垃圾渗滤液中微塑料分析的消解方法评价

微塑料（MPs）是近年来国内外关注度极高的新兴污染物,建立实际环境样品中MPs的分析方法是开展相关研究的基础。对于复杂污水样品而言,样品的消解过程至关重要,将极大地影响MPs的准确分析。选择垃圾渗滤液为典型复杂污水样品,采用样品浊度和色度变化、残余悬浮固体量、MPs在颗粒物中的占比为评价指标,对盐酸消解、30%过氧化氢消解及芬顿试剂消解3种常用消解方法的消解效果进行了比较。结果表明,30%过氧化氢对垃圾渗滤液样品的消解效果最佳,MPs在全部颗粒物中的占比达63.7%,极大地缩减了后续MPs定性分析的时间,降低了分析难度,且对渗滤液中MPs的回收率也高达（103±3）%。在此基础上,讨论了消解效果与过氧化氢投加量/样品浊度（V_H2O2/T₁）的关系。当V_H2O2/T₁为0.15~0.20 mL/NTU时,样品残余悬浮固体量最低,消解效果最佳。     

Transport and fate of organic wastes in groundwater at the Stringfellow hazardous waste disposal site, southern California

In January 1999, wastewater influent and effluent from the pretreatment plant at the Stringfellow hazardous waste disposal site were sampled along with groundwater at six locations along the groundwater contaminant plume. The objectives of this sampling and study were to identify at the compound class level the unidentified 40-60% of wastewater organic contaminants, and to determine what organic compound classes were being removed by the wastewater pretreatment plant, and what organic compound classes persisted during subsurface waste migration. The unidentified organic wastes are primarily chlorinated aromatic sulfonic acids derived from wastes from DDT manufacture. Trace amounts of EDTA and NTA organic complexing agents were discovered along with carboxylate metabolites of the common alkylphenolpolyethoxylate plasticizers and nonionic surfactants. The wastewater pretreatment plant removed most of the aromatic chlorinated sulfonic acids that have hydrophobic neutral properties, but the p-chlorobenzene-sulfonic acid which is the primary waste constituent passed through the pretreatment plant and was discharged in the treated wastewaters transported to an industrial sewer. During migration in groundwater, p-chlorobenzenesulfonic acid is removed by natural remediation processes. Wastewater organic contaminants have decreased 3- to 45-fold in the groundwater from 1985 to 1999 as a result of site remediation and natural remediation processes. The chlorinated aromatic sulfonic acids with hydrophobic neutral properties persist and have migrated into groundwater that underlies the adjacent residential community.     

WAVE INDUCED FLOW AND TRANSPORT IN SEDIMENT BEDS1

ABSTRACT: The fate of contaminants in large water bodies is highly influenced by the transfer of flow and solutes across the water sediment interface. In this paper, an analytical model is presented where flow in both sediment bed and open channel is coupled at the interface through a boundary layer occupying the upper part of the sediment bed. The presence of this layer allows not only the capture of the inertia effects through a drag term in the generalized Darcy's equation, but also the specification of different soil parameters for the two porous zones. The flow is advective and driven by wave action along the water surface. The resulting system is solved for the pressure and flux in each sediment layer. The generated transport velocity fields are linked to a random walk simulation that is used to examine the trajectories of solute particles. Comparison of these trajectories against experimental tracer tests suggests a pattern very similar to the one attributed to the presence of surface mounds. The results clearly show the significance of the boundary layer and the drag term for soil with high permeability and the impact of both the thickness of the boundary layer and the length of the gravity wave relative to the depth of the water channel on the transport and exchange across the interface. The paper also examines the sensitivity of the mass exchange to the permeability of the two porous zones.     

Air quality assessment for land disposal of industrial wastes

Air pollution from hazardous waste landfills and lagoons is largely unknown. Routine monitoring of toxic air contaminants associated with hazardous waste facilities is difficult and very costly. The method presented in this paper would be useful for air quality assessment in the absence of monitoring data. It may be used as a screening process to examine the question of whether or not volatilization is considered to be significant for a given contaminant and also to evaluate permit applications for new hazardous waste facilities concerning waste volatilization problems.     

