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ZOOPLANKTON ASSEMBLAGES IN SEMATAN RIVER
SEMATAN SARAWAK
Nurul Syaza Bt ZainGI
QL 123 N974 Bachelor of Science with Honours 2011 (Aquatic Resource Science and Management)
2011
hsat Khldt MaklamatAkademik UNlVERSm MALAYSIA SARAWAK
Zooplankton Assemblages in Sematan River Sematan Sarawak
PKHIDMAT MAKLUMAT AKADIMIK
111111111 fIlii 111111111 1000235688
Nurul Syaza Bt Zainol
This project is submitted in partial fulfillment ofthe requirements for the degree of
Bachelor of Sciences with Honours
(Aquatic Resource Science and Management)
I Faculty of Resource Science and Technology
UNIVERSITI MALAYSIA SARA W AK
2011
Acknowledgement
Alhamdulillah Thanks for God I would like to express my thankfulness to my
supervisor En Mohd Nasarudin Harith for his supports and guidance through this year until
able to complete this study I would love to thank my parents Zainol b Yusoff and Habsah bt
Hamid and other family members for their financial and emotional supports Thank you to Mr
Azlan Mr Nazri Miss Nur Atiqah bt Mohamad Yusoff and all FRSTs staff that involved in
Sematan River water sampling and for their helps and advices Last but not least I would like
to express my gratitude to all Aquatic Sciences lectures and class members for their advice
support love and care
DECLARATION
I hereby declare that no portion of the work referred to in this dissertation has been submitted
in support of an application for another degree of qualifications of this or any other university
or institution of higher learning
Nurul Syaza Zainol (22069)
Program of Aquatic Resource Science and Management
Department of Aquatic Science
Faculty ofResources Sciences and Technology
University Malaysia Sarawak
II
Pusat Khidmat Mlkiumat AkJdemik UNIVERSm MALAVSIA SARAWAK
Table of Contents
Acnowledgement I
Declaration II
Table of Contents III
List of Abbreviation V
List of Tables VI
List of Figure VII
List of Appendices VIII
Abstract 1
10 Introduction 2
20 Literature Review 5
21 Distribution of zooplankton 5
22 Freshwater zooplankton 6
23 Classification of Zooplankton 9
24 Importance ofZooplankton 11
25 Relation between zooplankton and physico-chemical characteristic 12
26 Behaviors ofZooplankton 14
30 Material and Method 15
31 Sampling Site 15
32 Field work 17
33 Laboratory work and analysis 18
331 Zooplankton analysis 18
33 2 Water quality analysis 20
34 Data analysis 24
341 Species diversity ofzooplankton composition 24
342 Similarity analysis ofzooplankton composition 24
343 Statistical analysis 25
III
_ I
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
hsat Khldt MaklamatAkademik UNlVERSm MALAYSIA SARAWAK
Zooplankton Assemblages in Sematan River Sematan Sarawak
PKHIDMAT MAKLUMAT AKADIMIK
111111111 fIlii 111111111 1000235688
Nurul Syaza Bt Zainol
This project is submitted in partial fulfillment ofthe requirements for the degree of
Bachelor of Sciences with Honours
(Aquatic Resource Science and Management)
I Faculty of Resource Science and Technology
UNIVERSITI MALAYSIA SARA W AK
2011
Acknowledgement
Alhamdulillah Thanks for God I would like to express my thankfulness to my
supervisor En Mohd Nasarudin Harith for his supports and guidance through this year until
able to complete this study I would love to thank my parents Zainol b Yusoff and Habsah bt
Hamid and other family members for their financial and emotional supports Thank you to Mr
Azlan Mr Nazri Miss Nur Atiqah bt Mohamad Yusoff and all FRSTs staff that involved in
Sematan River water sampling and for their helps and advices Last but not least I would like
to express my gratitude to all Aquatic Sciences lectures and class members for their advice
support love and care
DECLARATION
I hereby declare that no portion of the work referred to in this dissertation has been submitted
in support of an application for another degree of qualifications of this or any other university
or institution of higher learning
Nurul Syaza Zainol (22069)
Program of Aquatic Resource Science and Management
Department of Aquatic Science
Faculty ofResources Sciences and Technology
University Malaysia Sarawak
II
Pusat Khidmat Mlkiumat AkJdemik UNIVERSm MALAVSIA SARAWAK
Table of Contents
Acnowledgement I
