UNIVERSITI PUTRA MALAYSIA ECOLOGICAL STUDIES …psasir.upm.edu.my/9396/1/FSAS_2002_25_A.pdf · The...
Transcript of UNIVERSITI PUTRA MALAYSIA ECOLOGICAL STUDIES …psasir.upm.edu.my/9396/1/FSAS_2002_25_A.pdf · The...
UNIVERSITI PUTRA MALAYSIA
ECOLOGICAL STUDIES ON ZOOPLANKTON FROM THE STRAITS OF MALACCA WITH SPECIAL REFERENCE TO COPEPODS
HAMID REZAEI-MARNANI
FSAS 2002 25
ECOLOGICAL STUDIES ON ZOOPLANKTON FROM THE STRAITS OF MALACCA WITH SPECIAL REFERENCE TO COPE PODS
By
HAMID REZAEI-MARNANI
Thesis Submitted to the School of Graduate Studies, Universiti Putra Malaysia, in Fulfillment of the Requirement for the Degree of Doctor of Philosophy
November 2002
DEDICATION
***************
To my son Ocean and my wife Elahe/, ***************
To the memory of my late father who can no longer accompany me on these stormy sew;. ***************
He asked, "And what is the Sea to you?"
I answered, "My life's Breath."
The breath of adventure and excitement,
Of challenge and wandering;
Happiness and fulfdment,
Despair and pain;
Of hope and youth,
Patience and yearning.
The breath that God has breathed into my soul, that
I should live with his sea.
Jerome Thomas
ii
Abstract of thesis presented to the Senate of Universiti Putra Malaysia in fulfilment of the requirement for the degree of Doctor of Philosophy.
ECOLOGICAL STUDIES ON ZOOPLANKTON FROM THE STRAITS OF MALACCA WITH SPECIAL REFERENCE TO COPEPODS
By
HAMID REZAEI-MARNANI
November 2002
Chairperson : Professor Fatimah Md. Yusoff, Ph.D.
Faculty : Science and Environmental Studies
The purpose of this study was to analyze the zooplankton composition and
distribution in relation to spatial and temporal variations in the Straits of Malacca. The
distribution of zooplankton, was determined using samples collected from 1 3 to 20
stations during four oceanographic expeditions along the Straits in different periods
between 1998 to 2000. Monthly zooplankton samples were also collected from two
stations at nearshore and offshore waters off Port Dickson from July 2000 to June
200 1 .
Copepods comprised an average of 71 .3%, 7 1 .2%, 70.9% and 57.9% of the total
zooplankton populations during consecutive cruises and were the main group of
zooplankton during each sampling period. Total zooplankton densities were higher in
the near-coastal area than the offshore area. A spatio-temporal variation of
zooplankton standing crop both in terms of biomass and density was not significant.
Higher mean density estimates of total zooplankton (mean of 1 2,9 1 8 ± 5,635 indo m·3)
and that of adult copepods (mean of 2,927 ± 1 ,085 indo m·3) were recorded during
III
cruise II (pre-SW monsoon) compared to other cruises. However. variation of
copepods was temporally insignificant but spatially significant. Higher zooplankton
densities were obtained at 10-20 m depth stratum than any other depth strata.
Maximum peak of copepod densities collected off Port Dickson waters coincided with
NE and pre-SW monsoons when samples were collected horizontally and vertically,
respectively. Depth and salinity in associations with other factors explained the
distributional patterns of copepods in the studied area.
A total of 1 19 species of pelagic copepods belonging to calanoids (76), cyclopoids
(9), harpacticoids (6) and poecilostomatoids (28) were determined during the course
of the present investigation. Of these, nine species are new records for the Straits of
Malacca. Two characteristic copepod communities in the northern and southern parts
of the Straits were distinguished. The shallow southern part was characterised by
high-density values and low species diversity (H' = 2.967), and the dominance of few
coastal species such as Oithona simplex and Paracalanus parvus. The deeper waters
of the northern part were characterised by low-density values, relatively high species
diversity index (H' = 3 .632).
