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Does the Availability of Various Types and Quantity of Food Limit the Community Structure of the Benthos (Mollusks) Inhabiting in the Hard-bottom Subtidal Area?

먹이생물의 종류와 양이 암반 조하대 저서동물(연체동물) 군집구조 결정요소가 될 수 있는가?

  • SON, MIN-HO (Marine Eco-Technology Institute) ;
  • KIM, HYUN-JUNG (Marine Eco-Technology Institute) ;
  • KANG, CHANG-KEUN (School of Earth Sciences and Environmental Engineering, Gwangju Institute of Science and Technology) ;
  • HWANG, IN-SUH (Marine Ecosystem Management Team, Korea Marine Environment Management Corporation) ;
  • KIM, YOUNG-NAM (Marine Ecosystem Management Team, Korea Marine Environment Management Corporation) ;
  • MOON, CHANG-HO (Department of Oceanography, Pukyong National University) ;
  • HWANG, JUNG-MIN (Marine Eco-Technology Institute) ;
  • HAN, SU-JIN (Marine Eco-Technology Institute) ;
  • LEE, WON-HAENG (Marine Eco-Technology Institute)
  • Received : 2019.01.10
  • Accepted : 2019.02.14
  • Published : 2019.02.28

Abstract

Effects of feeding type and food resource availability on community structure of mollusks inhabiting hard-bottom subtidal areas were investigated. By following guidance from several references, mollusks observed in this study were divided into 5 groups according to feeding type - 1) grazing, 2) filter feeding, 3) deposit feeding, 4) omnivorous and 5) predation. The results showed that both grazing and filter feeders were the most numerous, explaining grazing type in the East Sea accounting for 47.9%, 32.6% in the South Sea and 29.6% for filter feeding, and filter feeding as a dominant feeding type in Yellow Sea accounting for 42.3%. Results of this study showed distinctive difference in community structure depending on mechanism of feeding type and geographical areas where sampling took place. With the results, attempts were made to understand whether community structure could be affected by feeding type or feeding availability and found out that community structure depended heavily on food resource availability. In the East Sea where marine algal density was high, the algal community in the forms of thick-leathery and sheet often occurred in water column with high transparency which provides proper environment for growth. In the South Sea where grazing and filter feeding types were predominated similarly, the algal density was high, but had the relative highest phytoplankton density. Whereas in the Yellow Sea showing the lowest algal biomass compared to the one in the East and the South Sea, and phytoplankton density was similar to those. It might be a adequate environment for filter feeders than grazers. This study concluded that community structure of mollusks showing high abundance was present where food resource availability with types and quantity was high.

본 연구에서는 '국가해양생태계종합조사' 결과를 활용하여 "암반 조하대에 서식하는 연체동물의 군집구조가 먹이자원의 종류와 양에 따라 섭식형(feeding type)별로 차이를 보일 수 있는지?"를 확인하였다. 다수의 참고문헌을 바탕으로 연체동물 섭식형을 초식형, 여과섭식형, 퇴적물섭식형, 잡식형, 포식형으로 구분하였을 때, 조사해역에서는 초식형과 여과섭식형이 우점하였다. 해역별로는 동해에서 초식형 비율(47.9%)이 가장 높았고, 남해에서는 초식형(32.6%)과 여과섭식형의 비율(29.6%)이 유사하게 높았으며, 황해에서는 여과섭식형 비율(42.3%)이 우세하여 해역별로 섭식형에 따른 연체동물의 군집구조가 뚜렷한 차이를 보였다. 이 결과를 바탕으로 "연체동물의 해역별 섭식형에 따른 군집구조 차이가 우연한 것인지?" 아니면, 각 "섭식형별 활용 가능한 먹이자원의 종류와 양(조성율, %)적 차이에 의한 것인지?"를 파악한 결과, 섭식형에 따른 군집구조의 차이는 각 섭식형별 활용 가능 먹이자원의 종류와 양적 차이에서 기인됨을 확인하였다. 초식형이 우점한 동해에서는 투명도가 상대적으로 2배 정도 높아 해조류 성장에 유리하였으며, 그 중에서도 엽상형(sheet form)과 다육질형(thick-leathery form)의 해조류 군집이 발달되어 있어 초식형의 먹이자원이 풍부하였다. 한편, 초식형과 여과섭식형의 비율이 유사하게 높았던 남해에서는 해조류 군집이 발달되었을 뿐만 아니라, 식물플랑크톤 밀도가 상대적으로 가장 높았으며, 황해는 타 해역 대비 해조류의 서식량이 가장 낮은 반면 식물플랑크톤의 밀도는 유사하여 여과섭식형의 서식에 유리한 조건이었다. 따라서, 연체동물의 군집구조, 특히 섭식형에 기초한 'Feeding guild'로서의 군집구조는 우연히 결정되는 것이 아니라, 이들의 서식지 내에서 이용 가능한 먹이자원의 종류 및 양이 하나의 주요한 결정 요소로 영향을 미치는 것으로 판단되었다.

