Galgani F, Claro F, Depledge M, Fossi C
Ifremer, Immeuble Agostini, ZI Furiani, 20600 Bastia, Corsica, France.
Museum national d'Histoire naturelle, GTMF, CP41, 57 rue Cuvier, 75231 Paris cedex 05, France.
Mar Environ Res. 2014 Sep;100:3-9. doi: 10.1016/j.marenvres.2014.02.003. Epub 2014 Feb 24.
In its decision (2010/477/EU) relating to the European Marine Strategy Framework Directive (MSFD, 2008/56/EC), the European Commission identified the following points as focuses for monitoring: (i) 10.1.1: Trends in the amount, source and composition of litter washed ashore and/or deposited on coastlines, (ii) 10.1.2: Trends in the amount and composition of litter in the water column and accumulation on the sea floor, (iii) 10.1.3: Trends in the amount, distribution and composition of micro-particles (mainly microplastics), and (iv) 10.2.1: Trends in the amount and composition of litter ingested by marine animals. Monitoring the impacts of litter will be considered further in 2014. At that time, the strategy will be discussed in the context of the Mediterranean Sea, providing information on constraints, protocols, existing harm and research needed to support monitoring efforts. The definition of targets and acceptable levels of harm must take all factors into account, whether entanglement, ingestion, the transport and release of pollutants, the transport of alien species and socio-economic impacts. It must also reflect on the practical deployment of "ingestion" measures (10.2.1). The analysis of existing data will reveal the potential and suitability of some higher trophic level organisms (fish, turtles, birds and mammals) for monitoring the adverse effects of litter. Sea turtles appear to be useful indicator species, but the definition of an ecological quality objective is still needed, as well as research on alternative potential indicator species.
在其与《欧洲海洋战略框架指令》(MSFD,2008/56/EC)相关的决定(2010/477/EU)中,欧盟委员会确定了以下几点作为监测重点:(i)10.1.1:冲上和/或沉积在海岸线上的垃圾数量、来源和成分的趋势;(ii)10.1.2:水柱中垃圾的数量和成分以及在海底堆积情况的趋势;(iii)10.1.3:微颗粒(主要是微塑料)的数量、分布和成分的趋势;以及(iv)10.2.1:海洋动物摄入的垃圾数量和成分的趋势。对垃圾影响的监测将在2014年进一步审议。届时,将在地中海背景下讨论该战略,提供有关支持监测工作所需的限制因素、协议、现有危害和研究的信息。目标和可接受危害水平的定义必须考虑所有因素,无论是缠绕、摄入、污染物的运输和释放、外来物种的运输还是社会经济影响。它还必须思考“摄入”措施(10.2.1)的实际部署情况。对现有数据的分析将揭示一些较高营养级生物(鱼类、海龟、鸟类和哺乳动物)在监测垃圾不利影响方面的潜力和适用性。海龟似乎是有用的指示物种,但仍需要定义生态质量目标,以及对替代潜在指示物种进行研究。