农药使用的危险性评价

提出了农药使用危险性的单项因素及综合评价方法。其中必评因素包括,农药用量,急性和慢性毒性,三致作用,农药在作物和土壤中的半衰期,鱼毒,蜂毒以及对眼肤的刺激作用;附加参数包括,农药挥发性,代谢增毒作用,生物浓缩系数和除草剂对后茬作物的毒性。评价注重农药用量和急性毒性,在对205种农药进行评价的基础上,提出了我国用量最大的5种杀虫剂属危险级。     

摇蚊幼虫的水生态毒理学研究进展

本文综述了国外对摇蚊幼虫的水生态毒理学研究的最新进展，包括生物检测、生物积累和遗传毒理研究等几方面．国外的研究表明摇蚊幼虫可以作为常用试验生物（鱼类和蚤类）的补充，用于有毒化学品的急、慢性毒性生物检测和遗传毒性研究，以及生物积累试验，以评价化学品的生态效应，并对污染物进行生物监测．     

农药的生态风险评价

农药的日益增多和广泛应用,给农业带来收益,也给环境带来了巨大的压力.该文阐述了对农药进行生态风险评价的必要性和重要性,提出了农药的风险评价的基本流程,分析了农药的生态毒性影响.评价流程分6部分农药理化性质分析;农药迁移转化能力分析;农药生态毒性分析;农药对生物多样性的影响;农药对人体健康的影响;农药风险特征分析等.而生态学原理是评价的基础,生态毒性是实施评价的核心.     

略论工业化学品的风险评价

工业化学品的日益增多和广泛使用，给环境带来了很大的压力。工业化学品的风险评价问题，对环境管理至为重要，国家环保局及国内的工业企业正在讨论有关化学品毒性的控制问题。该文讨论了化学品风险评价的常用术语及基本程序，对生态毒性在评价中的地位特别予以强调，并提出了与其相关的评价程序，即理化参数分析；毒性扫描；亚急性毒性试验和慢性毒性试验或微生态系统试验。     

氯化钡的毒性研究

为制订我国饮用水卫生标准，对氯化钡的急性、蓄积性和亚慢性毒性进行了研究，急性毒性得氯化钡对大鼠和小鼠经口LD50值分别为147．5mg／kg和317．19mg／kg。蓄积试验表明，氯化钡有一定的蓄积作用。亚慢性毒性结果表明，10，100和300mg／1组大鼠肝、肾、肾上腺、心、脾可观察到轻度组织学变性。300mg／1组大鼠Hb含量降低，MCV增加，MCH降低，呈大细胞贫血象。心电图显示，高剂量组大鼠心率加快，GRS波群时间延长，R波电压偏高．生化指标可见血清Ca^2 ，CK，AKP，uN，TC等随剂量增高而降低。     

保护淡水水生生物硝基苯水质基准研究

以硝基苯为研究对象,在分析美国和中国2种类型水生态系统和生物区系特征的基础上,分别筛选两国水生生物物种的毒性数据,运用物种敏感度分布曲线法、毒性百分数排序法和评价因子法分别推导了2个国家保护淡水水生生物水质基准;同时,结合国内外主要水体ρ(硝基苯)分布特征,对地表水体中硝基苯生态风险进行了初步评价.结果表明:由于生物区系不同,同样方法得到的美国水质基准值明显高于中国水质基准值,其中物种敏感度分布曲线法得出的基准值最为合理.用物种敏感度分布曲线法得到中国硝基苯急性基准值为0.572mg/L,慢性基准值为0.114mg/L;美国硝基苯急性基准值为7.271mg/L,慢性基准值为2.031mg/L.风险表征结果显示,中国主要地表水体中硝基苯不存在潜在的生态风险.      

