Quantitative analyses of relationships between ecotoxicological effects and combined pollution

The responses of wheat Triticum aestivum, rice Oryza sativa, earthworms Eisenia foetida, and prawns Penaeus japonicus to combined acetochlor-Cu, Cd-Zn were studied in hydroponic and soil-culturing systems using the methods of ecotoxicology. In particular, systematically quantitative analyses were documented by field experiments. Results showed that ecotoxicological effects under the combined pollution were not only related to chemical properties of pollutants but also dependent on the concentration level of pollutants, in particular on the combination of concentrations of pollutants in ecosystems. Additionally, species of organisms, especially the type of ecosystem, determined the influences. To some extent, biological tissue targets attacked by pollutants were an important factor.     

Anthropogenic pollutants: a threat to ecosystem sustainability?

Pollutants, including synthetic organic materials and heavy metals, are known to adversely affect physiological systems in all animal species studied to date. While many individual chemicals can perturb normal functions, the combined actions of multiple pollutants are of particular concern because they can exert effects even when each individual chemical is present at concentrations too low to be individually effective. The biological effects of pollutants differ greatly between species reflecting differences in the pattern of exposure, routes of uptake, metabolism following uptake, rates of accumulation and sensitivity of the target organs. Thus, understanding of the effects of pollutants on wildlife and ecosystems will require detailed study of many different species, representing a wide range of taxa. However, such studies can be informed by knowledge obtained in more controlled conditions which may indicate likely mechanisms of action and suitable endpoint measurements. Responses may be exacerbated by interactions between the effects of pollutants and environmental stressors, such as under-nutrition or osmotic stresses and so changes in such variables associated with climatic changes may exacerbate physiological responses to pollutant burdens.     

Temporal dynamics of microbial communities in microcosms in response to pollutants

Elucidating the mechanisms underlying microbial succession is a major goal of microbial ecology research. Given the increasing human pressure on the environment and natural resources, responses to the repeated introduction of organic and inorganic pollutants are of particular interest. To investigate the temporal dynamics of microbial communities in response to pollutants, we analysed the microbial community structure in batch microcosms that were inoculated with soil bacteria following exposure to individual or combined pollutants (phenanthrene, n‐octadecane, phenanthrene + n‐octadecane and phenanthrene + n‐octadecane + CdCl₂). Subculturing was performed at 10‐day intervals, followed by high‐throughput sequencing of 16S rRNA genes. The dynamics of microbial communities in response to different pollutants alone and in combination displayed similar patterns during enrichment. Specifically, the repression and induction of microbial taxa were dominant, and the fluctuation was not significant. The rate of appearance for new taxa and the temporal turnover within microbial communities were higher than the rates reported in other studies of microbial communities in air, water and soil samples. In addition, conditionally rare taxa that were specific to the treatments exhibited higher betweenness centrality values in the co‐occurrence network, indicating a strong influence on other interactions in the community. These results suggest that the repeated introduction of pollutants could accelerate microbial succession in microcosms, resulting in the rapid re‐equilibration of microbial communities.     

多环芳烃(萘)与聚苯乙烯微球联合对普通小球藻的急性毒性效应

为了解多环芳烃类污染物与微塑料的联合毒性效应, 实验通过检测藻密度、叶绿素a含量(Chl.a)、总蛋白(TP)、丙二醛含量(MDA)、过氧化氢酶活性(CAT)和超氧化物歧化酶活性(T-SOD)等指标, 探究了环境中持久型污染物萘(Nap)和5 μm聚苯乙烯微塑料(MPs)联合胁迫对普通小球藻96h的急性毒性效应。结果表明: Nap和MPs单独和联合胁迫时对普通小球藻均有抑制作用, 单独胁迫时最高抑制率分别为68.26%和57.40%, 联合胁迫时最高抑制率为52.05%; 对Chl.a也均产生抑制作用, 与藻密度呈现出较好的一致性。在单独及联合胁迫下, TP含量均显著下降, MDA含量均显著上升。Nap单独胁迫时CAT和T-SOD活性均呈显著下降趋势; MPs单独胁迫和联合胁迫时, CAT和T-SOD活性均先上升后下降, 且联合胁迫实验组最终CAT和T-SOD活性均显著高于对照组。Nap和MPs对普通小球藻的EC₅₀-96h分别为81.35和383.3 mg/L, Nap较MPs对普通小球藻的毒性更强; Nap和MPs(毒性单位比1﹕1)对普通小球藻的EC₅₀-96h为1.320 TU, 联合毒性效应表现为拮抗作用。可见, MPs的存在降低了Nap的毒性, 在短期内体现出一定的保护作用。     

