lucinidae

Myochamidae

Mytilidae

Nuculanidae

Nuculidae

Pectinidae

Propeamussiidae

Psammobiidae

Solemyidae

Tellinidae

Trigonidae

UngulinidaeVeneridae

ECHINODERMS CrinoideaEchinoidea

HolothuroideaOphiuroidea

OTHER WORM PHYLA ChaetognathaHirudinea

NematodaNemertea

OligochaetaPhoronida

PlatyhelminthesSipuncula

OTHER PHYLA Anthozoa: ActinariaAnthozoa: Alcyonacea

BryozoaForaminifera

HydrozoaPorifera

PycnogonidaBranchiostomma

Fish: juvenile or unidentified

SDA SDA SDA SDA SDA SDA5 6 6 6 6 65 1 2 3 4 5

2 1

2

1 2 1

3

1 1 1

1 31 4 1 1

1 1 1 1

1

17

6 2

3 1

21

1 11 2 5 4 4 1

1 3

2 1 1

2 6 3

1 2 6 3

1 1 6 14 2 5 3 3

7

1 1 1 1

1 11

1

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APPENDIX J PSD RAW DATA

Ichthys Nearshore Environmental

Monitoring Program

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1. Raw Particle Size Distribution (PSD) data for samples collected from inshore locations between May and July 2012.

ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 48 54 35 43 95 96 68 72 77 71 46 40+150µm 29 35 16 21 90 91 63 68 60 53 24 22+300µm 22 29 10 11 40 48 60 66 29 25 14 12+425µm 21 28 10 10 28 32 59 64 18 16 11 8+600µm 20 27 9 9 21 22 57 62 12 10 9 6+1180µm 18 25 7 6 13 13 51 57 6 4 6 4+2.36mm 14 19 5 4 5 6 38 44 2 <1 2 2+4.75mm 10 10 4 4 <1 2 16 24 <1 <1 <1 1+9.5mm <1 <1 4 1 <1 <1 4 6 <1 <1 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 22 17 27 24 4 3 10 9 11 16 25 25Silt (2-60 µm) 31 25 31 28 <1 <1 22 16 9 11 28 29Sand (0.06-2.00 mm) 33 39 37 43 91 90 30 31 78 72 44 44Gravel (>2mm) 14 19 5 5 5 7 38 44 2 1 3 2Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.065 0.075 0.052 0.063 0.15 0.225 1.18 1.18 0.15 0.15 0.063 0.064

Site 1 Site 2 Site 3 Site 4 Site 5 Site 6Zone of Moderate Impact

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ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 77 85 98 98 78 78 66 53 89 84 63 66+150µm 21 26 98 97 71 69 35 23 85 79 46 44+300µm 2 4 82 92 52 44 22 14 57 55 36 32+425µm 1 2 66 80 48 38 17 11 44 44 32 29+600µm <1 1 54 70 45 36 12 8 33 36 28 26+1180µm <1 <1 40 54 36 31 5 4 22 27 22 20+2.36mm <1 <1 27 34 19 19 2 <1 10 16 16 14+4.75mm <1 <1 11 15 6 6 <1 <1 2 2 5 4+9.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 11 7 1 2 12 12 17 20 8 9 13 14Silt (2-60 µm) 9 8 1 <1 8 9 17 20 2 5 17 14Sand (0.06-2.00 mm) 80 85 71 64 61 60 64 59 80 70 54 58Gravel (>2mm) <1 <1 27 34 19 19 2 1 10 16 16 14Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.075 0.075 0.6 1.18 0.3 0.15 0.075 0.075 0.3 0.3 0.075 0.075

Site 7 Site 8 Site 9 Site 10 Site 11 Site 12Zone of Influence

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ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 62 57 76 95 72 76 77 81 76 69 84 83+150µm 56 48 71 94 69 70 71 75 72 65 79 77+300µm 35 21 45 86 66 60 57 57 61 58 40 39+425µm 34 18 30 62 65 58 50 50 55 55 33 32+600µm 33 17 21 34 64 56 44 44 51 53 31 30+1180µm 30 14 13 9 62 51 32 30 44 50 29 26+2.36mm 24 8 7 1 57 42 18 15 35 45 24 20+4.75mm 15 3 3 <1 45 30 6 3 21 36 7 9+9.5mm 4 2 <1 <1 28 11 <1 <1 10 28 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 6 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 18 23 15 5 9 9 12 12 8 9 9 10Silt (2-60 µm) 17 20 9 <1 16 14 10 7 14 21 7 7Sand (0.06-2.00 mm) 41 49 69 94 18 35 60 66 43 25 60 63Gravel (>2mm) 24 8 7 1 57 42 18 15 35 45 24 20Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.15 0.075 0.15 0.425 2.36 1.18 0.363 0.425 0.6 0.89 0.15 0.15

Site 13 Site 14 Site 15 Site 16 Site 17 Site 18Control 1

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ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 72 77 29 30 31 30 86 72 26 27 17 17+150µm 68 73 7 8 5 3 76 56 4 4 2 1+300µm 58 63 2 2 2 1 48 32 2 2 <1 <1+425µm 49 55 <1 1 1 <1 31 23 1 1 <1 <1+600µm 44 50 <1 <1 1 <1 18 15 1 1 <1 <1+1180µm 36 42 <1 <1 <1 <1 8 7 <1 <1 <1 <1+2.36mm 22 26 <1 <1 <1 <1 2 2 <1 <1 <1 <1+4.75mm <1 4 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+9.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 13 10 34 37 32 35 11 16 40 36 41 41Silt (2-60 µm) 12 11 37 25 25 30 1 12 26 34 33 40Sand (0.06-2.00 mm) 53 53 29 38 43 35 86 70 34 30 26 19Gravel (>2mm) 22 26 <1 <1 <1 <1 2 2 <1 <1 <1 <1Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.363 0.513 0.052 0.033 0.054 0.049 0.225 0.15 0.029 0.044 0.006 0.009

Control 2Site 19 Site 20 Site 21 Site 22 Site 23 Site 24

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2. Raw Particle Size Distribution (PSD) data for samples collected from offshore locations between May and July 2012

ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 60 57 61 67 86 83 83 82 72 62 no data no data+150µm 49 45 16 15 81 80 72 71 63 50 no data no data+300µm 44 41 4 3 77 76 65 64 60 46 no data no data+425µm 40 37 3 2 72 73 58 58 56 43 no data no data+600µm 34 31 2 2 65 68 48 49 52 39 no data no data+1180µm 21 20 1 <1 52 54 30 32 40 30 no data no data+2.36mm 12 12 <1 <1 39 39 18 21 30 21 no data no data+4.75mm 4 8 <1 <1 29 27 9 13 23 15 no data no data+9.5mm <1 3 <1 <1 19 17 <1 <1 8 11 no data no data+19.0mm <1 <1 <1 <1 8 <1 <1 <1 <1 <1 no data no data+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 no data no data+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 no data no data

Soil Classification based on Particle SizeClay (<2 µm) 25 25 20 23 8 10 12 12 13 17 no data no dataSilt (2-60 µm) 13 15 16 8 5 7 6 5 13 22 no data no dataSand (0.06-2.00 mm) 50 48 64 69 48 44 64 62 44 40 no data no dataGravel (>2mm) 12 12 <1 <1 39 39 18 21 30 21 no data no dataCobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 no data no data

Median Grain Size (mm) 0.113 0.075 0.075 0.075 1.18 1.18 0.513 0.513 0.6 0.113 no data no data

Control 1Site 1 Site 2 Site 3 Site 4 Site 5 Site 6

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ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 21 40 4 9 65 62 75 98 62 81 72 56+150µm 3 6 <1 1 47 47 67 93 52 74 43 32+300µm <1 <1 <1 <1 17 18 24 53 37 65 12 10+425µm <1 <1 <1 <1 12 12 10 29 33 63 8 7+600µm <1 <1 <1 <1 8 8 4 13 30 60 6 6+1180µm <1 <1 <1 <1 3 3 <1 2 25 54 3 4+2.36mm <1 <1 <1 <1 <1 <1 <1 <1 19 45 1 2+4.75mm <1 <1 <1 <1 <1 <1 <1 <1 13 36 <1 <1+9.5mm <1 <1 <1 <1 <1 <1 <1 <1 11 26 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 11 4 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 41 28 53 53 22 26 18 1 22 11 21 29Silt (2-60 µm) 38 26 38 38 11 12 4 2 15 8 6 15Sand (0.06-2.00 mm) 21 46 9 9 66 62 78 97 44 36 72 54Gravel (>2mm) <1 <1 <1 <1 1 <1 <1 <1 19 45 1 2Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.008 0.052 0.001 0.001 0.113 0.075 0.15 0.3 0.15 1.18 0.075 0.075

Site 1 Site 2 Site 3 Site 4 Site 5 Site 6Control 2

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Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX Page J-7

ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 21 40 4 9 65 62 75 98 62 81 72 56+150µm 3 6 <1 1 47 47 67 93 52 74 43 32+300µm <1 <1 <1 <1 17 18 24 53 37 65 12 10+425µm <1 <1 <1 <1 12 12 10 29 33 63 8 7+600µm <1 <1 <1 <1 8 8 4 13 30 60 6 6+1180µm <1 <1 <1 <1 3 3 <1 2 25 54 3 4+2.36mm <1 <1 <1 <1 <1 <1 <1 <1 19 45 1 2+4.75mm <1 <1 <1 <1 <1 <1 <1 <1 13 36 <1 <1+9.5mm <1 <1 <1 <1 <1 <1 <1 <1 11 26 <1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 11 4 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 41 28 53 53 22 26 18 1 22 11 21 29Silt (2-60 µm) 38 26 38 38 11 12 4 2 15 8 6 15Sand (0.06-2.00 mm) 21 46 9 9 66 62 78 97 44 36 72 54Gravel (>2mm) <1 <1 <1 <1 1 <1 <1 <1 19 45 1 2Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.008 0.052 0.001 0.001 0.113 0.075 0.15 0.3 0.15 1.18 0.075 0.075

Site 1 Site 2 Site 3 Site 4 Site 5 Site 6Control 2

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Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX Page J-8

ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 69 77 78 76 63 67 64 59 70 74 73 71+150µm 63 70 69 70 55 61 57 53 65 67 67 64+300µm 54 56 56 59 46 48 46 43 57 56 55 52+425µm 48 48 48 52 42 41 38 36 51 49 47 45+600µm 42 39 40 44 38 34 30 29 44 41 39 38+1180µm 32 27 28 33 32 23 19 17 32 29 25 26+2.36mm 22 17 19 20 26 14 9 8 19 19 14 15+4.75mm 16 12 12 8 22 6 4 2 10 13 8 10+9.5mm 5 8 3 <1 20 <1 <1 <1 4 7 4 6+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 16 14 13 16 17 18 23 25 17 16 18 18Silt (2-60 µm) 15 7 6 8 18 13 11 16 12 7 6 9Sand (0.06-2.00 mm) 47 62 62 56 39 55 57 51 52 58 62 58Gravel (>2mm) 22 17 19 20 26 14 9 8 19 19 14 15Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.3 0.363 0.363 0.425 0.15 0.225 0.15 0.15 0.425 0.363 0.3 0.3

Site 1 Site 2 Site 3 Site 4 Site 5 Site 6Zone of Impact (Near)

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Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX Page J-9

ZoneSiteReplicate 1 2 1 2 1 2 1 2 1 2 1 2Analyte grouping (%)+75µm 52 63 78 76 90 51 65 82 80 90 82 94+150µm 40 50 69 66 81 42 59 78 74 84 77 90+300µm 31 39 56 52 60 33 45 65 59 66 54 62+425µm 25 32 49 44 47 28 39 58 52 58 37 47+600µm 18 24 40 33 32 23 34 50 44 48 25 35+1180µm 10 13 26 16 14 14 28 40 30 31 14 20+2.36mm 3 5 12 5 5 8 20 28 18 20 7 9+4.75mm <1 <1 3 1 2 5 17 19 12 15 3 2+9.5mm <1 <1 <1 <1 <1 <1 6 5 3 10 1 <1+19.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+37.5mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1+75.0mm <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Soil Classification based on Particle SizeClay (<2 µm) 29 23 17 19 7 29 19 12 17 8 18 4Silt (2-60 µm) 14 10 3 5 3 18 13 5 3 2 1 2Sand (0.06-2.00 mm) 54 62 68 71 85 45 48 55 62 70 74 85Gravel (>2mm) 3 5 12 5 5 8 20 28 18 20 7 9Cobbles (>6cm) <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1

