Sedimentation characteristics of aquaculture-derived organic matter from a large yellow croaker (Larimichthys crocea) cage farm in Sansha Bay
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1. East China Sea Fisheries Research Institute, Chinese Academy of Fishery Sciences, Shanghai 200090, China;
2. College of Life and Environment, Wenzhou University, Wenzhou 325035, China

Clc Number:

S931

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    Abstract:

    To clarify the sedimentation characteristics of aquaculture-derived organic matter (AOM) from a large yellow croaker () cage farm in Sansha Bay, AOM samples in a sampling gradient (0-200 m away from the culture cage) were collected with sedimentation traps under two typical feeding conditions (commercial feed and raw fish). These samples were used to analyze sedimentation rate, particle organic matter (POM:particulate organic matter; POC:particulate organic carbon; PN:particulate nitrogen; TP:total phosphorus) fluxes, and their spatial expansion in this study. The sedimentation rate of AOM was (563.66±119.18) g/(m2·d) when commercial pellets were used as feed, which was significantly higher than that when raw fish was used. Particulate organic matter (POM), POC, PN, and TP fluxes were much higher when using commercial feed than raw fish, at (27.25±2.43) g/(m2·d), (6.03±0.58) g/(m2·d), (0.66±0.06) g/(m2·d), and (0.39±0.04) g/(m2·d) in the former experimental condition, and at (13.04±1.62) g/(m2·d), (3.57±0.45) g/(m2·d), (0.51±0.06) g/(m2·d), and (0.22± 0.04) g/(m2·d) in the latter situation, respectively. Particle organic matter fluxes and AOM sedimentation rates showed decreasing tendencies from 0-100 m away from the fish cage, with a particularly strong decline in the raw fish treatment. The percentage of particle organic matter in AOM also exhibited spatial variability, declining in the region from the fish cages to 50 m downstream. In summary, the environmental effects of a cage farm in Sansha Bay were much remarked when commercial pellets were used as feed. Environmental impacts derived from using both commercial pellets and raw fish were restricted to an area 50-100 m away from fish cages. The occurrence of conspicuous environmental impacts due to using commercial feeds was associated with a greater AOM sedimentation rate, and thus, studies on restricted feeding and on the efficiency of fish feed are essential to alleviate the negative impacts of aquaculture in the area.

