Environmental Research Unit, Dept of Science and Chemical Engineering, The University of Glamorgan, CF37 1DL, Pontypridd, Mid-Glamorgan, South Wales, UK.
Ecotoxicology. 1994 Dec;3(4):213-33. doi: 10.1007/BF00117989.
: A classification of terrestrial model ecosystems (TMEs) was introduced which is based upon the physical properties of intactness of the physical medium and openness to the atmosphere. This gave rise to four types of system, namely open and closed intact systems and open and closed homogeneous' systems. These systems have different capabilities with respect to fate and effect end-points with various substances. The large closed TMEs are generally very complex, require a high degree of operator skill, expensive and therefore not replicable. Whilst these can provide estimates of losses due to volatility, they are not useful for determining effect end-points because of low replicability; high replicability being necessary because of natural variation in organism response. Open systems, especially those having intact soil-cores, are usually smaller, less complex and therefore more replicable. These have provided useful information on integrative functional effect end-points, but can only produce mass balances with non-volatile substances. Homogenization of the medium has also helped elucidate ecotoxicological effects by increasing replicability, but may introduce artifacts because of the disruption to soil organisms.A major limitation of TME studies would seem to be that few effect end-points can be non-destructively sampled. Further investigations into these may provide information on recovery of terrestrial ecosystems over time after substance application, perhaps using multivariate statistical techniques. Other problems concerning TMEs are related to complexity and scale. In this respect ecosystem functions in which microorganisms play a major role, such as nutrient cycling, provide the greatest similarity when compared to field evaluations of the same substances, especially where the TME is intact. However, effects upon structural aspects of biological communities have in general not been well researched in TMEs. Once these have been added to the more complete set of functional end-points, TMEs will provide a very useful tool in hazard assessments of potentially harmful substances.
提出了一种基于物理介质完整性和对大气开放性的陆地模型生态系统(TME)分类方法。这导致了四种系统类型,即开放和封闭完整系统以及开放和封闭均质系统。这些系统对于各种物质的归宿和效应终点具有不同的能力。大型封闭 TME 通常非常复杂,需要高度的操作人员技能,昂贵且因此不可复制。虽然这些可以提供由于挥发性而导致的损失估计,但由于低可重复性,它们不适用于确定效应终点;由于生物体反应的自然变化,高可重复性是必要的。开放系统,特别是具有完整土壤核心的系统,通常较小,较不复杂,因此更具可重复性。这些为综合功能效应终点提供了有用的信息,但只能对非挥发性物质进行质量平衡。介质的均匀化也通过提高可重复性帮助阐明了生态毒理学效应,但由于对土壤生物的破坏,可能会引入假象。TME 研究的一个主要限制似乎是很少有效应终点可以进行非破坏性采样。进一步研究这些可能会提供有关物质应用后陆地生态系统随时间恢复的信息,也许可以使用多元统计技术。其他与 TME 相关的问题与复杂性和规模有关。在这方面,微生物起主要作用的生态系统功能在与相同物质的现场评估进行比较时提供了最大的相似性,尤其是当 TME 完整时。然而,TME 中一般没有很好地研究对生物群落结构方面的影响。一旦将这些影响添加到更完整的功能终点集,TME 将成为潜在有害物质危害评估的非常有用的工具。