Median Grain Size (mm) 0.075 0.15 0.363 0.3 0.363 0.075 0.15 0.513 0.425 0.513 0.3 0.363

Site 6Zone of Impact (Far)

Site 1 Site 2 Site 3 Site 4 Site 5

Page 182: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-001 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 91%2.36 86%1.18 82%0.600 80%0.425 79%0.300 78%0.150 71%0.075 52%

Particle Size (microns)54 33%38 30%19 29%10 28%5 26%3 24%1 22%

Median Particle Size (mm) 0.065

0.001 61Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay, medium fine sand and shell

CEL.060.T1B.HAR.S1.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 183: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-002 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 90%2.36 81%1.18 75%0.600 73%0.425 72%0.300 71%0.150 65%0.075 46%

Particle Size (microns)54 26%38 24%19 23%10 23%5 20%3 17%1 17%

Median Particle Size (mm) 0.075

0.001 63Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay, medium fine sand and shell

CEL.060.T1B.HAR.S1.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 184: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-003 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 96%2.36 95%1.18 93%0.600 91%0.425 91%0.300 90%0.150 84%0.075 65%

Particle Size (microns)52 42%37 37%18 36%9 33%5 31%3 29%1 27%

Median Particle Size (mm) 0.052

0.001 60Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and medium fine sand

CEL.060.T1B.HAR.S2.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.00

9

0.01

8

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 185: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-004 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 96%2.36 95%1.18 94%0.600 91%0.425 90%0.300 89%0.150 79%0.075 57%

Particle Size (microns)52 37%37 33%19 30%10 27%5 25%3 24%1 24%

Median Particle Size (mm) 0.063

0.001 61Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and medium fine sand

CEL.060.T1B.HAR.S2.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 186: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-005 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 95%1.18 87%0.600 79%0.425 72%0.300 60%0.150 11%0.075 5%

Particle Size (microns)56 4%40 4%20 4%10 4%5 4%4 4%1 4%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand

CEL.060.T1B.HAR.S3.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 187: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-006 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 97%2.36 93%1.18 87%0.600 78%0.425 68%0.300 53%0.150 9%0.075 4%

Particle Size (microns)56 3%40 3%20 3%10 3%5 3%4 3%1 3%

Median Particle Size (mm) 0.225

0.001 71Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand

CEL.060.T1B.HAR.S3.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 188: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-007 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 84%2.36 62%1.18 49%0.600 43%0.425 41%0.300 40%0.150 37%0.075 32%

Particle Size (microns)54 16%38 14%19 14%10 14%5 12%3 10%1 10%

Median Particle Size (mm) 1.180

0.001 82Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand

CEL.060.T1B.HAR.S4.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 189: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-008 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 94%

4.75 76%2.36 56%1.18 43%0.600 38%0.425 36%0.300 34%0.150 32%0.075 28%

Particle Size (microns)54 12%38 12%19 12%10 11%5 10%3 9%1 9%

Median Particle Size (mm) 1.180

0.001 84Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Shell, sand and silty clay

CEL.060.T1B.HAR.S4.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 190: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-009 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 98%1.18 94%0.600 88%0.425 82%0.300 71%0.150 40%0.075 23%

Particle Size (microns)54 17%38 16%19 14%10 14%5 12%4 11%1 11%

Median Particle Size (mm) 0.150

0.001 68Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S5.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 191: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-010 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 99%1.18 96%0.600 90%0.425 84%0.300 75%0.150 47%0.075 29%

Particle Size (microns)54 22%38 20%19 20%10 19%5 16%4 16%1 16%

Median Particle Size (mm) 0.150

0.001 67Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S5.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 192: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-011 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 97%1.18 94%0.600 91%0.425 89%0.300 86%0.150 76%0.075 54%

Particle Size (microns)52 38%37 35%18 33%9 30%5 27%3 25%1 25%

Median Particle Size (mm) 0.063

0.001 61Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S6.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.00

9

0.01

8

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 193: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-012 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 98%1.18 96%0.600 94%0.425 92%0.300 88%0.150 78%0.075 60%

Particle Size (microns)52 39%38 33%19 32%10 31%5 28%3 27%1 25%

Median Particle Size (mm) 0.064

0.001 61Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium fine sand and silty clay

CEL.060.T1B.HAR.S6.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 194: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-013 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 79%0.075 23%

Particle Size (microns)56 17%40 15%20 13%10 12%5 11%4 11%1 11%

Median Particle Size (mm) 0.075

0.001 64Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium fine sand and silty clay

CEL.060.T1B.HAR.S7.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 195: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-014 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 98%0.300 96%0.150 74%0.075 15%

Particle Size (microns)56 12%40 10%20 10%10 10%5 9%4 7%1 7%

Median Particle Size (mm) 0.075

0.001 64Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium fine sand and silty clay

CEL.060.T1B.HAR.S7.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 196: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-015 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 89%2.36 73%1.18 60%0.600 46%0.425 34%0.300 18%0.150 2%0.075 2%

Particle Size (microns)56 1%40 1%20 1%10 1%5 1%4 1%1 1%

Median Particle Size (mm) 0.600

0.001 78Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium coarse sand and shell

CEL.060.T1B.HAR.S8.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 197: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-016 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 85%2.36 66%1.18 46%0.600 30%0.425 20%0.300 8%0.150 3%0.075 2%

Particle Size (microns)56 2%40 2%20 2%10 2%5 2%4 2%1 2%

Median Particle Size (mm) 1.180

0.001 82Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium coarse sand and shell

CEL.060.T1B.HAR.S8.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 198: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-017 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 94%2.36 81%1.18 65%0.600 55%0.425 52%0.300 48%0.150 29%0.075 22%

Particle Size (microns)54 17%38 15%19 15%10 15%5 13%4 12%1 12%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S9.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 199: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-018 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 94%2.36 81%1.18 69%0.600 64%0.425 62%0.300 56%0.150 31%0.075 22%

Particle Size (microns)54 15%40 13%20 13%10 13%5 12%4 12%1 12%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S9.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 200: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-019 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 98%1.18 95%0.600 88%0.425 83%0.300 78%0.150 65%0.075 34%

Particle Size (microns)54 25%38 22%19 20%10 19%5 18%4 17%1 17%

Median Particle Size (mm) 0.075

0.001 64Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S10.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 201: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-020 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 99%1.18 96%0.600 92%0.425 89%0.300 86%0.150 77%0.075 47%