水生态毒理学中检测慢性毒性的短期试验方法

本文主要介绍了国外水生态毒理学研究和水质量管理中广泛应用的四种检测慢性毒性的短期试验方法．综述了其方法研究和应用的情况．这几种方法是鱼类和两栖类胚胎－幼体存活和致畸试验，黑头软口鲦幼体７天生长存活试验，网纹蚤７天存活繁殖试验和大型蚤慢性毒性的短期试验方法．文中还对研究和发展适合我国情况的检测慢性毒性的短期试验方法提出了建议．     

天津地区土壤中遗传毒性物质的分布规律

利用SOS／umu试验测试了天津地区41个土壤样品有机提取物的遗传毒性,研究了该地区土壤中遗传毒性物质污染水平及区域生态风险的分布规律．结果表明,在所研究区域中,遗传毒性的高风险区主要分布在天津市和塘沽、汉沽两个区．其中,汉沽区土壤有机组分遗传毒性值最高,其次为塘沽区和市区．与有限的文献报道数据相比,天津地区土壤有机组分的遗传毒性较高,且与该地区土壤中多环芳烃浓度的分布规律相似．研究结果表明,遗传毒性的生物效应标记方法可以用于区域生态风险评价,来快速筛选和甄别遗传毒性物质污染的高风险区．     

风险污染物短期高剂量暴露下的生态风险评估方法

水污染事故的短期高剂量暴露造成的急性生态危害及水生生物安全问题成为人们研究的重点,但我国以往的水污染事故,多采用地表水环境质量标准和生活饮用水卫生标准来判断水体是否安全,缺乏对水生生物保护的安全效应阈值或风险值.国外在水生生物保护方面,虽然限定了一些风险污染物对水生生物的安全效应阈值或称为无效应阈值或风险值,但其无效应阈值的计算是基于长期暴露下的慢性毒性值,其生态风险值也是基于长期暴露下的风险,缺少对水污染事件短期高剂量暴露下化学品的阈值限定及风险评估.本研究结合常规生态风险评价的理念及美国EPA短期暴露情况下保护水生生物基准值的制定方法,探讨了水污染事件的短期高剂量暴露情况下风险污染物的生态风险评价及生态效应阈值的计算方法,并进行了实例应用,同时对建立我国水污染事故生态风险评估方法体系提出了建议.     

铜锈环棱螺对镉污染沉积物慢性胁迫的生物标志物响应

沉积物毒性测试是评价水生态系统中沉积物污染生态风险的重要手段.建立合适的毒性测试生物是进行沉积物毒性测试的基本前提.铜锈环棱螺(Bellamya aeruginosa)在我国淡水水体中分布广泛,具有重要的生态价值.本研究将实验室培养的铜锈环棱螺暴露于不同含量的镉加标沉积物中28d,以评价该物种在镉污染沉积物慢性胁迫下生物标志物响应的敏感性.结果表明,除了谷胱甘肽(GSH)相对不敏感外,壳长增长率、肝胰脏超氧化物歧化酶(SOD)和过氧化氢酶(CAT)、以及肝胰脏和肾脏中的金属硫蛋白(MT)均表现出相对较高的敏感性,可用作重金属污染沉积物慢性胁迫的有效生物标志物.尤其是肝胰脏SOD和CAT可以用作指示低水平镉污染沉积物长期污染胁迫下的敏感生物标志物.此外,该物种的实验室培养和毒性测试操作容易进行,可以考虑将铜锈环棱螺作为我国淡水沉积物毒性评价的候选物种.     

我国土壤受试植物筛选与毒性预测

生态毒性数据缺乏是我国土壤基准与生态风险评估研究中一直存在的问题,开展本土受试植物的筛选可提供更多的生态毒理试验选材,从而获得不同物种的生态毒性数据.鉴于植物对土壤污染物的敏感性,从被子植物中依据分布范围、代表性和易于获得性等原则,对我国潜在的受试植物进行筛选,结果发现,13科53种被子植物分布广泛且易于获取,可作为本土受试植物;结合生态毒性数据的搜集与分析,其中12种受试植物的生态毒性数据相对丰富,并对部分典型污染物表现高敏感.此外在受试植物生态毒性预测模型研究方面,对12种受试植物两两进行建模预测,共得到132个物种种间关系估算模型(Interspecies Correlation Estimation,ICE),其中88个为显著性模型(F检验P<0.05);此处,回归分析了已构建ICE模型的评价参数,得出预测效果较好的ICE模型应满足交叉验证成功率≥ 80.00%、MSE ≤ 0.62、R² ≥ 0.76和分类学距离≤ 4的标准.最终筛选出25个符合上述标准的ICE模型,涉及禾本科-禾本科、十字花科-十字花科的相互预测,其中当燕麦Avena sativa、芜青Brassica rapa、普通小麦Triticum aestivum、玉蜀黍Zea mays和黑麦草Lolium perenne等作为替代物种时,预测物种的实际生态毒性值与预测值较为接近.受试植物的筛选与生态毒性预测模型的建立有助于生态毒性数据的产生,并为土壤污染管理和生态风险评估提供科学依据.     

