936 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 (Haliotis discus), (Gomphina veneriformis). 1 m, (MOMAF, 25), (Choi et al., 2; Seo and Choi, 21). (Daan, 1973; Mills, 1975; Mc
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1 한수지 47(6), , 214 Original Article Kor J Fish Aquat Sci 47(6), ,214 울진바다목장에서형망으로어획된수산자원의군집구조 윤병선 박정호 윤상철 1 양재형 2 손명호 * 국립수산과학원동해수산연구소, 1 자원관리과, 2 독도수산연구센터 Community Structure of Fisheries Resources Caught by Dredge in the Uljin Marine Ranching Area, Korea Byoung Sun Yoon, Jeong-Ho Park, Sang Chul Yoon 1, Jae Hyeong Yang 2 and Myoung Ho Sohn* Fisheries Resources and Environment Division, East Sea Fisheries Research Institute, National Fisheries Research and Development Institute, Gangneung , Korea 1 Fisheries Resources Management Division, National Fisheries Research and Development Institute, Busan , Korea 2 Dokdo Fisheries Research Center, National Fisheries Research and Development Institute, Pohang , Korea To elucidate the variation of species composition, biomass and size distribution of fishery resource in the Uljin marine ranching area was investigated at the 4 stations from 29 to 21 based on the dredge sampling. During the survey period, a total of 41 fishery resource species were sampled with a mean density of 2,554,633 ind./km 2 and mean biomass was 32,946 kg/km 2. A total 36 fishery resource species were sampled with a mean density of 3,198,793 ind./km 2 and mean biomass 41,177 kg/km 2 in 29 and it were sampled a total 31 species, mean 1,91,473 ind./ km 2 and 24,716 kg/km 2 in 21. The major individual-dominant species, occupying over 1% of total individuals, were Gomphina veneriformis (2,491,818 ind., 82.2%), Umbonium costatum (221,973 ind., 8.7%), Mactra chinensis (49,879 ind., 2.%), Glossaulax didyma hayashii (49,879 ind., 1.9%), Blepharipoda liberate (37,714 ind., 1.5%) and Paguridae spp. (27,266 ind., 1.1%). The major biomass-dominant species, occupying over 1% of total biomass, were G. veneriformis (25,124 kg, 76.3%), G. didyma hayashii (2,596 kg, 7.9%), M. chinensis (2,24 kg, 6.1%), Ovalipes punctatus (921 kg, 2.8%) and Glossaulax didyma didyma (567 kg, 1.7%). From the cluster analysis based on Bray- Curtis similarity matrix of fourth root transformed data of species number and individuals was divided into 2 different groups of the fishery resource community (Group A-St.1, Group B-Sts. 2, 3, 4). The 29 and 21 mean Shell length (mm) of G. veneriformis was mm, mm and M. chinensis was 62.3 mm, mm, respectively. Key words: Uljin marine ranching area, Dredge survey, Fisheries resources, Community structure 서론,, 198 (Fujita, 1987; Yotsui and Maesako, 1993; MIFFAF, 28)., (MOMAF, 25; MIFFAF, 28; Lee et al., 212).,. (Sebastes schlegelii), (Hexagrammos otakii) (Platichthys stellatus), (Paralichthys olivaceus) Kor J Fish Aquat Sci 47(6) , December 214 This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial Licens ( permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited. Received 7 November 214; Revised 15 December 214; Accepted 23 December 214 *Corresponding author: Tel: Fax: address: smh837@korea.kr Copyright 214 The Korean Society of Fisheries and Aquatic Science 935 pissn: , eissn:
2 936 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 (Haliotis discus), (Gomphina veneriformis). 1 m, (MOMAF, 25), (Choi et al., 2; Seo and Choi, 21). (Daan, 1973; Mills, 1975; Mclntyre, 1978), (Bilyard, 1987; Ling and Clark, 1983)... 조사정점및방법 재료및방법 2 km 2,, ( 1.5Ø) (Paik et al., 27) (3, 6, 9, 12 ) 4 (Fig. 1). 14 cm, 2 cm, 2.5 cm, 15 m., (Mactra chinensis) Vernier callipers (Shell length, SL).1 mm, ( ).1 g. (km 2 ). 생태지수및군집분석 (H, Piolou, 1977) (D, Simpson, 1949). Fig. 1. Map showing the sampling stations of fisheries resources with dredge from 29 to 21 in the Uljin marine ranching area, Korea. (C ij ) (S i, S j ) Bray-curtis (BC; Bray-Curtis, 1957) (%), fourth root. (dendrogram) (cluster analysis), complete linkage. SIMPER, PRIMER V5. (Clarke and Warwick, 21). 통계분석,,, SPSS version 12. for Windows paired t-test, t-test.,,,, ANOVA test Turkey-T.
