大窑湾疏浚水环境要素变化特征及其相关关系

根据大窑湾后６个泊位疏浚工程本底调查和疏浚监测结果，借助因子分析探讨了疏浚前后水环境要素的变化特征及相关关系，找出了控制污染物分布的主要因子，评价了疏浚对海洋环境的影响。     

三唑磷农药废水厌氧处理可行性研究

采用厌氧流化率工艺处理在唑磷农药废水，必须降低原水中ＮＨ３－Ｎ含量，调整营养比例，当ＣＯＤ：Ｎ：Ｐ＝（１８０～２００）：５：１时，在中温厌氧消化条件下，ＣＯＤ含量可从４１７０ｍｇ／ｌ，去除率约５０％，沼气产率达到０．２５６ｍ＾３／ｍ＾３．ｄ。因此，把厌氧处理作为好氧处理的预处理单元，能确保整个处理系统出水达标。     

加压活性炭生物膜法处理DSD有机废水

采用加压活性炭生物膜法处理以对硝基甲苯磺酸盐为主的难降解的有机废水的研究,是在活性炭生物膜法处理有机废水基础上发展起来的新技术。本实验结果表明,在加压9.8×10~4Pa(1kgt/cm~2)的条件下,COD_(Cr)去除率为62％～70％,比常压活性炭生物膜法高20％～25％;其容积负荷Nv=1.7～2.9kgCOD/m~3·d,比一般活性污泥法高3～6倍。     

甲醇残液生化处理系统中好氧菌特性研究

以甲醇残液生化处理系统中的生物污泥为材料,运用分离技术,获得好氧菌30株。研究了每株细菌的生理生化特性和培养特征,将30株细菌鉴定为9个属,并进一步探讨了甲醇残液生物降解的模式。     

锰砂表面改性去除酚类化合物的研究

本文叙述了锰砂表面改性(以下简称旧锰砂)处理含酚饮用水的实验研究,陈酚率可达99％。本实验对除酚因素(温度、pH值、流速和接触时间等)进行了实验研究。当进水酚浓度≤2.0mg/l时,经旧锰砂的吸附,可使酚浓度≤0.002mg/l。     

沈阳市中水回用对策研究及前景分析

为了解决全市水资源严重短缺问题，缓解污水排放对生态环境造成的破坏，沈阳市在今后5～10a内将建成中水回用系统，使城市中水回用率达到50％。结合沈阳市中水回用现状，分析了目前全市中水供应能力及市场需求，进行了2010年相应指标的预测，同时探讨了沈阳市中水回用存在的问题和解决方法。     

稀土生产废水对四道沙河、西河和黄河水质的影响

本文通过大量的环境现状调查，论述了包头市稀土湿法生产企业废水污染物排放情况以及对接纳水体四道沙河、西河和黄河包头段水质的影响及变化趋势。针对存在的环境问题，提出了防治污染的对策与建议。     

高压脉冲电凝聚技术处理活性染料废水试验研究

难生物降解有机废水是废水处理的难点。阐述了高压脉冲电凝聚技术处理高浓度、难生物降解有机废水的最新机理。采用高压脉冲电凝聚技术处理活性染料（活性红）生产废水．研究了影响高压脉冲电凝聚技术处理活性染料废水效果的操作条件及影响因素．结果表明，在最佳处理工艺条件下。CODCr浓度12628mg／L的生产废水经处理后CODCr去除率为65％左右。再经后续混凝沉淀，最终出水CODCr可降低到1000mg／L以下。     

污水处理厂沉淀池改进方案

根据某污水处理场沉淀池的COD和SS去除率较低的情况，文中着重探讨了问题的产生原因，并针对平流式沉淀池及斜管式沉淀池提出了相应的改进方案，实践证明改进后提高了COD和SS去除率30％，并明显降低了二级生物处理阶段的有机物负荷，节省了大量的暴气量通过改进达到了降低处理场其它环节的负荷和降低污水处理成本的目的。     

Comparison of UV-based advanced oxidation processes for the removal of different fractions of NOM from drinking water

This study examined the effectiveness for degradation of hydrophobic (HPO), transphilic (TPI) and hydrophilic (HPI) fractions of natural organic matter (NOM) during UV/H₂O₂, UV/TiO₂ and UV/K₂S₂O₈ (UV/PS) advanced oxidation processes (AOPs). The changing characteristics of NOM were evaluated by dissolved organic carbon (DOC), the specific UV absorbance (SUVA), trihalomethanes formation potential (THMFP), organic halogen adsorbable on activated carbon formation potential (AOXFP) and parallel factor analysis of excitation–emission matrices (PARAFAC-EEMs). In the three UV-based AOPs, HPI fraction with low molecular weight and aromaticity was more likely to degradate than HPO and TPI, and the removal efficiency of SUVA for HPO was much higher than TPI and HPI fraction. In terms of the specific THMFP of HPO, TPI and HPI, a reduction was achieved in the UV/H₂O₂ process, and the higest removal rate even reached to 83%. UV/TiO₂ and UV/PS processes can only decrease the specific THMFP of HPI. The specific AOXFP of HPO, TPI and HPI fractions were all able to be degraded by the three UV-based AOPs, and HPO content is more susceptible to decompose than TPI and HPI content. UV/H₂O₂ was found to be the most effective treatment for the removal of THMFP and AOXFP under given conditions. C1 (microbial or marine derived humic-like substances), C2 (terrestrially derived humic-like substances) and C3 (tryptophan-like proteins) fluorescent components of HPO fraction were fairly labile across the UV-based AOPs treatment. C3 of each fraction of NOM was the most resistant to degrade upon the UV-based AOPs. Results from this study may provide the prediction about the consequence of UV-based AOPs for the degradation of different fractions of NOM with varied characteristics.