Particle Size (microns)54 31%38 28%19 25%10 22%5 20%3 20%1 20%

Median Particle Size (mm) 0.075

0.001 62Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S10.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 202: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-021 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 98%2.36 90%1.18 78%0.600 67%0.425 57%0.300 43%0.150 15%0.075 11%

Particle Size (microns)56 10%40 10%20 9%10 8%5 8%4 8%1 8%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium coarse sand and shell

CEL.060.T1B.HAR.S11.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 203: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-022 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 98%2.36 84%1.18 73%0.600 64%0.425 56%0.300 45%0.150 21%0.075 16%

Particle Size (microns)56 12%40 12%20 10%10 9%5 9%4 9%1 9%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and shell

CEL.060.T1B.HAR.S11.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 204: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-023 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 95%2.36 84%1.18 78%0.600 71%0.425 68%0.300 64%0.150 54%0.075 37%

Particle Size (microns)54 21%38 18%19 16%10 14%5 13%4 13%1 13%

Median Particle Size (mm) 0.075

0.001 65Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, silty clay and shell

CEL.060.T1B.HAR.S12.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 205: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-024 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 96%2.36 86%1.18 80%0.600 74%0.425 71%0.300 68%0.150 56%0.075 34%

Particle Size (microns)54 20%38 16%20 14%10 14%5 14%4 14%1 14%

Median Particle Size (mm) 0.075

0.001 65Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, silty clay and shell

CEL.060.T1B.HAR.S12.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 206: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-025 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 85%2.36 76%1.18 70%0.600 67%0.425 66%0.300 65%0.150 44%0.075 38%

Particle Size (microns)54 22%38 21%19 21%10 21%5 18%3 18%1 18%

Median Particle Size (mm) 0.150

0.001 68Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, silty clay and shell

CEL.060.T1B.HAR.S13.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 207: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-026 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 97%2.36 92%1.18 86%0.600 83%0.425 82%0.300 79%0.150 52%0.075 43%

Particle Size (microns)54 30%38 28%19 28%10 26%5 25%3 25%1 23%

Median Particle Size (mm) 0.075

0.001 65Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S13.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 208: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-027 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 97%2.36 93%1.18 87%0.600 79%0.425 70%0.300 55%0.150 29%0.075 24%

Particle Size (microns)54 20%38 17%19 17%10 17%5 15%3 15%1 15%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S14.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 209: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-028 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 99%1.18 91%0.600 66%0.425 38%0.300 13%0.150 6%0.075 5%

Particle Size (microns)56 5%40 5%20 5%10 5%5 5%4 5%1 5%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Medium coarse sand

CEL.060.T1B.HAR.S14.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 210: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-029 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 72%

4.75 55%2.36 43%1.18 38%0.600 36%0.425 35%0.300 35%0.150 31%0.075 28%

Particle Size (microns)54 14%38 14%19 13%10 13%5 10%3 10%1 9%

Median Particle Size (mm) 2.360

0.001 89Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Shell, sand and silty clay

CEL.060.T1B.HAR.S15.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 211: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-030 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 89%

4.75 70%2.36 58%1.18 49%0.600 44%0.425 42%0.300 40%0.150 30%0.075 24%

Particle Size (microns)54 13%38 12%19 11%10 10%5 10%4 9%1 9%

Median Particle Size (mm) 1.180

0.001 82Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Shell, sand and silty clay

CEL.060.T1B.HAR.S15.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 212: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-031 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 94%2.36 82%1.18 68%0.600 56%0.425 50%0.300 43%0.150 29%0.075 23%

Particle Size (microns)54 16%38 15%19 14%10 14%5 13%4 12%1 12%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, silty clay and shell

CEL.060.T1B.HAR.S16.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 213: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-032 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 97%2.36 85%1.18 70%0.600 56%0.425 50%0.300 43%0.150 25%0.075 19%

Particle Size (microns)54 14%40 12%20 12%10 12%5 12%4 12%1 12%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, silty clay and shell

CEL.060.T1B.HAR.S16.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 214: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-033 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 90%

4.75 79%2.36 65%1.18 56%0.600 49%0.425 45%0.300 39%0.150 28%0.075 24%

Particle Size (microns)54 13%38 12%19 11%10 10%5 9%4 8%1 8%

Median Particle Size (mm) 0.600

0.001 77Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S17.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 215: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-034 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 93%9.5 72%

4.75 63%2.36 55%1.18 50%0.600 47%0.425 45%0.300 42%0.150 35%0.075 31%

Particle Size (microns)54 16%38 16%19 15%10 13%5 11%3 11%1 9%

Median Particle Size (mm) 0.890

0.001 81Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Shell, sand and silty clay

CEL.060.T1B.HAR.S17.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 216: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-035 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 93%2.36 76%1.18 71%0.600 69%0.425 67%0.300 60%0.150 21%0.075 16%

Particle Size (microns)57 11%40 11%20 10%10 10%5 9%4 9%1 9%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S18.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 217: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-036 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 91%2.36 80%1.18 73%0.600 70%0.425 68%0.300 61%0.150 23%0.075 17%

Particle Size (microns)56 11%40 11%20 11%10 11%5 10%4 10%1 10%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S18.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 218: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-037 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 78%1.18 64%0.600 56%0.425 51%0.300 42%0.150 32%0.075 28%

Particle Size (microns)54 18%38 17%19 15%10 13%5 13%4 13%1 13%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S25.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 219: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-038 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 96%2.36 74%1.18 58%0.600 51%0.425 45%0.300 37%0.150 27%0.075 23%

Particle Size (microns)54 15%38 14%19 13%10 11%5 10%4 10%1 10%

Median Particle Size (mm) 0.513

0.001 76Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand, shell and silty clay

CEL.060.T1B.HAR.S25.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 220: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-039 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 93%0.075 71%

Particle Size (microns)54 52%38 45%19 43%10 41%5 37%3 37%1 34%

Median Particle Size (mm) 0.052

0.001 59Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S26.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 221: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-040 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 92%0.075 71%

Particle Size (microns)54 53%38 51%19 47%10 44%5 39%3 39%1 37%

Median Particle Size (mm) 0.033

0.001 55Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S26.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 222: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-041 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 95%0.075 69%