3 울진바다목장형망수산자원의군집구조로수정 937 종수 결과 (29-21 ) , 12, 6, 3, 1 (Fig. 2) , , 8, 4 (paired t-test, P>.5) ( 8.6 ), 2 22 ( 11. ), 3 24 ( 9.9 ), 4 23 ( 11.1 ), Number of species Abundance(1, Ind./km 2 ) Biomass(kg/km 2 ) (Fig. 3, ANOVA, P>.5) , , 9 1.4, (ANOVA, P>.5). 개체수 2,554,633 ind./km 2, 29 3,198,793 ind./km 2, 21 1,91,473 ind./km (Fig. 2, paired t-test, P=.48). 29 3,45,53 ind./km 2, 134,643 ind./km 2, 12,494 ind./km ,841,224 ind./km 2, Biomass(kg/km 2 ) Abundance(1, Ind./km 2 ) Number of species Mar. Jun. Sep. Dec. Mar. Jun. Sep. Dec Year St.1 St.2 St.3 St.4 Station Fig. 2. Temporal variations of number of species, abundance and biomass of fisheries resources in the Uljin marine ranching area from 29 to 21. Fig. 3. Spatial variations of number of species, abundance and biomass of fisheries resources in the Uljin marine ranching area from 29 to 21.
4 938 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 59,857 ind./km 2, 4,756 ind./km 2 29 (paired t-test, P=.33). 1 2,125,134 ind./km 2, 2 2,62,969 ind./km 2, 3 2,882,125 ind./km 2, 4 2,688,34 ind./km 2 (Fig. 3, ANOVA, P>.5). 3 2,262,92 ind./km 2, 6 2,669,2 ind./km 2, 9 3,636,673 ind./km 2, 12 1,649,919 ind./km (ANOVA, P=.45), (ANOVA, P>.5). 생체량 32,946.4 kg/km ,176.6 kg/km ,716.3 kg/km (Fig. 2, paired t-test, P=.34) ,329.7 kg/km 2 1,949.5 kg/km 2, kg/km ,52.3 kg/km 2, kg/km 2, g/km 2 29 (paired t-test, P=.31). 1 24,817.8 kg/km 2, 2 34,557.4 kg/km 2, 3 35,827.1 kg/km 2, 4 36,583.4 kg/km 2 (Fig. 3, ANOVA, P>.5). 3 34,45.8 kg/km 2, 6 31,35.8 kg/km 2, 9 42,888. kg/km 2, 12 23,411.1 kg/km (ANOVA, P=.19), (ANOVA, P>.5). 우점종 1% 6 4, %. 2,491,818 ind./km 2 (82.2%), (Umbonium costatum) 221,973 ind./km 2 (8.7%). 49,879 ind./km 2 (2.%), (Glossaulax didyma hayashii) 49,879 ind./km 2 (1.9%), (Blepharipoda liberata) 37,714 ind./km 2 (1.5%), (Paguridae spp.) 27,266 ind./km 2 (1.1%) (Fig. 4). 29 2,491,818 ind./ km 2, 21 1,71,184 ind./km (paired t-test, P=.48), Abundance (Ind./km 2 ) Gomphina veneriformis Umbonium costatum Mactra chinensis Glossaulax didyma hayashii Blepharipoda liberata Paguridae sp. Mar. Jun. Sep. Dec. Mar. Jun. Sep. Dec Year Fig. 4. Temporal variations of the abundance of six dominant species in the Uljin marine ranching area from 29 to 21. (paired t-test, P>.5). 1.% %. 25,124 kg/km 2 (76.3%), 2,596 kg/km 2 (7.9%), 2,24 kg/km 2 (6.1%) (Ovalipes punctatus) 921 kg/ km 2 (2.8%), (Glossaulax didyma didyma) 567 kg/km 2 (1.7%) (Fig. 5) ,575 kg/km 2, 21 18,674 kg/km 2
5 울진바다목장형망수산자원의군집구조로수정 Gomphina veneriformis Glossaulax didyma hayashii Diversity(H') Biomass (kg/km 2 ) Mactra chinensis Ovalipes punctatus Dominance(D') Mar. Jun. Sep. Dec. Mar. Jun. Sep. Dec Year 1..5 Fig. 6 Temporal variations of the species diversity and the dominance index in the Uljin marine ranching area from 29 to Fig. 5. Temporal variations of the biomass of five dominant species in the Uljin marine ranching area from 29 to 21. (paired t-test, P<.5), (paired t-test, P>.5). 군집분석 Year Glossaulax didyma didyma Mar. Jun. Sep. Dec. Mar. Jun. Sep. Dec., (H').73, 29.61, (Fig. 6, paired t-test, P>.5). (D').69, 29.69, (paired t-test, P>.5).,, 2 Group (Fig. 7). Group A , Group B , Group B (Group B-1) (Group B-2). Group A Group B SIMPER 5% 7 (Table 1). 1.49% Group A ,295 ind./km 2 14,153 ind./km 2 Group B ,274 ind./km 2. Group A 5 ind./km 2 Group B 663 ind./km 2 1.4%. Group A Group B, (Neocrangon communis) (Ammodytes personatus) Group A. Group B Group B-1 Group B-2, Group B-1 65 ind./km 2 Group B-2 6,694 ind./ km %