根际圈在污染土壤修复中的作用与机理分析

根际圈以植物根系为中心聚集了大量的生命物质及其分泌物,构成了极为独特的“生态修复单元”。本文叙述了根在根际圈污染土壤修复中的生理生态作用,富集、固定重金属,吸收、降解有机污染物等功能;菌根真菌对根际圈内重金属的吸收、屏障及螯合作用,对有机污染物的降解作用;根际圈内细菌对重金属的吸附与固定,对有机污染物的降解作用以及根际圈真菌和细菌的联合修复作用等,同时对可能存在的机理进行了分析,认为根际圈对污染土壤的修复作用是植物修复的重要组成部分和主要理论基础之一,并指出利用重金属超富集植物修复重金属污染土壤具有广阔的应用前景;筛选对水溶性有机污染物高吸收富集及其根 发泌能力强的特异植物,同时接种利于有机污染物降解的专性或非专性真菌和细菌可能会成为有机污染土壤植物修复研究的重要方向之一。     

Pb2+、Cd2+对3种水生动物致毒效应影响的比较研究

在特定时间（12、24、48、72h）内,研究了Pb^2＋和Cd^2＋对草履虫（Paramecium caudatum）、三角涡虫（Dugesia japonica）和中华圆田螺（Cipangopaludia viviparrus）3种水生动物的单一和联合毒性效应.结果表明：在同等条件下,Cd^2＋对三者的致毒效应都明显强于Pb^2＋;3种动物中,草履虫最敏感,而圆田螺耐受能力最强;随单一毒物浓度的增大以及暴露时间的延长,两者的致毒效应都显著增大,表现出明显的浓度—效应和时间—效应关系;二者复合作用时,对3种动物的致毒效应主要表现为与二组分的浓度比例有关.复合致毒效应也表现出了明显的浓度—效应关系,并且浓度和暴露时间的交互作用对3种水生动物毒性都有显著的影响.     

土壤污染生态毒性效应评价研究进展

随着社会经济的高度发展,人类活动加剧,我国土壤污染问题突出,不仅威胁人体健康,同时也严重威胁动植物及微生物的安全,生态安全问题不容忽视。但是我国土壤污染风险管控目前主要关注人体健康,对生态系统的关注较少,缺乏土壤污染生态风险评估技术指南及基于生态风险的土壤环境质量基准及标准。准确评价土壤污染生态毒性效应,是制定土壤环境质量标准、实现生态风险评估及预警与管控的重要基础。针对土壤污染生态毒性效应评价问题,分别对土壤污染生态毒性效应特征、评价方法、评价终点、暴露-效应关系构建、生态毒性效应外推,以及群落水平与复合污染生态毒性效应评价等方面的关键问题展开了讨论,指出目前土壤污染生态毒性效应评价主要是基于单物种的急性毒性测试,利用个体和亚个体水平的指示物作为评价终点,缺乏针对群落及生态系统高水平评价终点的生态毒性效应评价方法,定量评价污染物尤其是复合污染物对土壤生物群落及生态系统的影响,是土壤污染生态毒性效应评价的关键问题和难点问题。建议今后重点开展以下3方面的工作1)群落及生态系统水平评价终点的筛选;2)土壤污染生态毒性效应环境影响因子识别及影响机制研究;3)土壤复合污染联合毒性效应定量评价及...     