Declaration II
Table of Contents III
List of Abbreviation V
List of Tables VI
List of Figure VII
List of Appendices VIII
Abstract 1
10 Introduction 2
20 Literature Review 5
21 Distribution of zooplankton 5
22 Freshwater zooplankton 6
23 Classification of Zooplankton 9
24 Importance ofZooplankton 11
25 Relation between zooplankton and physico-chemical characteristic 12
26 Behaviors ofZooplankton 14
30 Material and Method 15
31 Sampling Site 15
32 Field work 17
33 Laboratory work and analysis 18
331 Zooplankton analysis 18
33 2 Water quality analysis 20
34 Data analysis 24
341 Species diversity ofzooplankton composition 24
342 Similarity analysis ofzooplankton composition 24
343 Statistical analysis 25
III
_ I
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Acknowledgement
Alhamdulillah Thanks for God I would like to express my thankfulness to my
supervisor En Mohd Nasarudin Harith for his supports and guidance through this year until
able to complete this study I would love to thank my parents Zainol b Yusoff and Habsah bt
Hamid and other family members for their financial and emotional supports Thank you to Mr
Azlan Mr Nazri Miss Nur Atiqah bt Mohamad Yusoff and all FRSTs staff that involved in
Sematan River water sampling and for their helps and advices Last but not least I would like
to express my gratitude to all Aquatic Sciences lectures and class members for their advice
support love and care
DECLARATION
I hereby declare that no portion of the work referred to in this dissertation has been submitted
in support of an application for another degree of qualifications of this or any other university
or institution of higher learning
Nurul Syaza Zainol (22069)
Program of Aquatic Resource Science and Management
Department of Aquatic Science
Faculty ofResources Sciences and Technology
University Malaysia Sarawak
II
Pusat Khidmat Mlkiumat AkJdemik UNIVERSm MALAVSIA SARAWAK
Table of Contents
Acnowledgement I
Declaration II
Table of Contents III
List of Abbreviation V
List of Tables VI
List of Figure VII
List of Appendices VIII
Abstract 1
10 Introduction 2
20 Literature Review 5
21 Distribution of zooplankton 5
22 Freshwater zooplankton 6
23 Classification of Zooplankton 9
24 Importance ofZooplankton 11
25 Relation between zooplankton and physico-chemical characteristic 12
26 Behaviors ofZooplankton 14
30 Material and Method 15
31 Sampling Site 15
32 Field work 17
33 Laboratory work and analysis 18
331 Zooplankton analysis 18
33 2 Water quality analysis 20
34 Data analysis 24
341 Species diversity ofzooplankton composition 24
342 Similarity analysis ofzooplankton composition 24
343 Statistical analysis 25
III
_ I
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
DECLARATION
I hereby declare that no portion of the work referred to in this dissertation has been submitted
in support of an application for another degree of qualifications of this or any other university
or institution of higher learning
Nurul Syaza Zainol (22069)
Program of Aquatic Resource Science and Management
Department of Aquatic Science
Faculty ofResources Sciences and Technology
University Malaysia Sarawak
II
Pusat Khidmat Mlkiumat AkJdemik UNIVERSm MALAVSIA SARAWAK
Table of Contents
Acnowledgement I
Declaration II
Table of Contents III
List of Abbreviation V
List of Tables VI
List of Figure VII
List of Appendices VIII
Abstract 1
10 Introduction 2
20 Literature Review 5
21 Distribution of zooplankton 5
22 Freshwater zooplankton 6
23 Classification of Zooplankton 9
24 Importance ofZooplankton 11
25 Relation between zooplankton and physico-chemical characteristic 12
26 Behaviors ofZooplankton 14
30 Material and Method 15
31 Sampling Site 15
32 Field work 17
33 Laboratory work and analysis 18
331 Zooplankton analysis 18
33 2 Water quality analysis 20
34 Data analysis 24
341 Species diversity ofzooplankton composition 24
342 Similarity analysis ofzooplankton composition 24
343 Statistical analysis 25
III
_ I
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Pusat Khidmat Mlkiumat AkJdemik UNIVERSm MALAVSIA SARAWAK
Table of Contents
Acnowledgement I
Declaration II
Table of Contents III
List of Abbreviation V
List of Tables VI
List of Figure VII
List of Appendices VIII
