气相色谱/负离子化学电离质谱法测定地表水中硫丹及其代谢物

采用气相色谱/负离子化学电离质谱法测定地表水中的硫丹及其代谢物,用正己烷提取,外标法定量。α-硫丹、β-硫丹及硫丹硫酸酯在0.200μg/L～10.0μg/L范围内线性良好,方法检出限分别为0.010μg/L、0.008μg/L及0.010μg/L,空白加标平行测定的RSD为3.9%～4.8%,地表水样品加标回收率为85.5%～93.8%。     

固相微萃取-气相色谱法测定水中酞酸酯类化合物

建立了固相微萃取(SPME)-气相色谱(GC)法分析环境水样中痕量酞酸酯类化合物(PAEs)的方法。选用65 μm PDMS/CVB萃取纤维,在磁力搅拌转速为700 r/min、萃取温度为60℃条件下,对水样中的PAEs萃取富集50 min,然后直接注入GC进样口,在 250℃ 温度下解吸1.5 min后进行分析测定,6种PAEs能得到充分提取和分离。方法的检出限为0.010 8~0.029 3 μg/L。对水样进行3个质量浓度水平(0.025、0.125、0.25 μg/L)的加标实验,加标回收率为41.79%~132.80%,RSD为6.53%~18.74%(n=7),用该法测定了某制药厂的实际水样,测得DBP含量为0.018 6 μg/L,DEHP、 DMP、DEP、DOP、BBP均未检测到。     

SPE-HPLC法测定水中硝基苯酚类化合物

建立了以固相萃取为前处理条件,用液相色谱法测定水中10种硝基苯酚类化合物的分析方法。实验使用HLB(6 L/150 g)固相萃取柱富集水样中的目标化合物,二氯甲烷与乙酸乙酯体积比1:2的混合溶剂洗脱,采用Phenyl柱(4.6 mm×250 mm,5 μm)分离目标化合物,以乙腈(1%甲酸)/水(1%甲酸)为流动相进行梯度洗脱,二极管阵列检测器检测。10种硝基苯酚类物质在0.02~10 mg/L范围内呈现良好的线性。方法检出限为0.1~0.3 μg/L,水样加标相对标准偏差为5.19%~18.2%,平均加标回收率为49.8%~124%。该方法适用于水中10种硝基苯酚类化合物的测定。     

超高效液相色谱-串联质谱法分析土壤及沉积物中氨基甲酸酯农药

利用超高效液相色谱-串联质谱,建立土壤和沉积物中痕量氨基甲酸酯农药的分析方法。该方法用体积比1:1的二氯甲烷/甲醇对土壤和沉积物样品进行加速溶剂萃取,GCB/PSA固相萃取小柱对萃取液进行净化,内标法定量,用超高效液相色谱-串联质谱法分析土壤和沉积物中20种氨基甲酸酯农药。20种氨基甲酸酯农药在0.02~1.0 μg/mL范围内线性良好(r≥0.99),检测限为0.20~0.60 ng/g。沉积物加标样品(20ng/g)和土壤加标样品(20ng/g)的回收率分别为33.2%~101.9%、38.8%~120.5%,相对标准偏差为6.1%~28.0%、2.3%~16.0%。沉积物加标样品(2.0 ng/g)回收率为43.0%~100.0%,相对标准偏差为2.1%~11.3%。     

超高效液相色谱-串联质谱法同时检测溴代阻燃剂

采用Acquity BEH C18色谱柱,以甲醇-乙腈混合液和水为流动相,辅以电喷雾正离子模式多反应监测(MRM)进行定性定量分析,建立了一种同位素稀释超高效液相色谱-串联质谱(UPLC-MS/MS)同时检测四溴双酚A(TBBPA)、三-(2,3-二溴丙基)异氰脲酸酯(TBC)和3种六溴环十二烷(HBCD)异构体的方法。水样通过固相萃取进行净化,回收率达到85.3%~96.1%。土壤和底泥样品经加速溶剂萃取后,采用酸性硅胶和中性硅胶柱进行净化,回收率达到81.5%~102.7%。该方法对TBBPA、TBC、α-HBCD、β-HBCD、γ-HBCD在水和土壤中的检测限分别为1.0、1.2、2.0、0.8、1.2 ng/L和0.10、0.12、0.20、0.08、0.12 ng/g。     

