十二烷基苯磺酸钠(SDBS)及消油剂对刺参幼参的急性毒性

为探究表面活性剂对海洋棘皮动物的影响,测定了十二烷基苯磺酸钠(SDBS)和消油剂对刺参(Stichopus japonicas )幼参的急性毒性。结果显示,SDBS对刺参幼参的72 h-LC₅₀和96 h-LC₅₀分别为2.50和1.71 mg·L^-1;消油剂对刺参幼参的96 h-LC₅₀为7 498.94 mg·L^-1。刺参幼参相对于多刺裸腹溞(Moina macrocopa )和脊尾白虾仔虾(Palaemon carincauda )对SDBS的敏感性较高,相对于安氏伪镖水蚤(Pseudodiaptomus annandalei )对SDBS的敏感性则较低,SDBS对刺参幼参的毒性明显大于十二烷基磺酸钠(SDS),消油剂的96 h-LC₅₀ 远远大于SDBS和SDS,毒性非常小,但这仅是对刺参幼参而言,大多数研究忽视了消油剂自身对生物体存在的影响,因此这方面的研究工作还需要继续开展。     

微波辅助固相顶空-气相色谱法测定人造板材中的苯系物

采用微波辅助固相顶空-气相色谱法测定了人造板材中的苯系物含量,考察了不同微波功率作用下3种苯系物随时间的变化趋势,在优化的条件下测定了3种苯系物的含量.该法检出限为3.6—13.4 ng.g-1板材,RSD为2.7%—9.8%,回收率为86.9%—109.4%,方法简便、快速,适合固体板材中苯系物的直接快速分析.     

硫酸铵细粒子对苯二次有机气溶胶光学特性的影响

苯系物光氧化产生的二次有机气溶胶（SOA）能够散射、吸收大气辐射,扰动区域气候变化.硫酸铵（（NH₄）₂SO₄）是大气中常见的无机细粒子,其大的比表面积可作为半挥发性化合物凝结和反应中心,进而影响SOA的化学组分和光学特性.本文采用烟雾箱研究（NH₄）₂SO₄细粒子对苯SOA在200~600 nm范围内的平均质量吸收系数（mass absorption coefficient,MAC）的影响情况.实验结果表明,低浓度（小于100 μg·m^-3）（NH₄）₂SO₄细粒子仅作为凝结核心,不会影响苯SOA的光学性质.高浓度（大于100 μg·m^-3）（NH₄）₂SO₄细粒子对咪唑类吸光产物的形成有促进作用.苯SOA的MAC值随着（NH₄）₂SO₄细粒子浓度的增加而逐渐增大,却随着细粒子酸度的增大而逐渐减小.水分子的增加会产生更多的NH₄⁺,从而有利于咪唑类化合物的产生,苯SOA的MAC值则随着相对湿度的增加而逐渐增大.而当相对湿度高于70%时,乙二醛水合反应增强,四醇产物脱水、聚合形成的高分子量产物增多,从而导致MAC值减小.这为研究高浓度（NH₄）₂SO₄细粒子背景下,人为源SOA的光学特性提供了实验依据.     

苯急性暴露对Sprague-Dawley大鼠全基因组DNA甲基化的影响

现有文献表明,DNA甲基化异常与肿瘤的发生密切相关,其中全基因组DNA甲基化水平的改变已经被认为是癌症发生的生物标志物;同时,大量遗传毒理学实验证明苯可以引起DNA突变和断裂,然而苯暴露引起全基因组DNA甲基化异常的现象,目前鲜有文献报道。为了揭示苯引起全基因组DNA甲基化变化的致毒机制,本实验中,Sprague-Dawley（SD）雄性大鼠经口灌胃急性暴露于以500 mg.kg-1（以体质量计）的苯中,在暴露6、12、24、30 h后采集SD雄性大鼠体内血液、肝脏、肾脏和肺,利用高效液相色谱分析方法检测全基因组DNA甲基化水平。结果表明,SD雄性大鼠血液和肝脏的全基因组DNA甲基化水平显著下降,而在肾脏和肺中没有显著地变化,表现出组织特异性。本实验率先报道了苯的暴露可以引起全基因组DNA甲基化水平的异常,从表观遗传学的角度解释了苯影响人体健康的机制。     

二次热解吸直接进样气相色谱法测定空气中苯系物

文章建立了空气中苯系物的分析方法,方法用Tenax TA吸附管吸附空气中苯系物,二次热解吸直接进毛细管气相色谱分析。该方法定性、定量准确,线性响应良好,回归方程的线性相关系数大于0．9991,相对标准偏差在2．1％～5．3％之间,加标回收率大于92％,具有良好的重现性。测定干扰小,检测灵敏度高,当采样体积1L时,平均解吸率在95％以上,苯系物的最低检出浓度可达0．5ug／m^3。本方法适合测定空气中低浓度的苯系物。     

SDS、SDBS胶团强化超滤Cu~(2+)的比较

采用模拟含Cu2+废水,以阴离子表面活性剂SDS和SDBS胶团强化超滤分离Cu2+(Cu2+固定为0.6 mmol/L),通过对渗透通量、渗透浓度、去除率、富集率的比较,从而得出SDS、SDBS分离效果的优劣.结果表明,添加SDS的渗透通量始终高于SDBS[其中SDS平均渗透通量为29.92 L.(m2.h)-1,而SDBS只有16.55 L.(m2.h)-1],渗透浓度始终低于SDBS,当渗透液Cu2+浓度接近为0时,SDBS、SDS所需浓度分别为2 mmol/L和6 mmol/L.SDS的Cu2+去除率和平均富集率高于SDBS(SDS平均去除率为85.06%,平均富集率为4.18;SDBS对应值分别为69.05%,4.05).此外,SDS自身的平均富集率也高于SDBS(SDS为3.89,SDBS为3.13).由此可见,SDS比SDBS更适合去除Cu2+.     

