沈阳市工业污染源指标化控制的研究

本文在研究沈阳市工业污染源构成基础上，根据沈阳市水系统主要污染物总量控制目标，提出了主要污染源主要污染物指标化控制目标．通过污水治理技术经济分析，探讨实现工业污染源环境目标管理的途径．     

七台河市大气污染特征及变化浅析

通过对七台河市2006年1月起空气连续监测系统正式运行以来的监测数据分析,归纳、总结七台河市大气污染物随季节变化规律,每日、小时变化规律及市区不同地区大气污染物分布特征,并对这种特征及变化规律进行分析.     

铁氧体化法在重金属污染物解毒处理中的应用

综合介绍铁氧体化法在重金属污染物解毒处理方面的应用研究情况，提出毒害性污染物解毒处理的概念，并进一步指出开发降解性毒害污染物解毒处理工艺中值得注意的问题。     

典型室内空气污染现状研究

研究典型室内空气污染现状及其对人体健康的影响,探讨影响典型室内空气质量的主要因素及其室内外主要污染物的相关性,并提出一些改进措施,为深入分析典型室内外污染物相关性及其净化技术方法打下基础.     

水环境有机污染物预测的径向基函数网络模型

水环境中有机污染物的扩散迁移是一个由多种因素影响的复杂的非线性过程，根据河流有机污染物的浓度与其影响因素之间存在的映射关系，以实际监测数据为基础，建立了一个水环境有机污染物浓度预测的径向基函数网络模型，实例验证表明，该方法预测精度较高，具有一定的应用与推广价值。     

黄孢原毛平革菌在多种氨氮浓度下木质素降解酶的产生

在氨氮浓度0．0308-0．924g／L，下对黄孢原毛平革菌(Phanerochaete chrysosporium)在空气环境中进行自由悬浮振荡培养，在氨氮浓度0．0308-0．308g／L下可检测到木质素过氧化物酶活性，最高酶活为42．8U/L；在氨氮浓度0．0308g／L和0．154g/L下可检测到漆酶活性，最高酶活为35．0U／L，在氨氮浓度不低于0．154g/L时，葡萄糖消耗速率大致相当，明显高于在氨氮浓度0．0308g／L下的葡萄糖消耗速率；氨氮在葡萄糖耗尽时达到最低值，然后开始增大；木质素过氧化物酶和漆酶的活性峰与葡萄糖和氨氮的最大消耗基本对应。实验结果对木质素降解酶发酵和白腐真菌在环境工程中的直接应用具有启发意义。     

机动车排放检测运行体系的相关研究

机动车污染物排放标准与其检测方法是相辅相成的，不同的机动车检测方法对应不同的机动车排放污染物限值。该文主要对机动车排放检测运行体系中的怠速和简易工况检测方法进行了对比性研究，并对机动车实施常规检测的年检和监督手段的路检进行了对比分析，从而得出：工况法检测对于尾气排放情况的模拟要优于怠速法检测，并可对NOx进行有效控制，所以建议在有条件的地区，应该尽量实施工况法检测：年检和路检的数据有较大的差异，反映出对在用车的监督不力，今后应加强；高排放车辆的贡献率所占的比例与发达国家相比太小，说明机动车总体控制水平较低。     

Sorption kinetics of parent and substituted PAHs for low-density polyethylene (LDPE): Determining their partition coefficients between LDPE and water (KLDPE) for passive sampling

Low-density polyethylene (LDPE) has been widely used as a sorbent for passive sampling of hydrophobic organic contaminants (HOCs) in aquatic environments. However, it has seen only limited application in passive sampling for measurement of freely dissolved concentrations of parent and substituted PAHs (SPAHs), which are known to be toxic, mutagenic and carcinogenic. Here, the 16 priority PAHs and some typical PAHs were selected as target compounds and were simultaneously determined by gas chromatography–mass spectrometer (GC–MS). Some batch experiments were conducted in the laboratory to explore the adsorption kinetics of the target compounds in LDPE membranes. The results showed that both PAHs and SPAHs could reach equilibrium status within 19–38?days in sorption kinetic experiments. The coefficients of partitioning between LDPE film (50?μm thickness) and water (K_LDPE) for the 16 priority PAHs were in good agreement with previously reported values, and the values of K_LDPE for the 9 SPAHs are reported in this study for the first time. Significant linear relationships were observed, i.e., log K_LDPE?=?0.705?×?log K_OW?+?1.534 for PAHs (R²?=?0.8361, p?<?0.001) and log K_LDPE?=?0.458?×?log K_OW?+?3.092 for SPAHs (R²?=?0.5609, p?=?0.0077). The selected LDPE film was also proven to meet the condition of “zero sink” for the selected target compounds. These results could provide basic support for the configuration and in situ application of passive samplers.     