Keywords

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Fig. 1. Sampling site of hard-bottom subtidal mollusks and algae in the Korean coasts on May and August from 2015 to 2017 with a specified underwater quadrate and scuba diving.

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Fig. 2. Percent composition of feeding type of hard-bottom subtidal mollusks sampled quantitatively from the East Sea of Korea from 2016 to 2017 (in detail see Table 1) with scuba diving and a specified underwater quadrate (a: - 5 m, b: - 15 m).

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Fig. 3. Percent composition of feeding type of hard-bottom subtidal mollusks sampled quantitatively from the South Sea of Korea from 2015 (or 2016) to 2017 (in detail see Table 1) with scuba diving and a specified underwater quadrate (a: - 5 m, b: - 15 m).

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Fig. 4. Percent composition of feeding type of hard-bottom subtidal mollusks sampled quantitatively from the Yellow Sea of Korea in 2015 and 2017 (in detail see Table 1) with scuba diving and a specified underwater quadrate (a: - 5 m, b: - 15 m).

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Fig. 5. Spacial variation of transparency in the Korean coasts on May and August from 2015 to 2017 measured with a Secchi disk in situ. Location in detail see the Table 2.

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Fig. 6. Percent composition of feeding type of the hard-bottom subtidal mollusks in the Korean coasts. Annual, stational and vertical data were pooled for analysis (a: East Sea, b: South Sea, c: Yellow Sea).

Table 1. Sampling site, in detail, of hard-bottom subtidal mollusks and algae in the Korean coasts on May and August from 2015 to 2017 with a specified underwater quadrate and scuba diving

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Table 2. Survey stations of the transparency in the Korean coasts. Data were collected from MEIS data bank (2015-2017; http://www.meis.go.kr/rest/main)

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Table 3. Sampling stations of the phytoplankton in the Korean coasts. Data were collected from MEIS data bank (2015-2017; http://www.meis.go.kr/rest/main)

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Table 4. Spacial and vertical variation of percent composition (%) of the mollusk’s feeding type based on the quantitative hard-bottom subtidal samples for 2015-2017 with scuba diving and a specified underwater quadrate in the Korean coasts

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Table 5. Spacial and vertical variation of algae biomass with total and two functional forms (sheet (S) and thick-leathery (TL) forms; Litter et al., 1983). Stations represent sum of the number of sampling stations in the each location. Data of the each location were pooled for analysis. Mean represents means of biomass (gDW/m2) of all algae and of the two functional forms at the two vertical positions (- 5 and - 15 m), respectively

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Table 6. Spacial variation of the phytoplankton density in the Korean coasts on May and August from 2015 to 2017. Location in detail see the Table 3

