北京市不同区域采暖期大气颗粒物中多环芳烃的分布特征

利用分级采样器分别采集北京市不同区域采暖期的大气颗粒物,分析多环芳烃的组成及含量.结果表明北京市大气总悬浮颗粒物中总多环芳烃的含量城乡结合带为7486—43687ng·m-3,郊区为11993—39786ng·m-3.在城乡结合带,80%以上的多环芳烃存在于粒径<20μm的颗粒物中;在郊区,77%以上的多环芳烃存在于粒径<20μm的颗粒物中.比较不同环数的多环芳烃在不同粒径范围内大气颗粒物中的分配比例,发现随环数的减少其分配比例呈现归一化.不同粒径范围的颗粒物中苯并(a)芘均与总多环芳烃含量显著相关(p<0001).     

东莞市夏季大气颗粒物中的多环芳烃及硝基多环芳烃

以东莞市2011年夏季不同区域的大气颗粒物为研究对象,定性定量分析了其中多环芳烃(PAHs)及硝基多环芳烃(NPAHs)的浓度、组成.采用特征比值法分析了PAHs及NPAHs的来源,并通过PEFs毒性评价法评价了颗粒物中多环芳烃及硝基多环芳烃的BaP等效毒性,估算出个体致癌指数.结果表明东莞市颗粒物上16种多环芳烃总含量在12.60—193.95 ng·m-3范围内,6种硝基多环芳烃的总含量在5.88—62.79 ng·m-3,隧道环境中多环芳烃及硝基多环芳烃的浓度最高.除隧道环境中颗粒物的等效毒性及个体致癌指数超标外,东莞市颗粒物上PAHs及NPAHs对人体均不构成严重威胁.     

使用安捷伦7000A三重串联四极杆GC/MS/MS系统测定大气颗粒物中的硝基多环芳烃

采用毛细管GC结合安捷伦7000A三重串联四极杆GC/MS(G7010AA)系统的多反应监测(MRM)模式分析了大气颗粒物中的硝基多环芳烃(nitro-PAHs).传统硝基多环芳烃的分析方法是在样品前处理之后,使用单四极杆GC/MS的选择离子监测SIM模式或者多维GC/MS,但基于MS/MS检测模式超强的选择性,可直接分析大气颗粒物的粗提物.实际样品中的硝基多环芳烃可以检测到pg·μL-1的级别,相对应于大气样品中pg·m-3级的含量.     

北京市冬季大气气溶胶中PAHs的污染特征

利用大流量颗粒物采样器采集了2005-2006年冬季北京市大气气溶胶中PM10和PM2.5样品,采用气相色谱/质谱技术对样品中的多环芳烃进行检测.结果表明:北京市冬季大气颗粒物PM10和PM2.5中PAHs总量分别为520.5±476.9ng·m-3和326.8±294.3ng·m-3,且大部分存在于细粒子中,4环以上的稠环芳烃占总浓度的87%.根据荧蒽/芘等比值指标判别,北京市冬季PAHs主要以燃煤排放为主,其次是石油燃烧交通排放.风速增大和太阳辐射曝辐量增强,都会降低颗粒物中多环芳烃浓度.     

北京中关村地区大气多环芳烃的污染

1981年至1982年在北京中关村等处八个采样点逐月采集大气颗粒物,用高效液体色谱法分析了十二种多环芳烃化合物,并对这些地区燃煤设施、能源消耗情况作了调查。结果表明,空气中多环芳烃含量在地区、季节上差别明显。本文讨论了上述差异的原因及多环芳烃的防治途径。     

上海市某工业区大气颗粒物(PM10)中多环芳烃的来源和分布特征

利用大气采样器采集上海市某工业区焦化厂,电厂和氯碱厂的大气颗粒物(PM10),结果显示,工业区中低环化合物占优势;焦化厂、电厂和氯碱厂含量最高的化合物分别是萘、苊和菲;煤炭燃烧是该工业区焦化厂和电厂多环芳烃的主要来源,氯碱厂多环芳烃可能主要是来自于其上风向的焦化厂,二者可能有弱的相关性;苯并(a)芘含量处于中等污染水平.     