碱提取-丙基化衍生法同时测定土壤中的甲基汞和乙基汞

建立了碱提取-丙基化衍生方式同时测定土壤中甲基汞和乙基汞的方法。优化了仪器分析条件，研究了碱提取温度、提取时间、缓冲溶液加入量和衍生化试剂加入量对测定结果的影响。应用本方法对5种实际土壤样品进行测定，甲基汞和乙基汞的方法检出限分别为0.5 μg/kg和0.3 μg/kg，相对标准偏差分别为1.3%~17%和0.94%~16%，平均回收率分别为88.2%~110%和66.1%~110%。该法适用于批量土壤样品中甲基汞和乙基汞的分析测定。     

超高效液相色谱法快速检测地表水中丁基黄原酸

建立了直接进样-超高效液相色谱分离-紫外吸收测定地表水中丁基黄原酸的分析方法。通过对流动相的优化,确定最佳分析条件:0.050 mol/L超纯水乙酸铵溶液(pH约为9.5):乙腈=80:20等度洗脱,Waters ACQUITY UPLC BEH C₁₈色谱柱(50 mm×2.1 mm,1.7 μm)分离,流速0.30 mL/min,进样体积10.0 μL,302 nm紫外吸收。结果显示,0.5～20.0 μg/L范围线性良好,R=0.9998; 2.0、10.0、20.0 μg/L重复测定,变异系数小于5%,精密度良好;实际水样加标回收率为95.5%～101.6%;以3倍信噪比计算得出检出限为0.80 μg/L。该方法分析速度快,2 min内可完成,满足环境质量监测要求。     

固相萃取-气相色谱法测定水中多种农药类内分泌干扰物

建立了水样中用固相萃取小柱提取和净化、GC-ECD检测、GC-MSD定性证实的农药类内分泌干扰物检测方法,该方法样品提取、浓缩、净化步骤简便,能实现31种目标物同时检测。方法检测限0.05~0.50μg/L。添加回收率69%~101%,相对标准偏差低于10%。选择农药包括有机氯类(如滴滴涕、六六六、三氯杀螨醇、艾氏剂、异狄氏剂、狄氏剂、七氯、硫丹、氯丹等),氨基甲酸酯类(如甲草胺、乙草胺等),除虫菊酯类(如氯氰菊酯、速灭菊酯等)及其它农药(如氟乐灵、除草醚、毒死蜱)。该方法应用到测定某水库的水样,水库中31种农药类内分泌干扰物总浓度为48.8~890 ng/L,平均浓度295 ng/L。     

气相色谱法测定土壤和沉积物中12种有机磷农药

建立了索氏提取-固相萃取（SPE）小柱净化-GC-NPD测定土壤和沉积物中的12种有机磷农药的方法。用正己烷-丙酮（9：1）进行索氏提取，SPE硅胶小柱净化，15 mL乙酸乙酯洗脱。适用于土壤和沉积物的干样和湿样中12种有机磷农药的测定，取样量为10 g时，方法检出限为0.304~1.469 μg/kg，样品加标平均回收率为67.10%~109.8%，相对标准偏差为3.39%~14.7%。     

离子色谱-三重四级杆质谱法测定生活饮用水中痕量碘乙酸

水样经MAX固相萃取小柱富集后,用体积分数为1%的甲酸-甲醇溶液洗脱,洗脱液经0.22 μm滤膜过滤,在离子色谱柱上分离后采用三重四级杆质谱法测定水样中的碘乙酸。该方法在0 μg/L~1 000 μg/L范围内线性良好,方法检出限为0.3 μg/L。生活饮用水样品3个质量浓度水平的加标回收率为94.0%~106%,5次测定结果的RSD为2.1%~5.3%。将该方法用于测定江苏地区生活饮用水,结果未检出,高碘地区原水的加氯模拟消毒试验测得消毒后水样中碘乙酸为1.3 μg/L。     

Insecticide Contamination of Jamaican Environment. IV. Transport of the Residues Coffee Plantations in the Blue Mountains to Coastal Waters in Eastern Jamaica

