两级气浮--生物接触氧化工艺处理乳化液废水

采用两级所浮及生物接触氧化工艺对高浓度乳 化液含油废水处理工艺进行了研究。试验和运行研究结果表明，采用ＰＦＳ混凝剂有较好的破乳效果，二级气浮出水再经生物接触氧化工艺处理后，ＣＯＤＣｒ和油总去除率分别为９９．５％、９９．９％，各项指标均达到排放标准。     

团结协作开创未来--卢鉴章主任委员在中国煤炭学会环境保护专业委员会1999年年会暨学术研讨会上的讲话(摘要)

中国煤炭学会环境保护专业委员会1999年年会暨“煤矿矿区水资源保护与水资源化”学术研讨会今天在宜昌召开,这是我们专业委员会成立后的第四次年会,也是第四次学术研讨会。在此,谨向参加这次会议的同志们表示热烈的欢迎和感谢！     

上海市绿色食品的发展前景与策略

为更好地协调环境、资源、食品、健康的关系,适应人们对农产品需求的变化及社会可持续发展的需要,世界各国纷纷提出了发展无污染农产品的设想。我国亦于1990年推出了“绿色食品”活动。该文在综观国内外绿色食品研究和发展概况的基础上,分析了上海市发展绿色食品的有利条件,并提出了发展对策和建议。     

区域环评中废水排放量的预测方法研究

阐述了区域环评污染物排放源强的预测原则,对区域开发活动中废水量和COD排放量的预测方法作了详细论述,并以温州滨海新区环评为例作了实证研究.     

郑州市固体废物现状及控制对策探讨

通过对基准年（１９９８年）郑州市固体废物污染现状调查及存在问题分析，预测了２０００～２０１５年固体废物的产生量，提出郑州市固体废物远景规划目标，并明确实现这一目标的污染控制对策及具体投资项目。     

绿色贸易壁垒若干问题的探讨

分析了国际贸易中绿色贸易壁垒的成因，即环境问题的全球化、社会化以及西方国家第三次贸易保护主义浪潮的兴起；介绍了这种新兴的技术性壁垒的基本形式，包括环境标准和法规、环境标志制度及其门槛提高、成本内在化与绿色补贴、包装的环保要求等；最后对绿色贸易壁垒的一些特点作了客观性的评价。     

政府机构改革中强化环保执法监督的措施探析

全面推进机构改革是党的十五大提出的战略任务。本文从已经开始的国务院和省级机构改革的总体方案和即将开始的市、县机构改革的实际情况出发，具体分析机构改革对环境保护行政主管部门实施和强化统一监督管理职能面临的机遇和挑战，提出今后强化环保执法监督的对策措施。     

Photocatalytic degradation of acetaminophen in modified TiO2 under visible irradiation

This study investigated the photocatalytic degradation of acetaminophen (ACT) in synthetic titanium dioxide (TiO₂) solution under a visible light (λ >440 nm). The TiO₂ photocatalyst used in this study was synthesized via sol–gel method and doped with potassium aluminum sulfate (KAl(SO₄)₂) and sodium aluminate (NaAlO₂). The influence of some parameters on the degradation of acetaminophen was examined, such as initial pH, photocatalyst dosage, and initial ACT concentration. The optimal operational conditions were also determined. Results showed that synthetic TiO₂ catalysts presented mainly as anatase phase and no rutile phase was observed. The results of photocatalytic degradation showed that LED alone degraded negligible amount of ACT but with the presence of TiO₂/KAl(SO₄)₂, 95 % removal of 0.10-mM acetaminophen in 540-min irradiation time was achieved. The synthetic TiO₂/KAl(SO₄)₂ presented better photocatalytic degradation of acetaminophen than commercially available Degussa P-25. The weak crystallinity of synthesized TiO₂/NaAlO₂ photocatalyst showed low photocatalytic degradation than TiO₂/KAl(SO₄)₂. The optimal operational conditions were obtained in pH 6.9 with a dose of 1.0 g/L TiO₂/KAl(SO₄)₂ at 30 °C. Kinetic study illustrated that photocatalytic degradation of acetaminophen fits well in the pseudo-first order model. Competitive reactions from intermediates affected the degradation rate of ACT, and were more obvious as the initial ACT concentration increased.     

盐酸脱附Pb(Ⅱ)负载氨基膦酸树脂的基本性能

氨基膦酸树脂是一种常用的广谱性重金属螯合树脂,对水中的Pb(Ⅱ)具有很好的选择性分离去除能力,但吸附Pb(Ⅱ)后的树脂再生较为困难。系统研究了盐酸脱附Pb(Ⅱ)-负载氨基膦酸树脂D860的基本性能,优化了基本脱附参数。实验表明,采用盐酸作为脱附剂具有较为良好的脱附效果,10%吸附量树脂脱附反应平衡较快仅需10 min,脱附本身受Pb(Ⅱ)在盐酸溶液中的溶解度影响显著。脱附流速从1 BV/h升高到5 BV/h,脱附效果受到的影响很小。升高温度可以提高PbCl2溶解度,进而提高脱附效率。固定床脱附采用1.0 mol/L盐酸,在1 BV/h和303 K条件下,仅需7 BV脱附剂即可实现较高的脱附效率。     

Environmental monitoring of alcohol sulfates and alcohol ethoxysulfates in marine sediments

The study describes the environmental monitoring of anionic surfactants―alcohol sulfates (AS) and alcohol ethoxysulfates (AES)—in marine sediments. Concentration values were obtained after pressurised liquid extraction (PLE) and liquid chromatography–tandem mass spectrometry analysis (LC–MS/MS). Samples were collected from a range of wastewater discharge points along the coast of the provinces of Huelva, Málaga, Granada and Almería. Urban, agricultural and industrial wastewaters are discharged at the selected 38 sampling sites. Principal component analysis was carried out in order to evaluate the distribution and behaviour of these compounds in these coastal environments. Evaluation of the data revealed that the behaviour and sources of AS and AES in marine sediments are different, and that the distribution of AES depends on the length of the alkyl chain, while the number of ethoxylated units is not relevant. Additionally, the 38 sampling sites can be grouped into only two types of outfalls according to their AS distribution. The concentration of compounds in sediment samples ranged from 7.52 to 13.50 mg kg^?1 for AS, from 3.04 to 10.68 mg kg^?1 for AES–C₁₂E_x and from 3.83 to 11.56 mg kg^?1 for AES–C₁₄E_x.