环境污染纠纷调处与环境行政处罚之区别浅析——兼与章锦华同志商榷

指出了环境污染纠纷调处与环境行政处罚的性质，程序，结果等均不相同，在理论上不能将两者混一谈，实践中应区别对待。     

面向新世纪的MARPOL73／78公约及其附则Ⅱ

国际海事组织目前正在对《ＭＡＲＰＯＬ７３／７８公约》附则Ⅱ－控制散装液体有毒物质污染规则作重大修改，内容包手胡毒液体物质和化学品，这很可能对主管机关、船公司和化工界造成严重的冲击。     

Interfacial effects of suspended particles on biodegradation of N (2,4 dimethyl phenyl) N'' methylformamidine hydrochloride and dibutyl phthalate in waters

ＩｎｔｅｒｆａｃｉａｌｅｆｅｃｔｓｏｆｓｕｓｐｅｎｄｅｄｐａｒｔｉｃｌｅｓｏｎｂｉｏｄｅｇｒａｄａｔｉｏｎｏｆＮ（２，４ｄｉｍｅｔｈｙｌｐｈｅｎｙｌ）Ｎ’ｍｅｔｈｙｌｆｏｒｍａｍｉｄｉｎｅｈｙｄｒｏｃｈｌｏｒｉｄｅａｎｄｄｉｂｕｔｙｌｐｈｔｈ...     

基于GIS的船运液体化学品溢漏大气扩散模拟系统

将地理信息系统应用在船运液体化学品溢漏事故上，利用Mapinfo自带的二次开发工具MapBasic对船运液体化学品溢漏大气扩散模拟系统进行开发研究，介绍了系统设计的总体结构，系统的功能模块，详细叙述了系统的建设过程，数学模型建立，数据库建立与管理，编程语言及其关键技术，系统能连续运态地模拟显示溢漏化学品大气扩散污染范围，为应急反应科学决策服务。     

环境化学污染对人类的生殖危害

目前认为，环境化学物污染已对人类生殖造成一定的有害影响，综述近年来国内外有关环境中金属元素、有机化学品、气体及农药等化学物质对人类生殖影响的研究报道，为进一步开展环境生殖研究提供参考。     

政策环境影响评价与公众参与——国家有毒化学品立法EIA中的公众参与

阐明在我国开展政策EIA的必要性,从可持续发展的角度探讨政策EIA中公众参与的目的、意义、方法和特点,并介绍和分析国家有毒化学品立法EIA开始阶段中的公众参与。     

煤炭非燃料利用与洁净煤技术

煤炭是中国的主要能源和资源，也是主要的污染源。煤炭燃料利用的不洁净使得其能源主导地位受到石油、天然气和新能源越来越大的挑战。寻求合理、高效、洁净的煤炭非燃料利用新途径应当成为煤化工发展的重要方向。本文在分析了煤炭燃料利用存在问题和前景的基础上，强调煤炭非燃料利用应当成为洁净煤技术的一种主要形式，并指出煤炭非燃料利用的合理途径。     

有毒化学品的污染评价与控制技术

对有毒化学品进行简介 ;建议从生理毒性、属性毒性及生命周期等方面建立有毒化学品的污染评价系统 ,为有毒化学品的应用、管理和处理处置提供理论依据 ;针对不同的有毒化学品及其排放情况与浓度组分拟选用物化处理法、化学处理法及生物处理法作为污染控制技术。     

湖泊、水库水的强化混凝除藻的试验研究

就高锰酸钾复合药剂强化混凝对湖泊、水库水中藻类的去除进行了研究，试验表明：投加一定量的高锰酸钾复合药剂可显著提高水中藻类的去除率。将经与预氯化、预投加高锰酸钾除藻工艺进行比较，表明高锰 酸钾复合药剂强化混凝除藻效率明显优于传统预氯化、预投加高锰酸钾除藻工艺。     

Best Management Practices for Silvicultural Chemicals and the Science Behind Them

Silvicultural chemicals include fertilizers and pesticides applied for forest management. All states east of the Rockies have at least some form of silvicultural chemical best management practices (SCBMPs) and it is widely accepted that SCBMPs effect some protection of water quality. All SCBMPs recommend handling and application precautions and a minimum width streamside management zone (SMZ) on each side of streams for protection of water quality and aquatic ecosystems. Typically these zones increase in width as stream width increases. In areas where cold-water fish are present, additional widths are designated for their protection. Minimum SMZ widths range from 8 to 91 meters on each side of the stream bank for intermittent and perennial streams. Most SMZ recommendations do not cover ephemeral drainages, ditches or canals. SMZs are generally described as being site specific with width dependent on slope, soil type and other conditions as well as the stream's designation as perennial or intermittent. The science behind SCBMPs is often elusive. Spray drift can be controlled through proper selection and use of application technology while considering site specific conditions. SMZs greatly reduce the amount of herbicides reaching streams. Available toxicological data and research on aquatic ecosystem impacts from herbicide use suggest that additional protection from silvicultural chemicals may not be necessary. However, there is evidence to suggest that protection of ephemeral and intermittent channels can further reduce entry of silvicultural chemicals into streams and also reduce sedimentation. This may be the most fruitful area of research we can pursue in light of the knowledge gaps listed.