CuO/CSAC催化剂的制备及酸性大红GR废水的处理

以椰壳活性炭(CSAC)为载体负载CuO制备了CuO/CSAC催化剂。采用正交实验优化了CuO/CSAC催化剂的制备工艺条件,采用单因素实验和响应面实验优化了CuO/CSAC催化剂处理模拟酸性大红GR废水的工艺参数。结果表明:在CSAC加入量5 g、煅烧时间2.5 h、煅烧温度300 ℃、0.5 mol/L的硝酸铜溶液用量15 mL的最佳工艺条件下,CuO/CSAC催化剂微孔结构丰富,CuO特征峰明显;CuO/CSAC催化剂处理酸性大红GR废水的最佳工艺参数为pH 5.0,曝气时间4.10 h,催化剂加入量0.57 g,可将100 mL初始COD 962 mg/L、初始色度32 700倍的废水分别处理至残余COD 41.5 mg/L,残余色度28.4倍。建立了以残余COD和残余色度为响应值的工艺模型,计算值与实验值的相对误差均在±10%以内。     

Arsenic contamination in groundwater and its possible sources in Hanam, Vietnam

This study investigated the arsenic (As) level in groundwater, and the characteristics of aquifer sediment as related to the occurrence of As in groundwater in Hanam, Vietnam. The deposition and transport of As-containing substances through rivers were also examined. Arsenic concentrations in 88% of the groundwater samples exceeded the As limit for drinking water based on the WHO standards. The dominating form of arsenic was As(III). The maximum total As content in bore core sediment was found in a peat horizon of the profiles and generally, elevated levels of As were also found in other organic matter-rich horizons. Total As contents of the bore core sediments were significantly correlated with crystalline iron oxide, silt and clay contents, suggesting that As in aquifer sediment was mainly associated with iron (hydr)oxides and clay mineral. In the groundwater, As concentration showed significant correlations with the total concentrations of Fe and HCO (3)(-). Significant correlations between HCl-extractable As and non-crystalline Fe oxide, total C, N, and S were also observed in the profiles. The results support the hypothesis that under favorable reductive conditions established by the degradation of organic matter, the dissolution of iron (hydr)oxides releases adsorbed As into the groundwater. The deposition of As in the sediments from the Red River were significantly higher than that in the Chau Giang River, suggesting that the Red River is the main source of As-containing substances deposited in the study area.     

山东省近岸海域水质现状及变化趋势研究

通过对2003-2007年山东省近岸海域水质监测数据的分析,总结其近岸海域的水质状况及污染特征,并采用秩相关系数法对山东省近岸海域水质状况时空变化趋势进行分析与评价。结果表明,山东省近岸海域水质以一、二类海水为主,黄海近岸海域水质略好于渤海。全省近岸海域污染以有机污染为主,主要污染因子为无机氮和化学需氧量。2003-2007年,山东省近岸海域水质变化趋势基本稳定,但主要污染物化学需氧量的含量呈上升趋势。     

白马雪山国家级自然保护区与周边社区冲突分析

针对白马雪山国家级自然保护区与周边社区村民在环保观念、管理模式、资源利用以及补偿措施等方面的矛盾冲突,对其产生的原因进行了分析,并从社区经济发展、社区村民传统生活习惯约束、社区管理机构完善和少数民族传统文化有效利用等方面提出了主要的缓解冲突的措施和方法。     

污水生物生态处理工艺中的脱氮机理研究

通过水解池-美人蕉湿地、水解/接触氧化池-菖蒲湿地现场实验装置考察了生物-生态工艺深度净化分散生活污水的效果。结果表明,水解池-美人蕉湿地尽管湿地停留时间达到7 d,出水NH⁺₄-N仍难以达到一级A（GB18918-2002）标准;而增加接触氧化池后,湿地停留时间仅2 d,组合工艺出水水质远优于一级A出水要求。美人蕉湿地脱氮的主要途径是湿地微生物的硝化/反硝化,植物吸收约占28%。对经接触氧化处理,NH⁺₄-N、NO^-₃-N浓度均较高的进水,菖蒲湿地可在C/N小于2时高效脱氮。菖蒲湿地对TN的去除占组合工艺TN去除量的79%,其中植物吸收仅占湿地除氮总量的8%。湿地介质的厌氧氨氧化活性试验表明,菖蒲湿地介质表面的微生物在无有机碳源存在的条件下,可使培养液中的NH⁺₄-N与NO^-₃-N、NO^-₂-N短期内发生同步脱氮,厌氧氨氧化可能是菖蒲湿地在进水低碳源条件下脱氮的主要原因。     