Abstract 1
10 Introduction 2
20 Literature Review 5
21 Distribution of zooplankton 5
22 Freshwater zooplankton 6
23 Classification of Zooplankton 9
24 Importance ofZooplankton 11
25 Relation between zooplankton and physico-chemical characteristic 12
26 Behaviors ofZooplankton 14
30 Material and Method 15
31 Sampling Site 15
32 Field work 17
33 Laboratory work and analysis 18
331 Zooplankton analysis 18
33 2 Water quality analysis 20
34 Data analysis 24
341 Species diversity ofzooplankton composition 24
342 Similarity analysis ofzooplankton composition 24
343 Statistical analysis 25
III
_ I
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
40 Result and Discussion 26
41 Zooplankton assemblages 26
411 Zooplankton genera occurrence 26
412 Zooplankton genera composition and abundances 29
413 Comparison of individual zooplankton composition in
different season 34
414 Zooplankton Diversity 39
415 Zooplankton Similarities 41
42 Water Quality Parameters 43
421 Selected physico-chemicals parameters 43
43 Relationship ofEnvironmental parameter to zooplankton assemblages 55
44 Correlation analysis between zooplankton diversity and
environmental parameter 59
50 Conclusion 62
60 References 64
70 Appendices 69
IV
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
I
List of Abbreviations
TEMP Temperature
DO Dissolved oxygen
BOD Biochemical oxygen demand
pH Potential ofHydrogen
TSS Total suspended solids
N03-N Nitrate nitrogen
NH4-N Ammonia- nitrogen
pol Orthophosphate
NTU Nephelometric Turbidity Units
degC Degree Celsius
mglL milligram per Liter
L Liter -Ii
v
I
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
I
I
Table
1
2
3
4
5
6
7
8
9
10
List of Tables
Description
Classification of zooplankton based on sizes
Classification of zooplankton based on their planktonic life
Briefdescription of sampling stations
Nutrient water analysis (Hach DR 2010)
Zooplankton genera occurrence in all stations
Distribution of zooplankton composition at all stations
Different zooplankton composition of dry and wet season
Zooplankton diversity
Sorensens index ()of zooplankton genera found in all stations
Correlation analysis (r) between zooplankton diversity and water quality variable
Page
9
10
18
21
28
33
34
39
41
61
VI
1
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Figure
1 (a) I
1 (b)
1 (c)
2
3
4
5
6
7
8
9
10
11
12
13
14
15
List of Figures
Description Page
Malaysia 16
Sematan area 16
6 Sampling site in Sematan River involved during this study Percentage () of zooplankton groups in Sematan River Comparison of individual zooplankton composition in dry and wet season Temperature value recorded at six sampling stations in Sematan River pH value recorded at six sampling stations in Sematan River
16
29
34
43
44
Dissolve oxygen value recorded at six sampling stations in Sematan River Biological Oxygen Demand (BODs) value recorded at six sampling stations in Sematan River
45
46
Salinity value recorded at six sampling stations in Sematan River Turbidity value recorded at six sampling stations in Sematan River
ORP value recorded at six sampling stations in Sematan River
47
48
49
Clorophyl a (mgm3) value recorded at six sampling
stations in Sematan River 50
Ammonia-nitrogen (mgL) value r~corded at six sampling stations in Sematan River
Nitrate-nitrogen (mgL) va)ue recorded at six sampling stations in Sematan River
51
52
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
53
Nitrite-nitrogen (mgL) value recorded at six sampling stations in Sematan River
54
VII
I
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
I
List of Appendices
Appendices Description Page
A Abundance ofthe common zooplankton genera in 69 Sematan River
B Dominant genera and amount of zooplankton 70
C Water Quality Parameters 71
VIII
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Zooplankton Assemblages in Sematan River Sematan Sarawak
Nurul Syaza Bt Zainol
Program of Aquatic Resource Science and Management Faculty of Resources Sciences and Technology
University Malaysia Sarawak
ABSTRACT
