Variation of MCPA, metribuzine, methyltriazine-amine and glyphosate degradation, sorption, mineralization and leaching in different soil horizons

Pesticide mineralization and sorption were determined in 75 soil samples from 15 individually drilled holes through the vadose zone along a 28 km long transect of the Danish outwash plain. Mineralization of the phenoxyacetic acid herbicide MCPA was high both in topsoils and in most subsoils, while metribuzine and methyltriazine-amine was always low. Organic matter and soil pH was shown to be responsible for sorption of MCPA and metribuzine in the topsoils. The sorption of methyltriazine-amine in topsoil was positively correlated with clay and negatively correlated with the pH of the soil. Sorption of glyphosate was tested also high in the subsoils. One-dimensional MACRO modeling of the concentration of MCPA, metribuzine and methyltriazine-amine at 2 m depth calculated that the average concentration of MCPA and methyltriazine-amine in the groundwater was below the administrative limit of 0.1 μg/l in all tested profiles while metribuzine always exceeded the 0.1 μg/l threshold value.     

Seasonal and spatial occurrence and distribution of atmospheric polycyclic aromatic hydrocarbons (PAHs) in rural and urban areas of the North Chinese Plain

Passive air sampling (PAS) was employed to study the occurrence of gaseous and particle-bound PAHs in the North Chinese Plain. The averaged concentrations of gaseous and particle-bound PAHs were 485 ± 209 ng/m³ and 267 ± 161 ng/m³, respectively. The PAHs concentrations at urban sites were generally higher than those at rural ones with ratios <1.5 in spring, summer and fall, but differences between them were not significant for the wintertime and annually averaged concentrations. This urban-rural distribution pattern was related to the PAHs emission sources. PAHs spatial variation can be partially (49%) explained by emission with a simple linear regression method. Both the gaseous and particle-bound PAHs were highest in winter and lowest in summer, with winter/summer ratios of 1.8 and 8, respectively. Emission strength was the most important factor for the seasonality.     

基于物种敏感度分布的不同岩溶地下河中多环芳烃分布特征及生态风险评价

为明确重庆青木关和老龙洞地下河流域地下水中多环芳烃(PAHs)的含量及其污染水平,全年共采集两流域地下河水样品84个,利用气相色谱质谱联用系统(GC-MS)分别测定了地下水中的16种PAHs含量,分析了PAHs在两条地下河流域中的空间分布特征,并应用物种敏感度分布法(species sensitivity distri...     

东北地区城市大气颗粒物中多环芳烃的污染特征

2008年4月至2009年1月期间,在东北三省(辽宁、吉林、黑龙江)设立30个观测点位,研究了东北城市大气颗粒物中PAHs的浓度水平、分布及来源.结果表明,不同季节14种PAHs总浓度的变化范围是16.3 ～712.1 ng/m3,呈冬季高、夏季低的季节变化特征;PAHs组成以4～5环化合物为主,3～4环化合物受温度的影响较大,表现出较强的季节波动;8个城市中抚顺和吉林PAHs污染最重,城市不同功能区中以工业区污染较重;燃煤和机动车尾气是区域PAHs的主要来源.     

低浓度石油类测定过程中的问题探讨

分析了影响低浓度石油类测定的一些因素,通过合理的方法克服这些影响因素之后,测定结果才能准确可靠。试验测得1000ml水样直接萃取法测定石油类的方法检出限为0.01mg/L,证明用该方法可以定量测定石油类浓度在0.05mg/L附近的低浓度水样。     

气相色谱-质谱法测定废酸油渣中的16种多环芳烃

建立了废酸油渣中16种多环芳烃超声萃取、Florisil萃取柱净化、气相色谱-质谱测定的方法.笔者对提取方式、提取剂类型和体积、提取时间和次数、净化方式等进行研究,采用无水硫酸钠分散,二氯甲烷作为提取剂超声40 min,提取液经纯水清洗、离心后取适量有机相经过3 g Florisil萃取柱净化,采用气相色谱-质谱选择离...     