纤维膜过滤特性的数值模拟

一个高性能过滤膜除了与纤维自身结构参数有关联外,过滤时的操作条件对其也有重要影响。为研究纤维膜过滤效率、过滤压降与过滤速度、孔隙率以及过滤膜厚度之间的关系,以更好地对实际过滤进行优化,本研究从纤维膜的过滤机理进行出发,采用FLUENT多孔介质离散相模型对纤维过滤器的流场进行模拟。结果表明,膜前后压降会随着过滤速度和膜厚度的增大而增大;一定范围内纤维膜孔隙率适度增加,截留率变化不大,但是膜压差会逐渐减小;同时过滤速度对颗粒截留率有影响,速度增大时,粒子轨迹发生偏移,导致过滤膜一部分过早发生堵死,而一部分作用减弱,影响了过滤效果。     

粉煤灰制备混凝剂及其砸黄河水的处理效果

以粉煤灰和铁泥为原料、加入一定量NaCl作助溶剂室温下制备粉煤灰混凝剂,考察酸灰比与酸浓度对Fe3＋、Al“溶出率及混凝剂对黄河水处理效果的影响。结果表明,Fe3＋、A13＋的最佳溶出条件为酸灰比3mL／g、HCl浓度4mol／L,此时Fe“溶出率为28．1％,浓度为11．81g／L;A13＋溶出率为5．2％,浓度为1．86g／L。粉煤灰混凝剂对黄河水的处理效果在投加量2．38mL／L、沉降时间30min、pH6．2～7．5时最佳,对浊度、ss和COD。。平均去除率分别为89．7％、83．6％和62．3％,优于传统市售混凝剂PAC和Fc,Fe3＋、AI3＋同时存在有利于各自优势的发挥从而提高混凝效果。     

活性炭纤维负载TiO2光催化降解甲醛的影响因素

利用自制光催化气体反应器体系,以活性炭纤维负载TiO2作催化剂,在紫外光照射下模拟降解室内污染气体甲醛,测试了活性炭纤维负载TiO2催化剂的催化活性,探讨了紫外光光强、催化剂的酸度、反应器内湿度及反应时间等控制反应的主要因素对甲醛降解率的影响。结果表明,活性炭纤维与TiO2的协同作用大大提高了对甲醛的降解效果;紫外光强增倍对甲醛降解率有一定提高,但提高幅度仅为11.71%;活性炭纤维用pH=5的TiO2溶胶浸泡做催化剂对甲醛的降解效果最好,60 min内降解率达到68.37%;反应器内的湿度为81%甲醛降解率最高,反应60 min后达82.2%;随着反应时间的延长,甲醛降解率的上升幅度不断减小,最高只能达到94.59%。     

城镇污水厂污泥农用重金属源头控制技术措施

城镇污水厂污泥堆肥农用是一种经济合理的利用方式,但其前提是污泥中的重金属必须满足相应控制标准要求。末端降低或去除污泥中的重金属,需要一定的技术、资金和人力资源,推广起来有难度;采用"源头控制技术措施",可从根本上消减污泥中重金属,确保污泥堆肥农用的安全、可靠,且其操作简单,经济合理,方便实施。     

Agricultural Pesticide Residues in Farm Ditches of the Lower Fraser Valley,British Columbia,Canada

Transient and permanent farm ditches flowing to the Lower Fraser River tributary fish streams of British Columbia, Canada, were sampled at several locations in 2003–2004 to determine the occurrence and concentration of residues of selected pesticides, their transformation products, and soluble/extractable Cu⁺⁺ ions. Of the 43 compounds analyzed, 28 and 22 pesticides were detected in transient farm ditch water and sediments, respectively. About 34% fewer pesticides, however, were found in both matrices of permanent farm ditches. Average concentrations (μ g L^?1) of those most frequently detected in permanent farm ditch water were atrazine (0.20), α -chlordane (0.06), desethylatrazine (0.13), diazinon (0.55), dieldrin (0.28), endosulfan sulfate (0.16), glyphosate (6), metalaxyl (0.27); and soluble Cu⁺⁺ ions (25). Those most often found in ditch sediments (μ g kg^?1) were aminomethylphosphonic acid (AMPA) (2,300), 1,1,1-trichloro-2,2-bis-(4-chlorophenyl)ethane (DDT) (250), endosulfan sulfate (500), glyphosate (1,225); and extractable Cu⁺⁺ ions (58,000). The risk potential of these pesticide residues to non-target aquatic organisms inhabiting Fraser River tributary fish streams contiguous to permanent farm ditches is evaluated and discussed.