The heavy metal concentrations in mixed zooplankton were relatively low: ranging
from 1 . 1 9- 1 0 1 3 .70 Jlg gol wet weight for copper, 16.54-235.78 Jlg gol wet weight for
zinc, 3.92-36.08 Jlg gol wet weight for lead and from 0.32-4.09 Jlg gol wet weight for
cadmium. Concentrations of copper and zinc were higher in near-coastal than offshore
areas, whereas those of lead and particularly cadmium were higher in offshore areas.
iv
PERPU STAKAAN NIYEftilTI PUTIlA MALAYSIA
Abstrak tesis yang dikemukakan kepada Senat UniJersltl Putra Malaysia sebagai memenuhi keperluan untuk ijazah Doktor Falsafah.
KAJIAN EKOLOGI KE AT AS ZOOPLANKTON DARI SELAT MELAKA DENGAN RUJUKAN KHAS KEPADA KOPEPOD
Oleh
HAMID REZAEI-MARNANI
November 2002
Pengerusi : Profesor Fatimah Md. Yusoff, Ph.D.
Fakulti : Sains dan Pengajian Alam Sekitar
Tujuan kajian ini adalah untuk menganaiisis komposisi dan taburan zooplankton
mengikut faktor ruang dan masa. Taburan zooplankton telah dianalisis dengan
menggunakan sampel daripada 13-20 stesen yang telah dikumpul melalui empat
ekspedisi oseanografi Selat Melaka dari tahun 1998 hingga 2000. Sampel bulanan
kopepod juga telah dikumpul daripada dua stesen di persisiran dan luar persisiran
perairan Port Dickson sepanjang Julai 2000 hingga Jun 2001.
Secara puratanya kopepod menyumbang sebanyak 7 1.3%, 7 1.2%, 70.9% dan 57.9%
daripada keseluruhan populasi zooplankton dalam ekspedisi tersebut dan merupakan
komponen zooplankton utama dalam setiap tempoh persampelan. Zooplankton
menunjukkan kepadatan yang lebih tinggi di perairan pantai berbanding dengan
kawasan perairan yang jauh dari pantai. Hasilan semasa zooplankton bagi kedua-dua
unit biojisim dan kepadatan menunjukkan variasi tidak nyata dari segi faktor ruang
dan masa.
v
Anggaran min densiti yang lebih tinggi bagi jumlah keseluruhan zooplankton (min
12,9 1 8 ± 5,635 indo m-3) dan kopepod dewasa (min 2,927 ± 1 ,085 indo 0103) telah
direkodkan semasa ekspedisi II (Pra-monsun Barat Daya). Walau bagaimanapun
variasi taburan plankton kopepod didapati tidak menunjukkan perbezaan mengikut
faktor masa tetapi berbeza mengikut faktor mango Kepadatan zooplankton yang tinggi
dijumpai pada kedalaman 1 0-20 01 berbanding lapisan kedalaman yang lain.
Kepadatan tertinggi kopepod yang di sampel secara mendatar dan menegak perairan
Port Dickson didapati bersamaan dengan jangkamasa monsun Timor Laut dan Barat
Daya. Faktor sekitaran seperti kedalaman dan saliniti atau melalui gabungan dengan
faktor lain didapati mencorakkan taburan kopepod di kawasan kajian.
Sejumlah 1 19 spesies kopepod pelagik yang terdiri daripada kalanoid (76), siklopoid
(9), harpaktikoid (6) dan posilostomatoid (28) telah dikenalpasti. Daripada jumlah ini,
sebanyak sembilan spesies adalah rekod barn untuk perairan Selat Melaka. Dua ciri
komuniti kopepod di sektor utara dan selatan selat telah dikenalpasti. Sektor selatan
selat yang cetek telah dicirikan dengan nilai-nilai kepadatan yang tinggi dengan
kepelbagaian spesies yong rendah (H' = 2.967), serta kedominan beberapa spesies
zooplankton air cetek seperti Oithona simplex dan Paracalanus parvus. Perairan yang
lebih dalam di sektor utara dicirikan dengan nilai ketumpatan rendah dan
kepelbagaian spesies yang agak tinggi (H' = 3.632).
