Brooks Steven, Lyons Brett, Goodsir Freya, Bignell John, Thain John
Norwegian Institute for Water Research (NIVA), Oslo, Norway.
J Toxicol Environ Health A. 2009;72(3-4):196-208. doi: 10.1080/15287390802539038.
Biological effects techniques have been used with the aim to further integrate biological effects measurements with chemical analysis and apply these methods to provide an assessment of mussel health status. Live native mussels were collected from selected coastal and estuarine sites around the British Isles, including the rivers Test, Thames, Tees, and Clyde, and Lunderston Bay. A suite of biological effects techniques was undertaken on these mussels, including whole organism responses (scope for growth), tissue responses (histopathology), and subcellular responses (lysosomal stability, multi-xenobiotic resistance [MXR], and Comet assay). In addition, whole mussel homogenates were used to measure organic (polycyclic aromatic hydrocarbons [PAH], polychlorinated biphenyls [PCB]) and metal concentrations. Overall the mussels collected from the Thames were in relatively poor health, based on histopathological markers, significantly higher DNA damage, and elevated expression of MXR detoxifying proteins. In contrast, the mussels collected from the River Test were in the best health, based on histopathological markers, respiration rate (SFG), and low frequency of DNA damage. In conclusion, the biological effects techniques were able to distinguish between relatively contaminated and clean environments, with the Thames mussels in worst health. Mussel tissue chemistry data were not able to explain the variations in biological response. Evidence indicates that the difference in the health of the mussels between the different sites was due to either effects of contaminants that were not measured, or the combined effects of mixture toxicity resulting in a threshold effect.
生物效应技术已被用于进一步将生物效应测量与化学分析相结合,并应用这些方法来评估贻贝的健康状况。从英伦诸岛周围选定的沿海和河口地点采集活的本地贻贝,包括泰斯特河、泰晤士河、蒂斯河、克莱德河以及伦德斯顿湾。对这些贻贝进行了一系列生物效应技术检测,包括整体生物反应(生长范围)、组织反应(组织病理学)和亚细胞反应(溶酶体稳定性、多异种生物抗性[MXR]和彗星试验)。此外,还使用整个贻贝匀浆来测量有机污染物(多环芳烃[PAH]、多氯联苯[PCB])和金属浓度。总体而言,根据组织病理学指标、显著更高的DNA损伤以及MXR解毒蛋白的表达升高情况,从泰晤士河采集的贻贝健康状况相对较差。相比之下,根据组织病理学指标、呼吸速率(SFG)和低频率的DNA损伤情况,从泰斯特河采集的贻贝健康状况最佳。总之,生物效应技术能够区分相对受污染和清洁的环境,泰晤士河的贻贝健康状况最差。贻贝组织化学数据无法解释生物反应的差异。有证据表明,不同地点贻贝健康状况的差异要么是由于未测量的污染物的影响,要么是由于混合毒性的综合作用导致了阈值效应。