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- 中盐度富营养化内岸海水养殖蓝贻贝(蓝贻贝属):缓解潜力、威胁和成本效益

-Blue mussel ( spp.) cultivation in mesohaline eutrophied inner coastal waters: mitigation potential, threats and cost effectiveness.

作者信息

Ritzenhofen Lukas, Buer Anna-Lucia, Gyraite Greta, Dahlke Sven, Klemmstein Annemarie, Schernewski Gerald

机构信息

Leibniz-Institute for Baltic Sea Research, Warnemünde, Rostock, Germany.

Marine Research Institute, Klaipeda University, Klaipeda, Lithuania.

出版信息

PeerJ. 2021 May 20;9:e11247. doi: 10.7717/peerj.11247. eCollection 2021.

DOI:10.7717/peerj.11247
PMID:34055477
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC8141286/
Abstract

The EU-water framework directive (WFD) focuses on nutrient reductions to return coastal waters to the good ecological status. As of today, many coastal waters have reached a steady state of insufficient water quality due to continuous external nutrient inputs and internal loadings. This study focuses first on the current environmental status of mesohaline inner coastal waters to illustrate their needs of internal measures to reach demanded nutrient reductions and secondly, if mussel cultivation can be a suitable strategy to improve water quality. Therefore, nitrogen, phosphorus, chlorophyll a, and Secchi depth of nine mesohaline inner coastal waters in north east Germany were analyzed from 1990 to 2018. Two pilot mussel farms were used to evaluate their effectiveness as a mitigation measure and to estimate potential environmental risks, including the interactions with pathogenic vibrio bacteria. Further, estimated production and mitigation potential were used to assess economic profitability based on the sale of small sized mussels for animal feed and a compensation for nutrient mitigation. The compensation costs were derived from nutrient removal costs of a waste water treatment plant (WWTP). Results show that currently all nine water bodies do not reach the nutrient thresholds demanded by the WFD. However, coastal waters differ in nutrient pollution, indicating that some can reach the desired threshold values if internal measures are applied. The mitigation potential of mussel cultivation depends on the amount of biomass that is cultivated and harvested. However, since mussel growth is closely coupled to the salinity level, mussel cultivation in low saline environments leads to lower biomass production and inevitably to larger cultivation areas. If 50% of the case study area Greifswald Bay was covered with mussel farms the resulting nitrogen reduction would increase Secchi depth by 7.8 cm. However, high chlorophyll a values can hamper clearance rates (<20 mg m = 0.43 l h dry weight g) and therefore the mitigation potential. Also, the risk of mussel stock loss due to high summer water temperatures might affect the mitigation potential. The pilot farms had no significant effect on the total organic content of sediments beneath. However, increased values of spp. in bio deposits within the pilot farm (1.43 10 ± 1.10 10CFU 100 ml (reference site: 1.04 10 ± 1.45 10 CFU 100 ml) were measured with sediment traps. Hence, mussel farms might act as a sink for spp. in systems with already high vibrio concentrations. However, more research is required to investigate the risks of Vibrio occurrence coupled to mussel farming. The economic model showed that mussel cultivation in environments below 12 PSU cannot be economic at current market prices for small size mussels and compensations based on nutrient removal cost of WWTPs.

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/8c9e4b5c70a0/peerj-09-11247-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/319ee8513ef4/peerj-09-11247-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/094c8c4c41a7/peerj-09-11247-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/535728b790db/peerj-09-11247-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/71a10f6b9ee2/peerj-09-11247-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/1a7cd9686993/peerj-09-11247-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/e7109a9a5afc/peerj-09-11247-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/8c9e4b5c70a0/peerj-09-11247-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/319ee8513ef4/peerj-09-11247-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/094c8c4c41a7/peerj-09-11247-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/535728b790db/peerj-09-11247-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/71a10f6b9ee2/peerj-09-11247-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/1a7cd9686993/peerj-09-11247-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/e7109a9a5afc/peerj-09-11247-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/6f17/8141286/8c9e4b5c70a0/peerj-09-11247-g009.jpg
摘要

欧盟水框架指令(WFD)侧重于减少营养物质,以使沿海水域恢复到良好的生态状态。截至目前,由于持续的外部营养物质输入和内部负荷,许多沿海水域已达到水质不足的稳定状态。本研究首先关注中盐度内沿海水域的当前环境状况,以说明其实现所需营养物质减少的内部措施需求,其次关注贻贝养殖是否可以作为改善水质的合适策略。因此,分析了1990年至2018年德国东北部九个中盐度内沿海水域的氮、磷、叶绿素a和塞氏深度。使用两个贻贝养殖试点来评估其作为缓解措施的有效性,并估计潜在的环境风险,包括与致病性弧菌的相互作用。此外,基于出售小型贻贝作为动物饲料以及对营养物质缓解的补偿,利用估计的产量和缓解潜力来评估经济盈利能力。补偿成本来自污水处理厂(WWTP)的营养物质去除成本。结果表明,目前所有九个水体均未达到WFD要求的营养阈值。然而,沿海水域的营养污染情况各不相同,这表明如果采取内部措施,一些水域可以达到期望的阈值。贻贝养殖的缓解潜力取决于养殖和收获的生物量数量。然而,由于贻贝生长与盐度水平密切相关,在低盐度环境中进行贻贝养殖会导致生物量产量降低,不可避免地需要更大的养殖面积。如果在案例研究区域格赖夫斯瓦尔德湾的50%区域覆盖贻贝养殖场,由此产生的氮减少量将使塞氏深度增加7.8厘米。然而,高叶绿素a值会妨碍清除率(<20毫克/立方米 = 0.43升/小时干重克),从而影响缓解潜力。此外,夏季水温过高导致贻贝种群损失的风险可能会影响缓解潜力。试点养殖场对下方沉积物的总有机含量没有显著影响。然而,使用沉积物捕集器测量发现,试点养殖场内生物沉积物中的弧菌数量增加(1.43×10⁶±1.10×10⁶CFU/100毫升(参考站点:1.04×10⁶±1.45×10⁶CFU/100毫升)。因此,在弧菌浓度已经很高的系统中,贻贝养殖场可能成为弧菌的汇聚地。然而,需要更多研究来调查与贻贝养殖相关的弧菌出现风险。经济模型表明,在当前小型贻贝市场价格以及基于污水处理厂营养物质去除成本的补偿情况下,在盐度低于12PSU的环境中进行贻贝养殖不具有经济可行性。

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Only as strong as the weakest link: structural analysis of the combined effects of elevated temperature and pCO on mussel attachment.仅取决于最薄弱环节:高温与pCO₂对贻贝附着综合影响的结构分析
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