薪柴燃烧源和燃煤源中多环芳烃的成分谱研究

采集了薪柴燃烧源、燃煤源产生的PM10颗粒物样品,采用超声萃取、硅胶-氧化铝柱层析分离、气相色谱/质谱联用技术,对美国环保总局推荐的优控多环芳烃进行了定量分析。薪柴源、燃煤源产生的多环芳烃单体质量浓度分别在0.81～199.52、9.86～591.95ng/m3之间;对结果进行归一化处理,从而确定了薪柴源、燃煤源产生的多环芳烃成分谱。对比两种污染源发现,薪柴源产生的多环芳烃以荧蒽和芘为主,燃煤源以荧蒽、苯并苝的含量最高。薪柴源产生的多环芳烃中,4环芳烃含量非常高,归一化含量达到60%,其他环数芳烃的含量很低;燃煤源中,3、4环芳烃含量较高,5、6环芳烃次之,它们之间的差别不如薪柴源各环芳烃之间的差别大。     

大气中多环芳烃(PAHs)在松针和SPMD上的分布

通过松针监测与半渗透膜被动式采样技术 (SPMD ) ,分析了我国珠江三角洲地区大气中多环芳烃的含量特征、来源及其分布 ,同时对这两种被动式采样技术进行了比较 松针及SPMD主要富集气态多环芳烃 (2— 4环 ) ,气态多环芳烃在松针和SPMD样品中的总含量分别为 313 9— 30 4 3 5ng·g-1和 14 5—116 9ng·SPMD-1·d-1 大气中多环芳烃含量的区域差异明显 ,珠江三角洲中部地区 (广州、佛山和东莞 )大气中多环芳烃的含量高 ,沿海地区的珠海、香港偏低 ,分子标志物指数表明 ,珠江三角洲大气中的多环芳烃主要是热成因 (燃烧 )来源 松针和SPMD对气态多环芳烃的监测具有很好的一致性 ,是进行区域大气污染评价的良好生物指示物     

室内空气中多环芳烃污染的测量和特征性研究

本文就室内空气中多环芳烃典型污染源－室内燃煤和室内吸烟排放的多环芳烃组成和含量进行了测定，并同室外大气（对照）中多环芳烃组成含量进行了对比，研究了室内环境不同污染源排放多环烃组成和含量的特征性，结果表明，室内燃煤污染同燃煤型室外大气源排放多环芳烃具有相似组成含量特征，而室朵烟草烟雾污染源的多环芳烃组成含量特征，则与室外煤型和交通型均有显著区别。     

城市室内环境多环芳烃污染与源的相关性

本实验选择了天津市４类典型室内环境和２处室外对照点，共１９个采样点。现场采样测定了１０种ＰＡＨｓ组成含量。结果显示，室内燃煤和室内吸烟是室内环境中多环芳烃排放的主要污染源。同作为对照的室外大气中多环芳烃组成和含量进行了对比，研究了室内环境不同污染源排放多环芳烃组成和含量的特征性。提出了室内燃煤污染同燃煤型室外大气源排放多环芳烃具有相似组成含量特征，而室内烟草烟雾污染源的多环芳烃组成含量特征则与室外     

煤飞灰环境标准参考物中PAHs的表征

本文采用不同提取方法以及不同溶剂对煤飞灰环境标准参考物质样品中PAHs的提取效率进行了考察.采用HPLC,毛细管GC以及GC-MS对飞灰样品中的PAHs进行了分析表征,并对前两种分析方法的精密度、准确性和所得结果的一致性进行了研究.     

徐州市区大气颗粒物中多环芳烃的污染特征

采用高效液相色谱技术（HPLC）对徐州市大气颗粒物中优控的16种多环芳烃（PAHs）进行定量研究。结果表明：萘、芴、苊等低分子量芳烃的含量相对较低;苯并（g,h,i）苝、茚并（1,2,3-cd）芘、苯并（k）荧蒽、苯并（a）芘等高分子量芳烃的含量相对较高;含量最高的单体为荧蒽,占待检的16种PAHs的19%以上。不同环数多环芳烃含量大小顺序为：4环〉5环〉6环〉3环〉2环。可吸入颗粒物（PM10）中苯并（a）芘和∑PAHs在不同功能区的分布特征大体上一致,并呈现一定规律性：交通干线区〉工业区〉风景文化区〉居民区〉新城区。由此可以初步认为徐州市区PM10中的PAHs主要来源于燃煤和汽车尾气。     

