The diversity and abundance of planktonic copepods were analysed from zooplankton samples collected within six times throughout the year in the Merambong seagrass area. A total of 48 species from 20 genera and 15 families comprising an average of 78.8%, of the total zooplankton populations were recorded throughout the sampling period. Among the copepod groups, calanoids were the most abundant inhabiting all the stations, taking an average of 51.2% of the total copepod populations. The most common species observed in the area were Paracalanus parvus, Paracalanus elegans, Oithona rigida, and Euterpina acutifrons. The highest copepod density was recorded at 17.0±2.8 x104 individuals/m3. Copepod species diversity (H’) and species richness (d) were highest at H’ = 3.58 and d=7.08, respectively. Species evenness (J) was, however, relatively constant (0.9) during the entire sampling period. The findings from this study provide important baseline information for future research and monitoring programs

Md. Yusoff, Fatimah

Peralta, Hazel Monica Matias

Universiti Putra Malaysia Institutional Repository

Status of planktonic copepod diversity in the Merambong seagrass meadow, Johor, Peninsular Malaysia ABSTRACT The diversity and abundance of planktonic copepods were analysed from zooplankton samples collected within six times throughout the year in the Merambong seagrass area. A total of 48 species from 20 genera and 15 families comprising an average of 78.8%, of the total zooplankton populations were recorded throughout the sampling period. Among the copepod groups, calanoids were the most abundant inhabiting all the stations, taking an average of 51.2% of the total copepod populations. The most common species observed in the area were Paracalanus parvus, Paracalanus elegans, Oithona rigida, and Euterpina acutifrons. The highest copepod density was recorded at 17.0±2.8 x104 individuals/m3. Copepod species diversity (H’) and species richness (d) were highest at H’ = 3.58 and d=7.08, respectively. Species evenness (J) was, however, relatively constant (0.9) during the entire sampling period. The findings from this study provide important baseline information for future research and monitoring programs.  Keyword: Copepod; Seagrass area; Diversity; Abundance 

Status of planktonic copepod diversity in the Merambong seagrass meadow, Johor, Peninsular Malaysia

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See	discussions,	stats,	and	author	profiles	for	this	publication	at:	https://www.researchgate.net/publication/273627206Status	of	Planktonic	Copepod	Diversity	in	theMerambong	Seagrass	Meadow,	Johor,Peninsular	MalaysiaArticle	·	March	2015DOI:	10.5923/j.ije.20150502.01READS782	authors:Hazel	Monica	Matias	PeraltaUniversiti	Tun	Hussein	Onn	Malaysia27	PUBLICATIONS			122	CITATIONS			SEE	PROFILEFatimah	Md	YusoffUniversiti	Putra	Malaysia,	Serdang,	Selangor140	PUBLICATIONS			1,205	CITATIONS			SEE	PROFILEAll	in-text	references	underlined	in	blue	are	linked	to	publications	on	ResearchGate,letting	you	access	and	read	them	immediately.Available	from:	Hazel	Monica	Matias	PeraltaRetrieved	on:	18	July	2016International Journal of Ecosystem 2015, 5(2): 39-43 DOI: 10.5923/j.ije.20150502.01  Status of Planktonic Copepod Diversity in the Merambong Seagrass Meadow, Johor, Peninsular Malaysia  Hazel Monica Matias-Peralta1,*, Fatimah Md. Yusoff2  1Department of Technology and Heritage, Faculty of Science, Technology and Human Development, Universiti Tun Hussein Onn Malaysia, Johor, Malaysia 2Marine Biotechnology Laboratory, Institute of Bioscience, Universiti Putra Malaysia, Serdang, Malaysia  Abstract  The diversity and abundance of planktonic copepods were analysed from zooplankton samples collected within six times throughout the year in the Merambong seagrass area. A total of 48 species from 20 genera and 15 families comprising an average of 78.8%, of the total zooplankton populations were recorded throughout the sampling period. Among the copepod groups, calanoids were the most abundant inhabiting all the stations, taking an average of 51.2% of the total copepod populations. The most common species observed in the area were Paracalanus parvus, Paracalanus elegans, Oithona rigida, and Euterpina acutifrons. The highest copepod density was