A survey of 120 coffee farmers in the Portland watershed revealed that they lacked training in pesticide application, and had no concept of the transport of residues in the environment and their impact on non-target organisms.Residues of organochlorine (OC) and organophosphorous compounds (OP) were monitored monthly for over a year in plantation soil, and water, sediment and fauna of three rivers and coastal waters of Portland watershed by gas chromatography. OP residues were not detected in any sample while OC residues were below detection levels in Rio Grande. The mean concentration ± standard error of residues detected in water (g L^_1), sediment (ng g^_1) and fauna (ng g^_1 in wet weight) were: -endosulfan 2.7 ± 1.29, 3.8 ± 0.15 and 15.9 ± 1.61, respectively, in Spanish River, 1.56 ± 0.43, 24.3 ± 16.44 and 9.0 ± 1.86, respectively, in Swift River; 0.40 ± 0.02, 1.77 ± 0.68 ± 12.63, respectively, in sea coast; -endosulfan, 1.2 ± 0.48, 0 and 8.1 ± 1.99, respectively, in Spanish River, 1.9 ± 0.49, 0.75 ± 0.32 and 11. ± 4.32, respectively, in Swift River; 0, 5.1 ± 0.30 and 30.9 ± 15.96, respectively, in sea coast; endosulfan sulphate, 0.12 ± 0.12, 4.8 ± 1.62 and 10.0 ± 2.02, respectively, in Spanish River, 3.6 ± 0.95, 3.1 ± 0.56 and 7.9 ± 1.29, respectively, in Swift River and 0, 3.9 ± 2.17 and 24.0 ± 14.67, respectively, in sea coast.Dieldrin residues were detected only once in water (0.2 ± 0.03) and sediment (0.02 ± 0.003) of Spanish River, water (0.76 ± 0.09) of Swift River and sediment (0.1 ± 0.005) of sea coast; pp DDE was found twice in water (3.1 ± 1.53) and sediment (0.1 ± 0.007) of Swift River and water (0.8 ± 0.22) and sediment (6.14 ± 0.41) of sea coast. Arochlor was detected only twice (0.011 and 0.153) in water of Spanish River.     

Insecticide Contamination of Jamaican Environment. V. Island-Wide Rapid Survey of Residues in Surface and Ground Water

Residues of organochlorines and organophosphates were determined by gas chromatography in water and sediment from 26 locations in 17 major rivers, 7 natural springs and 13 wells across Jamaica. Samples were collected on only one occasion between May and July, 1994. Residues of endosulfan were detected in all but three rivers; -endosulfan in 15 samples of sediment (0.9–108.1, mean = 28.93, S.E. = 7.198 g kg-1) and 13 of water (0.01–0.35, mean = 0.11, S.E. = 0.035 g L-1), -endosulfan in 5 sediment (15.29–49.35, mean = 30.56, S.E. = 7.132 g kg-1) and 12 water (0.05–0.31, mean = 0.14, S.E. = 0.031 g L-1) samples, and endosulfan sulphate in waters of three rivers (0.003–0.244 g L-1). Chlorpyrifos was present in 9 sediment (0.423-135.2, mean = 18.38, S.E. = 10.699 g kg-1) and two water (0.001–0.022 g L-1) samples, diazinon and ethoprophos in the sediment of one river each. Mean levels (g L-1) of and isomers and sulphate of endosulfan were 0.16 (S.E. = 0.057), 0.12 (S.E. = 0.036) and 0.15 (S.E. = 0.089), respectively, in four of the seven springs and 0.23 (S.E. = 0.052), 0.11 (S.E. = 0.029) and 0.26 (S.E. = 0.088), respectively, in seven of the thirteen wells monitored.     

Dissipation of Endosulfan and Dichlorvos Residues In/On Cauliflower Curds

Dissipation behaviour of endosulfan and dichlorvos in/on cauliflower, variety Snowball-16, was studied during rabi season (Sep.–March) 2003–2004. Endosulfan and dichlorvos were sprayed @ 350 and 110g a.i. with 115 g a.i., respectively, 80 days after transplanting. Samples were taken at the interval of 0 (1h after spray), 3, 5, 7, and 10 days after spray (DAS) in triplicate and residues were estimated on GC-ECD system equipped with capillary column. The initial deposits of 3.452 and 0.295μgg⁻¹ of endosulfan and dichlorvos dissipated to 0.084 (97.56%) and 0.009 (96.95%), respectively after 10 DAS. Residues of endosulfan reached below maximum residue limit of 2μgg⁻¹ one day after spray and of dichlorvos were below MRL value of 0.5μgg⁻¹ even on 0 day. Dissipation pattern followed first order kinetics for both the insecticides with half life periods of 1.81 and 2.08 days for endosulfan and dichlorvos, respectively.     