Kepekatan logam berat dalam zooplankton adalah secara relatifnya; berjulat 1 . 19-
10 13 .70 �g gol berat basah bagi kuprum, 1 6.54-235.78 �g gol berat basah bagi zinc,
3.92-36.08 �g gol berat basah untuk plumbum dan 0.32-4.09 J.1g gol berat basah bagi
vi
kadmium. Kepekatan kuprum dan zink adalah lebih tinggi di kawasan berhanlpiran
pantai daripada kawasan luar pantai, manakala bagi plumbum dan kadmium nilainya I
adalah lebih tinggi di kawasan luar pantai.
vii
ACKNOWLEDGEMENTS
The contributions of my supervisors, Professors Fatimah Md. YusotT and
Othman Ross and Dr. Aziz Arshad are gratefully acknowledged. Thanks are due to the
crew of RIV KK Mersuji and those of RIV KK Jenahak for their technical and
friendly support and their professionalism during the cruises. Field assistance was
given by S. Zubaidah, A. Othman, F. Alasvandi, P. Kuppan, K. Shams, A. Dadollahi,
A. Moussavi and K.A. Aguol. I am sincerely grateful to Professors A. Kawamura, A.T.
Law, A. Ichikawa and T. Noro for their useful comments and suggestions pertinent to
sampling methods and the manuscript. I am also thankful to the following persons for
their critical comments and for the identification of some the copepod species: Dr. N.
Iwasaki, Dr. S. Ohtsuka, Dr. G.A. Boxshall, Dr. R. Huys, Dr. R. Bottger-Schnack and
Dr. Mulyadi.
I am also indebted to E. Ranai-rad, whose computer assistance made this work
possible. Thanks are also due to N. Somchit for the help on SURFER plots. I am
grateful to P. Roustaian, S. Jahangard, A. Christianus, L. Asgari and S. Sugiyama for
their kind supports and encouragement throughout the course of this research. The
present work was supported by JICA (Japan International Cooperation Agency) funds
through the University of Putra Malaysia, Faculty of Science and Environmental
Studies, Malacca Straits Research and Development Centre (MASDEC), and IRP A
project No 0 1-02-04-01 65 .
viii
I certify that an Examination Committee on 14th November 2002 to conduct the final examination of Hamid Rezaei-Marnani on his Doctor of Philosophy thesis entitled "Ecological Studies on Zooplankton from the Straits of Malacca with Special Reference to Copepods" in accordance with Universiti Pertanian Malaysia (Higher Degree) Act 1980 and Universiti Pertanian Malaysia (Higher Degree) Regulations 198 1 . The Committee recommends that the candidate be awarded the relevant degree. Members of the Examination Committee are as follows:
JAPAR SIDIK BUJANG, Ph.D. Associate Professor, Faculty of Science and Environmental Studies, Universiti Putra Malaysia (Chairman)
FATIMAH MD.YUSOFF, Ph.D. Professor, Faculty of Science and Environmental Studies, Universiti Putra Malaysia (Member)
OTHMAN BIN HAJJ ROSS, Ph.D. Professor, Faculty of Science and Technology, Universiti Kebangsaan Malaysia (Member)
AZIZ ARSHAD, Ph.D. Lecturer, Faculty of Science and Environmental Studies. Universiti Putra Malaysia (Member)
TORKEL GISSEL NIELSEN Professor, Department of Marine Ecology, National Environmental Research Institute, Denmark (External Examiner)
AMSHER MOHAMAD RAMADILI, Ph.D. Professor/Deputy Dean School of Graduate Studies Universiti Putra Malaysia
Date: 2 8 NOV 2002
ix
This thesis submitted to the Senate of Universiti Putra Malaysia has been accepted as fulfilment of the requirement for the degree of Philosophy. The members of the Supervisory Committee are as follows:
FATIMAH MD.YUSOFF, Ph.D. Professor, Faculty of Science and Environmental Studies, Universiti Putra Malaysia (Chairperson)
OTHMAN BIN HAJI ROSS, Ph.D. Professor, Faculty of Science and Technology, Universiti Kebangsaan Malaysia (Member)
AZIZ ARSHAD, Ph.D. Lecturer, Faculty of Science and Environmental Studies, Universiti Putra Malaysia (Member)
x
AINI IDERIS, Ph.D. Professorl Dean School of Graduate Studies Universiti Putra Malaysia
Date: 9 JAN 2000
DECLARATION
I hereby declare that the thesis based on my original work except for quotations and citations which have been duly acknowledged. I also declare that it has not been previously or concurrently submitted for any other degree at UPM or other institutions.
