Managing vegetation for multiple benefit outcomes – Diagnosis and Prognosis

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Managing vegetation for multiple benefit outcomes Diagnosis and Prognosis Richard Thackway Presentation to Murray Darling Basin Authority 22 September 2016

Transcript of Managing vegetation for multiple benefit outcomes – Diagnosis and Prognosis

Page 1: Managing vegetation for multiple benefit outcomes – Diagnosis and Prognosis

Managing vegetation for multiple benefit outcomes –

Diagnosis and Prognosis

Richard Thackway

Presentation to Murray Darling Basin Authority22 September 2016

Page 2: Managing vegetation for multiple benefit outcomes – Diagnosis and Prognosis

MDBA has identified two development areas for native vegetation:

1. Analysis framework for evaluation of extent and condition of woody vegetation communities

2. Developing scenarios for future landscape transformation

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Definitions

• Change in a plant community (type) due to effects of land management practices:

– Structure

– Composition

– Regenerative capacity• Resilience = the capacity of an plant community to recover to

a reference state following a change/s in land management

• Transformation = changes to vegetation condition over time• Condition, resilience and transformation are assessed relative

to fully natural a reference state

Vegetation condition

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VAST = Vegetation Assets States and TransitionsNVIS = National Vegetation Information System

VIVIVIIIIII0

Native vegetationcover

Non-native vegetationcover

Increasing modification caused by use and management

Transitions = trend

Vegetation thresholds

Reference for each veg type (NVIS)

A framework for assessing modification of native vegetation extent and condition

Condition states

Residual or unmodified

Naturally bare

Modified Transformed Replaced -Adventive

Replaced - managed

Replaced - removed

Thackway & Lesslie (2008)

Diagnostic attributes of VAST (classes):• Vegetation structure• Species composition• Regenerative capacity

VAST-2 criteria and indicators Change & Trend

NVIS

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Accounting for changes in native veg type, extent and condition

Land managers use LMP to influence ecological function at sites and across landscapes by changing:• Vegetation structure• Species composition and • Regenerative capacity

LMP deliberately &/or unintentionally do this by:• Modifying • Removing and replacing• Enhancing• Restoring• Maintaining• Improving

*

* Natural disturbances

Function

Structure & Composition

LMP = land management practices

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Goal is to develop whole of landscape monitoring of criteria and indicators relative to reference states

0

20

40

60

80

100

1985 1990 1995 2000 2005 2010

Year

FPC

Source: Tim Danaher and Phil Tickle

Site and landscape scales

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1925

Occupation

Relaxation

Anthropogenic change

Net benefit

time

1900 2025 1950

Reference

chan

ge in

veg

etati

on in

dica

tor o

r ind

ex

1850 1875 1975 2000

VAST classes

Evaluation of ecosystem change thatrely on remote sensing metrics however …

Hyperspatial, hypertemoral &

hyperspectral remote sensing

Aerial photos and digital

imagery

Aerial photos

Quantitative

Baseline

Time before remote sensing

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Caution - remote sensing change is relative to a baseline - it is only half the answer – NEED REFERENCE STATE

Zero/constant baseline (e.g. environmental planting = reveg)

Resp

onse

va

riabl

e/s

Time

Start ofactivity/

intervention

Time

Varying baseline (e.g. environmental watering)

Resp

onse

va

riabl

e/s

Single intervention & climatic variability

BaselineResponse to activity/ intervention

Indicator 13: Overstorey height

Indicator 4: ground water

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Photo by Peter Coyne

1740

1906

Phillip Island, South Pacific – extent and condition

Photo State Library NSW: JW Beattie

1860 already denuded

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year

scor

e %

Pine – Hardwood Subtropical Rainforest, Phillip Island, Sth Pac

Pigs released

Uninhabited island

Pigs died out

Goats, rabbit and fowl released

Goats died out

Rabbits eradicated

Rabbit control

commenced

Commenced passive & active

restoration. Minimal ecological

monitoring

Phase 1 Phase 2 Phase 3 Phase 4

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Evaluation framework

• Has been extensively used to evaluate condition outcomes – Diagnosing and reporting condition (i.e. status and trend) of veget

ation types – Evaluating examples of restoration and regeneration

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Tran

sfor

mat

ion

scor

e

Years

1800

2016

Reference

Developing scenarios for future landscape transformation

Modified

Transformed

Replaced/ managed

Residual

Replaced/adventive

VAST Classes

1850 19501900 2000 2050 2100Replaced/ removed

Baseline

Classes can be modelled as extent and condition

Extent native

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NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Reference pre-European: Sydney Blue Gum High Forest