A study on the zooplankton assemblages in Sematan River Sematan Sarawak was carried out to evaluate the species composition species diversity species similarity abundance distribution and selected water physicoshychemical parameters Zooplankton and water samples were collected from six sampling stations at 7-8 August 2010 for dry season and 15-16 January 2011 for wet season Zooplankton and water samples be analyzed using standard methods in interpreting infonnation about zooplankton assemblages and its relationship to environmental parameters A total 900 zooplankton belonging to seven groups four taxa and 14 genera were identified Copepoda dominated the zooplankton population which made up of 6844 of total abundance Zooplankton abundance followed the order Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostracagt Rotifera A dominant genus identified in this study was Limnocalanus which represented 2956 of total amount The seasonal pattern was observed which recorded zooplankton composition was much higher during dry season (866 individuals) compared to wet season with lowest present (31 individuals) Species diversity values vary from 0562 to 2042 and recorded mostly in high value for each station during dry season The Sorensens index value falls were much larger in range between 1333 to 7619 among all stations Water temperature of different season turbidity dissolve oxygen pH and nutrients were main environmental parameters which were found to influence zooplankton composition in Sematan River
Key words Zooplankton assemblages environmental parameters dry and wet seasons Sematan River
ABSTRAK
Kajian ke atas kehadiran zooplankton di Sungai Sematan telah dijalankan untuk merekodkan komposisi spesis kepelhagaian spesis persalPan spesies kelimpahan dan parameter telpilih di permukaan air Zooplankton dan sampel air diambit dari enam stesen pada 7-8 Ogos 2010 untuk rusim panas dan 15-16 Januari 2011 untuk musim hujan Zooplankton dan sampel air dianalisis menggunakan kaedah piawai untuk menghasilkan maklumat berkaitan kehadiran zooplankton dan hUbungannya dengan parameter persekitaran Sejumlah 900 zooplankton dari tujuh kumpulan empat taxa dan 14 genera telah dikenakpasti Copepoda menidominasi populasi zooplankton iaitu 6488 dan jumlah kelimpahan Jumlah zooplankton mengikut urutan Copepoda gt Cladocera gt Mollusca gt Protozoa gt Ostracoda gt Anostraca gt Rotijera Genus yang dominan adalah Limnocalanus iaitu 2956 dari jumlah keseluruhan Kelimpahan berdasarkan musim komposisi zooplankton adalah lebih tinggi semasa musim panas (866 individu) berbanding dengan musim hujan (31 individu) Nitai kepelbagaian sepsis yang direkodkan adalah dari 0562 kepada 2042 dan merekodkan nitai yang tinggi untuk setiap stesen semasa musim panas Suhu air berdasarkan perbezaan musim kekeruhan kandungan oksigen pH dan nutrien adalah parameter persekitaran yang utama dalam mempengaruhi komposisi zooplankton di Sungai Sematan
KflkI kunci Kehadiran zooplankton parameter persekitaran musim panas dan musim hujan Sungai Sematan
1
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
10 INTRODUCTION
Zooplankton are essentially non-motile organisms but drift with water current and
therefore they are susceptible to pollutants in the water (Uttah et al 2008) The
physico-chemical parameters and nutrient status of water body play an important role
in governing the production of zooplankton which is the natural food of many species
of fishes (Basu et aI 20 I 0) Dominance of zooplankton community and their
seasonality are highly variable in different water bodies according to their nutrient
status age morphometry and other locational factors of the water (Rajashekhar et al
2009)
Zooplankton can be divided into few different groups such as crustacean rotifers
coelenterates ctenophores annelids and mollusk (Pary1992) Zooplankton more
specifically three taxonomic groups Phylum Rotifera Subclass Copepoda and
Suborder Cladocera are an integral component of freshwater ecosystems (OBrien
2007) In general freshwater zooplankton are dominated by four major group such as
protozoa rotifer and two subclasses of crustacean the cladocerans and copepods
Crustaceans are the most abundant and the main group of zooplankton species
especially those in the orders of Calanoid~ Cyclopoida and Cladocera and the
cyclopoid copepod are often dominat~d in the assemblage (Schiel ND) Cladocerans