芳烃化合物水溶解度及分配系数的估算

将分子连接性指数法(Molecular Connectivity Index,MCI)与几何平均连接性指数法(Geometrical Mean Connectivity Index,GMCI)相结合,改进了GMCI的点价计算方法。使用新方法计算了34种芳烃化合物0～4阶指数的点价值,并分别通过对溶解度和点价值,分配系数和点价值进行逐步多元回归分析,建立了新的指数和溶解度、分配系数之间的定量关系模型,回归方程的相关系数为0.961、0.962,都达到了良好级,估计标准误差为0.3454、0.2674,优于MCI法和GMCI法。     

Commuter exposure to BTEX in public transportation modes in Bangkok, Thailand

Measurements and monitoring of volatile organic compounds (VOCs) have been conducted in the metropolitan Bangkok. However, in-vehicle levels of VOCs are still lacking. This study investigated VOCs concentrations in four public transportation modes in Bangkok, Thailand during two rush hour periods (7:00-9:00 a.m. and 4:00-7:00 p.m.). The four modes included an air-conditioned bus (A/C bus), non-air-conditioned bus (non-A/C bus), electric sky train, and a passenger boat traveling along the canal. Comparison among three important bus routes was also studied. In-vehicle air samples were collected using charcoal sorbent tubes and then analyzed by a gas chromatography-mass spectrometer. Results showed that the transportation modes significantly influenced the abundance of in-vehicle benzene, toluene, ethylbenzene, and m,p-xylene (BTEX). Median concentrations of BTEX were 11.7, 103, 11.7, and 42.8 μg/m3 in A/C bus; 37.1, 174, 14.7, and 55.4 μg/m3 in non-A/C bus; 2.0, 36.9, 0.5, and 0.5 μg/m3 in sky train; and 3.1, 58.5, 0.5, and 6.2 μg/m3 in boat, respectively. Wilcoxon rank sum test indicated that toluene and m,p-xylene in the sky trains were statistically lower than that in the other three modes at a p-value of 0.05. There were statistical differences in TEX concentrations among the bus routes in the non-A/C buses. In addition, the benzene to toluene ratios implied that tail-pipe emissions were important contributor to the abundance of in-vehicle VOCs.     

Bio-removal of mixture of benzene, toluene, ethylbenzene, and xylenes/total petroleum hydrocarbons/trichloroethylene from contaminated water

Four pure cultures were isolated from soil samples potentially contaminated with gasoline compounds either at a construction site near a gas station in Fai Chi Kei, Macau SAR or in the northern parts of China (Beijing, and Hebei and Shandong). The e ects of di erent concentrations of benzene, toluene, ethylbenzene, and three isomers (ortho-, meta-, and para-) of xylene (BTEX), total petroleum hydrocarbons (TPH), and trichloroethylene (TCE), when they were present in mixtures, on the bio-removal e ciencies of microbial isolates were investigated, together with their interactions during the bio-removal process. When the isolates were tested for the BTEX (50–350 mg/L)/TPH (2000 mg/L) mixture, BTEoX in BTEoX/TPH mixture was shown with higher bio-removal e ciencies, while BTEmX in BTEmX/TPH mixture was shown with the lowest, regardless of isolates. The TPH in BTEmX/TPH mixture, on the other hand, were generally shown with higher bio-removal e ciencies compared to when TPH mixed with BTEoX and BTEpX. When these BTEX mixtures (at 350 mg/L) were present with TCE (5–50 mg/L), the stimulatory e ect of TCE toward BTEoX bio-removal was observed for BTEoX/TCE mixture, while the inhibitory e ect of TCE toward BTEmX for BTEmX/TCE mixture. The bio-removal e ciency for TPH was shown lower in TPH (2000 mg/L)/TCE (5–50 mg/L) mixtures compared to TPH present alone, implying the inhibitory e ect of TCE toward TPH bio-removal. For the mixture of BTEX (417 mg/L), TPH (2000 mg/L) along with TCE (5– 50 mg/L), TCE was shown co-metabolically removed more e ciently at 15 mg/L, probably utilizing BTEX and/or TPH as primary substrates.     

不同下垫面苯系物的挥发行为研究

结合石油化工区挥发性污染物泄漏控制的需要,选取淄博地区代表性的砂土、壤土和水3种下垫面,对苯系物的挥发行为进行试验研究,得到了不同类型下垫面中苯系物单组分及其混合物的挥发动力学曲线、最优拟合公式和挥发动力学模型.结果表明,3种下垫面中,苯系物组分及混合物的挥发速率大小依次为:苯>甲苯>BTEX>二甲苯>乙基苯;而苯系物在静水面上的挥发最快,砂土中次之,壤土中挥发最慢.另外,3种下垫面中苯系物的挥发速率常(系)数与蒸气压的关系均呈线性正相关,挥发速率系数随着组分蒸气压的增大而明显增大.下垫面对苯系物挥发的影响机制主要表现为对挥发面积和介质在挥发扩散过程中可利用孔隙通量的影响.