对"有毒重金属"实施2种总量控制监管方式的利害分析

首先,必须明确认定：对第一类污染物实施《源头总量控制》是污控执法和促进经济结构改革的保证条件.这种监管方式自2008年《第一次全国污染源普查工业污染源产排污系数手册》公布以来,更具有其切实实施的可行性.《源头总量控制》与《水环境总量控制》两种监管方式既是各自独立、缺一不可,又是相互依赖和相互补充的关系,目前一些地方的规划管理者模糊和混淆了两类污染物和两种监管的内容和方式,笼统以《水环境总量控制》来监管所有污染物,丢弃了《源头总量控制》,使本应严加管理的饮用水水源地丧失了控制第一类污染物的能力.我国《地面水环境质量标准》（GB 3838-88）中第一类污染物的水质指标与我国实际的水环境背景值有很大差距,存在着＂放宽允排量＂和＂价态转化引发危害＂的问题;以一个10 t电解铅的企业为例,证明两种监管方式的铅允排量相差甚大.总之,把第一类污染物与第二类污染物统一实施《水环境容量总量控制》将带来众多的危害,应当严格实施《源头总量控制》与《水环境总量控制》相结合的监管方式.     

睾丸酮丛毛单胞菌对喹啉类化合物的降解

对喹啉、异喹啉、2-甲基喹啉、3-甲基喹啉、4-甲基喹啉和6-甲基喹啉在睾丸酮丝毛单胞菌(Comamonas testosteroni Q10)作用下的降解及底物之间的相互作用进行研究．结果表明,喹啉和3-甲基喹啉不仅能有效地被降解,而且细菌也有明显的生长,而其它化合物虽有部分降解但没有观察到细胞生长．底物初始浓度的增加对菌Q10有一定抑制作用．喹啉的存在对其它化合物的降解具有不同的促进效应,其中尤以6-甲基喹啉和4-甲基喹啉最为明显．能在较短时间内得到完全去除,而在各二元体系中喹啉的降解受到这些化合物的抑制作用．     

Cd(Ⅱ)-邻菲咯啉络合物极谱吸附波测定水中微量镉

在ＰＨ＝４．７４的０．２ｍｏｌ／ＨＡｃ－ＮａＡｃ缓冲体系中,Ｃｄ（Ⅱ）－邻菲咯啉络合物在单扫描波极谱仪上于－０．７９Ｖ处产生一灵敏的吸附还原波,其二次微分极谱波灵敏度高,波形好。     

活性炭吸附室内空气中挥发性有机化合物

活性炭吸附室内空气中挥发性有机化合物的１０％穿透时间与气相浓度及挥发性有机化合物的种类有关,通过对苯、甲苯和丙酮的实验研究,得出了由高浓度估算室内低浓度时炭床１０％穿透时间的经验公式ｔｂ,１＝ｔｂ,ｈ（Ｃ０,１／Ｃ０,ｈ）＾ａ,其中ａ值是与炭床性能及挥发性有机化合物种类有关的参数,可通过实验确定。     

珠穆朗玛峰北坡绒布冰川区水体的化学特征

１９９７－０５在珠峰地区绒布冰川采集的４类水样的实测资料表明,本区各类水体都呈碱性,ＰＨ值的大小顺序为：湖水〉湖水〉表层雪。河水和湖水的阴离子以ＳＯ＾２－４为最大,而表层雪样品以Ｃｌ－最大;     

嗅觉测定技术的进展与恶臭污染管理政策的改进

介绍了３种有关恶臭的测定方法及其发展趋向,即色谱质谱法（ＧＣ／ＭＣ）,电子算法和嗅觉测定法,目前世界上广泛采用以臭味浓度作为恶臭污染的控制指标,嗅觉测定法是广泛接受的臭味测定方法,本文就嗅觉测定法的定义,设备及其质量控制的方法作了详细的介绍,并比较了欧洲、美国、溴大利亚以及香港等地区当前对于恶臭污染的将嗅觉测定法进行标准化的进程。     