recorded at 17.0±2.8 x104 individuals/m3. Copepod species diversity (H’) and species richness (d) were highest at H’ = 3.58 and d=7.08, respectively. Species evenness (J) was, however, relatively constant (0.9) during the entire sampling period. The findings from this study provide important baseline information for future research and monitoring programs. Keywords  Copepod, Seagrass area, Diversity, Abundance  1. Introduction Copepods are one of the most important components of the zooplankton in marine ecosystems. Particularly, the planktonic marine copepods with size less than 1 mm in length are considered the most abundant metazoans on Earth [1]. Ubiquitous throughout the world’s ocean systems, they form an integral link in marine food webs by bridging the production of the phytoplankton with the meso- and macroplankton [2]. In addition they are the principal conduit for the flow of energy between primary producers and the higher trophic levels. Studies of zooplankton in coastal and even oceanic waters of the world have shown that copepods constitute the most important group in marine zooplankton communities [2]. Copepods dominate the zooplankton of most tropical waters including Malaysia. In fact, studies in the coastal and neritic waters along the Straits of Malacca of the Malaysian Peninsula show that planktonic copepods accounted for more than 60% of the zooplankton collected [3]. The studies also showed that abundance of copepods and meroplanktonic forms in the inshore waters are higher compared with offshore waters [3].  * Corresponding author: hmp1229@gmail.com (Hazel Monica Matias-Peralta) Published online at http://journal.sapub.org/ije Copyright © 2015 Scientific & Academic Publishing. All Rights Reserved  Seagrass beds are a major feature of shallow marine and estuarine areas throughout the world, which support and provides nursery and feeding areas for many species of fish assemblages particularly of those with high commercial values [4-6]. Moreover, the seagrass ecosystems are of great importance to many of the world’s coastal areas because of their important role in enhancing biodiversity through seagrass associated organisms [7], [8]. In Malaysia, the Merambong seagrass meadow which is considered the largest contiguous seagrass meadow and the only one remaining in all of Peninsula is home to many important commercial fish species and crustaceans. In addition, a myriad of microinvertebrates such as zooplankton, particularly planktonic copepods inhabits this ecosystem. Many studies [9-11], have shown the importance of planktonic copepod as food for many species of fish inhabiting the seagrass areas. However, despite their apparent importance in this ecosystem, planktonic copepods have rarely been assessed. Therefore, the objective of this study is to provide the status of planktonic copepod diversity in the seagrass ecosystem in the Merambong shoal, Johor of the Peninsular Malaysia. 2. Materials and Method  2.1. Sampling Location 40 Hazel Monica Matias-Peralta et al.:  Status of Planktonic Copepod Diversity  in the Merambong Seagrass Meadow, Johor, Peninsular Malaysia  The seagrass meadow popularly known as Merambong shoal is approximately 40-ha oval shaped meadow which stretches almost 2 km long at the largest patch located between the Causeway second link and the Pulau Merambong, Southwest of Johor in Peninsular Malaysia [12]. It is the most extensive seagrass covered subtidal shoal in Malaysian waters. The seagrass bed occurs on sandy, muddy banks of Sungai Pulai mangrove estuary on shallow water with an average depth of 2-3 m and a maximum depth of 5 m. The seagrass bed is vegetated by seagrass species which were mainly Enahulus acroides, Halopila spp. and Syringodium spp. among others (Figure 1). Around the area nearby the seagrass meadow is slated for heavy industry – a large port, chemical processing plants, oil and gas refineries and storage and a power plant. 