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Seaweed distribution on the area of artificial reefs in Geumo-do, Yeosu

전남 여수 금오도 인공어초 설치 해역의 해조류 분포

  • Kim, C.W. (Korea National College of Agriculture and Fisheries) ;
  • Jeong, D.S. (Korea National College of Agriculture and Fisheries)
  • Published : 2015.07.30

Abstract

The distribution of seaweed was examined in Jeonnam archipelago marine ranching area, the coastal of geumo-do, Yosu. Abundance and distribution of seaweed in dropping site of artificial reef were sampled at 6 station at October 2007. Seaweed community were investigated with quadrat method at line-transect by scientific SCUBA divers. as a result, 30 species in total, 4 green, 9 brown and 15 red seaweed were identified. Range of seaweed biomass in all sampling stations were about 1,600~4,000 g/m2. At intertidal zone, appearance of individuals and dominance rate were showed higher than below the subtidal line and at depth from 4m to 6m, individuals, dominance rate and biomass were represented low level. characteristic of water in marine ranching area is turbidity and also compensation depth is low. For that reason, individuals of seaweed community were smaller from depth of 4 meters. Therefore, when equip the artificial reef for preparation of seaweed beds need consider that equipment periods(early spring; before releasing marine seaweed spore) and suitable water depth(3~6m).

2017년도 여수 금오도에서 패조류 어초설치와 해조번식을 위한 베드장 조성을 위하여 해조류 생물상 조사한 결과 해조류 출현종은 녹조류 4종, 갈조류 9종, 홍조류 15종으로 총 30종이 출현하였으며 현존량도 1600~4000g/m2로 같은 시기의 다른 지역보다 높게 나타났다. 상부인 조간대에서는 출현종수와 우점도가 가장 높게 나타났으며 조하대인 수심 1~3m에서는 해조류 현존량이 높은 것으로 나타났다. 그러나 수심 4~6m의 하부에서는 출현종, 우점도 및 현존량 모두 낮게 나타났다. 본 조사시 나타난 특징은 금오도 지역은 조하대 수심 4~6m권에서 갯녹음현상 발생으로 해조류 군집이 급격이 감소되어 이 해역에 해조류형 어초나 해조배드를 설치하여 자원량을 증강시키는 것이 필요 할 것으로 사료되었다. 또한 해조류형 어초시설의 경우 투하시기는 해조류의 포자가 방출되기 전인 시기인 초봄시기에 시설되는 것이 바람직 할 것으로 생각되며 수심은 보상심도가 유지되는 3~6m권내에 설치 될 수 있도록 하는 것이 효율적이라고 판단된다.

Keywords

References

  1. Arevalo, R., S. Pinedo, and E. Ballesteros, 2007. Changes in the com-position and structure of Mediterranean rocky-shore communities following a gradient of nutrient enrichment: Descriptive study and test of proposed methods to assess water quality regarding macroalgae. Mar. Poll. Bull., 55: 104-113.
  2. Bray, J. R. and Curtis, J. T., 1957. An ordination of upland forest community of Southern Wisconsin. Ecol. Ybnogr., 27: 325-349.
  3. Choi, C. G., J. H. Kim, and I.K. Chung, 2008. Temporal variation of seaweed biomass in Korean coasts: Yokjido, Gyeongnam Prov-ince. Algae, 23: 311-316.
  4. Clarke, K. R. and R. M. Warwick, 2001. Change in marine communities: an approach to statistical analysis and interpretation. PRIMER-E Ltd., Polymouth U.K.
  5. Lee, K. H., H. I. Yoo, and H. G. Choi, 2007. Seasonal community structure and vertical distribution of medicinal seaweeds at Kkotji in Taean Peninsula, Korea. Algae, 22: 209-219.
  6. Lee, Y. P. 2008. Marine algae of Jeju. Academy Press, Seoul, 477pp.
  7. Margalef, R., 1958. Information theory in ecology. Gen. Syst., 3:157-175.
  8. McNaughton, S. J., 1967. Relationship among functional properties of California Grassland. Nature, 216: 168-169.
  9. McNaughton, S. J., 1968. Structure and function in California grassland. Ecology, 49: 962-972.
  10. Pielou, E. C., 1966. The measurement of diversity in different types of biological collections. T. Theoret. Biol., 13: 131-144.
  11. Shannon, C. E. and W. Weaver, 1963. The mathematical theory of communication. Univ. Illinois, Press, Urbana, pp.177.
  12. Wells, E., M., Wilkionson, P. Wood, and C., Scanlan, 2007. The use of macroalgal species richness and composition on intertidal rocky seashores in the assessment of ecolodical quality under the Euro-pean water framework directive. Mar. Pollut. Bull., 55: 151-161.
  13. Yoshida, T., 1998. Marine algae of Japan. Uchida Rokakuho Publ. Tokyo. 1222pp.
  14. 柿元 皓, 1966. 人工魚礁の效果範圍につ いて. 水産增殖. 14(4) 181-189.
  15. 菊地省吾, 浮永久, 秋山和未, 鬼頭鈞, 1975. アワビ餌料藻類の造林技術開發.淺海 域における增養殖漁場の開發に關する 綜合硏究. 東北水硏硏究資料集. 10-31.
  16. 강재원, 1968. 한국동식물도감. 제8권 식물편(해조류), 문교부.