温敏性水凝胶对金属离子Y3+,UO2+2的浓集分离

利用合成的ＰＮＩＰＡＡｍ／ＡＡｃ交联共聚温敏性水凝胶分别对水溶液中微量的Ｙ＾２＋,ＣＵ２＾２＋离子进行浓集分离研究。实验结果表明,凝胶能有效浓集Ｙ＾２＋,ＵＯ２＾２＋离子,在ＰＨ＝１～４范围内,凝胶的溶胀比及对Ｙ＾３＋,ＵＯ２＾２＋的浓集率均随ＰＨ的增大而增大,浓集率分别达到８０％和９０％,凝胶溶胀比的增大浓集量分别为５．２９３ｍｇ．ｇ＾－１、３６．１６ｍｇ．ｇ＾－１凝胶的表面积也对浓集率有限大影     

LFG控制利用工程基本参数的试验研究

通过深圳市玉龙坑垃圾填埋场的现场抽气试验。本文进行了填埋气本安全控制与回收利用工程基本参数的研究。     

A review of biomarker compounds as source indicators and tracers for air pollution

An overview of the application of organic geochemistry to the analysis of organic matter on aerosol particles is presented here. This organic matter is analyzed as solvent extractable bitumen/ lipids by gas chromatography-mass spectrometry. The organic geochemical approach assesses the origin, the environmental history and the nature of secondary products of organic matter by using the data derived from specific molecular analyses. Evaluations of production and fluxes, with cross-correlations can thus be made by the application of the same separation and analytical procedures to samples from point source emissions and the ambient atmosphere. This will be illustrated here with typical examples from the ambient atmosphere (aerosol particles) and from emissions of biomass burning (smoke). Organic matter in aerosols is derived from two major sources and is admixed depending on the geographic relief of the air shed. These sources are biogenic detritus (e.g., plant wax, microbes, etc.) and anthropogenic particle emissions (e.g., oils, soot, synthetics, etc.). Both biogenic detritus and some of the anthropogenic particle emissions contain organic materials which have unique and distinguishable compound distribution patterns (C₁₄-C₄₀). Microbial and vascular plant lipids are the dominant biogenic residues and petroleum hydrocarbons, with lesser amounts of the pyrogenic polynuclear aromatic hydrocarbons (PAH) and synthetics (e.g., chlorinated compounds), are the major anthropogenic residues. Biomass combustion is another important primary source of particles injected into the global atmosphere. It contributes many trace substances which are reactants in atmospheric chemistry and soot paniculate matter with adsorbed biomarker compounds, most of which are unknown chemical structures. The injection of natural product organic compounds into smoke occurs primarily by direct volatilization/steam stripping and by thermal alteration based on combustion temperature. Although the molecular composition of organic matter in smoke particles is highly variable, the molecular tracers are generally still source specific. Retene has been utilized as a tracer for conifer smoke in urban aerosols, but is not always detectable. Dehydroabietic acid is generally more concentrated in the atmosphere from the same emission sources. Degradation products from biopolymers (e.g., levoglucosan from cellulose) are also excellent tracers. An overview of the biomarker compositions of biomass smoke types is presented here. Defining additional tracers of thermally-altered and directly-emitted natural products in smoke aids the assessment of the organic matter type and input from biomass combustion to aerosols. The precursor to product approach of compound characterization by organic geochemistry can be applied successfully to provide tracers for studying the chemistry and dispersion of ambient aerosols and smoke plumes. Presented at the 6th FECS Conference on Chemistry and the Environment, Atmospheric Chemistry and Air Pollution, August 26–28, 1998, Copenhagen.     

化学法处理高浓度电镀废水

分析、总结了采用化学法处理高浓度电镀废水中的含氰废水、含镍废水、含铬废水和含酸废水的工程设计、调试和实际运行情况。实践表明,化学法处理高浓度电镀废水是行之有效的,而用PH／ORP计控制好废水处理中的化学反应是稳定运行的关键。