NUMERICAL AND ANALYTICAL SOLUTIONS OF DISPERSION IN A FINITE,ADSORBING POROUS MEDIUM1

ABSTRACT Numerical and analytical solutions are developed for the distribution of a contaminant within an adsorbing porous medium in a unidirectional flow field subject to a step function for input concentration. The medium is considered to be homogeneous, isotropic, and areally finite. As a by-product, solutions are also obtained for the case of a non-absorbing porous medium. An example that demonstrates the applicability of the solutions is presented.     

不同挺水植物在生活污水中生长量及去污能力比较研究

以千屈菜、香根草、芦苇、香蒲、美人蕉、水葱、风车草7种常见挺水植物为对象,研究了在生活污水中进行培养的植物生长量和氮磷积累量差异以及改善水质指标的能力差异。结果表明:芦苇和美人蕉的生长量显著高于其他植物,美人蕉的氮磷积累量最高,美人蕉和芦苇对污水的综合处理效果最好。     

阴离子表面活性剂SDS和SDBS对紫贻贝生化指标的影响研究

以青岛胶州湾现场调查数据为依据,选择阴离子表面活性剂十二烷基硫酸钠(SDS)和十二烷基苯磺酸钠(SDBS)作为污染物,以近海底栖生物紫贻贝为受试生物,研究了长期暴露后紫贻贝生化指标(SOD,CAT,GSH,GPx,GST,iNOS,AKP)的变化.结果表明,经过72 d不同浓度暴露后,SDBS实验组紫贻贝体内的SOD、CAT和iNOS活性均有显著下降（除CAT 0.1 mg/L组外）,GSH、GST和GPx在3.0　mg/L SDS和SDBS组较各自对照组均有显著升高.SDBS对紫贻贝生化指标影响的显著性水平大于SDS. 统计分析显示,SDBS暴露组下GST与GPx呈显著正相关关系,iNOS与SOD也表现出一定正相关,但GSH与CAT、GSH与SOD呈现显著负相关关系.此外,结果发现后闭壳肌中iNOS可能是一个具有应用前景的阴离子表面活性剂暴露生物标志物.     

单体同位素判识地下水MTBE衰减的研究进展

有机单体同位素分析(CSIA)技术能够测定有机化合物单体中特定元素的稳定同位素比值,是一种发展中的新的技术方法。依靠CSIA提供的数据可以确定污染物MTBE来源,判识生物降解的途径,量化降解的程度。更重要的是,通过同位素动力学分馏模型的建立,CSIA技术可以作为评价和预测污染物衰减的程度和衰减时间的强有力工具。文章主要综述了应用CSIA技术解析污染物MTBE衰减过程的应用进展。     

地下水污染风险评价中特征污染物量化方法探讨

针对地下水污染风险评价中的外界胁迫脆弱性评价缺乏有效量化体系这一问题,通过地下水污染源解析,提出了基于特征污染物及其对应排放量的量化体系;通过特征污染物属性解析及利用层次分析法确定研究侧重点,构建了该体系中的特征污染物量化方法.将该量化方法应用于北京市地下水污染风险评价,结果表明,依据不同研究侧重点得出的3种特征污染物危害性计算结果具有明显差异,并且3种危害性排序与对应的3种属性排序亦存在差异.由此表明,确定研究侧重点的主观倾向对特征污染物危害性计算结果有决定性影响.此外,在计算过程中,以序列值的方式解决3种属性的归一化及不同类别特征污染物属性量化结果的统一,会造成不同特征污染物之间相对属性特征的放大或缩小.     

基于QSAR关系预测PCBs和部分PAHs在LDPE中的扩散系数

分子扩散系数（D）是获得污染物与环境介质之间的平衡分配系数（K）的重要前提,然而通过实验测定获取污染物的扩散系数的过程过于繁琐,因此需开发一种更为简单、高效、准确的预测模型来定量预测扩散系数.为此,本文搜集了一些多环芳香烃（PAHs）和多氯联苯（PCBs）在低密度聚乙烯膜（LDPE）上扩散系数（log D）的实测值,基于定量结构-活性关系（QSAR）,利用逐步多元线性回归（MLR）构建了预测D值的模型.模型的决定系数R_adj²为0.941,交叉验证系数Q_LOO²为0.934,外部系数Q_ext²为0.895.结果表明,该QSAR模型具有良好的拟合优度、稳健性和预测能力,其可用来预测应用域内有机污染物在LDPE膜上的扩散系数.