Particle Size (microns)54 48%38 41%19 40%10 38%5 34%3 34%1 32%

Median Particle Size (mm) 0.054

0.001 60Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S27.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 223: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-042 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 99%0.150 97%0.075 70%

Particle Size (microns)52 51%37 47%19 41%10 38%5 37%3 37%1 35%

Median Particle Size (mm) 0.049

0.001 59Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S27.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 224: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-043 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 98%1.18 92%0.600 82%0.425 69%0.300 52%0.150 24%0.075 14%

Particle Size (microns)56 12%40 12%20 11%10 11%5 11%4 11%1 11%

Median Particle Size (mm) 0.225

0.001 71Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and clay

CEL.060.T1B.HAR.S28.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 225: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-044 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 98%1.18 93%0.600 85%0.425 77%0.300 68%0.150 44%0.075 28%

Particle Size (microns)54 21%38 19%19 18%10 18%5 16%3 16%1 16%

Median Particle Size (mm) 0.150

0.001 68Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Sand and silty clay

CEL.060.T1B.HAR.S28.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 226: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-045 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 96%0.075 74%

Particle Size (microns)52 57%38 52%19 48%10 44%5 42%3 42%1 40%

Median Particle Size (mm) 0.029

0.001 54Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S29.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 227: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-046 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 98%0.150 96%0.075 73%

Particle Size (microns)52 54%37 48%18 45%9 43%5 40%3 38%1 36%

Median Particle Size (mm) 0.044

0.001 58Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S29.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.00

9

0.01

8

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 228: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-047 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 99%0.425 99%0.300 99%0.150 99%0.075 83%

Particle Size (microns)52 61%37 59%18 54%10 53%5 49%3 46%1 41%

Median Particle Size (mm) 0.006

0.001 43Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S30.R1

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

8

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 229: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 9-Jul-2012

COMPANY: DATE RECEIVED: 19-Jun-2012

ADDRESS: REPORT NO: EN1202231-048 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 100%0.425 99%0.300 99%0.150 99%0.075 83%

Particle Size (microns)52 61%37 56%18 53%10 50%5 46%3 46%1 41%

Median Particle Size (mm) 0.009

0.001 46Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Technician, NewcastleAuthorised Signatory

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Inpex Sub Benthos Trip 1B Grab

Silty clay and fine sand

CEL.060.T1B.HAR.S30.R2

AS1289.3.6.1/AS1289.3.6.3

25-Jun-12

Cardno Ecology Lab

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

8

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 230: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-001 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 96%2.36 88%1.18 79%0.600 66%0.425 60%0.300 56%0.150 51%0.075 40%

Particle Size (microns)54 33%38 32%19 28%10 28%5 25%4 25%1 25%

Median Particle Size (mm) 0.113

0.001 66Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF C1 - S1 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 231: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-002 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 97%

4.75 92%2.36 88%1.18 80%0.600 69%0.425 63%0.300 59%0.150 55%0.075 43%

Particle Size (microns)54 35%38 33%19 30%10 28%5 26%3 25%1 25%

Median Particle Size (mm) 0.075

0.001 64Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF C1 - S1 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 232: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-003 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 99%0.600 98%0.425 97%0.300 95%0.150 84%0.075 39%

Particle Size (microns)54 27%38 25%19 23%10 21%5 20%3 20%1 20%

Median Particle Size (mm) 0.075

0.001 63Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Fine sand and silty clay

SUB BENTHOS OFF C1 - S2 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 233: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-004 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 99%0.600 98%0.425 98%0.300 97%0.150 85%0.075 33%

Particle Size (microns)54 30%38 29%19 26%10 25%5 23%3 23%1 23%

Median Particle Size (mm) 0.075

0.001 63Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Fine sand and silty clay

SUB BENTHOS OFF C1 - S2 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 234: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-005 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 92%9.5 81%

4.75 71%2.36 61%1.18 48%0.600 35%0.425 28%0.300 23%0.150 19%0.075 14%

Particle Size (microns)54 10%38 10%19 9%10 9%5 8%4 8%1 8%

Median Particle Size (mm) 1.180

0.001 82Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and shell

SUB BENTHOS OFF C1 - S3 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 235: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-006 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 83%

4.75 73%2.36 61%1.18 46%0.600 32%0.425 27%0.300 23%0.150 20%0.075 17%

Particle Size (microns)54 13%38 11%19 11%10 11%5 10%3 10%1 10%

Median Particle Size (mm) 1.180

0.001 83Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF C1 - S3 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 236: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-007 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 91%2.36 82%1.18 70%0.600 52%0.425 42%0.300 35%0.150 28%0.075 17%

Particle Size (microns)54 16%38 14%19 14%10 13%5 12%4 12%1 12%

Median Particle Size (mm) 0.513

0.001 76Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF C1 - S4 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 237: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-008 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 87%2.36 79%1.18 68%0.600 51%0.425 43%0.300 36%0.150 29%0.075 18%

Particle Size (microns)54 16%38 16%19 14%10 14%5 13%4 12%1 12%

Median Particle Size (mm) 0.513

0.001 76Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF C1 - S4 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 238: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-009 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 92%

4.75 77%2.36 70%1.18 60%0.600 48%0.425 44%0.300 40%0.150 37%0.075 28%

Particle Size (microns)54 17%38 16%19 15%10 14%5 13%3 13%1 13%

Median Particle Size (mm) 0.600

0.001 77Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and silty clay

SUB BENTHOS OFF C1 - S5 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 239: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-010 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 89%

4.75 85%2.36 79%1.18 70%0.600 61%0.425 57%0.300 54%0.150 51%0.075 39%

Particle Size (microns)54 25%38 23%19 22%10 21%5 18%3 17%1 17%

Median Particle Size (mm) 0.113

0.001 66Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF C1 - S5 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 240: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-013 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 100%0.425 100%0.300 99%0.150 97%0.075 79%

Particle Size (microns)50 63%37 59%18 56%10 52%5 47%3 43%1 41%

Median Particle Size (mm) 0.008

0.001 45Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Silty clay and fine sand

SUB BENTHOS OFF C2 - S1 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

8

0.03

7

0.05

00.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 241: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-014 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 100%0.425 100%0.300 99%0.150 94%0.075 61%

Particle Size (microns)52 45%38 38%19 35%10 32%5 30%3 28%1 28%

Median Particle Size (mm) 0.052

0.001 60Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Silty clay and fine sand

