Centre for Fish and Wildlife Health, Vetsuisse Faculty, University of Bern, Laenggass-Strasse 122, 3012, Bern, Switzerland.
Environ Sci Pollut Res Int. 2011 Aug;19(7):2465-76. doi: 10.1007/s11356-012-0978-x. Epub 2012 Aug 31.
Numerous environmental chemicals, both long-known toxicants such as persistent organic pollutants as well as emerging contaminants such as pharmaceuticals, are known to modulate immune parameters of wildlife species, what can have adverse consequences for the fitness of individuals including their capability to resist pathogen infections. Despite frequent field observations of impaired immunocompetence and increased disease incidence in contaminant-exposed wildlife populations, the potential relevance of immunotoxic effects for the ecological impact of chemicals is rarely considered in ecotoxicological risk assessment. A limiting factor in the assessment of immunotoxic effects might be the complexity of the immune system what makes it difficult (1) to select appropriate exposure and effect parameters out of the many immune parameters which could be measured, and (2) to evaluate the significance of the selected parameters for the overall fitness and immunocompetence of the organism. Here, we present - on the example of teleost fishes - a brief discussion of how to assess chemical impact on the immune system using parameters at different levels of complexity and integration: immune mediators, humoral immune effectors, cellular immune defenses, macroscopical and microscopical responses of lymphoid tissues and organs, and host resistance to pathogens. Importantly, adverse effects of chemicals on immunocompetence may be detectable only after immune system activation, e.g., after pathogen challenge, but not in the resting immune system of non-infected fish. Current limitations to further development and implementation of immunotoxicity assays and parameters in ecotoxicological risk assessment are not primarily due to technological constraints, but are related from insufficient knowledge of (1) possible modes of action in the immune system, (2) the importance of intra- and inter-species immune system variability for the response against chemical stressors, and (3) deficits in conceptual and mechanistic assessment of combination effects of chemicals and pathogens.
许多环境化学物质,包括持久性有机污染物等已知的有毒物质以及药品等新兴污染物,已知会调节野生动物物种的免疫参数,这可能对个体的适应性产生不利影响,包括它们抵抗病原体感染的能力。尽管在接触污染物的野生动物种群中经常观察到免疫功能受损和疾病发病率增加,但免疫毒性效应对于化学物质的生态影响的潜在相关性在生态毒理学风险评估中很少被考虑。免疫毒性效应评估的一个限制因素可能是免疫系统的复杂性,这使得很难(1)从可以测量的许多免疫参数中选择适当的暴露和效应参数,以及(2)评估所选参数对生物体整体适应性和免疫能力的意义。在这里,我们以硬骨鱼类为例,简要讨论了如何使用不同复杂程度和整合水平的参数来评估化学物质对免疫系统的影响:免疫介质、体液免疫效应物、细胞免疫防御、淋巴组织和器官的宏观和微观反应以及宿主对病原体的抵抗力。重要的是,化学物质对免疫能力的不利影响可能仅在免疫系统被激活后,例如在病原体挑战后,而不是在未感染鱼类的静止免疫系统中才能检测到。免疫毒性检测和参数在生态毒理学风险评估中的进一步发展和实施的当前限制主要不是由于技术限制,而是由于(1)免疫系统中可能的作用模式、(2)种内和种间免疫系统变异性对化学应激物反应的重要性以及(3)对化学物质和病原体组合效应的概念和机制评估的不足。