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Measurement of soluble and insoluble hexavalerst chromium in ambient particulate matter

机译:环境颗粒物质中可溶性和不溶性六甲铬的测量

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Background: Hexavaient chromium (Cr(Ⅵ)), a pulmonary carcinogen, can present as both soluble and insoluble forms in environment, which may have different toxicities. It is thus important to separately quantify ambient Cr(Ⅵ) in both soluble and insoluble forms. Aims: To determine soluble and insoluble Cr(Ⅵ) in NIST 1648a (a reference urban particulate matter (PM)), ambient PM10 collected from 3 urban areas in NJ, i.e. Meadowlands, NJ Turnpike Exit 13 in Elizabeth and Rahway, and ambient PM10 collected from the suburban area in NJ, i.e. Piscataway. Methods: We developed a method to measure total Cr(Ⅵ) in ambient PM, which comprised collection of PM usinga Teflon filter, microwave extraction with 3% Na2CO3-2% NaOH, and detection with IC-UV (1,5-diphenylcarbazide colorimetry at 540 nm). The method detection limit was 0.33 ng/m3. Soluble Cr(Ⅵ) in ambient PM was measured by previously established method in our lab. Insoluble Cr(Ⅵ) was determined to be the difference between total Cr(Ⅵ) and soluble Cr(Ⅵ). Results: The soluble and total Cr(Ⅵ) in NIST 1648a were 1.75±0.24 mg/kg (N = 6, %CV = 14%) and 26.0+3.1 mg/kg (N = 4, %CV = 11.996). The concentrations (mean±SD) of ambient soluble Cr(Ⅵ) in Meadowlands, Elizabeth, Rahway and Piscataway were 0.30±0.16, 0.21±0.13, 0.3310.36 and 0.20±0.18 ng/m3 in the summer sampling period, and 0.11±0.04, 0.19±0.09, 0.14±0.07 and 0.03±0.01 ng/m3 in the winter sampling period. The concentrations of ambient total Cr(Ⅵ) in Meadowlands, Elizabeth, Rahway and Piscataway were 1.25±0.58,1.56±0.48, 0.99±0.76 and 0.86±0.50 ng/m3 in the summer sampling period and 1.32±0.56,1.41±0.56,1.05±0.36 and 0.94±0.49 ng/m3 in the winter sampling period. Conclusions: Soluble and insoluble Cr(Ⅵ) co-existed in both NIST 1648a and collected ambient PM10. The soluble Cr(Ⅵ) in ambient PM10 accounted for 14.3 - 42.7% of total Cr(Ⅵ) in the summer, greater than 4.2 -14.4% in the winter.
机译:背景:Hexavaient铬(Cr(Ⅵ)),肺致癌物质,可呈现在环境可溶性和不溶性形式的,其可以具有不同的毒性。因此重要的是,以分别量化环境的Cr(Ⅵ)在可溶性和不溶性形式。目的:为了确定可溶性和不溶性的Cr(Ⅵ)在NIST 1648A(基准城市颗粒物质(PM)),环境PM10从NJ,即菁,在Elizabeth和拉威NJ收费公路出口13,和环境PM10 3个城市地区收集从郊区在新泽西州,即皮斯卡塔韦收集。方法:我们开发测量总铬(Ⅵ)在室温PM,其包含PM usinga Teflon过滤收集,用3%Na2CO3-2%的NaOH,并用IC-UV(1,5-二苯比色法检测微波提取的方法在540nm处)。该方法的检测限为0.33毫微克/立方米。可溶性铬(Ⅵ)在室温PM是由我们实验室以前建立的方法测定。不溶性的Cr(Ⅵ)被确定为总铬(Ⅵ)和可溶性铬(Ⅵ)之间的差。结果:可溶性和总铬(Ⅵ)在NIST 1648A分别为1.75±0.24毫克/千克(N = 6,%CV = 14%)和26.0 + 3.1毫克/千克(N = 4,%CV = 11.996)。浓度环境可溶性铬(Ⅵ)中的菁(平均值±SD),伊丽莎白,拉威和皮斯卡塔韦分别为0.30±0.16,0.21±0.13,0.3310.36而在夏天0.20±0.18毫微克/立方米采样周期,和0.11± 0.04,0.19±0.09,0.14±0.07和0.03±0.01毫微克/立方米在冬季采样周期。环境总铬(Ⅵ)的麦中的浓度,伊丽莎白,拉威和皮斯卡塔韦分别为1.25±0.58,1.56±0.48,0.99±0.76和0.86±0.50毫微克/立方米在夏季采样周期和1.32±0.56,1.41±0.56, 1.05±0.36和0.94±0.49毫微克/立方米在冬季采样周期。结论:可溶性和不溶性的Cr(Ⅵ)共存两个NIST 1648A和收集的环境PM10。可溶性铬(Ⅵ)在室温PM10占14.3 - 在夏天总铬(Ⅵ)的42.7%,大于在冬季4.2 -14.4%。

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