我国沙尘暴灾害及其治理对策初步研究

分析研究了沙尘暴的成因、时空分布、发展趋势及造成的灾害，结合国外经验提出了我国治理的对策建议。     

新疆室内环境污染监测和治理工作现状与建议

针对目前室内环境监测工作出现的种种问题，就如何规范的开展室内环境监测工作，更好地为社会提供真实、准确、有效的监测数据，本文提出相关的探讨。     

Disembodied and Disembedded? The Social and Economic Implications of Atmospheric Change and Biodiversity

The social and economic implications of atmospheric change on biodiversity need to be seen in a global context of major shifts in the conceptualization and management of our relationship with nature. Traditionally, we have conceptualized the atmosphere and the other creatures of the biosphere as separate from the human, but their quasi-autonomy is now becoming subject to more and more human management. This raises not only economic issues, but social, political, and ethical concerns that will have substantial influence on public policy. Among these are the commodification of genetic material; the privatization of traditional knowledge; and the management of information. In this broader context, the paper examines an array of current and proposed strategies of response to changes in biodiversity as a result of climatic and other stresses.     

Atmospheric Change and Biodiversity: Co-Networks and Networking

Canada responded to the Global Biodiversity Convention by completing the Canadian Biodiversity Strategy in 1995. At the same time, Environment Canada also completed a national Science Assessment on Biodiversity. During this period, the Smithsonian Institution, in partnership with Parks and Environment Canada, initiated the implementation of a global biodiversity monitoring program in Canada. Under the auspices of the United Nations Man and the Biosphere Program, the SI/MAB monitoring protocols and plots have spread across Canada at an unprecedented rate. National champions in the science and educational sectors, working within an inter-disciplinary ecological framework, have guided the development, education, quality control and sharing of atmosphere-biodiversity observations electronically.Atmospheric-Biodiversity Networks and Networking have traditionally operated within separate mandates with little degree of integration. Air-Bio Networks were designed within an integrated framework to better understand the atmospheric stress on biodiversity and the adaptation actions, nationally and regionally. Detailed examples of the cumulative effects of climate change, stratospheric ozone depletion, acid deposition, ground-level ozone, suspended particulate matter and hazardous air pollutants on biodiversity will be discussed using a Southern Ontario case study. In addition, recommendations will be presented for future paired SI/MAB plots, linked networks and networking for adaptation within the context of climate, chemical and ecological gradients.     

太原市冬、夏季醛酮化合物污染特征及来源分析

针对太原市空气臭氧污染较为严重的问题,开展臭氧主要前体物醛酮化合物质量浓度及其变化规律研究.利用2,4-二硝基苯肼固相吸附/高效液相色谱方法,通过对太原市2019年冬季和夏季大气的醛酮化合物进行分析,发现太原市冬季总醛酮化合物的平均质量浓度为13μg/m3,低于夏季的27μg/m3.其中甲醛、乙醛和丙酮质量浓度最高,且...     

Dissipation and residue of metalaxyl and cymoxanil in pepper and soil

A simple and accurate method of determining metalaxyl and cymoxanil in pepper and soil was developed by ultra-performance liquid chromatography–photodiode array detection. The limits of detection were 0.015 mg/kg for metalaxyl and 0.003 mg/kg for cymoxanil. The limits of quantification were 0.05 mg/kg for metalaxyl in pepper and soil as well as 0.01 mg/kg for cymoxanil in pepper and soil. Recoveries of pepper and soil were investigated at three spiking levels and ranged within 77.52 to 102.05 % for metalaxyl and 87.15 to 103.21 % for cymoxanil, with relative standard deviations below 9.30 %. For field experiments, the half-lives of metalaxyl were 3.2 to 3.9 days in pepper and 4.4 to 9.5 days in soil at the three experimental locations in China. At harvest, pepper samples were found to contain metalaxyl and cymoxanil well below the maximum residue limit MRLs of the European Union (EU) following the recommended dosage and the interval of 21 days after last application.     

废旧干电池的环境污染防治及回收利用

介绍了各种干电池的基本化学组成，分析了废旧干电池污染环境的主要途径及对人类的危害，并就回收利用问题提出建议。