2.2. Sample Collection and Processing Samples collection was undertaken for a period of one year on a bi-monthly basis (from September 2005 – July 2006). Copepod samples were collected using conical shaped (with mouth opening size of 45.0 cm and 1.0 m length) plankton net with 100µ mesh with acrylic plastic cod end. Samples were collected by vertical tows from the deepest depth ( 4.0 m during the highest high tides when water can go up 4.5m in depth) to the surface at every station. Samples were collected from four randomly selected stations (between 1°20'13.20"N 103°36'6.24"E and 1°19'0.51"N 103°35'5.36"E) in the seagrass ecosystem. The samples were then transferred in labelled bottles and preserved with 10% buffered (pH 8.0-8.2) formalin. Samples were filtered in a 350 µm mesh size net filter to separate the bigger organisms (in this case the entire copepod portion passed through the net due to their smaller size). After which the remaining portion were sorted out under dissecting microscope (Nikon model SMZ645) to separate the copepod from non-copepod portions. 2.3. Analyses Copepod species were identified and counted in a Bogorov counting chamber under dissecting microscope (up at least 500 x magnifications). The copepod density was calculated using standard formula [6]. Three biodiversity indices were calculated for each sample: number of species, the Shannon-Weaver Diversity Index, Margalef’s species richness [(d = (S-1)/log(N)] and Pielou’s evenness [(J=H’/loge(S)]. 3. Result In this study, copepods comprised an average of 78.8% (ranging from 77.7% to 81.9%) of the total zooplankton populations throughout the study period (Figure 2). From the copepod samples, a total of 48 species from 20 genera and 15 families were identified (Table 1). Among the copepod groups, calanoids were the most abundant inhabiting all the stations, contributing 51.2% of the total copepod populations. Although, the percentage of calanoids varied from highest  61% to the lowest 28%, throughout the sampling period, they still contribute the highest total average among the other groups. Likewise, calanoid copepods were the most diverse group represented by 33 species (Table 1).   Figure 1.  Map showing the location of the sampling site  Sampling site  International Journal of Ecosystem 2015, 5(2): 39-43 41    Figure 2.  Percentages of copepods and non-copepod portion of the total zooplankton collected throughout the sampling period in the seagrass area Table 1.  List of copepod species found in the seagrass meadows CALANOIDA i. Acartiidae  1 Acartia bispinosa Giesbrecht, 1889  2 Acartia erythraea Carl, 1907  3 Acartia pacifica Steuer, 1915 ii. Calanidae  4 Canthocalanus pauper (Giesbrecht, 1888)  5 Nannocalanus minor (Claus, 1863)  6 Undinula vulgaris (Dana, 1849) iii. Centropagidae  7 Centropages furcatus (Dana, 1849)  8 Centropages orsinii Giesbrecht, 1889  9 Centropages sinensis Chen & Zhang, 1965  10 Centropages tenuiremis Thompson & Scott, 1903 iv. Clausocalanidae  11 Clausocalanus farrani Sewell, 1929  12 Clausocalanus furcatus (Brady, 1883)  13 Clausocalanus minor Sewell, 1929 v. Paracalanidae  14 Acrocalanus gibber Giesbrecht, 1888  15 Acrocalanus gracilis Giesbrecht, 1888  16 Acrocalanus longicornis Giesbrecht, 1888  17 Paracalanus aculateus Giesbrecht, 1888  18 Paracalanus crasirostris (F. Dahl, 1894)  19 Paracalanus elegans Andronov, 1972  20 Paracalanus parvus (Claus, 1863) vi Pontellidae  21 Labidocera acuta (Dana, 1849)  22 Labidocera euchaeta Giesbrecht, 1889  23 Labidocera jaafari Othman, 1986  24 Labidocera javaensis Mulyadi, 1997  25 Labidocera kröyeri (Brady, 1883)  26 Labidocera minuta Giesbrecht, 1889  27 Pontellopsis regalis (Dana, 1849) vii Temoridae  28 Temora discaudata Giesbrecht, 1889  29 Temora stylifera Dana, 1849  30 Temora turbinate  (Dana, 1849) viii Tortanidae  31 Tortanus barbatus (Brady, 1883)  32 Tortanus forcipatus  Giesbrecht, 1889  33 Tortanus gracilis  (Brady, 1883) CYCLOPOIDA ix. Oithonidae  34 Oithona aruensis  Nishida & Ferrari, 1983  35 Oithona brevicornis Nishida, 1985b  36 Oithona rigida (Giesbrecht, 1896)  37 Oithona simplex Farran, 1913 HARPACTICOIDA x. Clytemnestridae  38 Clytemmnestra scutellata Dana, 1848 xi. Euterpinidae  39 Euterpina acutifrons (Dana, 1848) xii. Miraciidae  40 Macrosetella gracilis (Dana, 1848)  41 Miracia efferata (Dana, 1848) POECILOSTOMATOIDA xiii. Sapphirinidae  42 Copilia lata Dana, 1849  43 Copilia mirabilis Dana, 1849 xiv. Corycaeidae  44 Corycaeus crassiusculus Dana, 1849  45 Corycaeus longistylis Dana, 1849  46 Corycaeus pacificus F. Dahl, 1894  47 Corycaeus speciosus Dana, 1849 