Trace elemental characterization of fly ash

The purpose of this study was to determine heavy metal concentrations in ash samples taken from the filter of the gas cleaning system of biomass incinerators in Austria. Knowing the concentrations of heavy metals is important for the decision of further treatment or utilization of the ashes. The heavy metals contained in the ashes remain in the bottom ash of the incinerator or leave the incinerator with the off-gas and are collected in the off-gas filter. The amount of the metals in the collected fly ash depends on the composition of the input material. The aim of this study was to examine this influence and compare the results with literature data. For measurement, the fly ash samples were at first dissolved in a microwave digestion unit using nitric acid and hydrochloric acid. Afterwards, 20 metals were analyzed by inductively coupled plasma optical emission spectrometry. Al, Fe, Mg, Mn, and Zn were found in higher concentrations in the fly ash samples. The enrichment factor between the concentrations in the fly ash and the concentrations in the input material was on average in the range of 18.     

Utilization of MSWI fly ash as partial cement or sand substitute with focus on cementing efficiency and health risk assessment

• Washed MSWI fly ash was used as partial cement or sand substitute. • Sand replacing is beneficial for strength, while cement replacement reduces strength. • Cementing efficiency factor and mortar pore structure explain the strength results. • Health risk assessment was conducted for MSWI fly ash blended cement mortar. • CR and HI contributed by different exposures and heavy metals were analyzed. The strength of cement substituted mortar decreases with the increase in fly ash amount, whereas the strength increases when the fly ash is blended as sand substitute. A mortar with highest strength (compressive strength= 30.2 Mpa; flexural strength= 7.0 Mpa) was obtained when the sand replacement ratio was 0.75%. The k value (cementing efficiency) of fly ash varied between 0.36 and 0.15 for the fly ash fraction in binder between 5% and 25%. The k values of fly ash used for sand replacement were all significantly above that used for cement substitution. The macropores assigned to the gaps between particles decreased when the fly ash was used as sand replacement, providing an explanation for the strength enhancement. The waste-extraction procedure (toxicity-sulphuric acid and nitric acid method (HJ/T 299-2007)) was used to evaluate metal leaching, indicating the reuse possibility of fly ash blended mortar. For the mortar with the mass ratio of fly ash to binder of 0.5%, the carcinogenic risks (CR) and non-carcinogenic hazard quotient (HQ) in sensitive scenario for blended mortar utilization were 9.66 × 10^-7 and 0.06, respectively; these results were both lower than the threshold values, showing an acceptable health risk. The CR (9.89 × 10^-5) and HQ (3.89) of the non-sensitive scenario for fly ash treatment exceeded the acceptable threshold values, indicating health risks to onsite workers. The main contributor to the carcinogenic and non-carcinogenic risk is Cr and Cd, respectively. The CR and HQ from inhalation was the main route of heavy metal exposure.     

电厂煤飞灰单个颗粒的化学表征

用扫描电镜Ｘ射线能谱对电厂煤飞灰单个颗粒进行了形貌，粒度和化学组成的观察与分析，用Ｘ射线衍射鉴定了煤飞灰粗细颗粒中元素存在的化学形态（化合物或物相）结果表明，煤飞灰中有较多球形颗粒，还有一些不规则形颗粒，主要含有Ｓｉ，Ａｌ，Ｃａ，Ｆｅ，Ｓ，Ｋ等，不同形貌，大小颗粒中的组分含量差别较大，但大多以硅铝酸盐为基体，其它元素分布在颗粒表层（约１μｍ）中，粗细颗粒中均有石英和氧化铁，但粗粒中还富含Ｃａ和Ｆｅ     

煤矿塌陷区造田复土中粉煤灰含量对高羊茅生理功能的影响

以小区试验进行了粉煤灰复土造田种植高羊茅的试验 .对高羊茅生长发育、生理功能和矿质积累的研究结果表明 :含 30 %以下粉煤灰复合土能提高高羊茅植株光合作用和氮素利用能力 ,促进植株生长 ,不会对植株产生伤害 ;当复合土中粉煤灰含量达 4 0 %时 ,高羊茅光合作用、蒸腾作用和氮素利用能力降低 ,细胞膜脂质过氧化水平升高 ,膜透性增大 ,SOD、POD和CAT活性降低 ,植株生长被抑制 ;随着复合土中粉煤灰含量的升高高羊茅植株Mn、Zn、Ca、Mg的质量分数升高 ,Cu的质量分数无显著变化 .研究建议粉煤灰复土造田以 30 %粉煤灰复合土为宜 .图 3表 6参 19     