Hamid Rezaei-Marnani
Date: ;2. 'B j';).. J 9..��!t.
xi
TABLE OF CONTENTS
Page
DEDICATION II ABSTRACT III ABSTRAK v ACKNOWLEDGEMENTS Vlll APPROVAL IX DECLARATION Xl LIST OF TABLES xv LIST OF FIGURES XVlll LIST OF PLATES XXI LIST OF ABBREVIATIONS XXII
CHAPTER
I INTRODUCTION 1
Background of the Study 2
Statement of Problems 3
Importance of the Study 4
Objectives of the Study 6
II LITERATURE REVIEW 7
Introduction 7 General Hydrographical Conditions in the Straits of Malacca 7 Variability in Zooplankton 9 Composition and Density of Zooplankton 1 3 Vertical and Horizontal Distribution 1 4 Distribution of Species in Relation to Hydrographic Conditions 1 7 Zooplankton Biomass 1 9 Trophic Structure 22 Indicator Species 25 Heavy Metals in Zooplankton 27
III GENERAL METHODOLOGY 3 1
Zooplankton 3 1 Sampling Techniques 3 1
Laboratory Analysis 33
Biomass Estimates 33
Wet Weight 33
Dry Weight 33
xii
Density Estimates 34
Taxonomic Determinations 35
Trophic Groups of Copepods 36
Analysis of Heavy Metals 36
Sampling Techniques 36
Analytical Procedures 37
Statistical Analysis of Data 37
IV ZOOPLANKTON DISTRIBUTION IN THE STRAITS OF 44 MALACCA
Introduction 44
Materials and Methods 45
Sampling Techniques 45
Study Area 45
Hydrological Measurements 46 Trophic Groups 46
Results 50
Variations of Environmental Parameters 50
Total Zooplankton (First Method of Counting) 50
Zooplankton Biomass (Spatio-Temporal Variations) 50
Biomass at Depth Strata 52
Composition of Total Zooplankton 56
Spatio-Temporal Distribution 59 Near-coastal vs Neritic Waters 63
Total Zooplankton at Depth Strata 63
Copepod Assemblages (Second Method of Counting) 73
Composition 73
Spatio-Temporal Distribution and Community 76 Structure Community Analysis 88
Relationship among Stations 88
Community Differences 92
Associations of Copepod Species 99
Linking to Environmental Parameters 99
Distribution of Copepods at Depth Strata 100 Community Structure at Depth Strata 106 Community Differences at Depth Strata 106 Trophic Groups 107
Indicator Species 114 Discussion 116
V COPEPOD ANNUAL CYCLE IN PORT DICKSON 148 COASTAL WATERS
xiii
Introduction 148
Materials and Methods 149
Study Area 149
Sampling Techniques 149
Hydrological Measurements 151
Laboratory Analysis 151
Results 151
Variations of Environmental Parameters 151
Composition of Copepods 153
Spatio-Temporal Variations 154
Samples Taken by Vertical Tow 155
Samples Taken by Horizontal Tow 155
Zooplankton Biomass 163
Nearshore vs Offshore Densities 166
Community Analysis 167
Community Structure 167 Community Differences 169
Linking to Environmental Parameters 170
Trophic Groups 173
Discussion 173
VI HEAVY METALS Cu, Zn, Pb AND Cd IN ZOOPLANKTON 182
Introduction 182 Materials and Methods 182
Study Area and Sampling Techniques 183 Results 184
Heavy Metals in Zooplankton from the Malacca Straits 184
Spatial Distribution 184
Near-Coastal vs Offshore Waters 184
Relationship among Stations 187
Heavy Metals in Zooplankton from Port Dickson 189
Seasonal Variations 191
Nearshore vs Offshore Concentrations 191
Linking to Environmental Parameters 193
Discussion 193
VII GENERAL DISCUSSION AND CONCLUSION 202
BIBLIOGRAPHY 212
APPENDICES 247
BIODATA OF THE AUTHOR 263