Dynamics of plant responses to combinations of air pollutants

The focus of this review is on how plants respond to combinations of multiple air pollutants. Global pollution trends, plant physiological responses and ecological perspectives in natural and agricultural systems are all discussed. In particular, we highlight the importance of studying sequential or simultaneous exposure of plants to pollutants, rather than exposure to individual pollutants in isolation, and explore how these responses may interfere with the way plants interact with their biotic community. Air pollutants can alter the normal physiology and metabolic functioning of plants. Here we describe how the phenotypic and molecular changes in response to multiple pollutants can differ compared to those elicited by single pollutants, and how different responses have been observed between plants in the field and in controlled laboratory conditions and between trees and crop plants. From an ecological perspective, we discuss how air pollution can result in greater susceptibility to biotic stressors and in direct or indirect effects on interactions with organisms that occupy higher trophic levels. Finally, we provide an overview of the potential uses of plants to mitigate air pollution, exploring the feasibility for pollution removal via the processes of bio‐accumulation and phytoremediation. We conclude by proposing some new directions for future research in the field.     

合成生物学在环境修复中的应用

环境问题是21世纪人类面临的最严重的挑战。随着现代工农业飞速发展,生态环境日益恶化,难降解污染物如新兴污染物逐渐显现,已成为制约社会经济可持续发展的重要因素。微生物具有强大的环境修复能力,但是其进化速度远不及新兴污染物出现的速度,亟需应用合成生物学的技术来解决这一难题。在充分认识难降解有机污染物微生物降解(途径)特性的基础上,利用我国丰富的微生物与基因资源,运用合成生物学的手段,定向设计和改造现有降解菌株,构建能够降解一种或多种污染物的工程菌株;同时针对复合型污染,如废水等,在建立典型有机污染物代谢、调控和抗逆相关基因元件的模块库基础上,引入人工菌群等策略,对生物系统进行理性设计和组装,构建典型环境污染物的高效降解菌群,可有效促进我国新兴污染物微生物分解代谢的研究,为环境修复的工程应用提供技术支持。     

Joint effects of nutrients and contaminants on the dynamics of a food chain in marine ecosystems

We analyze the joint effect of contaminants and nutrient loading on population dynamics of marine food chains by means of bifurcation analysis. Contaminant toxicity is assumed to alter mortality of some species with a sigmoidal dose-response relationship. A generic effect of pollutants is to delay transitions to complex dynamical states towards higher nutrient load values, but more counterintuitive consequences arising from indirect effects are described. In particular, the top predator seems to be the species more affected by pollutants, even when contaminant is toxic only to lower trophic levels.     

Activation of the heat shock response in plants by chlorophenols: transgenic Physcomitrella patens as a sensitive biosensor for organic pollutants

The ability to detect early molecular responses to various chemicals is central to the understanding of biological impact of pollutants in a context of varying environmental cues. To monitor stress responses in a model plant, we used transgenic moss Physcomitrella patens expressing the beta-glucuronidase reporter (GUS) under the control of the stress-inducible promoter hsp17.3B. Following exposure to pollutants from the dye and paper industry, GUS activity was measured by monitoring a fluorescent product. Chlorophenols, heavy metals and sulphonated anthraquinones were found to specifically activate the hsp17.3B promoter (within hours) in correlation with long-term toxicity effects (within days). At mildly elevated physiological temperatures, the chemical activation of this promoter was strongly amplified, which considerably increased the sensitivity of the bioassay. Together with the activation of hsp17.3B promoter, chlorophenols induced endogenous chaperones that transiently protected a recombinant thermolabile luciferase (LUC) from severe heat denaturation. This sensitive bioassay provides an early warning molecular sensor to industrial pollutants under varying environments, in anticipation to long-term toxic effects in plants. Because of the strong cross-talk between abiotic and chemical stresses that we find, this P. patens line is more likely to serve as a direct toxicity bioassay for pollutants combined with environmental cues, than as an indicator of absolute toxicity thresholds for various pollutants. It is also a powerful tool to study the role of heat shock proteins (HSPs) in plants exposed to combined chemical and environmental stresses.     

The developing framework of marine ecotoxicology: Pollutants as a variable in marine ecosystems?