xv. Oncaeidae  48 Oncaea media Giesbrecht, 1891 The copepod community in the seagrass area was characterized by the dominance and abundance of Paracalanus parvus, Paracalanus elegans, Oithona rigida and Euterpina acutifrons (Fig. 4). Both P. parvus and P. elegans contributed more than 11% of the total copepod abundance, while, O. rigida and E. acutifrons contributed   9% and 8%, respectively to the total copepod abundance (Fig. 4). On the other hand, copepod diversity (Shannon Weiner index (H’) ranged from H’ = 3.41 to H’ = 3.62, being highest during the month of January (Fig. 5). Similarly, the species richness was highest at d = 7.34 during the month of January. Species richness varied from d=5.95 to d=7.34. However, species evenness was found relatively constant at J’=0.97-J=0.99. 4. Discussion  In accordance with other studies [13-16, 3] in the Malaysian coastal waters, copepods were found to dominate the zooplankton population in the seagrass area. The planktonic copepods in the seagrass bed contributed more than 75% of the total zooplankton populations throughout the year. According to [16] planktonic copepods are considered to play a key role in the transfer of energy between primary producers and higher trophic levels in coastal, shelf, and oceanic waters. Calanoid species are the 42 Hazel Monica Matias-Peralta et al.:  Status of Planktonic Copepod Diversity  in the Merambong Seagrass Meadow, Johor, Peninsular Malaysia  most abundant and widely distributed vertically. They are probably the most ecologically significant animals at the first consumer level of the marine plankton and are also the most prominent among the primary carnivores. Studies have suggested that successful growth and reproduction of these planktonic organisms can occur throughout the year both during the wet and dry seasons.   Figure 3.  Overall percentage abundance of different copepod groups in the seagrass area  Figure 4.  Monthly variations in species relative abundance (%) of the four most dominant species in the seagrass meadows and the monthly variations in mean total copepod density (individuals/m3) In the present study, the smaller copepods such as Oithona spp and Paracalanus spp were very common in the seagrass area, which conforms to those of [17-19] who reported significant contribution of smaller copepods not only in terms of dominance and abundance but also sometimes in terms of biomass and grazing pressure on the phytoplankton. These copepods are common in the coastal and estuarine waters [17-19], indicating nearness and linkage to the mangrove environments [20]. Together with Euterpina acutifrons, Paracalanus parvus, Paracalanus elegans and Oithona rigida were responsible for the variation in the total number of the copepod community in the study area.    Figure 5.  Monthly variations of different species diversity indices (species richness, evenness, and Shannon-Weaver diversity index) and variations in the total number of species present in the seagrass meadows Copepods have been regarded as being good indicator of climatic trends and anomalies although they are generally considered as part of zooplankton community [21]. According to [22], copepods are excellent candidate for the study of ecosystem response to climate variability because their life cycle is short. This characteristic makes copepod populations potentially capable to respond to environmental changes and reflect event-scale changes in environmental conditions, hence provide early indications of biological response to climate variability [23]. Moreover, many copepod species are known to be indicator species, whose presence or absence may represent the relative influence of different water types on ecosystem structures [24].  5. Conclusions Due to the great importance of copepods in the coastal ecosystems and for the reasons that diversity of planktonic copepods is rarely assessed in the seagrass area, investigation on their status is essential. The result of this study will provide important baseline information for future scientific research and monitoring programs particularly in the productive seagrass ecosystems ACKNOWLEDGEMENTS This research is supported by the e-Science fund (Project No. 04-01-04-SF0418), IOC-TEMA Research Grant No: 4500025145 and JSPS ACORE MOE program. We thank Perumal Kuppan and Eduardo Peralta for their technical assistance.    