生物毒性检测在水质安全评价中的应用

水质安全不仅关乎生态系统的健康,更关乎人类的生存与发展.借助水质标准浓度限值的传统方法评价水质安全存在一定不足,生物毒性测试能直观反映水体中所有共存污染物的综合毒性特征,已逐渐发展成为水质安全评价的重要补充.在大量文献资料调研、整理的基础上,首先从污染物的生物效应出发,总结了常用的致死毒性、遗传毒性、内分泌干扰性等效应的生物毒性测试方法;其次,讨论了水质毒性评价中常用的生物毒性测试方法和相应的毒性评价指标;最后,归纳总结了基于生物毒性测试的水质安全评价方法,包括潜在毒性法、毒性单位分级评价法、潜在生态毒性效应指数法、基于成组生物毒性测试的水质安全评价等,并讨论了各种方法的优缺点.本文既系统梳理了毒性测试在水质安全评价领域的研究进展,也为该领域后续的发展奠定了基础.     

Toxicity assessment for chlorpyrifos-contaminated soil with three di erent earthworm test methods

Earthworm toxicity tests are useful tools for terrestrial risk assessment but require a hierarchy of test designs that differ in effect levels （behavior, sublethal, lethal）. In this study, the toxicity of chlorpyrifos contaminated soil on earthworms was assessed. In addition to the acute and chronic tests, an avoidance response test was applied. Earthworms were exposed to sublethal and lethal concentration of chlorpyrifos, and evaluated for acute toxicity, growth, fecundity and avoidance response after a certain exposure period. The test methods covered all important ecological relevant endpoints （acute, chronic, behavioral）. Concentration of 78.91 mg/kg, chlorpyrifos caused significant toxic effects in all test methods, but at lower test concentrations, only significant chronic toxic effects could be observed. In present study, chlorpyrifos had adverse effect on growth and fecundity in earthworm exposed to 5 mg/kg chlorpyrifos after eight weeks. The avoidance response test, however, showed significant repellent effects at concentration of 40 mg/kg chlorpyrifos. For chlorpyrifos, concentration affecting avoidance response was far greater than growth and fecundity, it seemed likely that earthworms were not able to escape from pesticide-contaminated soil into the clean soil in field and hence were exposed continuously to elevated concentrations of pesticides.     

Toxicity assessing for chlorpyrifos-contaminated soil with three different earthworm test methods

Earthworm toxicity tests are useful tools for terrestrial risk assessment but require a hierarchy of test designs that differ in effect levels (behavior, sublethal, lethal). In this study, the toxicity of chlorpyrifos contaminated soil on earthworms was assessed. In addition to the acute and chronic tests, an avoidance response test was applied. Earthworms were exposed to sublethal and lethal concentration of chlorpyrifos, and evaluated for acute toxicity, growth, fecundity and avoidance response after a certain exposure period. The test methods covered all important ecological relevant endpoints (acute, chronic, behavioral). Concentration of 78.91 mg/kg, chlorpyrifos caused significant toxic effects in all test methods, but at lower test concentrations, only significant chronic toxic effects could be observed. In the present study, chlorpyrifos had adverse effect on growth and fecundity in earthworm exposed to 5 mg/kg chlorpyrifos after eight weeks. The avoidance response test, however, showed significant repellent effects concentration of 40 mg/kg chlorpyrifos. For chlorpyrifos, concentration affecting avoidance response was far greater than growth and fecundity, it seemed likely that earthworms were not able to escape from pesticide-contaminated soil into the clean soil in field and hence were exposed continuously to elevated concentrations of pesticides.     

土壤铅镉铬暴露下赤子爱胜蚓的回避行为和急性毒性

为了评价土壤重金属污染的生态毒理学效应,根据OECD(经济合作与发展组织)试验指南,研究了人工土壤中Pb、Cd、Cr暴露下赤子爱胜蚓(Eisenia fetida)的回避行为和急性毒性. 回避试验结果表明:赤子爱胜蚓产生完全回避反应的土壤w(Pb)、w(Cd)、w(Cr)分别为2 000、120、120 mg/kg. 急性毒性试验的结果表明,土壤Pb、Cd、Cr对赤子爱胜蚓14 d LD₅₀(半数致死浓度)的分别为2 526.05、362.83、229.44 mg/kg. 在检测Pb、Cd和Cr污染土壤时,赤子爱胜蚓回避试验的灵敏度要高于急性毒性试验. 该研究结果揭示出,赤子爱胜蚓的回避行为指标能够成为土壤生态系统风险评价和毒性效应研究的生物标志物预警指标.      