are usually most abundant in freshwater ecosystem and the common genera are
Daphnia and Bosmina (Edmondson 1982)
2
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Zooplankton are important contributors in the food webs ofopen-water ecosystems for
both marine and freshwaters They act as important link in the transfer of energy from
the primary producers to the consumers Community structure biomass and
production are influenced by both producers and consumers which function
simultaneously (Mayer et at 1997) Its intermediate position between phytoplankton
and fish the zooplankton can responds to changes in both food and predation (Baloch
et at 2010)
Water quality the physico-chemical and biological characteristics of water plays an
important role in plankton productivity (Yeamin et at 2007) Biological monitoring is
the use of living organisms of zooplankton in purpose to determine the presence
amounts changes in and effects of physical chemical and biotic factors in the
environment (Uttah et at 2008 Baker 1976) The important aspect in water
biological monitoring is species diversity Species diversity can determine the health
status ofan environment (Uttah et at 2008 Ogbeibu and Edutie 2002) The types and
numbers of invertebrates living in the river can determined the health of the river
(Uttah et at 2008) Different types of invertebrate species will have different
tolerances rate to pollution and they are also influenced by the quality of their habitat
Zooplankton play role as indicators of condition of their habitats as they can respond
quickly to their aquatic environmental changes (Basu et at 2010 Thorpe and Covich
1991 and Carriack and Schelske 1997) The factors that influenced the growth and
distribution of zooplankton are some of abiotic factors such as pH alkalinity
temperature carbon dioxide and nutrients which are responsible for the organic
production (Yeamin et aI 2007 Pulle and Khan 2003) The biotic factors such as
3
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
food limitation predation and competition also influence the zooplankton distribution
(Ferdous and Muktadir 2009 Beyst et at 2001 Christou 1998) According to
Pandey (2004) a study that was conducted in river Ramjan of Bihar India revealed
that abiotic parameters such as pH transparency temperature dissolved oxygen and
some micronutrients are related to zooplankton abundance
The previous zooplankton studies in Sarawak have been carried out in Kuching Bay by
Volin (2005) Batang Lupar by Arbe (2007) and Punang Lawas amp Limbang River by
Nuratiqah (2009) However there is still inadequate data especially the assemblages of
zooplankton in Sematan River Thus study of zooplankton assemblages at Sematan
River need to be carried out in order to find the relationship between zooplankton
assemblages and their abundance to the water quality parameters The objectives of the
study are to (1) identify and quantify zooplankton community in Sematan River (2)
discuss the variations in selected water quality parameters (3) find the relationship
between zooplankton distributions with water quality parameters
4
I
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Pusat Khidmat Maldumat Akademlk VNlVERSm MALAYSIA SARAWAK
20 LITERATURE REVIEW
21 Distribution of Zooplankton
Zooplankton are microorganism that float freely in surface water column of water
bodies (Shanna 2008) They are attract to sunlight and nutrient that available and be
adapted to suspension in the sea and freshwater (Battish 1992) They move in the
sunlight zone where food resources are most abundant and they also found in deep
ocean water (Ferdous and Muktadir 2009) Zooplankton distribution primarily
determined by water waves and current (Sharma 2008) They are very weak swimmers
and they drift in water column of ocean seas and fresh water bodies (Ferdous and
Muktadir 2009)
Their abundance and species compltsition of zooplankton community are also
controlled and influenced by their susceptibility to environmental stressors of physical
chemical and biological factors of the water ecosystem Water parameters such as
temperature salinity pH and electrical conductivity can influence the composition and
