CBET Research Group, Department of Zoology and Animal Cell Biology, Faculty of Science and Technology (ZTF/FCT) & Research Centre of Experimental Marine Biology and Biotechnology (Plentzia Marine Station, PiE-UPV/EHU), University of the Basque Country, Bilbo 48080, Basque Country, Spain.
ICBAS - Institute of Biomedical Sciences of Abel Salazar, University of Porto, Department of Populations Study, Laboratory of Ecotoxicology (ECOTOX), Rua de Jorge Viterbo Ferreira, 228, 4050-313 Porto, Portugal & CIIMAR - Interdisciplinary Centre of Marine and Environmental Research, University of Porto, Research Team of Ecotoxicology, Stress Ecology and Environmental Health (ECOTOX), Portugal.
Aquat Toxicol. 2019 Jan;206:164-175. doi: 10.1016/j.aquatox.2018.11.016. Epub 2018 Nov 20.
Mussels are widely used in toxicological experimentation; however, experimental setups are not standardized yet. Although there is evidence of changes in biomarker values during food digestion and depending on the mussel nutritive status, the mode of feeding differs among toxicological experiments. Typically, mussels are fed with different diets in different long-term experiments, while fasting is the most common approach for short-term studies. Consequently, comparisons among experiments and reliable interpretations of biomarker results are often unfeasible. The present investigation aimed at determining the influence of fasting (against feeding with Isochrysis galbana) on biomarkers and their responsiveness in mussels exposed for 96 h to the water accommodated fraction (WAF) of a heavy fuel oil (0%, 6.25%, 12.5% and 25% WAF in sea water). PAH tissue levels in digestive gland and a battery of biomarkers were compared. WAF exposure led to decrease of cytochrome-C-oxidase activity, modulated glutathione-S-transferase activity, augmented lipid peroxidation, inhibited acetyl cholinesterase (AChE) activity, and led to lysosomal enlargement (Vv and S/V) and membrane destabilisation, lipofuscin accumulation, and histopathological alterations (Vv, MLR/MET and CTD ratio) in the digestive gland epithelium; and were integrated as IBR/n (biological response index). Overall, no significant changes were recorded in AChE activity, S/V and CTD ratio in any experimental treatment, while all the other biomarkers showed significant changes depending on the fasting/feeding condition, the exposure to WAF and/or their interaction. As a result, the integrated biomarker index IBR/n was higher at increasing WAF exposure levels both in fasted and fed mussels albeit the response was more marked in the latter. The response profiles were qualitatively similar between fasted and fed mussels but quantitatively more pronounced in fed mussels, especially upon exposure to the highest concentration (25% WAF). Therefore, it is highly recommended that mussels are also supplied with food during short-term, like during long-term toxicological experiments. This practice would avoid the interference of fasting with biological responses elicited by the tested chemicals and allow for reliable comparison with data obtained in long-term experiments and monitoring programmes.
贻贝被广泛用于毒理学实验;然而,实验设置尚未标准化。尽管有证据表明,在食物消化过程中和根据贻贝营养状况,生物标志物值会发生变化,但毒理学实验中的喂养方式不同。通常,在不同的长期实验中,贻贝会用不同的饮食喂养,而禁食是短期研究中最常见的方法。因此,实验之间的比较和对生物标志物结果的可靠解释往往是不可行的。本研究旨在确定禁食(与用异角藻喂养相比)对暴露于重油水可溶部分(WAF,海水中 0%、6.25%、12.5%和 25% WAF)96 小时的贻贝的生物标志物及其反应性的影响。比较了消化腺中的多环芳烃组织水平和一组生物标志物。WAF 暴露导致细胞色素 C 氧化酶活性降低,谷胱甘肽 S-转移酶活性调节,脂质过氧化增强,乙酰胆碱酯酶(AChE)活性抑制,溶酶体增大(Vv 和 S/V)和膜稳定性破坏,脂褐素积累和组织病理学改变(Vv、MLR/MET 和 CTD 比值)在消化腺上皮中;并整合为 IBR/n(生物反应指数)。总的来说,在任何实验处理中,AChE 活性、S/V 和 CTD 比值均未记录到显著变化,而所有其他生物标志物均根据禁食/喂养条件、WAF 暴露和/或它们的相互作用而发生显著变化。因此,在禁食和喂养的贻贝中,IBR/n 综合生物标志物指数随着 WAF 暴露水平的增加而增加,尽管在后者中反应更为明显。禁食和喂养贻贝的反应谱在定性上相似,但在喂养贻贝中更为明显,尤其是在暴露于最高浓度(25% WAF)时。因此,强烈建议在短期实验中,如在长期毒理学实验中,也为贻贝提供食物。这种做法将避免禁食对受试化学品引起的生物反应的干扰,并允许与长期实验和监测计划中获得的数据进行可靠比较。