Introductory Chapter: Marine Monitoring Pollution

H. Fouzia, Boufeniza Redouane Larbi, Adem Amina, Chabi Nacera, Bachari Nour El Islam
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Abstract

Monitoring the quality of the marine and coastal environment combines activities of various kinds and is defined as a type of activity that can be exercised on a regulatory basis (this is a control) or to evaluate levels or trends for a scientific study. This definition made it possible to clarify later, after a good number of debates, the definition of the monitoring objectives. It was at the origin of the extensive definition produced by the Oslo and Paris Conventions (the OSPAR Convention), which constitutes the most current reference: “continuous monitoring is the repeated measure of the quality of the marine environment and of each of its compartments, namely, water, sediment and living environment; natural or anthropogenic activities or inputs that may affect the quality of the marine environment; and the effects of its activities and contributions” [1]. Monitoring of the coastal and marine environment in particular requires the study of water (physical chemistry, temperature, salinity, oxygen, bacteriology, etc.), the sediment (grain size, micro, etc.), and living (benthos, plants, magnoliophytes, algae, fish, coral, biomonitoring, bioindicators). The methods and means of analysis and monitoring features of the marine and coastal environment (physical and chemical parameters, pollutants, nutrients, etc.) are numerous. Measurements are essential for understanding and interpreting data to accomplish the goals of surveillance [2]. The study of environmental pollution implies as a precise knowledge as possible of the distribution of pollutants in ecosystems and their effects on living organisms. Sometimes, it is customary to distinguish between a chemical monitoring whose purpose is to determine the level of contamination by a particular pollutant biotope and biomass and other biological monitoring which aims to assess the impact at a given moment or time of environmental pollution on exposed populations and communities. Since the critical level of ecotoxicological concentration-response relationship to a given pollutant is known, it will subsequently be possible to establish environmental protection standards for the pollutant under consideration.
导论章:海洋污染监测
监测海洋和沿海环境的质量结合了各种各样的活动,并被定义为一种可以在监管基础上进行的活动(这是一种控制),或为科学研究评估水平或趋势。这一定义使得在经过多次辩论之后澄清监测目标的定义成为可能。这是《奥斯陆公约》和《巴黎公约》(《OSPAR公约》)所作的广泛定义的起源,该定义构成了最新的参考:“持续监测是对海洋环境及其每一个部分,即水、沉积物和生活环境的质量的反复测量;可能影响海洋环境品质的自然或人为活动或投入;以及其活动和贡献的影响”[1]。对沿海和海洋环境的监测尤其需要对水(物理化学、温度、盐度、氧气、细菌学等)、沉积物(粒度、微生物等)和生物(底栖动物、植物、木兰植物、藻类、鱼类、珊瑚、生物监测、生物指标)进行研究。分析和监测海洋和沿海环境特征(物理和化学参数、污染物、营养物质等)的方法和手段很多。测量对于理解和解释数据以实现监测目标至关重要[2]。对环境污染的研究意味着要尽可能精确地了解生态系统中污染物的分布及其对生物体的影响。有时,习惯上将化学监测与其他生物监测区分开来,前者的目的是确定某一特定污染物生物群落和生物量的污染程度,后者的目的是评估环境污染在某一时刻或时间对受污染人口和社区的影响。由于已知与某一污染物的生态毒理学浓度-反应关系的临界水平,因此将有可能为所考虑的污染物建立环境保护标准。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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