不同下垫面类型对地表径流中多环芳烃污染特征的影响分析

为了解下垫面对径流中多环芳烃(PAHs)污染特征的影响,对4次降雨事件中不同下垫面地表径流中的PAHs污染特征进行了分析.研究发现,屋面(A点)与交通路面(C点)的PAHs污染负荷远远大于另两种下垫面,降雨事件平均浓度分别达到26.66μg·L-1和27.87μg·L-1.各场降雨事件都存在随着降雨历时污染物浓度逐渐降低的过程,其中交通路面变化最为剧烈,PAHs浓度由初始的33.50μg·L-1经90 min后下降至16.36μg·L-1,而屋面则在径流结束前伴有浓度回升的现象.径流中溶解态PAHs含量远低于颗粒态含量,以2—3环略占优势,达31%—42%;而在颗粒态PAHs中5—6环则相对更多.广场路面(B点)和交通路面(C点)由于汇流面积较大,具有较明显的初期冲刷效应;屋面(A点)的冲刷效应相对较弱;草地(D点)则未表现出初期冲刷效应.研究结果表明下垫面对径流中PAHs的含量和消除均有一定影响,但与PAHs组分的相对比例无明显相关.     

广州大坦沙污水处理厂挥发有机物的去除及其向空气中的排放

对广州大坦沙污水处理厂各工艺阶段污水中挥发性有机物(VOCs)的测试表明,进水中主要有害VOCs为苯系物和卤代烃;进水和出水比较,苯 甲苯、乙苯、二甲苯(合称BTEX) 的去除率接近100%,污水中几种主要卤代烃的去除效率范围为79%—89%.VOCs主要的去除作用发生在生物反应池,特别是厌氧阶段,本研究还对污水处理厂几种典型挥发有机物排放到周围空气中的量进行了理论估计,计算表明卤代烃进入空气中的比例高于BTEX.     

Monitoring of environmental exposure to polycyclic aromatic hydrocarbons: a review

Polycyclic aromatic hydrocarbons (PAHs) are a large group of organic compounds with two or more fused aromatic rings. They have a relatively low solubility in water, but are highly lipophilic. Most of the PAHs with low vapour pressure in the air are adsorbed on particles. When dissolved in water or adsorbed on particulate matter, PAHs can undergo photodecomposition when exposed to ultraviolet light from solar radiation. In the atmosphere, PAHs can react with pollutants such as ozone, nitrogen oxides and sulfur dioxide, yielding diones, nitro- and dinitro-PAHs, and sulfonic acids, respectively. PAHs may also be degraded by some microorganisms in the soil. PAHs are widespread environmental contaminants resulting from incomplete combustion of organic materials. The occurrence is largely a result of anthropogenic emissions such as fossil fuel-burning, motor vehicle, waste incinerator, oil refining, coke and asphalt production, and aluminum production, etc. PAHs have received increased attention in recent years in air pollution studies because some of these compounds are highly carcinogenic or mutagenic. Eight PAHs (Car-PAHs) typically considered as possible carcinogens are: benzo(a)anthracene, chrysene, benzo(b)fluoranthene, benzo(k)fluoranthene, benzo(a)pyrene (B(a)P), dibenzo(a,h)anthracene, indeno(1,2,3-cd)pyrene and benzo(g,h,i)perylene. In particular, benzo(a)pyrene has been identified as being highly carcinogenic. The US Environmental Protection Agency (EPA) has promulgated 16 unsubstituted PAHs (EPA-PAH) as priority pollutants. Thus, exposure assessments of PAHs in the developing world are important. The scope of this review will be to give an overview of PAH concentrations in various environmental samples and to discuss the advantages and limitations of applying these parameters in the assessment of environmental risks in ecosystems and human health. As it well known, there is an increasing trend to use the behavior of pollutants (i.e. bioaccumulation) as well as pollution-induced biological and biochemical effects on human organisms to evaluate or predict the impact of chemicals on ecosystems. Emphasis in this review will, therefore, be placed on the use of bioaccumulation and biomarker responses in air, soil, water and food, as monitoring tools for the assessment of the risks and hazards of PAH concentrations for the ecosystem, as well as on its limitations.     

长江重庆段表层水体中多环芳烃的分布及来源分析

采集了长江重庆段干流以及重要支流共7个断面的表层水样,采用液相色谱法分析15种优先控制的多环芳烃(PAHs).结果表明,水体中总PAHs浓度范围为6.44—109.39 ng·L-1,平均值为41.83 ng·L-1.在5个断面水体中检出苯并(a)芘,浓度为0.05—1.32 ng·L-1,低于我国地表水标准限值(2.8 ng·L-1).长江重庆段的PAHs浓度水平低于大部分国内其他河流,与国外一些河流的浓度水平相当.PAHs组成以中低环PAHs(3环和4环)为主,平均比例分别为55.7%和38.8%,高环PAHs(5环和6环)含量较低,分别占3.6%和1.9%.示踪PAHs比值法结果显示长江重庆段表层水体PAHs主要来源于石化产品的泄漏污染.