6 94 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 Fig. 7. Dendrogram and schematic representation of space distribution based on Bray-Curtis similarity matrix of fourth root transformed data of species number and abundance in the Uljin marine ranching area from 29 to 21. Table 1. Species contributions to dissimilarity between Group A and Group B in the Uljin marine ranching area from 29 to 21 Rank Species Average abundance (Ind./km 2 ) Group A Group B Contribution (%) Cumulation (%) 1 Umbonium costatum 2,56 2, Mactra chinensis Gomphina veneriformis 18,23 19, Neocrangon communis Glossaulax didyma hayashii Paguridae spp Ammodytes personatus (Table 2). Group B-1 22,83 ind./km 2 Group B-2 15,214 ind./ km %.,, (Matuta planipes),,, Group B-1 Group B-2 Group B-2. 각장조성 mm, mm (t-test, P<.5), mm
7 울진바다목장형망수산자원의군집구조로수정 941 Table 2. Species contributions to dissimilarity between Group B-1 and Group B-2 in the Uljin marine ranching area from 29 to 21 Rank Species Average abundance (Ind./km 2 ) Group B-1 Group B-2 Contribution (%) Cumulation (%) 1 Umbonium costatum 65 6, Gomphina veneriformis 22,83 15, Paguridae sp Blepharipoda liberata Matuta planipes Ovalipes punctatus Glossaulax didyma didyma Mactra chinensis 311 1, mm, mm 29.7 mm, mm 29.7 mm, mm 29.8 mm (Fig. 8, t-test, P<.5) mm mm mm, mm mm mm mm 5-52 mm, mm mm, mm 5-51 mm, mm mm mm, mm (t-test, P<.5), mm 21, mm mm, mm mm, mm 5.9 mm (Fig. 8, t-test, P<.5). 1, mm mm mm 38-4 mm mm 7-74 mm mm mm, 48-5 mm mm, mm 7-74 mm. 고찰 , 12, 6, 3, 2, 1 m, 2 cm, 2.5 cm. (Choi et al., 2; Hwang and Kim, 23; Ko et al., 212),.,. Cha et al. (212) 2, Jung et al. (213) 1. Choi et al. (2) 24, Ko et al. (212) 29, 3 m. 27 (MIFFAF, 28) 28 (MIFFAF, 29) , ,
8 942 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 Fig. 8. Length frequency distribution of Gomphina veneriformis and Mactra chinensis by year and station in the Uljin marine ranching area from 29 to 21.., ,.,. 2,491,818 ind./km 2 (82.2%) 25,124 kg/ km 2 (76.3%), ,556 kg/ km 2 43,839 kg/km 2 (MIFFAF, 28; 29) % % 75.6%
9 울진바다목장형망수산자원의군집구조로수정 ,973 ind./ km 2 (8.7%) 282 kg/km 2 (.9%), (Choi et al., 2; Yoon et al., 211), 27 (MIFFAF, 28; 29). 49,879 ind./ km 2 (2.%) 2,24 kg/km 2 (6.1%) ,925 kg/km 2, 1,123 kg/km %. 49,879 ind./km 2 (1.9%) 17,65 ind./km 2 (.7%), 2,596 kg/km 2 (7.9%) 567 kg/km 2 (1.7%), ,28 kg/km kg/km 2. 37,714 ind./km 2 (1.5%) 21 ind./km 2 (.6%), 27,266 ind./km 2 (1.1%) 195 ind./km 2 (.6%), 22,31 ind./km 2 (.9%), 921 kg/km 2 (2.8%), (MIFFAF, 28; 29). Group A Group B, Group A ,295 ind./km 2 14,153 ind./km 2 2 Group B ,274 ind./km 2. Group B., Group A Group B, Group A 5-15 m Group B Group B. Group B-1 Group B-2, Group B-1 Group B-2,,,,, Group B mm, mm, mm, mm. Lee et al. (1999) 25. mm, Park et al. (23) 31.1 mm, Kim (213) mm, (MIFFAF, 28; 29) mm, mm 5% 28. mm 1% %, %. Lim (29) mm, mm, Ahn (29) mm, mm, , Park and Zhang (28) 5 (51.94 mm), % % % %, % %