population density of zooplankton (Sampaio et at 2002) The composition of
zooplankton also can be influenced by the distribution of phytoplankton and its species
composition (K~jalainen et at 1996)
5
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
I
22 Freshwater Zooplankton
The freshwater zooplankton are commonly smaller in size and only represented by
fewer animal compare to marine counterparts (Davies and Otene 2009) The
freshwater zooplankton comprised of Protozoa Rotifera Crustacea Cladocera
Copepoda Ostracoda and Meroplankton organism including insect larvae (Davies and
Otene 2009 Parsons 1980)
221 Protozoa
Planktonic protozoans are classified as unicellular ciliated or flagellated organisms
Ciliates organism are many species in all size classes from lt20 11m to about 2 mm
They graze bacteria unicellular algae filamentous cyanobacteria other protozoa and
occasionally rotifers and micro zooplankton Flagellated organism uses the flagella for
locomotion feeding or both Flagellates are the principal consumers of suspended
bacteria and important grazers of the bacteria in surfaces and sediments (Finlay
1998) Protozoa are feed on either picoplankton or nanoflagellates and small
nanophytoplanktons according to their size (Ferdous and Muktadir 2009) The relative
size of the ~rotozoan to its prey also influences their most efficient food-capturing
mechanism Where the predator to prey length ratio exceeds 10 1 filter-feeding
prevails Where the ratio is smaller than 10 1 raptorial feeding (seeking out and
capturing relatively large individual food particles) is more common (Finlay 1998
Fenchel 1986)
6
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
222 Rotifer
Rotifers can be classified as soft-bodied metazoans of invertebrates and they are
having a very short life cycle among other type of plankton There are only about 100
rotifer species that widely spread are planktonic organism and rotifer life cycles are
influenced by temperature food and photoperiod (Ferdous and Muktadir 2009
Dhanapathi 2000) Rotifers are considered to be the most diverse group of
zooplankton (Baloch 2010) Rotifer may increase into large number in rapidly under
favorable environmental conditions of that area (Dhanapathi 2000)
223 Cladoceran
Cladocerans are an important group among zooplankton They form the most valuable
and nutritive group of crustaceans for fishes in the food chain in water column
(Ferdous and Muktadir 2009) Cladocerans are mostly herbivorous in their feeding
habit (Baloch 2010) that feed on smaller zooplankton bacterioplankton and algae
(Ferdous and Muktadir 2009 Murugan et at 1998) They are able to response against
pollutants which can react in the low concentration ofcontaminants in water column
224 Copepod
Copepods zooplankton have toughest or hardest exoskeleton which can help them to
swim faster compare to any other zooplankton (Ferdous and Muktadir 2009) Their
feeding habits are differing between the three orders of zooplankton copepods
Generally Cyclopoid copepods are carnivorous that live on other zooplankton and fish
7
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
larvae They also feed on algae bacteria and detritus The calanoid copepods are
commonly omnivorous that feed on such as ciliates rotifers algae bacteria and
detritus Their food intake of calanoid copepods is mostly dependent on their age sex
season and food availability The other group is harpacticoid copepods that are mostly
benthic (Ferdous and Muktad ir 2009) Copepod also can tolerate in harsher
environmental forms due to their physical structures and versatile feeding habits
(Ferdous and Muktadir 2009)
225 Ostracod
Ostracods generally are bottom dwellers of water column (Ferdous and Muktadir
2009) They mostly live on detritus and dead phytoplankton These organisms are act
as food for fish and benthic macroipvertebrates in waterbodies (Chakrapani et al
1969 Ferdous and Muktadir 2009)
8
I
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
--- shy Ir
23 Classification of Zooplankton
The classifications of zooplankton are based on their size and duration of their
planktonic life In this aspect zooplankton can be divided into picoplankton
nanoplankton microplankton mesozoplankton macroplankton and megaplankton
