火焰原子吸收分光光度法测定生活垃圾堆肥中镍

通过试验研究,建立了硝酸-氢氟酸-高氯酸消解、火焰原子吸收分光光度法测定生活垃圾堆肥产品中的镍。该方法的检出限为5mg/kg(按称取0.5g试样消解定容至50ml计算),用于不同地域堆肥样品中镍的测定,其相对标准偏差(RSD)均在6.51%以下,加标回收率介于91.2%~102%之间,可作为一种较理想的检验堆肥产品质量的方法。     

火焰原子吸收分光光度法测定生活垃圾堆肥产品中铬

通过试验研究,建立了硝酸-氢氟酸-高氯酸消解、火焰原子吸收分光光度法测定生活垃圾堆肥产品中的铬。该方法的检出限为5mg/kg（按称取0．5g试样消解定容至50ml计算）,用于不同地域堆肥样品中铬的测定,其相对标准偏差（RSD）均在8．90％以下,加标回收率介于90．9％～105．8％之间,可作为一种较理想的检验堆肥产品质量的方法。     

APDC-MIBK萃取火焰原子吸收分光光度法测定生活垃圾堆肥产品中铅、镉的研究

通过试验研究,建立了硝酸-氢氟酸-高氯酸消解、APDC-MIBK萃取火焰原子吸收分光光度法测定生活垃圾堆肥产品中的铅、镉.该方法铅的检出限为2mg/kg,镉的检出限为0.2mg/kg(按称取0.5g试样消解定容至50ml计算),用于不同地域堆肥样品测定,铅、镉的相对标准偏差(RsD)分别为2.29%～8.16%和5.17%～11.7%,加标回收率介于86.8%～107.2%和88.0%～108.0%之间.     

碱消解-火焰原子吸收分光光度法测定固体废物中的六价铬

采用碱消解-火焰原子吸收分光光度法测定固体废物中的六价铬，样品消解温度控制在90 ℃～95 ℃范围内，消解时间为1 h，消解液pH值调节至9.0±0.2。方法检出限与测定下限分别为0.05 mg/kg与0.20 mg/kg，对不同基体实际样品平行测定的RSD为1.4%～13.0%，加标回收率为93%～130%。     

冷原子荧光法测定生活垃圾堆肥产品中汞

通过试验研究,建立了用王水消解、冷原子荧光法测定生活垃圾堆肥产品中汞的方法.本方法的检出限为0.006 mg/kg (按称取0.5 g试样消解定容至50 ml计算),用于国内不同地域的堆肥样品测定,其相对标准偏差(RSD)在2.55%～10.7%之间,加标回收率介于91.0%～108.0%,可作为一种较理想的检验堆肥产品质量的方法.     

氢化物发生-原子荧光法测定生活垃圾堆肥产品中砷

通过试验研究,建立了硝酸-高氯酸消解,原子荧光法测定生活垃圾堆肥产品中的砷.该方法的检出限为0.06mg/kg(按称取0.5g试样消解定客至50ml计算),用于不同地域堆肥样品中砷的测定,其相对标准偏差(RSD)均在8.99%以下.加标回收率介于89.0%～107.0%之间.     

原子吸收法测定土壤中铅的方法

通过湿法消解土壤样品,利用石墨炉原子吸收分光光度法(GAAS)和火焰原子吸收分光光度法(FAAS)测定不同土壤样品中铅的含量,以验证2种方法的有效性并加以对比。实验结果表明:2种方法均满足土壤中铅含量的测定要求,测定的标准土样含量均在标准值的不确定度范围内,GAAS方法测定结果更接近保证值。二者的相对标准偏差(RSD)值均低于1.5%,FAAS方法的精密度更高,且具有快速简单等优势。     

微波消解-分光光度法测定土壤中的全硼

研究了分光光度法测定土壤中的全硼时样品的微波消解方法.建立了合理的分析步骤.进行了微波消解条件的选择及测定结果精密度、准确度实验.实验结果为:消解完全仅需25min,相对标准偏差7.6%,其方法的加标回收率为98.4%～112%.结果表明,微波消解-分光光度法测定土壤中的全硼是一种快速、准确且低环境污染的方法.     