SUB BENTHOS OFF C2 - S1 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 242: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-015 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 100%0.425 100%0.300 100%0.150 99%0.075 96%

Particle Size (microns)47 86%33 85%17 80%9 71%5 64%3 60%1 53%

Median Particle Size (mm) <0.001

0.001 #N/ASample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Silty clay

SUB BENTHOS OFF C2 - S2 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.00

9

0.01

7

0.03

3

0.04

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 243: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-016 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 100%0.600 100%0.425 100%0.300 99%0.150 99%0.075 91%

Particle Size (microns)50 77%35 75%18 71%9 67%5 61%3 59%1 53%

Median Particle Size (mm) <0.001

0.001 #N/ASample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Silty clay

SUB BENTHOS OFF C2 - S2 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.00

9

0.01

8

0.03

5

0.05

00.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 244: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-017 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 99%1.18 97%0.600 92%0.425 88%0.300 83%0.150 53%0.075 35%

Particle Size (microns)54 33%38 31%19 28%10 27%5 24%3 22%1 22%

Median Particle Size (mm) 0.113

0.001 66Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium fine sand and silty clay

SUB BENTHOS OFF C2 - S3 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 245: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-018 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 97%0.600 92%0.425 88%0.300 82%0.150 53%0.075 38%

Particle Size (microns)55 34%39 32%19 30%10 28%5 26%3 26%1 26%

Median Particle Size (mm) 0.075

0.001 65Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium fine sand and silty clay

SUB BENTHOS OFF C2 - S3 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 246: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-019 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 99%0.600 96%0.425 90%0.300 76%0.150 33%0.075 25%

Particle Size (microns)55 19%39 19%19 18%10 18%5 18%3 18%1 18%

Median Particle Size (mm) 0.150

0.001 69Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium fine sand and clay

SUB BENTHOS OFF C2 - S4 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 247: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-020 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 100%1.18 98%0.600 87%0.425 71%0.300 47%0.150 7%0.075 2%

Particle Size (microns)57 2%40 2%20 1%10 1%5 1%4 1%1 1%

Median Particle Size (mm) 0.300

0.001 72Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium sand

SUB BENTHOS OFF C2 - S4 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 248: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-021 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 89%9.5 89%

4.75 87%2.36 81%1.18 75%0.600 70%0.425 67%0.300 63%0.150 48%0.075 37%

Particle Size (microns)55 28%38 26%19 24%10 23%5 22%3 22%1 22%

Median Particle Size (mm) 0.150

0.001 67Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF C2 - S5 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 249: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-022 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 96%9.5 74%

4.75 64%2.36 55%1.18 46%0.600 40%0.425 37%0.300 35%0.150 26%0.075 19%

Particle Size (microns)54 12%38 12%19 12%10 11%5 11%3 11%1 11%

Median Particle Size (mm) 1.180

0.001 84Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Shell, sand and clay

SUB BENTHOS OFF C2 - S5 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 250: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-023 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 99%1.18 97%0.600 94%0.425 92%0.300 88%0.150 57%0.075 28%

Particle Size (microns)54 27%38 26%19 23%10 22%5 21%3 21%1 21%

Median Particle Size (mm) 0.075

0.001 65Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium fine sand and clay

SUB BENTHOS OFF C2 - S6 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 251: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-024 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 98%1.18 96%0.600 94%0.425 93%0.300 90%0.150 68%0.075 44%

Particle Size (microns)54 37%38 35%19 33%10 30%5 29%3 29%1 29%

Median Particle Size (mm) 0.075

0.001 63Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Medium fine sand and silty clay

SUB BENTHOS OFF C2 - S6 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 252: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-025 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 94%

4.75 88%2.36 79%1.18 69%0.600 58%0.425 51%0.300 44%0.150 34%0.075 22%

Particle Size (microns)54 19%38 18%19 17%10 17%5 17%3 17%1 17%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF SD - S1 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 253: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-026 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 93%2.36 85%1.18 70%0.600 56%0.425 48%0.300 41%0.150 28%0.075 14%

Particle Size (microns)57 13%40 13%20 12%10 10%5 10%4 10%1 9%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and shell

SUB BENTHOS OFF SD - S1 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 254: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-027 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 95%2.36 88%1.18 76%0.600 64%0.425 57%0.300 51%0.150 41%0.075 30%

Particle Size (microns)54 26%38 25%19 21%10 20%5 20%3 20%1 20%

Median Particle Size (mm) 0.225

0.001 71Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF SD - S2 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 255: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-028 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 97%

4.75 95%2.36 88%1.18 73%0.600 57%0.425 48%0.300 42%0.150 32%0.075 25%

Particle Size (microns)54 20%38 19%19 17%10 16%5 16%3 15%1 15%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF SD - S2 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 256: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-029 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 88%2.36 80%1.18 70%0.600 59%0.425 52%0.300 46%0.150 35%0.075 26%

Particle Size (microns)54 20%38 18%19 17%10 16%5 15%3 15%1 15%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF SD - S3 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 257: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-030 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 88%2.36 79%1.18 70%0.600 62%0.425 56%0.300 52%0.150 44%0.075 35%

Particle Size (microns)54 30%38 29%19 25%10 23%5 21%3 19%1 19%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF SD - S3 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 258: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-031 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 95%2.36 87%1.18 77%0.600 65%0.425 58%0.300 50%0.150 40%0.075 30%

Particle Size (microns)54 29%39 28%19 26%10 24%5 23%3 21%1 21%

Median Particle Size (mm) 0.225

0.001 71Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF SD - S4 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 259: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-032 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 98%

4.75 95%2.36 90%1.18 82%0.600 71%0.425 65%0.300 58%0.150 49%0.075 40%

Particle Size (microns)55 31%39 31%19 30%10 28%5 25%3 23%1 23%

Median Particle Size (mm) 0.150

0.001 67Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF SD - S4 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 260: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-033 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 93%2.36 76%1.18 53%0.600 32%0.425 20%0.300 13%0.150 7%0.075 5%

Particle Size (microns)57 5%40 5%20 5%10 5%5 4%4 3%1 3%

Median Particle Size (mm) 0.890

0.001 81Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and shell

SUB BENTHOS OFF SD - S5 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 261: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-034 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 97%