xiv
LIST OF TABLES
Table Page 1 Comparison of zooplankton densities for various systems within the 15
Malaysian coastal waters. 2 Some ecological data for zooplankton species occurring in different 23
oceanic regions of the world. " List of indicator species of water mass in different tropical seas. 27 .) 4 Statistical analyses performed during oceanographic cruises in the 42-43
Straits of Malacca and monthly samplings off Port Dickson waters. 5 Sampling regime of zooplankton during 1st expedition in the Straits 48
of Malacca. 6 Sampling regime of zooplankton during 2nd expedition in the Straits 48
of Malacca. 7 Sampling regime of zooplankton during 3rd expedition in the Straits 49
of Malacca. 8 Sampling regime of zooplankton during 4th expedition in the Straits 49
of Malacca.
9 Mean biomass of total zooplankton during each cruise, and at 55 stations and locations that presented maximum biomass.
1 0 List of observed zooplankton species other than copepods in the 64 Straits of Malacca.
1 1 Stations that presented maximum zooplankton density during 65 different cruises.
1 2 Results of two-way ANOV A based on estimates of zooplankton and 65 copepod densities and zooplankton biomass. Here, the random factor, location (northern, central and southern parts of the Straits) and the fixed factor treatment (cruise I, II, III, IV).
13 Correlation matrices for various biological properties in the Straits. 66
14 List of observed copepod species in the Straits of Malacca 77-80 (including monthly sampling in Port Dickson).
1 5 Number of adult copepod families, genera and species identified. 80
16 Mean density (ind. mol) and relative density (%) of copepod orders 8 1 during each cruise.
1 7 Characterization of adult copepods during different cruises. 8 1
1 8 Characterization of adult copepods in all the combined cruises in 8 1 different parts of the Malacca Straits.
1 9 Results of two-way ANOV A based on densities of adult copepods, 89 copepod orders, species richness and diversity index (Shannon). The random factor is location (northern, central and southern parts of the Straits) and the fixed factor, cruise (I, II, III, IV) (n = 69).
xv
20 Summary of the results of one-way ANOSIM. Value of ANOSIM 97 statistic (R) for global test for differences between groups (north, centre, south) in each matrix during the four cruises in the Straits of Malacca.
21 Results of one-way ANOSIM for differences in adult copepod 97 communities among cruises based on the Bray-Curtis similarity matrix using square root-transformed species density data.
22 Major species, ranked in order of importance, contributing to the 98 average dissimilarities between samples from north-south and centre- south parts in the Malacca Straits during cruise IV, as determined by SIMPER analyses based on forth-root transformed estimates and the Bray-Curtis measure of similarity.
23 Major species, ranked in order of importance, contributing to the 100 average dissimilarities between samples from north-south and centre-south parts in the Malacca Straits during combined cruises, as determined by SIMPER analyses based on forth-root transformed estimates and the Bray-Curtis measure of similarity.
