Ecosystem attributes of trophic models before and after construction of artificial oyster reefs using Ecopath
Xu, Min1,2,3,6,7; Qi, Lu4; Zhang, Li-bing1,2,3; Zhang, Tao1,2,3; Yang, Hong-sheng1,2,3; Zhang, Yun-ling5
刊名AQUACULTURE ENVIRONMENT INTERACTIONS
2019
卷号11页码:111-127
关键词Ecopath model Artificial oyster reef Apostichopus japonicus Rapana venosa Ecosystem properties Sea ranching
ISSN号1869-215X
DOI10.3354/aei00284
通讯作者Zhang, Li-bing(tzhang@qdio.ac.cn)
英文摘要The deployment of artificial reefs (ARs) is currently an essential component of sea ranching practices in China due to extensive financial support from the government and private organizations. Blue Ocean Ltd. created a 30.65 km(2) AR area covered by oysters in the eastern part of Laizhou Bay, Bohai Sea. It is important for the government and investors to understand and assess the current status of the AR ecosystem compared to the system status before AR deployment. We provide that assessment, including trophic interactions, energy flows, keystone species, ecosystem properties and fishing impacts, through a steady-state trophic flow model (Ecopath with Ecosim). The model estimated values of 4721.2 and 4697.276 t km(-2) yr(-1) for total system throughput and 534.74 and -519.9 t km(-2) yr(-1) for net system production before and after AR deployment, respectively. After AR deployment, sea cucumber and oyster showed the same trophic level (TL = 2.0) while veined whelk Rapana venosa had TL = 3.0. The mean TL of catches was 2.484 after AR deployment and the primary production required to support fisheries (PPR) was 1104 t km(-2). Detritus production dominated over primary production and represented 73.82% (2530.82 t km(-2)) of total primary production required. The sea cucumber showed the lowest PPR/catch value (5.6) among functional groups, indicating that fishing catch biomasses were close to primary production values. The total primary production to total respiration and total primary production to total biomass ratios showed higher system maturity after AR deployment. The trophic flow diagram showed 1 grazing and 2 detritus food chains. Pelagic and bottom fish and different benthic organisms, including large crustaceans and zoobenthos, were the dominant community before AR deployment. Zoobenthos was the key functional group, followed by large crustaceans and Gobiidae, which were the most important prey for top predators after AR deployment. We draw the following conclusions for the management of this area: (1) AR deployment contributes to the maturity of the improved ecosystem; (2) the artificial oyster system is similar to a natural reef system; (3) the enhancement and release of benthic animals in the AR area benefit the ecosystem; and (4) low TL catches do not cause the system to collapse.
资助项目Taishan Industry Leader Talent Project ; Strategic Priority Research Program of the Chinese Academy of Sciences[XDA11020703] ; Qingdao Postdoctoral Applied Basic Research[Y7KY02106N] ; NSFC-Shandong Joint Fund for Marine Science Research Centers[U1406403] ; Key Research and Development Plan (major key technology) Project in Shandong[2016ZDJS06A02] ; National Marine Public Welfare Research Project[201305043] ; Postdoctoral International Exchange Program Introduction Project[Y8KY02102L] ; Laboratory for Marine Fisheries Science and Food Production Processes ; Qingdao National Laboratory for marine science and technology[2016LMFS-B08] ; Creative Team Project of the Laboratory for Marine Ecology and Environmental Science, Qingdao National Laboratory for Marine Science and Technology[LMEES-CTSP-2018-1]
WOS研究方向Fisheries ; Marine & Freshwater Biology
语种英语
出版者INTER-RESEARCH
WOS记录号WOS:000461445200002
内容类型期刊论文
源URL[http://ir.qdio.ac.cn/handle/337002/155241]  
专题海洋研究所_海洋生态与环境科学重点实验室
通讯作者Zhang, Li-bing
作者单位1.Chinese Acad Sci, Inst Oceanol, CAS Key Lab Marine Ecol & Environm Sci, Qingdao 266071, Peoples R China
2.Qingdao Natl Lab Marine Sci & Technol, Lab Marine Ecol & Environm Sci, Qingdao 266237, Peoples R China
3.Chinese Acad Sci, Ctr Ocean Mega Sci, Qingdao 266071, Peoples R China
4.Ocean Univ China, Qingdao 266100, Peoples R China
5.Hebei Prov Res Inst Engn Technol Coastal Ecol Reh, Tangshan 063610, Peoples R China
6.Minist Agr, Key Lab East China Sea & Ocean Fishery Resources, Shanghai 200090, Peoples R China
7.Chinese Acad Fishery Sci, East China Sea Fisheries Res Inst, Shanghai 200090, Peoples R China
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Xu, Min,Qi, Lu,Zhang, Li-bing,et al. Ecosystem attributes of trophic models before and after construction of artificial oyster reefs using Ecopath[J]. AQUACULTURE ENVIRONMENT INTERACTIONS,2019,11:111-127.
APA Xu, Min,Qi, Lu,Zhang, Li-bing,Zhang, Tao,Yang, Hong-sheng,&Zhang, Yun-ling.(2019).Ecosystem attributes of trophic models before and after construction of artificial oyster reefs using Ecopath.AQUACULTURE ENVIRONMENT INTERACTIONS,11,111-127.
MLA Xu, Min,et al."Ecosystem attributes of trophic models before and after construction of artificial oyster reefs using Ecopath".AQUACULTURE ENVIRONMENT INTERACTIONS 11(2019):111-127.
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