Klaschka Ursula
University of Applied Sciences Ulm, Prittwitzstr. 10, 89075, Ulm, Germany.
Environ Sci Pollut Res Int. 2009 Jun;16(4):370-88. doi: 10.1007/s11356-008-0093-1. Epub 2009 Feb 3.
BACKGROUND, AIM, AND SCOPE: Many-if not all-organisms depend on so-called infochemicals, chemical substances in their surroundings which inform the receivers about their biotic and abiotic environment and which allow them to react adequately to these signals. Anthropogenic substances can interfere with this complex chemical communication system. This finding is called infochemical effect. So far, it is not known to what extent anthropogenic discharges act as infochemicals and influence life and reproduction of organisms in the environment because adequate testing methods to identify chemicals which show the infochemical effect and to quantify their effects have not been developed yet. The purpose of this article is to help and find suitable test designs.
Test systems used in basic research to elucidate the olfactory cascade and the communication of environmental organisms by infochemicals are plentiful. Some of them might be the basis for a quantified ecotoxicological analysis of the infochemical effect. In principle, test systems for the infochemical effect could be developed at each step of the chemosensory signal transduction and processing cascade.
Experimental set-ups were compiled systematically under the aspect whether they might be usable for testing the infochemical effect of single chemicals in standardized quantifying laboratory experiments. For an appropriate ecotoxicological assessment of the infochemical effect, experimental studies of many disciplines, such as molecular biology, neurobiology, physiology, chemical ecology, and population dynamics, should be evaluated in detail before a decision can be made which test system, respectively which test battery, might be suited best. The test systems presented here are based on the knowledge of the genetic sequences for olfactory receptors, binding studies of odorants, signal transmission, and reactions of the receivers on the level of the organisms or the populations. The following basic approaches are conceivable to identify the role of an infochemical: binding studies to the odorant-binding protein or to the odorant receptor binding protein (e.g., by in situ hybridization and immunohistochemical studies), measurement of electrical signals of the receptor cells in the tissue (e.g., electroolfactograms, electroantennograms), registration of phenotypic changes (e.g., observation under the microscope), behavioral tests (e.g., in situ online biomonitoring, use of T-shaped olfactometers, tests of avoidance responses), measurement of population changes (e.g., cell density or turbidity measurements), and multispecies tests with observation of community structure and community function. The main focus of this study is on aquatic organisms.
It is evident that the infochemical effect is a very complex sublethal endpoint, and it needs further studies with standardized quantitative methods to elucidate whether and to what extent the ecosystem is affected. The collection of approaches presented here is far from being complete but should serve as a point of depart for further experimental research.
This article is the first to compare various approaches for testing the infochemical effect. The development of a suitable test system will not be easy as there are a multitude of relevant chemicals, a multitude of relevant receptors, and a multitude of relevant reactions, and it must be expected that the effective concentrations are very low. The chemical communication is of utmost importance for the ecosystem and justifies great endeavors to find solutions to these technical problems.
The infochemical effect is a new chapter in ecotoxicology. Will a new endpoint, the so-called infochemical effect, be required in addition to the actual standard test battery of Annex 5 to Commission Directive 92/69/EEC (EC 1992)? Finding the answer to this question is a big challenge that could be met by a comprehensive research project.
背景、目的和范围:许多(如果不是所有的话)生物体依赖于所谓的信息化学物质,即其周围环境中的化学物质,这些物质向接收者传递有关其生物和非生物环境的信息,并使它们能够对这些信号做出适当反应。人为物质会干扰这种复杂的化学通讯系统。这一发现被称为信息化学效应。到目前为止,尚不清楚人为排放物在多大程度上作为信息化学物质并影响环境中生物体的生命和繁殖,因为尚未开发出用于识别具有信息化学效应的化学物质并量化其影响的适当测试方法。本文的目的是帮助找到合适的测试设计。
基础研究中用于阐明嗅觉级联以及环境生物体通过信息化学物质进行通讯的测试系统很多。其中一些可能是对信息化学效应进行定量生态毒理学分析的基础。原则上,可以在化学感应信号转导和处理级联的每个步骤开发信息化学效应测试系统。
从是否可用于在标准化定量实验室实验中测试单一化学物质的信息化学效应这一角度,系统地汇编了实验装置。为了对信息化学效应进行适当的生态毒理学评估,在决定哪种测试系统或测试组合最适合之前,应详细评估分子生物学、神经生物学、生理学、化学生态学和种群动态等多学科的实验研究。这里介绍的测试系统基于嗅觉受体的基因序列知识、气味剂的结合研究、信号传递以及生物体或种群水平上接收者的反应。可以设想以下基本方法来确定信息化学物质的作用:与气味剂结合蛋白或气味剂受体结合蛋白的结合研究(例如通过原位杂交和免疫组织化学研究)、测量组织中受体细胞的电信号(例如嗅觉电图、触角电图)、记录表型变化(例如显微镜观察)、行为测试(例如原位在线生物监测、使用T形嗅觉计、回避反应测试)、测量种群变化(例如细胞密度或浊度测量)以及观察群落结构和群落功能的多物种测试。本研究的主要重点是水生生物。
显然,信息化学效应是一个非常复杂的亚致死终点,需要用标准化定量方法进行进一步研究,以阐明生态系统是否以及在多大程度上受到影响。这里介绍的方法集合远非完整,但应作为进一步实验研究的起点。
本文首次比较了测试信息化学效应的各种方法。开发合适的测试系统并不容易,因为有大量相关化学物质、大量相关受体和大量相关反应,而且预计有效浓度会非常低。化学通讯对生态系统至关重要,因此有理由付出巨大努力来找到解决这些技术问题的方法。
信息化学效应是生态毒理学中的新篇章。除了欧盟委员会指令92/69/EEC(EC 1992)附件5的实际标准测试组合外,是否还需要一个新的终点,即所谓的信息化学效应?找到这个问题的答案是一项巨大挑战,可能需要一个全面的研究项目来应对。