Bioavailability and toxicity of cadmium to microorganisms and their activities in soil: a review

Significant quantities of cadmium (Cd) have been added to the soils globally due to various anthropogenic activities, raising concerns for environmental health. Microorganisms play a unique role in the soil ecosystem, because of their contributions to soil fertility. Contrasting trends, reported on the toxic effects of heavy metals including Cd on soil microorganisms and their activities, are attributable to short-term studies often limited to a single soil type and conducted under controlled laboratory conditions. There is a paucity of reliable field data on Cd alone, since most field studies on Cd-microorganism interactions in soils are based on sewage sludge containing multimetals and organic substances. No single parameter can be used to generalize Cd toxicity and different parameters can provide contrasting results. A battery of relevant tests, rather than just one single assay, involving important microbial activities should therefore be included in ecotoxicity studies. The bioavailability of Cd and associated toxicity to soil biota vary with time, soil type, speciation, ageing, Cd-source, organisms and the environmental factors. The available fraction or soil solution Cd, and not the total concentration of Cd, seems to correlate well with the toxicity parameters.     

Bioavailability and toxicity of cadmium to microorganisms and their activities in soil: a review

Significant quantities of cadmium (Cd) have been added to the soils globally due to various anthropogenic activities, raising concerns for environmental health. Microorganisms play a unique role in the soil ecosystem, because of their contributions to soil fertility. Contrasting trends, reported on the toxic effects of heavy metals including Cd on soil microorganisms and their activities, are attributable to short-term studies often limited to a single soil type and conducted under controlled laboratory conditions. There is a paucity of reliable field data on Cd alone, since most field studies on Cd-microorganism interactions in soils are based on sewage sludge containing multimetals and organic substances. No single parameter can be used to generalize Cd toxicity and different parameters can provide contrasting results. A battery of relevant tests, rather than just one single assay, involving important microbial activities should therefore be included in ecotoxicity studies. The bioavailability of Cd and associated toxicity to soil biota vary with time, soil type, speciation, ageing, Cd-source, organisms and the environmental factors. The available fraction or soil solution Cd, and not the total concentration of Cd, seems to correlate well with the toxicity parameters.     

土壤镉暴露对玉米和大豆的生态毒性评估

以中国东北黑土为培养基,通过室内急性毒性实验,采用Trimmed Spearman-Karber方法计算EC50值(半抑制浓度),并分析作物的生物累积系数(BAF),定量化评估了土壤中镉对玉米和大豆的生态毒性及生物有效性.测量终点为种子发芽率、根长和幼茎长.结果表明,土壤镉暴露给农作物带来一定的负生长效应.种子发芽率不是评估土壤镉生态毒性的敏感因子,根生长是敏感的毒性测量终点.镉在植株体内的累积及迁移与作物种类和土壤镉浓度有关.玉米植株体内累积了较大量的镉,而大豆植株体内镉由根向幼茎的迁移较为显著.     

人工纳米颗粒对水生生物的毒性效应及其机制研究进展

随着纳米科技的飞速发展和纳米产品的普及,人工纳米颗粒(NPs)的生物毒性效应研究逐渐成为国内外关注的热点.以水环境和水生生物为对象,综述了近几年来NPs对水生生物的毒性效应、毒性机制等方面的研究进展.文中按NPs的分类总结了NPs对微生物、藻类、原生动物和鱼类等水生生物的毒性效应,着重论述了NPs的可能毒性机制及其与NPs的独特物理化学性质之间的关系,并在细胞和分子水平上探讨了NPs的摄取、跨膜运输等方面的可能机制.在自然水体中,NPs因其化学行为受水化学条件等影响而表现出不同于实验室研究中的生物毒性效应,本文也对这方面的研究进行了讨论和总结.最后分析了目前水生生物纳米毒性研究中的瓶颈和方法、技术方面的问题,并对以后应注重开展的研究进行了展望.