(Table 1) Classification of zooplankton based on their stage of development can be
divided into two categories meroplankton and holoplankton
Table 1 Classification of zooplankton based on sizes
(Adapted from Callieri 2002 as cited in Dussart 1965)
Class Example Size
Nanoplankton Flagellates 2-20 1
lm
Microzooplankton Protozoan rotifer 20-200lm
Macrozoop lankton Amphipod shrimp fish larvae 200-2000lm
Megaplankton Copepod gt2000lm
Microzooplankton are a diverse group of organisms that are found in all aquatic
habitats The arthropods which include in the abundant and diverse of copepod are
66 of the total meso zooplankton species (Diebel 1992) The change in the
abundance or species composition of meso zooplankton may reflect fundamental
change in the ocean environment that affecting phytoplankton (Clark 1992) This is
because meso zooplankton are the primary consumers of phytoplankton and plays
important function in energy economy of the sea that forming a vital connection
9
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
between the phytoplankton at the base of the food web to the higher consumer level of
finfis h shellfish bird and mammals (Diebel 1992)
Zoopl ankton can be divided into duration of their planktonic life or their development
stage as summarized in Table 2 which are Holoplankton and Meroplankton (Michael
1990) Holoplankton will remain as plankton for their entire life while meroplankton
will a ct as planktonic organism only in larval stages of their life cycle (Harnzah 2007)
Table 2 Classification of zooplankton based on their planktonic life
(Adapted from Michael 1990)
Class
Holopl ankton
Merop lankton
Example
Copepod d ino flagellatedkrill amphipods
Fish larvae sea urchins seastars crustaceans worm gastropods
Description
Remain plankton for their entire life cycle
Act as planktonic organism only a portion of their life cycle
10
1
II
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
24 Importance of Zooplankton
Zooplanktons contribute significantly to biological productivity of freshwater
ecosystems (Naz 2008) The availability of zooplankton is an important factor that
determines the relative survival of juvenile fishes (Fernando 1994) Young fishes
mostly breed in area where the planktonic organisms are plenty to get sufficient food
for their survival and growth especially in pelagic area Therefore the occurrences and
distribution ofzooplankton can influence the pelagic fishery potentials fishes
Zooplankton plays significant role in aquatic ecosystems (Baloch et at 2010) due to
central position between the autotrophs (algae phytoplankton) and other heterotrophs
(fish and other carnivores) They form an important link in the food web of aquatic
ecosystems (Tevlin and Burgis 1979 Gulati 1982) In addition they are primary
consumer of second trophic level in aquatic food web in most aquatic environments
(Basu et aI 2010 Licandro and Ibaney 2000) Zooplankton forms the principal source
of food for omnivorous and carnivorous fishes (Hossain et at 2007 Prasad and Singh
2003) and also support the necessary amount of protein for the rapid growth of larval
carps (Basu et at 2010 Hussain and Rahman 2008) Zooplankton function to provide
fish with nutrients seeing as fish requires proteins fats carbohydrates mineral salts
and water in the right quantity (Davies and Otene 2009 Guy 1992) Fish can modify
zooplankton biomass and thus also phytoplankton concentration due to changes in the
intensity ofzooplankton grazing (Gulati 1982)
11
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Zooplanktons act as an important group as most of them feed upon and incorporate the
primary producers into their bodies and then make themselves available to next higher
organisms in the food chain (Michael 1968) They contribute significantly to
biological productivity of freshwater ecosystem and playa major role in the energy
transfer at secondary level (Naz 2008) They are very important in the energy
economy of the sea that forming a vital connection between the phytoplankton at the
base of the food web to the higher consumer level including finfish shellfish bird
and mammals (Deibel 1992) Community structure biomass and production are