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References

  1. Barnes, R.S.K. and R.N. Hughes, 1988. An Introduction to Marine Ecology. Blackwell Scientific Publications, London, 351 pp.
  2. Bohnsack, J.A., 1979. Photographic quantitative sampling of hard-bottom benthic communities. Bulletin of Marine Science, 29: 242-252.
  3. Brown, K.M., 1997. Size-specific aspects of the foraging ecology of the southern oyster drill Stramonita haemastoma (Kool, 1987). Journal of Experimental Marine Biology and Ecology, 214: 249-262. https://doi.org/10.1016/S0022-0981(96)02775-X
  4. Burns, C.W., 1968. The relationship between body size and filter-feeding cladocera and the maximum size of particle ingested. Limnology and Oceanography, 13: 675-678. https://doi.org/10.4319/lo.1968.13.4.0675
  5. Choi, I.Y., B.K. Hong, K.A. Jeon and M.H. Son, 2006. Echinoderm fauna of Dokdo, Korea. Fisheries Science and Technology, 39: 231-235.
  6. Dauvin, J.C., G. Bellan and D. Bellan-Santini, 2010. Benthic indicators: from subjectivity to objectivity-Where is the line? Marine Pollution Bulletin, 60: 947-953. https://doi.org/10.1016/j.marpolbul.2010.03.028
  7. DeMott, W.R., 1989. Optimal foraging theory as a predictor of chemically mediated food selection by suspension-feeding copepods. Limnology and Oceanography, 34: 140-154. https://doi.org/10.4319/lo.1989.34.1.0140
  8. Grace, R.V., 1983. Zonation of sublittoral rocky bottom marine life and its changes from the outer to the inner Hauraki Gulf, northeastern New Zealand. Tane, 29: 97-108.
  9. Kim, N.G. and J.G. Jang, 2012. Stomach contents of the sea urchins, Anthocidaris crassispina and Hemicentrotus pulcherrimus and characterization of the marine algal community along the Tongyeong coast of Korea. Korean Journal Fisheries and Aquatic Science, 45: 686-693. https://doi.org/10.5657/KFAS.2012.0686
  10. Kwon, J.N., M.J. Jung, D.I. Kim and M.H. Son, 2010. Correlation between community structure of hervivore and succession of macro-algal flora in the subtidal area of East coast of Korea. Korean Journal of Malocology, 26: 185-199.
  11. Levinton, J.S., 1982. Marine Ecology. Prentice-Hall International, Inc., London, 526 pp.
  12. Lim, H.S., J.W. Choi and M.H. Son, 2018. Macrozoobenthic community structure in the shallow subtidal soft-bottom around Wando-Doam Bay during summer season. Journal of Korean Society of Oceanography, 23: 91-108.
  13. Lindeman, K.C., D.A. McCarthy, K.G. Holloway-Adkins and D.B. Snyder, 2009. Ecological Functions of Nearshore Hardbottom Habitats in East Florida: A Literature Synthesis. CSA International, Inc., Florida, 112 pp.
  14. Litter, M.M., D.S. Litter and P.R. Taylor, 1983. Evolutionary strategies in a tropical barrier reef system: functional-form groups of marine macroalgae. Journal of Phycology, 19: 229-237. https://doi.org/10.1111/j.0022-3646.1983.00229.x
  15. Macdonald, T.A., B.J. Burd, V.I. Macdonald and A. van Roodselaar, 2010. Taxonomic and Feeding Guild Classification for the Marine Benthic Macroinvertebrates of the Strait of Georgia, Britich Columbia. Canadian Technical Report of Fisheries and Aquatic Sciences 2874, 63 pp.
  16. Maeng, J.H., K.Y. Kim, Y.R. Kim, M.B. Shon, J.H. Kim and M.H. Son, 2015. Difference in macrobenthic community structures at thermal effluent discharge areas of two nuclear power plants in Korea. Journal of the Korean Society for Marine Environment and Energy, 18: 157-165. https://doi.org/10.7846/JKOSMEE.2015.18.3.157
