Office of Science, New Jersey Department of Environmental Protection, 428 E. State St., Trenton, NJ 08625, USA.
Sci Total Environ. 2010 Oct 1;408(21):4993-8. doi: 10.1016/j.scitotenv.2010.07.035. Epub 2010 Aug 9.
In contrast to Cr(+3), Cr(+6) is carcinogenic and allergenic. Although Cr(+6) can occur naturally, it is thought that most soil Cr(+6) is anthropogenic, however, the extent of Cr(+6) in the background environment is unknown. Cr(+6)-containing chromite ore processing residue (COPR) from chromate manufacture was deposited in numerous locations in Jersey City (JC), New Jersey. In the 1990's, significantly elevated concentrations of total Cr (Cr(+6)+Cr(+3)) were found in house dust near COPR sites. We undertook a follow-up study to determine ongoing COPR exposure. We compared Cr(+6) in house dust in JC to selected background communities with no known sources of Cr(+6). Samples were collected from living areas, basements and window wells. Cr(+6) was detected in dust from all JC and background houses. In the JC homes, the mean (+ or - SD) Cr(+6) concentration for all samples was 3.9 + or - 7.0 microg/g (range: non-detect-90.4 microg/g), and the mean Cr(+6) loading was 5.8 + or - 15.7 microg/m(2) (range: non-detect-196.4 microg/m(2)). In background homes, the mean Cr(+6) concentrations of all samples was 4.6 + or - 7.8 microg/g, (range, 0.05-56.6 microg/g). The mean loading was 10.0 + or - 27.9 microg/m(2) (range, 0.22-169.3 microg/m(2)). There was no significant difference between Cr(+6) dust concentrations in Jersey City and background locations. Stratification by sample location within houses and sampling method gave similar results. Samples exceeding 20 microg/g were obtained only from single wood surfaces in different homes. Lower concentrations in window well samples suggests transport from outside is not the major source of indoor Cr(+6). Landscaping and groundcover may influence indoor Cr(+6). There appears to be a widespread low level background of Cr(+6) that is not elevated in Jersey City homes despite its historic COPR contamination. It is possible that house dust, in general, is a source of Cr(+6) exposure with potential implications for persistence of chromium allergic contact dermatitis.
与 Cr(+3) 相反,Cr(+6) 具有致癌性和致敏性。虽然 Cr(+6) 可能自然存在,但人们认为大多数土壤中的 Cr(+6) 是人为的,然而,背景环境中的 Cr(+6) 程度尚不清楚。来自铬酸盐制造的含铬铁矿加工残渣 (COPR) 的 Cr(+6) 铬矿在新泽西州泽西城 (JC) 的许多地方被存放。20 世纪 90 年代,在 COPR 附近地区的房屋灰尘中发现总 Cr(Cr(+6)+Cr(+3))的浓度显著升高。我们进行了一项后续研究,以确定正在进行的 COPR 暴露情况。我们将泽西城的房屋灰尘中的 Cr(+6) 与没有已知 Cr(+6) 来源的选定背景社区进行了比较。样品取自居住区域、地下室和窗户井。在泽西城和背景社区的房屋灰尘中均检测到 Cr(+6)。在泽西城的房屋中,所有样品的平均 (+或- SD)Cr(+6) 浓度为 3.9 +或- 7.0 microg/g(范围:未检出-90.4 microg/g),Cr(+6) 负载为 5.8 +或- 15.7 microg/m(2)(范围:未检出-196.4 microg/m(2))。在背景社区的房屋中,所有样品的平均 Cr(+6) 浓度为 4.6 +或- 7.8 microg/g(范围:0.05-56.6 microg/g)。平均负载为 10.0 +或- 27.9 microg/m(2)(范围:0.22-169.3 microg/m(2))。泽西城和背景地点之间的 Cr(+6) 灰尘浓度没有显著差异。对房屋内样本位置和采样方法的分层分析结果相似。仅从不同房屋的单个木材表面获得了超过 20 microg/g 的样品。窗井样品中的浓度较低表明,室内 Cr(+6) 不是由室外传输造成的。景观美化和地面覆盖物可能会影响室内 Cr(+6)。尽管泽西城有历史遗留的 COPR 污染,但似乎存在广泛的低水平背景 Cr(+6),这并未使泽西城的房屋灰尘中的 Cr(+6) 浓度升高。可能房屋灰尘通常是 Cr(+6) 暴露的来源,这可能对铬过敏接触性皮炎的持续存在有影响。