24 Summary of the environmental parameters that best (only six best 102 variable combinations) explain the biotic pattern at each cruise, accompanied by the correlation coefficient obtained (BIO-ENV analysis). Parameters measured .were: water column temperature, salinity, nitrate, ortho-phosphate, ammonium and depth.
25 Vertical density of copepod taxa at various depth strata in combined 105 stations in the north (N), centre (C), and south (S) parts of the Malacca Straits. Only species with a relative density of � 2% of the total density of copepods in a given stratum were considered.
26 Results of the one-way ANOSIM for testing the difference in 114 copepod communities among different depth strata in the Straits of Malacca.
27 Results of two-way ANOV A based on densities of copepod with 1 14 different feeding strategies. The random factor is location (northern, central and southern parts of the Straits) and the fixed factor, treatment (cruise I, II, III, IV) (n = 70).
28 Comparison of zooplankton biomass taken by vertical haul for 122 various tropical coastal systems within the Malaysian waters.
29 Comparison of mixed zooplankton and copepod density for various 136 tropical coastal systems.
30 Number of copepod families, genera and species identified from 161 Port Dickson waters.
31 Maximum and minimum monthly values for the copepods with the 161 APFF, at stations sampled by horizontal and vertical tows.
XVI
., .., -'-
33
34
35
36
37
38
39
40
41
Relationships between mean monthly rainfall and mean copepod 161 densities.
Results of the two-way ANOSIM test for treatment (monsoons) and 170 block effects (nearshore/offshore) based on the Bray-Curtis similarity matrix using square root-transformed species density data.
Summary of the environmental parameters that best (only six best 171 variable combinations) explain the biotic pattern by each sampling method (vertical and horizontal), accompanied by the correlation coefficient obtained (BIO-ENV analysis). Parameters measured were: water column temperature, salinity, nitrate, ortho-phosphate, ammonium, amount of rainfall, water transparency (Secchi disk), heavy metals (including Zn, Cu, Pb and Cd) and wind speed.
Summary of the environmental parameters that best (only six best 172 variable combinations) explain the biotic pattern by each sampling method (vertical and horizontal), accompanied by the correlation coefficient obtained (BIO-ENV analysis). Parameters measured were: water column temperature, salinity, nitrate, ortho-phosphate, ammonium and amount of rainfall.
Comparison of mean monthly zooplankton density taken by vertical 178 haul for various tropical coastal systems.
Results of Mann-Whitney U-test based on estimates of heavy metal 186 concentrations in the Malacca Straits (nt = 4; n2 = 11).
Results of Kruskal-Wallis test based on estimates of heavy metal 187 concentrations in different parts of the Malacca Straits (n = 15).
Spearman Rank-correlation coefficients for Copper, Zinc, lead and 187 Cadmium concentrations from mixed zooplankton.
Results of Mann-Whitney U-test based on estimates of heavy metal 191 concentrations in coastal waters of Port Dickson (nt = 10; n2 = 10).
Concentrations of heavy metals in zooplankton collected from 199 varIOUS sea areas.
XVII
LIST OF FIGURES
Figures Page
Surface water currents of Southeast Asian Seas in April (Wyrtki. 10 1961)
2 Surface water currents of Southeast Asian Seas in August (Wyrtki, 10 1961)
3 Surface water currents of Southeast Asian Seas in October (Wyrtki, 11 1961)
4 Surface water currents of Southeast Asian Seas in December (Wyrtki, 11 1961)
5 Schematic illustration of vertical hauling immediately after the lead 32 reached to the seabed.
6 Figure 6: Location of sampling stations. Stations shown with asterisk 47 (*) were also used for heavy metal analysis. Divisions referred to in the text are as follows: N: north, C: centre, S: south.
7 Distribution of zooplankton biomass (log transformed) during cruise I 53 and II.
8 Distribution of zooplankton biomass (log transformed) during cruise 54 III and IV.
9 Mean (± SE) estimates of zooplankton biomass of combined stations 55 in the northern, central and southern parts of the Straits of Malacca.