Marine ecosystems include a subset in which at least some interrelated geochemical, biochemical, physiological, population and community characteristics are changed by pollutants. Moderate contamination is relatively widespread in coastal and estuarine ecosystems, so the subset of ecosystems with at least some processes affected could be relatively large. Pollutant influences have changed and will probably continue to change on time scales of decades. Biological exposures and dose in such ecosystems are species-specific and determined by how the species is exposed to different environmental media and the geochemistry of individual pollutants within those media. Bioaccumulation models offer significant promise for interpreting such exposures. Biological responses to pollutants need to be more directly linked to exposure and dose. At the level of the individual this might be improved by better understanding relationships between tissue concentrations of pollutants and responses to pollutants. Multi-discipline field and laboratory studies combined with advanced understanding of some basic processes have reduced the ambiguities in interpreting a few physiological/organismic responses to pollutants in nature. Recognition of pollutant-induced patterns in population responses could lead to similar advances. A rational framework for ecotoxicology is developing, but its further advance is dependent upon better integration of ecotoxicology with basic marine ecology and biology.     

Protein profile variation in cultivated and native freshwater microorganisms exposed to chemical environmental pollutants

Assimilation of ³⁵S-precursors into microbial proteins was used to investigate toxicity and adaptational responses that occur in nutrient enriched and natural freshwater samples experimentally contaminated with benzene, toluene, trichloroethylene (TCE), or xylene. Experiments were conducted to analyze (1) the potential of using microbial community protein profiles for responsive identification of chemical pollutant exposure, (2) the inhibition of microbial productivity through reduction in rate of protein synthesis caused by specific chemical pollutants, and (3) whether selection of subpopulations in freshwater microbial communities challenged with chemical pollutants leads to adaptive strategies mediated by production of particular polypeptides. The results show that distinct banding patterns of polypeptides in the range of 30 to 100 kilodaltons that were obtained following collective cultivation of freshwater microorganisms differ with each chemical pollutant. Protein yield and radioisotope incorporation were reduced within ten minutes of microbial exposure to chemical pollutants in the following order: xylene < toluene < benzene < TCE. Adaptation of the freshwater microbial community to chemical pollutants prior to radioisotope incorporation produced differences in polypeptide profiles, in the banding patterns of radioactive polypeptides, and in the rate of radioisotope incorporation. The rate of radioisotope incorporation by freshwater microorganisms pre-adapted to chemical pollutants was lowest with xylene (88.1% reduction), followed by TCE (84.0% reduction), toluene (67.3% reduction), and benzene (43.5% reduction). In long-term radioisotope incorporation experiments, protein yield and polypeptide radioactivity was higher in the presence of chemical pollutants than in uncontaminated control samples, suggesting increased metabolic productivity attributable to the chemical pollutants. Correspondence to: O.A. Ogunseitan.     

Evolutionary responses of plants to anthropogenic pollutants

There is currently great concern over the possible adverse effects of atmospheric de position and other regionally distributed pollutants on plants and plant communitics. In Europe and North America there are major research efforts to determine whether such pollutants damage plants or affect ecosystem processes. A topic of growing concern is the possibility of genetic or evolutionary effects of pollutants. Past research has demonstrated that individuals, populations and varieties of a particular species can differ in their response to pollutants. Although such differences have been documented, the importance of evolutionary responses to regional, low level but chronic pollution remains to be established. The significance of regional chronic pollution is that effects on plants may no longer be limited to heavily industrialized or populated areas, but rather may also occur in virtually all natural ecosystems.     

土壤有机污染植物修复的机理与影响因素

在综述大量国内外文献的基础上,分析了土壤有机污染植物修复的机理,重点介绍了国内外在植物吸收转运、植物根际降解和植物修复模型的研究进展。同时,从污染物的物理化学性质、植物种类、土壤性质、共存有机物和气象条件5个方面分析了影响土壤有机污染植物修复的主要因素,并展望了该领域的研究方向：深化植物修复机理,完善植物修复模型。加强植物-微生物协同修复的机理研究和技术应用,利用表面活性剂提高植物修复效率,加强复合有机污染植物修复研究。     

Evaluation of “Classic” and Emerging Contaminants Resulting from the Application of Biosolids to Agricultural Lands: A Review

The presence of detectable amounts of contaminants in treated sewage sludge (concentrations μg/kg – mg/kg) has led to concerns that land applications of biosolids may result in an accumulation of contaminants in the soil and their subsequent translocation through the food chain. Despite advances in wastewater management (e.g., anaerobic, thermophilic, and mesophilic digestion), many compounds and their metabolites remain intact following treatment. This review looks at the main risk factors relating to the occurrence of “classic” (persistent organic pollutants [POPs]) and emerging pollutants (pharmaceuticals and personal care products) in biosolids. Relevant EU legislation and risk assessment strategies for the control of emerging contaminants are also considered. Organic pollutants regulated under the Stockholm Convention on POPs along with PPCPs were identified as contaminants of concern based on the risk factors: persistence, bioaccumulation, and toxicity (PBT). PPCPs were recognized as being of particular concern as their high transformation/removal rates are compensated by their continuous introduction into the environment. This study highlights the growing concern in relation to emerging contaminants in biosolids and highlights risk assessment strategies that can be used to characterize potential human/environmental risks.     

