海水中二甲基硫测定方法的研究

二甲基硫（ＤＭＳ）是雨水天然酸性的贡献者和影响气候变化的重要痕量气体，本文海水中ＤＭＳ测定方法，即采用冷却预浓缩技术处理海水样品，用带有火焰光度检测器气相色谱仪分析，此方法的精密度为１２％，准确度为１０％，对１００ｍｌ海水样品最小检测量为０．０５４ｎｇ（ＤＭＳ）。同时对色谱柱的选取，实验材料的选择，浓缩柱填充材料的选择，鼓气效率，干燥管，样品解析，样品保存等有关实验步骤进行了讨论。     

庐山地区底栖大型无脊椎动物耐污值与水质生物学评价

自1996年至1999年，对庐山自然保护区22个采样点的底栖大型无脊椎动物进行了调查．完成了庐山底栖大型无脊椎动物大多数科与部分属的耐污值核定工作，在Hilsenhoff(1988)与Lenat(1993)工作基础上，新增73科的耐污值．首次提出了蜚蠊目B1attodea、脉翅目Neuroptera、半翅目Hemiptera及鞘翅目Coleoptera水生类群的耐污值．其它主要水生昆虫11个目，凡在中国有分布记录或可能在中国及邻近地区有分布的科均收入并提出耐污值．摇蚊科中国常见的16属引用了Lenat(1994)推荐的耐污值，增加了甲壳纲Crustacea、寡毛纲O1igochaeta、腹足纲Gastropoda、腮瓣纲Lemellibranchia、蛭纲Hirudinea、涡虫纲Turbellria与蜱螨纲Acarina水螨总科Hydrachnoidea等的耐污值．利用上述耐污值系统，对22个采样点中的13个进行了连续水质生物监测，对其余9个采样点水质进行了评估．1996年5月至1999年9月期间，13个采样点水质由重污染至极清洁排序可分6类：如琴湖、东谷溪流、电站水库属重污染水体；天桥由轻污染至重污染；2级站、1级站、3级站由很清洁或清洁至一般；芦林湖、电站水库南支流很清洁；黄龙潭由很清洁至轻污染；三叠泉、第四纪冰川遗址、大月山水库为极清洁．多数采样点1996年11月水质好于5月份的水质．1999年所有采样点水质均比1996年2次调查时差，说明庐山水质污染呈加重趋势．图2表2参18     

太湖表层沉积物中重金属的形态分析

采用BCR三步分级提取法和ICP-AES测定了太湖沉积物中8种重金属不同形态的含量，初步评估了太湖沉积物中重金属的生物有效性，探讨了沉积物总有机碳（TOC）与重金属不同形态之间的关系。     

沉积物中多环芳烃和有机氯农药定量分析的质量保证和质量控制

以美国ＥＰＡ为方法为基础,进行了沉积物中多环芳烃和有机氯农药分析的质量保证和质量控制实验,采用回收率指示物控制回收率,用内标法定量。结果表明多环芳烃的指示物回收率为５０．６７－９７．３３％,目标化合物的回收率为５８．６７－９６．３３％,方法检测限为３．３０－９．２６μｇ．ｋｇ＾－１。     

膜—生物反应器中溶解性微生物产物的研究进展

本文就膜－生物反应器中溶解性微生物产物的生成特性及其影响的研究进展进行了总结。在膜－生物反应器中，膜的高效固液分离作用在提高系统容积负荷和出水水的同时，也使生物反应器成为一个相对封闭的系统，以腐殖质，多糖，蛋白质等物质为主要成分的溶解性微生物产物是上物处理出水中溶解性TOC或COD的主要组成部分，主要产生于微生物的基质分解过程和内源呼吸过程，其高分子物质的含量较多且可生物降解性较差，因此，在膜－生物反应器中会出现积累，溶解性微生物产物的过高积累不仅有可能降低膜过滤出水的水质稳定性，而且有可能影响污染活性，并引起膜污染。进水溶液和污染度是影响溶解性微生物产物产生量的重要因素。目前有关膜－生物反应器溶解性微生物产物的研究还很不完善，有很多问题需进一步研究。     

硝基苯类废水的预处理技术研究

Fe(OH)2对硝基苯具有强烈的还原作用，短时间内可把硝基苯还原为苯胺。催化铁屑法处理硝基苯类废水，除了包括铁屑法处理废水的各种反应外，还能使硝基苯在其表面直接还原，且反应在弱碱性条件下效果较好。m(Fe)：m(Cu)为10：1，pH为9．5，废水硝基苯进水质量浓度为250mg／L，反应时间为30min，硝基苯的去除率达100％。     

城市河流水质常规评价技术研究

运用综合水质标识指数法,对我国河流水质评价面临的关键技术问题,包括水质评价方法、水质评价项目,水质级别评价,水环境功能区达标评价、水质定性评价、河流及水系整体水质比较、水质随时间和空间变化等作了明确界定,并介绍了在上海河流水质评价中的应用。     

Effect of nitrogen and phosphorus on the water quality in the Three Gorges Reservoir Area during and after its construction

A survey concerning the concentration of the nutrients in the Three Gorges Reservoir Area was carried out. This paper presents the parameters(NO3^- -N, NO2^- -N, KjeldahI-N, non-ionic ammonia, P-PO4 and TP)determined at 16 sampling sites from 1997 to 1999. The dominant soluble nitrogen form was NO3^- -N followed by KjeldahI-N, NO2^- -N and non-ionic ammonia. Mean values of NO3^- -N, NO2^- -N, Kjeldahl-N and non-ionic ammonia ranged from 0.50 to 2.37 mg/L, 0.022 to 0.084 mg/L, 0.33 to 0.99 mg/L and 0.007 to 0.092 mg/L respectively.Mean values of P-PO4 at most sampling sites were higher than 0.1 mg/L for subject to eutrophication. The major factors influencing the concentrations of N and P might be agricultural runoff, municipal and industrial effluents. In addition, 6 kinds of soil were sampled at the area where would inundated after the dam completed. Two approaches were adopted to simulate the N and P release from the inundated soils. The results showed that the soils would release nitrogen and phosphorus to the overlying water when the soils were inundated. The characteristics of soil affected the equilibrium concentrations of N and P between the soil and the overlying water.     

Incorporating sorption/desorption of organic pollutants into river water quality model

Preliminary research was conducted about how to incorporate sorption/desorption of organic pollutants with suspended solids and sediments into single-chemical and one-dimensional water quality model of Jinghang Canal.Sedimentation-resuspension coefficient k3 was deduced; characteristics of organic pollutants, concentrations and components of suspended solids/sediments and hydrological and hydraulic conditions were integrated into k3 and further into river water quality model; impact of sorption/desorption of organic pollutants with suspended solids and sediments on prediction function of the model was discussed. Results demonstrated that this impact is pronounced for organic pollutants with relatively large Koc and Kow, especially when they are also conservative and foc of riversuspended solids/sediments is high, and that incorporation of sorption/ desorption of organic pollutants into river water quality model can improve its prediction accuracy.