10 Vertical distribution of total zooplankton biomass in the northern (a), 57 central (b) and southern (c) parts of the Straits of Malacca.
11 Composition (%) of major zooplankton groups during different cruises 60 in the Straits of Malacca.
12 Dendrograms showing classification of stations during each cruise, 67 comprising zooplankton density data. The distinguished clusters are marked with letters A and B.
13 Mean density of total zooplankton (averages from all stations 68 combined) during various cruises in the Straits of Malacca.
14 Mean density of copepods (averages from all stations combined) 68 during various cruises in the Straits of Malacca.
15 Distribution (log transformed, density) of total zooplankton during 69 cruises I and II.
16 Distribution (log transformed, density) of total zooplankton during 70 cruises III and IV.
17 Vertical distribution of total zooplankton density and the percentage 72 of different groups of zooplankton in the northern (a), central (b) and southern (c) parts of the Straits of Malacca.
xviii
18 Distribution (log transformed density) of adult copepods during 82 cruises I and II.
19 Distribution (log transformed density) of adult copepods during 83 cruises III and IV.
20 Species diversity indices during four cruises in the Straits of Malacca. 85
21 Mean (± SE) estimates of copepod species diversity index (a) and 86 adult copepod density (b) of combined stations in different parts of the Straits of Malacca.
22 Distribution of adult copepods (log transformed density), average for 87 4 cruises.
23 Mean (± SE) density estimates of calanoids (a), cyclopoids (b), 90 harpacticoids (c) and poecilostomatoids (d) in different parts of the Straits of Malacca.
24 Dendrogram of group classification by stations for all combined 91 cruises in the Straits of Malacca. � stations with high densities; B, stations with low (81) or moderate densities (82).
25 Dendrograms and Multidimensional Scaling (MDS) plots of stations 93-94 during cruises. The goodness-of-fit of each bidimensional representation is expressed by the corresponding stress value.
26 Species cluster formation based on Bray-Curtis analysis showing 101 affinities of dominant species (> 2% relative abundance) in combined cruises using group average strategy [cluster A (sub-clusters AI and A2), cluster B (sub-clusters BI, B2)]' The partitioning of coastal-neritic species from near-coastal species could be recognized only by few speCIes.
27 Dendrograms showing associations of dominant species at depth strata 104 (combined stations).
28 Percentage composition of copepod orders at depth strata in different 108 parts of the Straits of Malacca.
29 Vertical distribution of dominant calanoids Paracalanus parvus (a), 109-110 harpacticoids Euterpina acutifrons (b), poecilostomatoids Oncaea media (c) and cyclopoids Oithona simp/ex (d) in terms of relative density.
30 Vertical distribution of the copepods along with corresponding 1 1 2 diversity index (H') at depth strata in different parts of the Straits of Malacca.
31 Percentage composition of copepod trophic groups at depth strata in 113 different parts of the Straits of Malacca.
32 Location of stations during monthly sampling. 150
33 Seasonal variations of temperature (a), salinity (b), rainfall (c) and 156 water transparency (d) in the study area.
xix
34 Seasonal vanatlons of dominant copepod species belonging to 157 different orders taken by vertical tow in combined nearshore and offshore statipns.
35 Seasonal variations of copepod density at sampling stations (a), and in 158 combined nearshore/offshore stations (b) taken by vertical tow.
36 Seasonal variations of copepod density at sampling stations (a), and in 158 combined nearshore/offshore stations (b) taken by horizontal tow.
37 Seasonal variations of rainfall and copepod mean densities taken by 162 vertical (a) and horizontal (b) tows in combined nearshore and offshore stations.
38 Seasonal variations of total zooplankton biomass taken by vertical tow 165 (a), horizontal tow (b) and in combined methods of tows (c) at sampling stations.
39 Seasonal variations of species diversity index (H') at nearshore and 168 offshore stations by horizontal tow (a), vertical tow (b) and in combined stations (c).