Commenced managing area for recreation. Weed control. Arboretum abandoned

Cleared & sown to improved pasture for grazing & orchard

Commenced grazing native pastures

Indigenous people manage the area

Grazed area gazetted as State Forest, commenced planting arboretum

Area logged for building houses and fences

Commenced managing area as a future production forest. Weed control

Explorers traverse the area and site selected

Ceased grazing. Area purchased as a future working forest

Modified

Transformed

Replaced/ managed or removed

Residual

Replaced /adventive

VAST

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Before developing any scenarios it is critical to assess where, when and how landscapes were/are transformed relative to a reference

Spp compVeg structure

LU = Land Use, LMP = Land Management Practices

VAST Diagnostic attributes

LU & LMPYear

Time

Regen cap

/Function

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Bioregion: Mulga Lands

Reference state: Extent of pre-clearing Regional Ecosystem (RE) 6.3.13Atriplex spp., Sclerolaena spp., species of Asteraceae and/or short grasses open-herbland on alluvial plains

Source: Daniel Ferguson, Queensland Herbarium

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Need to assess which of the 10 key criteria are affected and by how much i.e. Condition

Soil

Vegetation

Regenerative capacity/ function

Vegetation structure & Species composition

1. Soil hydrological status2. Soil physical status3. Soil chemical status4. Soil biological status5. Fire regime6. Reproductive potential7. Overstorey structure8. Understorey structure9. Overstorey composition10. Understorey composition

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NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Function – Regenerative capacity

Criteria #1 Criteria #2

Criteria #3 Criteria #4

Disturbance regime

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NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Function – Regenerative capacity

Criteria #5 Criteria #6

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NSW, SB Bioregion, Cumberland SF, ex-comp 3a, 7a, 7b, 7c Vegetation structure

Indicators:#13: Height#14: Foliage cover#15: Age structure

Indicators:#16: Height#17: Foliage cover#18: Age structure

Criteria #7

Criteria #8

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NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Species composition

Criteria #9

Criteria #10

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Conclusions

• Vegetation types are kept in various extents and condition states depending on social and economic ideals, values, goals and drivers

• Conversions to non-vegetated, non-native and highly modified native commenced at European settlement; the reference state

• Conventional mapping and monitoring of vegetation type, extent and condition using remote sensing is only started around 70 years ago

• Transformations are changes in condition and extent relative to a reference state: function, structure & composition

• Net gains in condition and extent(spatially and temporally) can be accounted for as changes in function, structure and composition

• To achieve long term lasting changes in extent and condition we must engage land managers using language of public and private benefits

• Scenarios that aim to transform extent and condition must be informed locally by evidence of previous land management practices

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Thank you

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Supplementary Information

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Dynamics

Rainfall is assumed the main driver of natural system dynamicsIt is a key dataset used in developing chronologies of effects of land management on vegetation condition:• Period 1900 – current1

• Average seasonal rainfall (summer, autumn, …) is highly correlated to LMP2 and their effects on function, structure and composition

• Rainfall anomaly is calculated above and below the mean• Two year running trend line is fitted to give insights into El Niño and La

Niña events3

1. Bureau of Meteorology: modelled monthly rainfall 5km resolution national dataset 2. LMP – Land management practices3. El Niño events are associated with prolonged periods of below average rainfall and at times, devastating droughts. A rapid onset of a La Niña event, following a severe El Niño event, have been associated with major soil erosion events and major cycles of regeneration and germination

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Differentiating natural disturbance events and land management practices

Photos by Garry Dowling and Richard Thackway

2006 20132009

Low intensity grazing - cell grazing sheep

Severe dust storm Low intensity grazing - cell grazing sheep

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Reference state: Pre-clearing Regional ecosystem 6.3.13 Atriplex spp., Sclerolaena spp., species of Asteraceae and/or short grasses open-herbland on alluvial plains

Illustrates a baseline but not the Reference state

Photo: Melinda Laidlaw

High intensity cattle grazing -Continuous or set stocking

Source: https://publications.qld.gov.au/storage/f/2014-09-18T23%3A49%3A36.560Z/re-seq-landzones.pdf

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A Framework for Program Evaluation

Source: http://sphweb.bumc.bu.edu/otlt/mph-modules/ProgramEvaluation/ProgramEvaluation2.html

Need continuous social learning linked to adaptive management

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Yapp, Walker and Thackway (2010)

VAST 1 Residual/unmodified*

VAST II1 Transformed

* Reference state

Multiple benefits (ecosystem services) and condition states