贵阳市秋冬季PM2.5中重金属污染特征、来源解析及健康风险评估

为掌握贵阳市大气PM_2.5中重金属的污染特征、潜在来源和健康危害,于2017年10月—2018年2月白天(08:00—19:00)、夜间(20:00—翌日07:00)连续采集秋、冬两季大气颗粒物PM_2.5样品(n=202),采用电感耦合等离子体质谱(ICP-MS)法,检测样品中10种重金属(Pb、Cd、Cr、As、Zn、Mn、Co、Ni、Cu和V)含量,分析其昼夜质量浓度特征及变化规律,运用PMF(正定矩阵因子分析)模型和HMHR(健康风险评价模型)分别探讨其来源及健康风险.结果表明:①秋、冬两季大气颗粒物ρ(PM_2.5)日均值分别为(53±18)(62±20)μg/m3,均低于GB 3095—2012《环境空气质量标准》二级标准(75 μg/m3);ρ(As)、ρ(Zn)和ρ(Mn)均呈冬季高于秋季的特征,其他元素变化不明显.②白天ρ(PM_2.5)为(61±20)μg/m3,稍高于夜间〔(58±24)μg/m3〕;ρ(Pb)白天低于夜间,ρ(Ni)、ρ(Mn)、ρ(Zn)和ρ(Cu)则白天高于夜间,其他元素昼夜质量浓度无明显差异.③PMF模型分析表明,交通污染、燃煤、工业冶金和土壤扬尘是采样期间10种重金属的主要来源,其贡献率分别为39%、37%、14%、10%.④HMHR结果表明,Cd和Mn对儿童存在非致癌风险,其他重金属元素对人群无非致癌风险.致癌元素As、Cr和Cd的致癌风险值介于4.3×10-6~4.4×10-5之间,对人群可能存在致癌风险;而Ni和Co的致癌风险值均低于可接受水平(10-6).研究显示,贵阳市秋、冬两季PM_2.5中重金属污染水平整体较低,交通污染和煤炭燃烧是其主要来源,重金属元素中Cd、Mn、As和Cr对人群存在一定的健康风险.      

Regulating oil and gas facility stormwater discharge: An assessment of surface impoundments,spills, and permit compliance

Contaminated stormwater runoff from oil and gas (O&G) operations can pose a significant threat to surface waters. The purpose of this study is to examine the extent of this threat and identify more specific permitting requirements to protect surface waters. To better understand the extent of the threat, this paper identified and characterized the use of waste surface impoundments at O&G facilities as well as the threat level from O&G spills in California. To assess the efficacy of the current federal and California state-permitting regime, the paper evaluated stormwater permit compliance in two California counties. It also reviewed selected spill cases and associated Spill Prevention, Control and Countermeasure Plans and Stormwater Pollution Prevention Plans to identify the adequacy of current industry practices.The analysis showed that contaminated stormwater from O&G facilities can be better regulated. The U.S. Environmental Protection Agency does not require O&G facilities to file for an Industrial Stormwater General Permit even though many O&G industry practices have the potential to contaminate stormwater runoff from the site. When O&G facilities discharge a Reportable Quantity of a hazardous chemical or violate a water quality standard, they are required to enroll in the National Pollutant Discharge Elimination System permit program. Spills, although not a direct indication of stormwater runoff, can highlight polluted runoff discharges that should have been regulated. Medium and large spills that reached waterways were such a risk for which operators did not file for a permit. In California new filing requirements for the oil and gas industry require all facilities that discharge stormwater that has come into contact with any overburden, raw material, or intermediate products located on the site, to file for an Industrial Stormwater General Permit. As this study showed, there has been an increase in enrollment since the enactment of the new requirements. Having all facilities enroll in the general permit program, as done in California, would require minimum monitoring and maintenance that could help prevent spills. A further step to ensure better protocol is to require specific pollution control practices in addition to the current general permit requirements. Such permitting regimes not only can be implemented on the US federal level but also internationally.