4.75 90%2.36 83%1.18 73%0.600 62%0.425 55%0.300 50%0.150 41%0.075 35%

Particle Size (microns)55 27%39 24%19 23%10 22%5 20%3 20%1 19%

Median Particle Size (mm) 0.300

0.001 72Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF SD - S5 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 262: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-035 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 91%2.36 72%1.18 57%0.600 43%0.425 32%0.300 23%0.150 13%0.075 10%

Particle Size (microns)57 9%40 9%20 9%10 8%5 8%4 7%1 7%

Median Particle Size (mm) 0.600

0.001 79Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and shell

SUB BENTHOS OFF SD - S6 -R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 263: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-036 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 91%2.36 84%1.18 73%0.600 62%0.425 54%0.300 46%0.150 33%0.075 27%

Particle Size (microns)55 19%39 19%19 18%10 16%5 15%3 14%1 14%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF SD - S6 -R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

9

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 264: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-037 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 95%

4.75 84%2.36 78%1.18 68%0.600 58%0.425 52%0.300 46%0.150 37%0.075 31%

Particle Size (microns)55 27%38 26%19 20%10 19%5 17%3 17%1 16%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF Z1 (N) - S1 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

50.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 265: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-038 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 92%

4.75 88%2.36 83%1.18 73%0.600 61%0.425 52%0.300 44%0.150 29%0.075 23%

Particle Size (microns)54 18%38 16%19 15%10 15%5 14%3 14%1 14%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S1 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 266: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-039 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 97%

4.75 87%2.36 81%1.18 72%0.600 60%0.425 52%0.300 44%0.150 31%0.075 22%

Particle Size (microns)54 18%38 17%19 16%10 16%5 13%4 13%1 13%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S2 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 267: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-040 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 91%2.36 80%1.18 67%0.600 55%0.425 48%0.300 41%0.150 30%0.075 24%

Particle Size (microns)54 23%38 22%19 20%10 18%5 18%3 18%1 16%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S2 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 268: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-041 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 80%

4.75 78%2.36 74%1.18 68%0.600 62%0.425 58%0.300 54%0.150 45%0.075 37%

Particle Size (microns)52 26%38 24%19 22%10 21%5 19%3 18%1 17%

Median Particle Size (mm) 0.150

0.001 69Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF Z1 (N) - S3 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 269: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-042 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 94%2.36 86%1.18 77%0.600 66%0.425 59%0.300 52%0.150 39%0.075 33%

Particle Size (microns)54 27%38 25%19 22%10 21%5 19%3 19%1 18%

Median Particle Size (mm) 0.225

0.001 71Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF Z1 (N) - S3 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 270: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-043 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 96%2.36 91%1.18 81%0.600 70%0.425 62%0.300 54%0.150 43%0.075 36%

Particle Size (microns)54 33%38 32%19 28%10 27%5 25%3 23%1 23%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and silty clay

SUB BENTHOS OFF Z1 (N) - S4 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 271: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-044 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 98%2.36 92%1.18 83%0.600 71%0.425 64%0.300 57%0.150 47%0.075 41%

Particle Size (microns)54 36%38 34%19 30%10 28%5 25%3 25%1 25%

Median Particle Size (mm) 0.150

0.001 68Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and silty clay

SUB BENTHOS OFF Z1 (N) - S4 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 272: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-045 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 90%2.36 81%1.18 68%0.600 56%0.425 49%0.300 43%0.150 35%0.075 30%

Particle Size (microns)54 21%38 19%19 18%10 18%5 17%3 17%1 17%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF Z1 (N) - S5 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 273: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-046 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 93%

4.75 87%2.36 81%1.18 71%0.600 59%0.425 51%0.300 44%0.150 33%0.075 26%

Particle Size (microns)54 22%38 22%19 21%10 19%5 16%3 16%1 16%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S5 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 274: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-047 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 96%

4.75 92%2.36 86%1.18 75%0.600 61%0.425 53%0.300 45%0.150 33%0.075 27%

Particle Size (microns)54 22%38 22%19 21%10 20%5 19%3 18%1 18%

Median Particle Size (mm) 0.300

0.001 73Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S6 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 275: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-048 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 94%

4.75 90%2.36 85%1.18 74%0.600 62%0.425 55%0.300 48%0.150 36%0.075 29%

Particle Size (microns)54 21%38 20%19 20%10 19%5 18%3 18%1 18%

Median Particle Size (mm) 0.300

0.001 72Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (N) - S6 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 276: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-049 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 100%2.36 97%1.18 90%0.600 81%0.425 75%0.300 69%0.150 60%0.075 48%

Particle Size (microns)54 38%38 36%19 34%10 32%5 30%3 29%1 29%

Median Particle Size (mm) 0.075

0.001 62Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and silty clay

SUB BENTHOS OFF Z1 (F) - S1 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 277: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-050 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 95%1.18 87%0.600 76%0.425 68%0.300 61%0.150 50%0.075 37%

Particle Size (microns)54 33%38 29%19 27%10 24%5 23%3 23%1 23%

Median Particle Size (mm) 0.150

0.001 67Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and silty clay

SUB BENTHOS OFF Z1 (F) - S1 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 278: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-051 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 97%2.36 88%1.18 74%0.600 60%0.425 51%0.300 44%0.150 31%0.075 22%

Particle Size (microns)54 20%38 20%19 19%10 18%5 18%4 17%1 17%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, clay and shell

SUB BENTHOS OFF Z1 (F) - S2 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 279: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-052 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 99%2.36 95%1.18 84%0.600 67%0.425 56%0.300 48%0.150 34%0.075 24%

Particle Size (microns)54 24%38 22%19 20%10 19%5 19%3 19%1 19%

Median Particle Size (mm) 0.300

0.001 72Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and clay

SUB BENTHOS OFF Z1 (F) - S2 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 280: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-053 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 98%2.36 95%1.18 86%0.600 68%0.425 53%0.300 40%0.150 19%0.075 10%

Particle Size (microns)57 9%40 7%20 7%10 7%5 7%4 7%1 7%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand

SUB BENTHOS OFF Z1 (F) - S3 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 281: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-054 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 95%2.36 92%1.18 86%0.600 77%0.425 72%0.300 67%0.150 58%0.075 49%

Particle Size (microns)52 39%37 38%19 36%10 33%5 32%3 30%1 29%

Median Particle Size (mm) 0.075

0.001 62Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Silty clay and sand

SUB BENTHOS OFF Z1 (F) - S3 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

7

0.05

20.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 282: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-055 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 93%

