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Collection and transport of sentinel mussels in biomarker-based coastal pollution monitoring: Current flaws and reliable practices

机译:基于生物标志物的沿海污染监测中前哨贻贝的收集和运输:当前的缺陷和可靠的做法

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摘要

Biomarkers use to be recorded in sentinel mussels for biological effects assessment in coastal pollution monitoring. There are recommended procedures (e.g., by ICES) for biomarker determination but not for sample collection and transport. However, where and when mussels are collected and how samples are processed can be a major source of variability in biomarker values. Thus, the present study aims at contributing to identify reliable practices for collection and transport of intertidal mussels in biomarker-based coastal pollution monitoring. Mussels, Mytilus galloprovincialis, were handpicked from the high (2.5-3.0 m) and low (0.5-1.0 m) tide-mark levels at autumn tides in Gorliz, a relatively clean locality of the Basque Coast (Bay of Biscay). Then, they were processed by different ways: (a) in situ dissected immediately after sampling; (b) transported to the laboratory either in air or in seawater; and (c) dissected at different time intervals after sampling. Oxidative stress, lysosomal and tissue-level biomarkers were investigated. Oxidative stress and lysosomal biomarkers were significantly affected by collection and transport to the laboratory, due to the combination of air exposure (hypoxia) and digestion process. Consequently, it is recommended that sentinel mussels should be collected the nearest possible to the 0 tide-mark level and processed in situ as soon as possible, and always within 1 h upon collection. If in situ processing is not possible, mussels should be transported in air and processed within the shortest time possible. Finally, details on sampling should be always provided to made possible the proper interpretation and comparison of results.
机译:生物标记物被记录在前哨贻贝中,用于沿海污染监测中的生物效应评估。有建议的程序(例如,通过ICES)用于生物标志物的测定,但不用于样品的收集和运输。但是,贻贝的采集地点和时间以及样品的处理方式可能是生物标记值变化的主要来源。因此,本研究旨在为基于生物标志物的沿海污染监测识别潮间带贻贝的收集和运输提供可靠的方法。在巴斯克海岸(比斯开湾)相对干净的戈里兹(Gorliz)秋季潮中,从高潮位(2.5-3.0 m)和低潮位(0.5-1.0 m)中挑选贻贝(Mytilus galloprovincialis)。然后,以不同的方式对其进行处理:(a)取样后立即进行原位解剖; (b)以空运或海水运输到实验室; (c)在取样后的不同时间间隔进行解剖。研究了氧化应激,溶酶体和组织水平的生物标志物。由于空气暴露(低氧)和消化过程的结合,氧化应激和溶酶体生物标记物受到收集和运输到实验室的影响很大。因此,建议应尽可能地将前哨贻贝收集到0潮标水平,并在收集后的1小时内尽快就地进行处理。如果无法进行原位处理,则贻贝应在空气中运输并在尽可能短的时间内进行处理。最后,应始终提供采样细节,以使对结果的正确解释和比较成为可能。

著录项

  • 来源
    《Ecological indicators》 |2019年第8期|722-734|共13页
  • 作者单位

    Univ Basque Country, UPV EHU, Dept Zool & Anim Cell Biol, CBET Res Grp, Leioa, Basque Country, Spain|Univ Basque Country, Res Ctr Expt Marine Biol & Biotechnol, Plentzia Marine Stn, PiE UPV EHU, Plentzia, Basque Country, Spain;

    Univ Porto, Dept Populat Study, Lab Ecotoxicol ECOTOX, ICBAS Inst Biomed Sci Abel Salazar, Rua Jorge Viterbo Ferreira 228, P-4050313 Porto, Portugal|Univ Porto, CIIMAR Interdisciplinary Ctr Marine & Environm Re, ICBAS, Rua Jorge Viterbo Ferreira 228, P-4050313 Porto, Portugal;

    Univ Basque Country, UPV EHU, Dept Zool & Anim Cell Biol, CBET Res Grp, Leioa, Basque Country, Spain|Univ Basque Country, Res Ctr Expt Marine Biol & Biotechnol, Plentzia Marine Stn, PiE UPV EHU, Plentzia, Basque Country, Spain;

    Univ Basque Country, UPV EHU, Dept Zool & Anim Cell Biol, CBET Res Grp, Leioa, Basque Country, Spain|Univ Basque Country, Res Ctr Expt Marine Biol & Biotechnol, Plentzia Marine Stn, PiE UPV EHU, Plentzia, Basque Country, Spain;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Biomarkers; Confounding factors; Histopathology; Lysosomes; Mussel-watch; Oxidative stress; Sample processing; Sampling;

    机译:生物标志物;混杂因素;组织病理学;溶酶体;贻贝观察;氧化应激;样品处理;采样;

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