沈阳市机动车尾气的污染影响和控制对策

本文就沈阳市机动车尾气的污染现状,从法制建设、技术措施、民众参与等几个方面提出了尾气污染的控制对 策。     

煤沥青烟气对大鼠肺损伤及免疫功能的影响

采用自然吸入的暴露方法，通过分析肺灌洗液成分及脾脏淋巴细胞的转化功能，观察碳素厂冷压车间空气对大鼠肺损伤及免疫功能的影响，结果表明，在自然吸入染毒期间，引起大鼠肺灌洗液中乳酸氢酶、酸性磷酸酶和唾液含量或高，肺巨噬细胞及其Ｆｃ受体数降低，并且还引起脾脏淋巴细胞的转化能力下降。     

积极推行清洁生产提高企业经济效益

清洁生产是企业防治污染的方向,是提高环境保护管理水平的途径,文中主要阐述了企业推行清洁生产的条件及重要意义,为企业节能降耗实施可持续发展提供保障.     

大气中氨对农作物的影响

本文利用实验结论，阐述了大气中对农作物生长的影响及表现症状，分析了大气中不同浓度氨对农作物不同生长期的影响，对受氨污染地区农作物的种植选择及农业损失鉴定具有参考价值。     

绿色GDP核算框架下的水环境治理效益评价

水环境的治理对于经济、社会的发展都具有重要意义。在此,以国家“十五”重大科技水专项分课题武汉水专项的实施为背景,在绿色GDP核算框架下对水环境治理效益进行了评价。     

经济合理地推行总量控制计划

目前，我国正大力推行排放污染物总量控制计划。本文探讨了如何更经济更合理地实施控制计划，如何以最小的代价实际控制目标。     

大气飘尘对大鼠肺细胞的毒性比较

采用大白鼠气管内注入飘尘后分析肺灌洗液的方法，比较了上海不同地区飘尘对大鼠肺细胞的毒性；再运用毒性指数及效应指数，综合评价了上海市不同地区大气飘尘污染的状况。研究表明：从肺灌洗液的生化成份分析及细胞分类显示，以彭浦新村、隆昌路平凉路、康定路胶州路３个点的飘尘毒性较大。综合评价结果，彭浦新村的效应指数最大，以后依次为康定路胶州路、鲁班路斜土路、青云路、隆昌路平凉路等。     

生物炭环境效应和在农业面源污染防治中的作用

生物炭能够延缓肥料养分释放,提高肥料利用率,降低肥料及土壤养分流失,从而减轻农业面源污染。同时,生物炭进入土壤中,实现碳的封存固定,减少碳排放。     

锌离子对厌氧氨氧化脱氮效能的影响

通过序批实验的方法,直接接种厌氧氨氧污泥,研究了Zn2＋对厌氧氨氧化（Anammox）脱氮效能的影响。研究结果表明,当进水Zn2＋质量浓度小于2 mg/L时,对厌氧氨氧化生物活性有促进作用,可增强微生物的脱氮效能;当进水Zn2＋质量浓度在2 mg/L和4 mg/L之间时,脱氮效能无明显变化,说明对厌氧氨氧化微生物活性无明显影响;当进水Zn2＋质量浓度大于4 mg/L,对厌氧氨氧化反应有抑制作用,Zn2＋浓度越高,抑制作用越明显。 Zn2＋对厌氧氨氧化的半抑制质量浓度（CI,50）为32.3 mg/L,NO2--N与NH4＋-N转化比的平均值为1.28。     

Substance-related environmental monitoring

Background  Due to the requirements of the EU Water Framework Directive and other legal regulations (e.g., national laws like the German Federal Soil Protection Act), but also due to the implementation of the new EU chemicals management system REACH, environmental monitoring will gain increasing importance for the surveillance of environmental quality as well as for the assessment of chemicals. Against this background, the Work Group on ‘Environmental Monitoring’ of the Division of ‘Environmental Chemistry and Ecotoxicology’ within the German Chemical Society has compiled a position paper on substance-related environmental monitoring. Scope  Core elements of this position paper are the definitions of important terms like monitoring, exposure monitoring, effect monitoring, and integrated monitoring. Moreover, temporal and spatial aspects (monitoring of spatial distributions, trend monitoring, and retrospective monitoring) and their applications are discussed. The main focus of this position paper is the coverage of aspects which have to be observed for the preparation and implementation of a monitoring program. Essential is the clear specification of the targets of the monitoring which determine the development of the monitoring concept and its realization, e.g., if environmental media (compartments) or organisms are most appropriate as samples for the aim of the study. Of course, also the properties of the target substances are important (e.g., lipophilicity/bioaccumulation as pre-requisite for an exposure monitoring with organisms). Finally, the monitoring phases of sample planning, sampling, storage and transport of samples, selection of analytical methods, quality assurance measures as well as reporting are discussed. Perspectives  An important issue for the future is to link the quantification of chemicals in environmental compartments (exposure and pollution monitoring) more closely to the study of biological effects (effect monitoring) than has been the case up to now. Furthermore, by inclusion of a spatial differentiation, a comprehensive evaluation of the state of an ecosystem can be obtained and the relevance of the results improved. Practical examples of monitoring studies which illustrate various aspects covered in this position paper will be presented in a series of publications by members of the Work Group in the following issues of this journal.