influenced by both producers and consumers which function simultaneously (Mayer et
ai 1997) The abundance of producer and consumers composition will influenced to
the level ofcommunity structure ofzooplankton in water ecosystem
25 Relationship between zooplankton and physico-chemical characteristic
Zooplankton are highly sensitive to environmental variation and provide important
indication of environmental change or disturbance as a result of their abundance
species diversity or community composition (Sharma et ai 2008) The diversity of
species amount of biomass and abundance of zooplankton community can be used to
determine health of ecosystem (Uttah et ai 2008 Ogbeibu and Edutie 2002)
Zooplankton indicates the quality of the water body in which they are found and as
excellent indicator of the environmental condition by respond to low dissolve oxygen
high nutrient levels toxic contaminant poor or abundance food quality and predation
(Johnson 2000)
12
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
The community interactions in pelagic food webs are affected by small to large scale
of physical chemical and biological processes that are tropicaHy dynamic The
interactions are also governed by nutrient limitation competition predation and other
ecological forces (Mayer et at 1997) Water parameter such as temperature may give
different affect to the zooplankton that depends on their metabolic rate with their
respond to their temperature Organisms like zooplankton tend to adjust temperature
slowly because their metabolic rate cannot respond in drastic temperature change
(Makinster et at 2004) Some zooplankton can survive in colder weather in winter
month and some can thrive in wanner temperature Therefore different plankton group
will flourish under different temperature
Besides that pH is important to act as indicator of the water quality in the water bodies
(Jonna[agadda and Mhere 2000) Water ecosystem that have pH range 6-9 can be
threatened by increasing rate of acidic precipitation and the change in acidic levels will
give risk ofa zooplankton and phytoplankton declination (Makinster et at 2004)
Suspended solid also will give influence to the water quality parameters Too high or
too low concentration of total suspended solid in water may limit the growth and may
cause death of many aquatic organisms (Ntengwe 2006) Turbidity in water column is
caused by the occurrences of suspended of salid such as organic and inorganic matter
plankton silt and clay in the water hodies (Ntengwe 2006) Turbidity may cause the
major effects in blockage of light and smother of organism (Y ong 1999) Some
zooplankton will suffer and risk to declination of their composition due to clogged of
their feeding mechanism by suspended solid in the water
13
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14
Dissolved oxygen also influenced the zooplankton composition Water is considered as
healthy when dissolved oxygen is above SmglL (iLau 2003) The low level of
dissolve oxygen laquo2mgL) would indicate poor water quality and will give the negative
effect on the aquatic life organism
26 Behaviors of Zooplankton
Zooplankton conununity show vertical migration In the water column They
swimming actively both through up and back down again within 24 hours The pattern
of normal diel vertical migration (NDVM) occurs in nocturnal and diurnal Nocturnal
occur when zooplankton goes upward at night and diurnal occur downward during the
day While the reverse diel vertical migration (RDVM) also occurs but it pattern does
not conunon The pattern of migration occur when zooplankton go ascent through the
water column during the day and descent during the night The function for the both
migration are to avoid predators by fish and reduce the risk of mortality (Lampert
1989 in Hays et aI 1996)
Zooplankton are more varied by patchiness diurnal vertical migration and season
Through vertical migration of both type and their presence at varying depths the
zooplankton utilized to assess energy transfer at secondary level (Johanna 1992)
Zooplankton feed on phytoplankton and transfers of plant materials into animal tissue
and be the basic food for higher animals
14