40 Distribution of Pb concentrations in mixed zooplankton in the Straits 185 of Malacca.
41 Distribution of Cu concentrations (log transformed) in mixed 186 zooplankton in the Straits of Malacca.
42 Distribution of Zn concentrations in mixed zooplankton in the Straits 188 of Malacca.
43 Distribution of Cd concentrations in mixed zooplankton in the Straits 189 of Malacca.
44 Dendrogram (a) and multidimensional scaling plots (b) of stations 190 based on heavy metal concentrations along the Straits of Malacca. The goodness-of-fit of bidimensional representation is expressed by the corresponding stress value.
45 Seasonal variations of heavy metal concentrations 111 mixed 192 zooplankton at nearshore and offshore stations (ND: not detectable). The vertical bars represent the standard error.
46 Annual mean of heavy metal concentrations in mixed zooplankton at 194 nearshore and offshore stations (n =20).
xx
Plates
1
2
3
LIST OF PLATES
RN Mersuji
NORP AC net with flow-meter attached
Neuston net
xxi
Page
38
38
38
LIST OF ABBREVIATIONS
ANOSIM = Analysis of Similarity
ANOVA = Analysis of Variance
APFF = Annual Plankton Fluctuation Factor
BIO-ENV = Biotic-Environmental
C = Centre
ChI. a = Chlorophyll a
Contr. = Contribution
CR = Cruise
cv = Coefficient of variation
Diss. = Dissimilarity
Dry wt. = Dry weight
HSD = Honestly Significant Difference
indo = Individual
IRPA = Intensified Research in Priority Areas
km = Kilometre
JICA = Japan International Co-operation Agency
Log. = Logarithmic
MAS DEC = Malacca Straits Research and Development Centre
Max. = Maximum
MDS = Multidimensional Scaling
J.l.g = mlcro gram
Min. = Minimum
J.l.m = micro meter
xxii
mg m-3 = milligram per cubic meter
N = North
NO = Not detectable
ng = nano gram
NE = Northeast
NORPAC = North Pacific
p = Probability
PNE = Pre-northeast
PRIMER = Plymouth Routines in Multivariate Ecological Research
PSW = Pre-southwest
RJV = Research vessel
S = South
SD = Standard deviation
SE = Standard Error
SIMPER = Similarity Percentages
Stn. = Station
SW = Southwest
Unid. = Unidentified
vs = Versus
Wet wt. = Wet weight
Zoopl. = Zooplankton
xxiii
CHAPTER I
INTRODUCTION
The Straits of Malacca is partially landlocked and is situated on the Western
Malaysian Peninsula with a total coastline of 1000 km (Chin, 1993; Forbes, 1995).
The Straits is located in the tropical zone and supports a relatively abundant demersal
and pelagic fish and shrimp species (Ooi, 1 990). The Straits provides almost 70% of
the fishing resources for the Peninsular Malaysia (Chua et al., 1997). It is of particular
oceanographic interest due to upwelling processes in One Fathom Bank (Wyrtki,
1961; Uktolseya, 1988). The Straits is deeper in the north and gradually becomes
shallower in the south. The Straits is relatively a narrow channel due to the presence
of shoals, and shallow depths in certain parts such as the eastern end near Singapore;
and this limits its ability to dilute and flush out pollutants.
An understanding of marine planktonic food webs requires information on the
density, biomass and the interactions between all trophic levels. A pre-requisite for
the proper management of the fishery resources of the Straits area is an understanding
of some of the basic biological factors, such as spatial and temporal distributions of
zooplankton in relation to environmental parameters due to their importance as the
major food item of the pelagic fish has been reported (Subrahmanyan, 1 959).
Zooplankton constitute one of the important intermediate steps in the food-chain
pyramid of the coastal waters, as well as open ocean waters and plays a critical role in
the ecology of marine systems by serving as links between phytoplankton and
bacterioplankton, and higher trophic levels such as nekton and benthos.