闭管消解-萘乙二胺分光光度法测定水中总氮

通过实验研究了一种采用闭管消解-萘乙二胺分光光度法测定水样中总氮的新方法,分析了不同测试条件对测定结果的影响。结果表明:方法最佳消解时间为25min,宜选用535nm为实验波长,在10～25℃下显色5～20min完成测定。与标准方法比较,该方法具有灵敏度高、测定时间短的优点,可用于环境监测中水和废水的总氮分析。     

火焰原子吸收法测定饮用水中银的改进

对火焰原子吸收分光光度法测定饮用水中银的方法作了改进。试验发现在酸性条件下,不利于银的测定,改加氨水氰化钾溶液则取得满意的结果,提高了测定灵敏度。银的特征质量浓度为0 016mg·L-1/1%吸收,检测限为0 001mg/L,相对标准差<2.5%,加标回收率在98%～103%之间。     

夏季重大活动期间O3监测数据质量提升方法研究

2018年夏季上海合作组织成员国元首理事会环境空气质量保障工作开始前,中国监测总站对山东、江苏2个省份19个城市共计85个国控站点开展O3专项质控工作。结果表明,保障区域O3监测数据低、中、高浓度点相对误差变异系数分别为4. 7%、4. 3%和4. 8%,95%预测区间分别为[-7. 4%,9. 0%]、[-6. 9%,8. 3%]和[-8. 0%,8. 4%]。与之相比,2018年全国范围内开展外部比对的1 346个国控站点O3监测数据低、中、高浓度点相对误差变异系数分别为7. 4%、6. 5%和6. 2%,95%预测区间分别为[-13. 1%,15. 4%]、[-11. 7%,13. 2%]和[-11. 6%,12. 2%]。通过专项质控工作,保障区域O3监测数据质量明显提升,能够为夏季重大活动保障提供更为准确、可比的O3监测数据支持。     

气相色谱法测定土壤中37种有机磷农药残留

采用气相色谱法测定土壤中37种有机磷农药,当取样量为10 g时,37种有机磷农药方法检出限为0. 002～0. 015 mg/kg,测定下限为0. 008～0. 060 mg/kg。低含量加标样品中有机磷农药的加标回收率为72. 8%～104%,相对标准偏差为4. 2%～13. 8%;中含量加标样品中有机磷农药的加标回收率为71. 5%～101%,相对标准偏差为4. 3%～13. 5%;高含量加标样品中有机磷农药的加标回收率为74. 6%～109%,相对标准偏差为6. 8%～14. 6%。该方法灵敏度高、分离效果好、重现性好,能够满足土壤中37种有机磷农药残留检测的要求。     

原子荧光光谱法同时测定环境水体中痕量锡和锌

采用原子荧光光谱法同时测定环境水样中痕量锡和锌,优化了试验条件。锡在1.00μg/L～10.0μg/L、锌在20.0μg/L～200μg/L范围内线性良好,方法检出限锡为0.13μg/L,锌为1.76μg/L,锡和锌标准溶液测定的相对标准偏差分别为2.9%和4.0%,环境水样加标回收率锡为96.4%～106%,锌为92.0%～111%。     

GC/MS内标法测定土壤中多环芳烃的质量控制

阐述了GC/MS内标法测定土壤中多环芳烃时质量控制的基本内容、基本方法和基本操作。测定结果为：空白分析结果均小于检出限;空白加标精密度和准确度分别在7.80%~25.2%和49.2%~96.6%之间;样品加标精密度和准确度分别在7.77%~19.8%和67.2%~122%之间;检出限在0.05~0.08 mg/kg之间...     

Drinking water quality assessment in Southern Sindh (Pakistan)

The southern Sindh province of Pakistan adjoins the Arabian Sea coast where drinking water quality is deteriorating due to dumping of industrial and urban waste and use of agrochemicals and yet has limited fresh water resources. The study assessed the drinking water quality of canal, shallow pumps, dug wells, and water supply schemes from the administrative districts of Thatta, Badin, and Thar by measuring physical, chemical, and biological (total coliform) quality parameters. All four water bodies (dug wells, shallow pumps canal water, and water supply schemes) exceeded WHO MPL for turbidity (24%, 28%, 96%, 69%), coliform (96%, 77%, 92%, 81%), and electrical conductivity (100%, 99%, 44%, 63%), respectively. However, the turbidity was lower in underground water, i.e., 24% and 28% in dug wells and shallow pumps as compared to open water, i.e., 96% and 69% in canal and water supply schemes, respectively. In dug wells and shallow pumps, limits for TDS, alkalinity, hardness, and sodium exceeded, respectively, by 63% and 33%; 59% and 70%, 40% and 27%, and 78% and 26%. Sodium was major problem in dug wells and shallow pumps of district Thar and considerable percent in shallow pumps of Badin. Iron was major problem in all water bodies of district Badin ranging from 50% to 69% and to some extent in open waters of Thatta. Other parameters as pH, copper, manganese, zinc, and phosphorus were within standard permissible limits of World Health Organization. Some common diseases found in the study area were gastroenteritis, diarrhea and vomiting, kidney, and skin problems.     

