环境管理指标系统之建立与选择

介绍环境绩效评估发展的缘起及其发展趋势，叙述环境管理指标系统之间内涵与建立的步骤以及各类型环境绩效指标的种类及其稳定原则。     

海南小海潟湖环境的破坏与治理

从口门稳定性的角度,分析了三大人为工程(太阳河改道、在通道口修筑北堤和封堵南汊道及约5 km2的潮滩被围垦)所起的作用以及波浪动力对小海口门演变的影响,认为小海潟湖潮汐通道在其演变进程中,由于潮汐弱而波能相对较强,目前仍属波浪作用为主型,依据自己多年的研究工作,首次提出以口门复式断面和通道分汊的方法对小海及该类型潟湖进行治理.     

昆明市饮用水中卤代烃现状及成因研究

本文对昆明市饮用水经加氯消毒前后卤代烃污染物进行了两的的调查，结果表明昆明市饮用水中的主要卤代烃污染物是氯仿和四氯化碳两种，其浓度均远远低于国家标准。采用传统的煮混法即可去除80％以上的污染物。     

制定区域大气环境总量控制方案的技术方法

提出了区域大气环境总量控制方案制定的技术路线和主要技术，即污染物的基础允许排放量，平权允许排放量和优化允许排放量的确定方法，以上海市某加工区ＳＯ２总量控制方案作了实例分析。     

抚仙湖马料河人工湿地水质净化效果评估研究

从污染物去除百分率、污染物削减量及污染物表面负荷去除量等不同角度对抚仙湖马料河人工湿地的水质净化效果进行了分析,结果表明TN、NH3-N和TP的平均去除率分别约为60%、60%和50%,平均削减量约为14kg/d、5kg/d和1kg/d,去除污染物表面负荷平均为0.72g/m2.d、0.22g/m2.d、0.06g/m2.d。     

络合滴定－阳极溶出伏安法测定腐植酸与金属络合物的稳定常数

以金属离子络合滴定－阳极溶出伏安法（ＡＳＶ法）测定得出湘江底泥、灵石风化煤和德都泥炭３种腐植酸分别与Ｐｂ、Ｃｄ的络合稳定常数、络合容量和分子量３个参数．并探讨了可能的误差来源及消除方法。     

大气中硝酸和颗粒物硝酸盐的测定

研究了用扩散管差分法和多种叠滤膜法测量大气中粒物硝酸盐和气体硝酸，扩散管差分法可以测量颗粒物硝酸盐和气体硝酸，避免了采样时颗粒物硝酸盐的人为损失。Ｆｌｏｕｒｏｐｏｒｅ聚四氟乙烯膜等惰性膜也可以采集颗粒物硝酸盐，其后的ＮａＣｌ浸渍膜采集硝酸，而玻璃纤维膜几乎同时采集了颗粒物硝酸盐和硝酸。     

大理苍山洱海自然保护区旅游与环境可持续发展规划的研究

苍山洱海是国家级自然保护区，同时又是国家级风景名胜区，由于旅游业的开展而引发的环境、生态问题日趋突出。针对客观实际，在保护和开发并举的原则下，对该区域的旅游区、旅游模式等进行了规划，提出了旅游区域的环境保护指标、旅游容量，同时制定了相应的管理措施     

Bioaccumulation and elimination of avermectin B1a in the earthworms (Eisenia fetida)

The acute toxicity, bioaccumulation, and elimination of avermectin B1a (AVM B1a) in earthworm (Eisenia fetida) were investigated in different exposure systems. The LC50 of AVM B1a on earthworms were 24.1 mg/kg and 17.1 mg/kg, respectively, for 7 and 14 days in artificial soil. The LC50 tested by the filter paper for 2 days was 4.63 microg/cm2. The earthworms were cultivated in artificial soil containing 0.6 mg/kg and 3.0 mg/kg AVM B1a, respectively for bioaccumulation experiments. The AVM B1a residues in earthworms were determined with HPLC-fluorescence method. The results showed that AVM B1a was taken up from the concentrated artificial soil by the earthworms and the steady-state levels were reached after 9-18 days of exposure. On the 18th day, the final concentrations of AVM B1a in the earthworms treated with two different dosages were 107 ng/g and 165 ng/g, respectively; there were not significantly accumulation. About 80.0% and 94.8% of the accumulated AVM B1a were eliminated respectively in two groups within 1 day after they were exposed to AVM B1a-free soil, but a trace amount of AVM B1a was found for a relative long time in earthworms.     

Estimation of apparent rate coefficients for phenanthrene and pentachlorophenol interacting with sediments

To gain information on organic pollutants in water-sediment systems, a compartment model was applied to study the sorption course of phenanthrene and pentachlorophenol (PCP) in sediments. The model described the time-dependent interaction of phenanthrene and PCP with operationally defined reversible and irreversible (or slowly reversible) sediment fractions. The interactions between these fractions were described using first order differential equations. By fitting the models to the experimental data, apparent rate constants were obtained using numerical optimization software. The model optimizations showed that the amount of reversible phase increased rapidly in the first 10 d with the sorption time, then decreased after 10 d, while the amount of irreversible phase increased in the total sorption course. That suggested the mass transport between reversible phase and irreversible phase. The extraction efficiency with hot methanol ranged from 36% to 103% for phenanthrene and from 65% to 101% for PCP, with the trend of decreasing with sorption time.