  17. MEIS, http://www.meis.go.kr/rest/main, Accessed 11 Sep., 2018.
  18. Meyer, D.L., 1973. Feeding behavior and ecology of shallow-water unstalked crinoids (Echinodermata) in the Caribbean Sea. Marine Biology, 22: 105-129. https://doi.org/10.1007/BF00391776
  19. Okumus, I., N. Bascinar and M. Ozkan, 2002. The effects of phytoplankton concentration, size of mussel and water temperature on feed consumption and filtration rate of the Mediterranean mussel (Mytilus galloprovincialis Lmk). Turkey Journal of Zoology, 26: 167-172.
  20. Park, J.S., 1970. The chaetognaths of Korean waters. NFRDI, Busan, 174 pp.
  21. Pianka, E.R., 1982. Evolutionary Ecology, 3rd Edition. Happer & Row, Publishers, New York, 416 pp.
  22. Root, R.B., 1967. The niche exploitation pattern of the blue-gray gnatcatcher. Ecological Monograph, 37: 317-350. https://doi.org/10.2307/1942327
  23. Ruitton, S., P. Francour and C.F. Boudouresque, 2000. Relationships between algae, benthic harbivorous invertebrates and fishes in rocky subtidal communities of a temperate sea (Mediterranean). Estuarine, Coastal and Shelf Science, 50: 217-230. https://doi.org/10.1006/ecss.1999.0546
  24. Seo, I.S., B.M. Choi, K.B. Kim, M.H. Kim, K.T. Yoon, M.B. Shon, C.H. Hwang, J.U. Lee, J.Y. Park and M.H. Son, 2009. Community structure of macrobenthic invertebrates on the Gwaneumpo Tidal Flat, Hallyeohaesang National Park, Korea. Korean Journal of Nature Conservation, 7: 231-245. https://doi.org/10.30960/kjnc.2009.7.4.231
  25. Shimeta, J. and P.A. Jumars, 1991. Physical mechanism and rates of particle capture by suspension feeders. Oceanography and Marine Biology, Annual Review, 29: 191-257.
  26. Son, M.H., J.W. Lee, C.H. Moon, S. Kim and C.K. Chun, 2004a. Latitudinal variation of the number of species and species diversity in shelled gastropods of eastern coast of Korea. Korean Journal of Malacology, 20: 159-164.
  27. Son, M.H., B.K. Hong, S.Y. Hong, K.A. Jeon and C.H. Moon, 2004b. Report of twenty five additional molluscan species from rocky inter-and subtidal area of Dokdo Island, Korea. Korean Journal of Malacology, 20: 135-140.
  28. Van Alstyne, K.L., 1988. Herbivore grazing increase polyphenolic defenses in the intertidal brown alga Fucus distichus. Ecology, 69: 655-663. https://doi.org/10.2307/1941014
  29. Wenner, A.M., 1987. Crustacean and other invertebrates as indicators of beach pollution. In: Marine Organisms as Indicators, eds. Soule, D.F. and Kleppel, G.S., Springer-Verlag, New York, pp. 199-230.
  30. Werner, E. and B. Werner, 1954. Uber den Mechanismus des Nahrungserwerbs der Tunicaten, speziell der Ascidien. Helgol. Wiss. Meeresunters, 5: 57-92 https://doi.org/10.1007/BF01609109
  31. Yoo, J.W., H.J. Kim, H.J. Lee, C.G. Lee, C.S. Kim, J.S. Hong, J.P. Hong and D.S. Kim, 2007. Interaction between invertebrate grazers and seaweeds in the East coast of Korea. Journal of the Korean Society of Oceanography, 12: 125-132.
  32. Yoon, K.T., I.S. Seo, K.B. Kim, B.M. Choi and M.H. Son, 2009. Community structure of macrobenthic fauna in the Hallyeohaesang National Park from Korea Strait, Korea. Korean Journal of Environmental Biology, 27: 124-133.