    Reference
    [1] The Ministry of Agriculture Fishery and Fishery Administration. China Fishery Statistics Yearbook 2019[M]. Beijing:China Agriculture Press, 2019.[农业农村部渔业渔政管理局. 2019中国渔业年鉴[M]. 北京:中国农业出版社, 2019.]
    [2] Yokoyama H, Abo K, Ishihi Y. Quantifying aquaculture- derived organic matter in the sediment in and around a coastal fish farm using stable carbon and nitrogen isotope ratios[J]. Aquaculture, 2006, 254(1-4):411-425.
    [3] Jiang Z J, Fang J G, Wang G H, et al. Identification of aquaculture-derived organic matter in the sediment associated with coastal fish farming by stable carbon and nitrogen isotopes[J]. Journal of Environmental Science and Engineering, 2012, 1(2):142-149.
    [4] Ningde Municipal Statistical Bureau. Ningde Statistical Yearbook 2018[R]. 2018.[宁德市统计局. 宁德市统计年鉴2018[R]. 2018.]
    [5] Wu F, Guo W D, Zheng P R, et al. Distribution of phosphorus species in sediments of maricultural waters in Sandu Bay[J]. Marine Environmental Science, 2005, 24(4):24-27.[吴芳, 郭卫东, 郑佩如, 等. 三都澳养殖海域沉积物中P的形态分布特征[J]. 海洋环境科学, 2005, 24(4):24-27.]
    [6] Zhou J. Impacts of mariculture practices on the temporal distribution of macrobenthos in Sandu Bay, South China[J]. Chinese Journal of Oceanology and Limnology, 2012, 30(3):388-396.
    [7] Ji W W, Zhou J. Community structure of macrobenthos in response to mariculture practices in Sandu Bay[J]. Journal of Fishery Sciences of China, 2012, 19(3):491-499.[纪炜炜, 周进. 三都澳大型底栖动物群落结构及其对水产养殖的响应[J]. 中国水产科学, 2012, 19(3):491-499.]
    [8] Wei Z L. Studies on the strategy of bioremediation with macroalgae cultivation in an intensive mariculture Yantian bay, China[D]. Shanghai:Shanghai Ocean University, 2016.[韦章良. 三沙湾盐田港养殖海域大型海藻生态修复策略研究[D]. 上海:上海海洋大学, 2016.]
    [9] Shao L, Xing X L, Zhou J, et al. Ecological effects of the caged-fish and kelp cultures in semi-enclosed bay:evidence from diatom assemblages and environmental variables[J]. Indian Journal of Marine Sciences, 2018, 47(2):325-335.
    [10] Tang M. Environmental impacts of mariculture on sedimentary variables and polychaete community structure in Sansha Bay, Fujian Province[D]. Shanghai:Shanghai Ocean University, 2017.[唐盟. 福建省三沙湾养殖活动对底栖环境及多毛纲动物群落结构的影响[D]. 上海:上海海洋大学, 2017.]
    [11] Tang M, Zhou J. Impacts of cage farming on polychaete community in Sansha Bay, Fujian Province[J]. Oceanologia et Limnologia Sinica, 2017, 48(3):543-552.[唐盟, 周进. 福建三沙湾网箱养殖对多毛纲动物群落结构的影响[J]. 海洋与湖沼, 2017, 48(3):543-552.]
    [12] Peng G H, Fu J, Ma Z L, et al. Effects of mariculture activities on benthic environmental based on analysis of three biotic indices in Sansha Bay[J]. Acta Oceanologica Sinica, 2018, 40(4):106-118.[彭广海, 付婧, 马增岭, 等. 基于3种生物指数的三沙湾养殖活动底栖环境效应研究[J]. 海洋学报, 2018, 40(4):106-118.]
    [13] Wang N, Ji W W, Fu J, et al. Community structure of macrobenthos in summer and its relationship with the mariculture in Sansha Bay[J]. Marine Fisheries, 2019, 42(4):408- 420.[王楠, 纪炜炜, 付婧, 等. 三沙湾夏季大型底栖动物群落结构及其和水产养殖的关系[J]. 海洋渔业, 2019, 41(4):408-420.]
    [14] Yokoyama H, Takashi T, Ishihi Y, et al. Effects of restricted feeding on growth of red sea bream and sedimentation of aquaculture wastes[J]. Aquaculture, 2009, 286(1-2):80-88.
    [15] Ge C Z, Fang J G. The fluxes of setting particulate matter in inside and outside of the large aquaculture net cages in sea in summer[J]. China Environmental Science, 2006, 26(Suppl.):106-109.[葛长字, 方建光. 夏季海水养殖区大型网箱内外沉降颗粒物通量[J]. 中国环境科学, 2006, 26(增刊):106-109.]
    [16] Huang Y C A, Huang S C, Hsieh H J, et al. Changes in sedimentation, sediment characteristics, and benthic macrofaunal assemblages around marine cage culture under seasonal monsoon scales in a shallow-water bay in Taiwan[J]. Journal of Experimental Marine Biology and Ecology, 2012, 422-423:55-63.
    [17] Holmer M, Marba N, Diaz-Almela E, et al. Sedimentation of organic matter from fish farms in oligotrophic Mediterranean assessed through bulk and stable isotope (δ13C and δ15N) analyses[J]. Aquaculture, 2007, 262(2-4):268-280.
    [18] Sutherland T F, Martin A J, Levings C D, Characterization of suspended particulate matter surrounding a salmonid net- pen in the Broughton Archipelago, British Columbia[J]. Journal of Marine Science, 2001, 58(2):404-410.
    [19] Villanueva R D, Yap H T, Montaño M N E. Survivorship of coral juveniles in a fish farm environment[J]. Marine Pollution Bulletin, 2005, 51(5-7):580-589.
    [20] Sarà G, Scilipoti D, Mazzola A, et al. Effects of fish farming waste to sedimentary and particulate organic matter in a southern Mediterranean area (Gulf of Castellammare, Sicily):a multiple stable isotope study (δ13C and δ15N)[J]. Aquaculture, 2004, 234(1-4):199-213.
    [21] Dempster T, Sanchez-Jerez P, Bayle-Sempere J T, et al. Attraction of wild fish to sea-cage farms in the south-western Mediterranean Sea:spatial and short-term temporal variability[J]. Marine Ecology Progress Series, 2002, 242(1):237- 252.
    [22] Vita R, Marín A, Madrid J A, et al. Effects of wild fishes on waste exportation from a Mediterranean fish farm[J]. Marine Ecology Progress Series, 2004, 277:253-261.
    [23] Ye J Q. Resource and biological characteristics of large yellow croaker (Larimichthys crocea) in Guanjingyang[D]. Shanghai:Shanghai Ocean University, 2012.[叶金清. 官井洋大黄鱼的资源和生物学特征[D]. 上海:上海海洋大学, 2012.]
    [24] Sanz-Lázaro C, Belando M D, Marín-Guirao L, et al. Relationship between sedimentation rates and benthic impact on Maërl beds derived from fish farming in the Mediterranean[J]. Marine Environmental Research, 2011, 71(1):22-30.
    [25] Gacia E, Granata T C, Duarte C M. An approach to measurement of particle flux and sediment retention within seagrass (Posidonia oceanica) meadows[J]. Aquatic Botany, 1999, 65(1-4):255-268.
    [26] Zheng Q H. Physical and chemical variations and eutrophication status in important aquaculture waters of Sansha Bay[J]. Journal of Applied Oceanography, 2017, 36(1):24- 30.[郑钦华. 三沙湾重点水产养殖水域理化变化特征及富营养化状况[J]. 应用海洋学学报, 2017, 36(1):24-30.]
    [27] Hall P O J, Anderson L G, Holby O, et al. Chemical fluxes and mass balances in a marine fish cage farm. I. Carbon[J]. Marine Ecology Progress Series, 1990, 61(1-2):61-73.
    [28] Holby O, Hall P O J. Chemical fluxes and mass balances in a marine fish cage farm. II. Phosphorus[J]. Marine Ecology Progress Series, 1991, 70(3):263-272.
    [29] Hall P O J, Holby O, Kollberg S, et al. Chemical fluxes and mass balances in a marine fish cage farm. 4. Nitrogen[J]. Marine Ecology Progress Series, 1992, 89(1):81-91.
    [30] Cromey C J, Black K D. "Modelling the impacts of finfish aquaculture." Environmental effects of marine finfish aquaculture[M]. Berlin:Springer-Verlag, 2005:129-155.
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黄伟强,纪炜炜,付婧,马增岭,周进. 三沙湾大黄鱼网箱养殖衍生有机物的沉降特征[J]. Jounal of Fishery Sciences of China, 2020,[volume_no](6):709-719

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  • Online: June 19,2020
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