粉煤灰对土壤和作物生长的影响

粉煤灰施用量控制在60～600t／hm2,不会造成土壤、粮食的污染,且能改善土壤的物理、化学和生物学性质．有利于养分的转化。粉煤厂磁化后15～7．5t／hm2的施用量即可达到最佳的改上增产效果。本文在分析粉煤灰埋化性质的基础上,讨论了粉煤灰对土壤和作物生长的影响,同时也提出了降低粉煤灰中有害物质对土壤和作物不利影响的农用技术。     

Levels and patterns of polychlorinated biphenyls in residues from incineration of established source-classified MSW in China

Municipal solid waste (MSW) source-classified collection represents an advancement in resource cycling and secondary pollution control in China. Comparative experiments were performed to assess the levels and patterns of polychlorinated biphenyls in bottom ash, fly ash from boiler, and fly ash from bag filter from an MSW incineration plant with source-classified collection of MSW. Polychlorinated biphenyls were concentrated in the bag filter fly ash and in the bottom ash. The total amount of polychlorinated biphenyls was much lower than in fly ashes and bottom ash from traditional mixed waste incineration. Total concentration of coplanar polychlorinated biphenyls and toxic equivalent quantities were also reduced. Due to variations of feed waste, complete combustion, including continuously high incineration temperature, low CO concentrations and high air excess ratio were observed. Incineration temperature showed a negative correlation, while CO concentration showed a positive correlation with total and coplanar polychlorinated biphenyls, indicating that the latter can be reduced by controlling combustion conditions related to properties of feed waste.     

分子电性距离矢量用于多氯代二苯并呋喃光解半衰期的QSPR研究（Molecular Electronegativity Distance Vector（MEDV）Applied to Quantitative Structure-Property Relationship Study on Photolysis Half-Lives of PCDFs）

多氯代二苯并呋喃(PCDFs)是一种典型的持久性有机污染物(POPs),光解是其在环境中转化的主要途径.以分子电性距离矢量(Molecular Electronegativity Distance Vector,MEDV)为参数,应用多元线性回归(Multiple Linear Regression,MLR)和偏最小二乘回归(PLSR)对48种PCDFs在云杉针叶和飞灰表面的光解半衰期(t1/2)进行模拟分析,均获得由2个变量所建的定量结构-性质相关(QSPR)模型.多元线性回归结果:建模相关系数(R)分别为0.860和0.836,标准偏差(SD)分别为0.052和0.053,交互检验复相关系数(Rcv)分别为0.839和0.807,外部检验相关系数(Qex)t分别为0.939和0.853;偏最小二乘回归结果:建模相关系数(R)分别为0.857和0.829,交互检验复相关系数(Rcv)分别为0.849和0.807.结果表明,MEDV能较好地表征该类分子的结构信息,所建QSPR模型具有良好的稳定性和预测能力.     

Effects of fly ash, Pseudomonas striata and Rhizobium on the reproduction of nematode Meloidogyne incognita and on the growth and transpiration of pea

Glasshouse experiments were conducted twice to assess the ash amendments (0, 20, and 40% with soil), a phosphate solubilizing microorganism Pseudomonas striata and a root-nodule bacterium Rhizobium sp on the reproduction of root-knot nematode Meloidogyne incognita and on the growth and transpiration of pea. Amendments of fly ash with soil had no effect on transpiration. However, M. incognita reduced the rate of transpiration from 1st week onward after inoculation while inoculation of Rhizobium sp and P. striata increased transpiration from 1st week onward after their inoculation both in nematode inoculated and uninoculated plants. Increase in transpiration was greater when both organisms were inoculated together. Addition of 20 and 40% fly ash with soil was beneficial for plant growth both in nematode inoculated and uninoculated plants. Inoculation of above organisms also increases plant growth of nematode inoculated and uninoculated plants in different fly ash soil mixture but increase in growth was greater when both organisms were inoculated together. Use of 20% fly ash increased galling and nematode multiplication over plants grown in without fly ash while 40% fly ash had adverse effect on galling and nematode multiplication. Rhizobium sp had greater adverse effect on galling and nematode multiplication than P. striata. Use of both organisms together had greater adverse effect on galling and nematode multiplication than caused by either of them alone. Highest reduction in galling and nematode multiplication was observed when both organisms were used in 40% fly ash amended soil. However, highest transpiration was observed in plants without nematodes and inoculated with both organisms together both in with or without fly ash amended soil.