PHYLOGENETIC VARIATION IN THE TOLERANCE AND UPTAKE OF ORGANIC CONTAMINANTS

An investigation into the phylogenetic variation of plant tolerance and the root and shoot uptake of organic contaminants was undertaken. The aim was to determine if particular families or genera were tolerant of, or accumulated organic pollutants. Data were collected from sixty-nine studies. The variation between experiments was accounted for using a residual maximum likelihood analysis to approximate means for individual taxa. A nested ANOVA was subsequently used to determine differences at a number of differing phylogenetic levels. Significant differences were observed at a number of phylogenetic levels for the tolerance to TPH, the root concentration factor and the shoot concentration factor. There was no correlation between the uptake of organic pollutants and that of heavy metals. The data indicate that plant phylogeny is an important influence on both the plant tolerance and uptake of organic pollutants. If this study can be expanded, such information can be used when designing plantings for phytoremediation or risk reduction during the restoration of contaminated sites.     

Dynamic changes in microbial community structure and function in phenol-degrading microcosms inoculated with cells from a contaminated aquifer

Contamination of aquifers by organic pollutants threatens groundwater supplies and the environment. In situ biodegradation of organic pollutants by microbial communities is important for the remediation of contaminated sites, but our understanding of the relationship between microbial development and pollutant biodegradation is poor. A particular challenge is understanding the in situ status of microorganisms attached to solid surfaces, but not accessible via conventional sampling of groundwater. We have developed novel flow-through microcosms and examined dynamic changes in microbial community structure and function in a phenol-degrading system. Inoculation of these microcosms with a complex microbial community from a plume in a phenol-contaminated aquifer led to the initial establishment of a population dominated by a few species, most attached to the solid substratum. Initially, phenol biodegradation was incomplete, but as the microbial community structure became more complex, phenol biodegradation was more extensive and complete. These results were replicated between independent microcosms, indicating a deterministic succession of species. This work demonstrates the importance of examining community dynamics when assessing the potential for microbial biodegradation of organic pollutants. It provides a novel system in which such measurements can be made readily and reproducibly to study the temporal development and spatial succession of microbial communities during biodegradation of organic pollutants at interfaces within such environments.     

土壤-植物系统复合污染研究进展

土壤-植物系统复合污染研究是污染生态学的科学前沿,对于农业环境的生态安全具有重要意义．本文对复合污染概念的由来及其内涵的发展、土壤-植物系统可能发生的复合污染类型及其研究进展、土壤-植物系统复合污染所导致的生态效应及其定量表征进行了较为系统的概述,提出了土壤-植物系统中重金属-有机污染物和有机污染物-病原微生物也是复合污染的重要类型．指出了多种污染物交互行为、次生产物及其老化、分子毒理机制等方面的研究是今后土壤-植物系统复合污染的研究重点．同时对复合污染的研究方法以及结果的应用进行了展望,为土壤污染的预警防治与修复提供依据。     

菲、芘、1,2,4-三氯苯对土壤高等植物根伸长抑制的生态毒性效应

测定了草甸棕壤条件下,菲、芘、１,２,４—三氮苯对高等植物（小麦、白菜、西红柿）根伸长抑制串以及复合污染毒性效应。结果表明,菲、芘、１,２,４—三氮苯浓度与植物根伸长抑制串呈显著线性或对数相关（ｐ＝０．０５）。３种化学品对植物根伸长抑制的强弱顺序为１,２,４—三氮苯＞菲＞芘。这与３种化学品的水中溶解度大小显著相关。小麦是３种供试植物中对有机污染物最敏感植物。菲、芘、１,２,４—三氮苯复合污染主表现为协同作用。