Source apportionment of PM10 and PM(2.5) at Tocopilla, Chile (22 degrees 05' S, 70 degrees 12' W)

Tocopilla is located on the coast of Northern Chile, within an arid region that extends from 30 degrees S to the border with Perú. The major industrial activities are related to the copper mining industry. A measurement campaign was conducted during March and April 2006 to determine ambient PM10 and PM(2.5) concentrations in the city. The results showed significantly higher PM10 concentrations in the southern part of the city (117 microg/m3) compared with 79 and 80 (microg/m3) in the central and northern sites. By contrast, ambient PM2.5 concentrations had a more uniform spatial distribution across the city, around 20 (microg/m3). In order to conduct a source apportionment, daily PM10 and PM(2.5) samples were analyzed for elements by XRF. EPA's Positive Matrix Factorization software was used to interpret the results of the chemical compositions. The major source contributing to PM(2.5) at sites 1, 2 and 3, respectively are: (a) sulfates, with approximately 50% of PM2.5 concentrations at the three sites; (b) fugitive emissions from fertilizer storage and handling, with 16%, 21% and 10%; (c) Coal and residual oil combustion, with 15%, 15% and 4%; (d) Sea salt, 5%, 6% and 16%; (e) Copper ore processing, 4%, 5% and 15%; and (f) a mixed dust source with 11%, 7% and 4%. Results for PM10--at sites 1, 2 and 3, respectively--show that the major contributors are: (a) sea salt source with 36%, 32% and 36% of the PM10 concentration; (b) copper processing emissions mixed with airborne soil dust with 6.6%, 11.5% and 41%; (c) sulfates with 31%, 31% and 12%; (d) a mixed dust source with 16%, 12% and 10%, and (e) the fertilizer stockpile emissions, with 11%, 14% and 2% of the PM10 concentration. The high natural background of PM10 implies that major reductions in anthropogenic emissions of PM10 and SO2 would be required to attain ambient air quality standards for PM10; those reductions would curb down ambient PM(2.5) concentrations as well.     

怠速工况下汽车使用乙醇汽油排放污染物的变化

对怠速工况下使用乙醇汽油汽车尾气中污染物进行了检测.结果表明,使用乙醇汽油后,汽车尾气中CO和HC浓度明显降低,平均下降率为56.9%和38.2%;NOx平均下降率为15.0%;CO2浓度平均增长率为5.04%;苯系物浓度明显降低,平均下降率在45.5%～53.1%;醛类的浓度增加明显,平均增长率在47.8%～293%;丙酮、丁酮的浓度增加,分别为16.6%和25.3%.     

高压密闭消解土壤砷、汞、铅、镉酸体系比较

采用高压密闭消解系统消解土壤,氢化物发生-原子荧光光谱法(HG-AFS)测定As和Hg,石墨炉原子吸收光度法(GF-AAS)测定Pb和Cd,对比了不同消解酸体系对国家土壤标准参考样中As、Hg、Pb、Cd的消解效果。结果表明,盐酸-硝酸体系对As、Hg、Pb和Cd的消解平均回收率分别为26.1%、100.6%、69.7%、87.3%;硝酸-高氯酸-氢氟酸体系中As、Hg、Pb和Cd消解平均回收率分别为109.9%、84.7%、87.5%、90.1%;硝酸-双氧水体系对Hg、Pb、Cd消解平均回收率分别为104.8%、95.1%、93.3%,对As的回收率虽只有69.2%,但数据精密度最好。此外,从简化试验步骤,减少误差,提高检测效率及减少试验危险性等方面综合评价,认为硝酸-双氧水消解体系是采用高压密闭系统消解土壤重金属的最理想酸体系。     

气相色谱法测定土壤中菊酯类农药残留

以正己烷/丙酮混合溶剂(体积比为1∶1)为提取剂,采用Florisil柱净化、气相色谱电子捕获检测器测定土壤中菊酯类农药残留,优化了提取条件。4种菊酯类农药在0.010 mg/L~1.00 mg/L范围内线性良好,方法检出限为0.005 mg/L~0.010 mg/L,甲氰菊酯回收率为85.2%~103%,RSD为2.3%~5.4%;氯氰菊酯回收率为80.5%~103%,RSD为2.8%~6.7%;氰戊菊酯回收率为80.2%~103%,RSD为2.3%~6.0%;溴氰菊酯回收率为80.8%~103%,RSD为2.4%~6.2%。     

Exploring data quality for some inorganic and organic constituents of inhalable particulate matter (PM10)

Quality assurance (QA) assessments of air pollution data sets provide a basis for evaluating the significance of various substances in the atmosphere. For non-criteria pollutants, QA results are seldom reported in the technical literature and are often difficult to estimate. The present report provides a summary of QA results such as recovery, precision and accuracy data. Of the six trace elements and nine organic constituents compared in detail, recoveries, laboratory precision and laboratory accuracy values were 100%, ±3% to ±19% and-2 to-13% for the former group and 69% to 98%, ±7% to 23% and-15 to-34% for the later group. System precision varied from ±22% to ±47% for the trace elements and ±42% to ±83% for the organic constituents. Limitations in the interpretation of non-criteria particulate-phase pollutant data bases are discussed with some emphasis placed on receptor-modelling and risk assessment applications. Finally, the relevance of NBS certified materials for QA estimates in non-criteria air pollutant studies is also reviewed.