International Journal of Ecosystem 2015, 5(2): 39-43 43   REFERENCES [1] Turner, J.T. (2004). The Importance of Small Planktonic Copepods and Their Roles in Pelagic Marine Food Webs. Zoological Studies 43(2), pp. 255-266. [2] Matias-Peralta (2010). Copepod Biodiversity in Selected Tropical Coastal Zone Ecosystems in the Malacca Straits. PhD thesis. Universiti Putra Malaysia. Selangor, Malaysia, 222 pp [3] Rezaei, H. (2002). Ecological Studies on zooplankton from the Straits of Malacca with special reference to copepods. PhD thesis. Universiti Putra Malaysia. Selangor, Malaysia, 265 pp. [4] Pollard, D.A. (1984). A review of ecological studies on seagrass-fish communities with particular reference to recent studies in Australia. Aquatic Botany 18, pp. 3–42. [5] Gilmore, R.G. (1987). Subtropical-tropical seagrass communities of the southeastern United States: fishes and fish communities. Florida Marine Research Publication 42, pp. 117–137. [6] Bell, J.D., Pollard, D.A. (1989). Ecology of fish assemblages and fisheries associated with seagrasses. In: Larkum AWD, McComb AJ, Shepherd SA (eds) Biology of seagrasses. Elesevier, Amsterdam, pp. 565–609. [7] Waycott, M., Duarte, C.M., Carruthers, T.J.B., Orth, R.J. Dennison, W.C., et al. (2009). Accelerating loss of seagrasses across the globe threatens coastal ecosystems. Proceedings of the National Academy of Science of the United States of America 106, pp. 12377–12381.  [8] Orth, R.J., Carruthers, T.J.B., Dennison, W.C., Duarte, C.M., Fourqurean, J.W., et al. (2006). A global crisis for seagrass ecosystems. Bioscience 56, pp. 987–996. [9] Burchmore, J.J., Pollard, D.A., Bell J.D. (1984). Community structure and trophic relationships of the fish fauna of an estuarine Posidonia Australis seagrass habitat in port hacking, New South Wales. Aquatic Botany18, 71-87. [10] Walters, K. Bell, S.S. (1994). Significance of copepod emergence of benthic, pelagic, and phytal linkages in a subtidal seagrass bed. Marine Ecology Progress Series 108, pp. 237–249. [11] Bullard, S.G., Hay, M.E. (2002). Plankton tethering to assess spatial patterns of predation risk over a coral reef and seagrass bed. Marin Ecology Progress Series 225, pp. 17–28. [12] Japar, S.B., Mutaharah, Z.M. and Arshad, A. (2006). Distribution and significance of seagrass ecosystems in Malaysia. Aquatic Ecosystem Health Management 9, pp. 203-214. [13] Sewell, R.B.S. (1933). Notes on a small collection of marine Copepoda from Malay States. Bulletin of the Raffles Museum Singapore 8, pp. 25-31. [14] Chong, B. J., Chua, T.E. (1973). The preliminary study on the distribution of the cyclopoid copepods of the family Oithonidae in the Malaysian waters. Proceeding of Pacific Science Association Marine Sciences Symposium Hong Kong (Dec. 1973), pp. 32 – 36. [15] Arvin, P. L. (1977). 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Zooplankton abundance and grazing at Davies Reef, Great Barrier Reef, Australia. Marine Biology 105, pp. 75-82. [20] Roman, M.R., Dam, H.G., Gauzens, A.L., Napp, J.M. (1993). Zooplankton biomass and grazing at the JGOFS Sargasso Sea time series station. Deep-Sea Research 40, pp. 883-901. [21] Hopcroft, R.R., Roff, J.C., Lombard D. (1998). Production of tropical copepods in Kingston Harbour, Jamaica: the importance of small species. Marine Biology 130, pp. 593–604. [22] Beaugrand, G., Ibañez, F., Reid, P.C. (2000). Long-term and seasonal fluctuations of plankton in relation to hydroclimatic features in the English Channel, Celtic Sea and Bay Biscay. Marine Ecology Progress Series 232, pp. 179-195. [23] Mackas, D.L., Thompson, R.R., Galbraith, M. (2001). Changes in the zooplankton community of the British Columbia continental margin, 1985-1999 and their covariation and oceanographic conditions. Canadian Journal of Fisheries and Aquatic Science 58, pp. 685-702.   [24] Hays, G.C., Richardson, A.J., Robinson, C. (2005). Climate change and marine plankton. Trends in Ecology and Evolution 20, 337-344.  

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Status of planktonic copepod diversity in the Merambong seagrass meadow, Johor, Peninsular Malaysia

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