10 944 윤병선ㆍ박정호ㆍ윤상철ㆍ양재형ㆍ손명호 1% 3. mm, 52. mm. 사사 (214, RP-214-FR-56),. References Ahn JM. 29. Studies on the age and growth of Gomphina melanaegis inhabites Gyeongsangbuk-do coastal waters of the East Sea. pp24, KangnungWonju National University, Kangnung, Korea. Bilyard GR The value of benthic infauna in marine pollution montoring studies. Mar Pollut Bull, 18, Bray JR and Curtis JT An ordination of the upland forest communities of southern Wisconsin. Ecol Monogr 27, Choi JW, Je JG, Lee JH and Lim HS. 2. Distribution pattern of macrobenthic invertebrates on the shallow subtidal sandy bottoms near Kangrung, East coast of Korea. J Kor Soc Ocean, 5, Clarke KR and Warwick RM. 21. Changes in marine communities: an approach to statistical analysis and interpretation. Natural Environment Research Council, Plymouth Marine Laboratory, UK, 144. Cha BY, Lee CS, Moon TS and Park MS A study on bivalves in Yeongil Bay of Gyeongsangbuk-Do Province, Korea. Kor J Malacol 28, Daan N A quantitative analysis of the food of North Sea cod (Gadus morhua), Neth J Sea Res 6, Fujita D The report of interview to fisherman on "Isoyake" in Taisei-Cho, Hokkaido. Suisanzoshoku, 35, Hwang SD and Kim JS. 23. Change in community structure of shellfish in the Reclaimed Saemangeum Area. J Kor Fish Soc 36, Jung YH, Yoon KT, Park HS and Ma CW Spatial distribution and community structure of macrobenthos on the sandy shore of Anmyeondo, Korea. Ocean Polar Res 35, Kim YH, Kim SH, Chung EY, Lee CH and Kwak CW Gonad development and sexual maturity of Gomphina (Macridiscus) venerifotmis (Lamark, 1818) (Bivalvia: Veneridae) in the East Sea of Korea. Kor J Mal 29, Ko JC, Ko HJ, Kim BY, Cha HK and Chang DS Distribution characteristic of expoitable macrobenthic invertebrates of beach sediments in the southern coastal water of Jeju island. Kor J Malacol 28, Lee JB, Oh TY, Yeon IJ, Kim BY, Shin HO, Hwang BK, Lee KH and Lee YW Estimation of demersal fish biomass using hydroacoustic and catch data in the Marine Ranching Area (MRA) of Jeju. J Kor Soc Fish Tech 48, Lee JY, Park YJ and Chang YJ Gonadal development and reproductive cycle of Gomphina melanaegis (Bivalvia: Veneridae ). J Kor Fish Soc 32, Lim AH. 29. Studies on the fisheries ecology of Gomphina veneriformis off Uljin in Gyeongsangbuk-do. pp3, KangnungWonju national university, Kangnung, Korea. Ling WB and Clark RB Marine pollution research in China. Mar Pollut Bull 14, Mclntyre AD The Benthos of the western North Sea. Rapp Reun Con Lnt Eoplor Mer 172, Mills EL Benthic organism and the structure of marine ecosystems. J Fish Res Bd Ca 32, MIFFAF, 28. Studies on the development of marine ranching program 27 in the East, West and Jeju coast of Korea MIFFAF, 29. Studies on the development of marine ranching program 28 in the East, West and Jeju coast of Korea MOMAF, 25. Studies on the development of marine ranching program 25 in the east, west and Jeju coast of Korea Paik SG, Kang RS, Jeon JO, Lee JH and Yun SG. 27. Distribution patterns of sandy bottom macrobenthic community on the Hupo coastal area, in the East Sea of Korea. Ocean Polar Res 29, Park HW and Zhang CI. 28. A population ecological study of the hen clam (Mactra chinensis) in the Dong-li self-regulatory community of Busan. J Kor Soc Fish Tech 44, Park JJ, Lee JY, Lee JS and Chang YJ. 23. Gonadal development and gametogenic cycle of the Equilateral Venus, Gomphina veneriformis (Bivalvia: Veneridae). J Kor Fish Soc 36, Pielou EC Mathematical Ecology, 2nd. John Wiley and Sons, New York, 358. Seo JY and Choi JW. 21. The macrozoobenthic community at the expected sand excavation area in the southern continental shelf of Korea. J Kor Soc Ocean 2, Simpson EH Measurement of diversity. Nature 163, Yotsui T and Maesako N Restoration experiments of Eisenia bicyclis beds on barren grounds at Tsusima islands. Suisanzoshoku 41, 67-7.
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