4.75 83%2.36 80%1.18 72%0.600 66%0.425 61%0.300 55%0.150 41%0.075 35%

Particle Size (microns)54 26%38 25%19 23%10 23%5 22%3 22%1 19%

Median Particle Size (mm) 0.150

0.001 70Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, silty clay and shell

SUB BENTHOS OFF Z1 (F) - S4 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 283: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-056 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 95%

4.75 81%2.36 72%1.18 61%0.600 50%0.425 43%0.300 35%0.150 22%0.075 18%

Particle Size (microns)54 13%38 13%19 13%10 13%5 12%3 12%1 12%

Median Particle Size (mm) 0.513

0.001 76Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (F) - S4 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 284: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-057 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 97%

4.75 89%2.36 82%1.18 70%0.600 57%0.425 48%0.300 41%0.150 26%0.075 20%

Particle Size (microns)54 19%38 18%19 17%10 17%5 17%3 17%1 17%

Median Particle Size (mm) 0.425

0.001 75Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand, shell and clay

SUB BENTHOS OFF Z1 (F) - S5 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 285: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-058 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 90%

4.75 85%2.36 80%1.18 69%0.600 53%0.425 42%0.300 34%0.150 16%0.075 10%

Particle Size (microns)57 9%40 9%20 9%10 9%5 8%4 8%1 8%

Median Particle Size (mm) 0.513

0.001 76Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and shell

SUB BENTHOS OFF Z1 (F) - S5 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

70.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 286: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-059 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 99%

4.75 97%2.36 93%1.18 86%0.600 75%0.425 63%0.300 46%0.150 23%0.075 18%

Particle Size (microns)54 18%38 18%19 18%10 18%5 18%3 18%1 18%

Median Particle Size (mm) 0.300

0.001 72Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand and clay

SUB BENTHOS OFF Z1 (F) - S6 - R1

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.01

9

0.03

8

0.05

40.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 287: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

#REF!ALS Environmental

Newcastle, NSW

CLIENT: DATE REPORTED: 30-Jul-2012

COMPANY: DATE RECEIVED: 19-Jul-2012

ADDRESS: REPORT NO: EN1202683-060 / PSD

PROJECT: SAMPLE ID:

Particle Size Distribution Particle Size (mm)Percent Passing

150 100%75 100%

37.5 100%19.0 100%9.5 100%

4.75 98%2.36 91%1.18 80%0.600 65%0.425 53%0.300 38%0.150 10%0.075 6%

Particle Size (microns)56 4%40 4%20 4%10 4%5 4%4 4%1 4%

Median Particle Size (mm) 0.363

0.001 74Sample Comments: Analysed:

Loss on Pretreatment NA Limit of Reporting: 1%

Sample Description: Dispersion Method Shaker

Test Method: Hydrometer Type ASTM E100TRUE

Soil Particle Density (<2.36mm) 2.65 g/cm3

Hamish MurrayLaboratory Supervisor, NewcastleAuthorised Signatory

Sand

SUB BENTHOS OFF Z1 (F) - S6 - R2

AS1289.3.6.1/AS1289.3.6.3

23-Jul-12

Cardno Ecology Lab

Brookvale, NSW Australia 21004 Green Street

Samples analysed as received.Soil Particle Density required for Hydrometer analysis according to AS 1289.3.5.1—2006 was not requested by the client . Typical sediment SPD values used for calculations and consequently, NATA endorsement does not apply to hydrometer results

Certificate of Analysis

Kate Reeds

EL12047061 Cardno-Inpex

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

0.00

1

0.00

5

0.01

0

0.02

0

0.04

0

0.05

60.

075

0.15

0

0.30

0

0.42

50.

600

1.18

2.36

4.75 9.5

19.0

37.5

Clay Fine Silt MediumSilt

Coarse Silt Fine Sand MediumSand

CoarseSand

FineGravel

MediumGravel

CoarseGravel

NATA Accreditation: 825 Site: NewcastleThis document is issued in accordance with NATA’s accreditation requirements.Accredited for compliance with ISO/IEC 17025. This document shall not be reproduced, except in full.

ALS Laboratory Group Pty Ltd5 Rosegum RoadWarabrook, NSW 2304pH 02 4968 9433fax 02 4968 [email protected]

Page 1 of 1

Page 288: Subtidal Benthos Monitoring Baseline Report - inpex.com.au · Subtidal Benthos Monitoring Baseline Report Ichthys Nearshore Environmental Monitoring Program Prepared for INPEX Cardno

Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX

APPENDIX K DIST LM RESULTS

Ichthys Nearshore Environmental

Monitoring Program

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Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX Page K-1

Appendix K. Results of distance based linear model for infaunal assemblages and physico-chemical variables (median grain size, ORP and pH). 1. Infauna (inshore)

VARIABLES1 Median Grain Size2 pH3 ORP

Total SS(trace): 1.2625E5

MARGINAL TESTSVariable SS(trace) Pseudo-F P Prop.Median Grain Size 2121.7 0.78625 0.7196 1.68E-02pH 6870.7 2.6474 0.0014 5.44E-02ORP 3986 1.4996 0.0648 3.16E-02

res.df: 46

Specified solution Adj R 2̂ R^2

4.28E-02 0.10391

Percentage of variation explained by individual axes % explained variation % explained variation out of fitted model out of total variationAxis Individual Cumulative Individual Cumulative1 54.33 54.33 5.65 5.652 30.06 84.38 3.12 8.773 15.62 100 1.62 10.39

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Subtidal Benthos Baseline Monitoring gram Ichthys Nearshore Environmental Monitoring Program

Prepared for INPEX Page K-2

2. Infauna (offshore)

VARIABLES1 Median Grain Size Trial2 pH Trial3 ORP Trial

Total SS(trace): 1.5405E5

MARGINAL TESTSVariable SS(trace) Pseudo-F P Prop.Median Grain Size 3668.1 1.3659 0.1138 2.38E-02pH 3375.5 1.2545 0.1772 2.19E-02ORP 7156.9 2.7284 0.0002 4.65E-02

res.df: 56

Specified solution Adj R 2̂ R^2 4.21E-02 9.26E-02

Percentage of variation explained by individual axes % explained variation % explained variation out of fitted model out of total variationAxis Individual Cumulative Individual Cumulative1 53.52 53.52 4.95 4.952 25.67 79.19 2.38 7.333 20.81 100 1.93 9.26