Literature DB >> 20692023

Hexavalent chromium in house dust--a comparison between an area with historic contamination from chromate production and background locations.

Alan H Stern1, Chang Ho Yu, Kathleen Black, Lin Lin, Paul J Lioy, Michael Gochfeld, Zhi-Hua Tina Fan.   

Abstract

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. Copyright 2010 Elsevier B.V. All rights reserved.

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Year:  2010        PMID: 20692023      PMCID: PMC4300124          DOI: 10.1016/j.scitotenv.2010.07.035

Source DB:  PubMed          Journal:  Sci Total Environ        ISSN: 0048-9697            Impact factor:   7.963


  15 in total

1.  Reduction in residential chromium following site remediation.

Authors:  N C Freeman; P J Lioy; A H Stern
Journal:  J Air Waste Manag Assoc       Date:  2000-06       Impact factor: 2.235

2.  A wipe sampler for the quantitative measurement of dust on smooth surfaces: laboratory performance studies.

Authors:  P J Lioy; T Wainman; C Weisel
Journal:  J Expo Anal Environ Epidemiol       Date:  1993 Jul-Sep

3.  Exposure to chromium dust from homes in a Chromium Surveillance Project.

Authors:  N C Freeman; A H Stern; P J Lioy
Journal:  Arch Environ Health       Date:  1997 May-Jun

Review 4.  Risk assessment of the allergic dermatitis potential of environmental exposure to hexavalent chromium.

Authors:  A H Stern; R E Bagdon; R E Hazen; F N Marzulli
Journal:  J Toxicol Environ Health       Date:  1993-12

5.  Residential exposure to chromium waste--urine biological monitoring in conjunction with environmental exposure monitoring.

Authors:  A H Stern; N C Freeman; P Pleban; R R Boesch; T Wainman; T Howell; S I Shupack; B B Johnson; P J Lioy
Journal:  Environ Res       Date:  1992-08       Impact factor: 6.498

6.  The effect of remediation of chromium waste sites on chromium levels in urine of children living in the surrounding neighborhood.

Authors:  N C Freeman; T Wainman; P J Lioy; A H Stern; S I Shupack
Journal:  J Air Waste Manag Assoc       Date:  1995-08       Impact factor: 2.235

7.  Microenvironmental analysis of residential exposure to chromium-laden wastes in and around New Jersey homes.

Authors:  P J Lioy; N C Freeman; T Wainman; A H Stern; R Boesch; T Howell; S I Shupack
Journal:  Risk Anal       Date:  1992-06       Impact factor: 4.000

Review 8.  Dust: a metric for use in residential and building exposure assessment and source characterization.

Authors:  Paul J Lioy; Natalie C G Freeman; James R Millette
Journal:  Environ Health Perspect       Date:  2002-10       Impact factor: 9.031

9.  Panel discussion: analysis of chromium: methodologies and detection levels and behavior of chromium in environmental media.

Authors:  M Gochfeld
Journal:  Environ Health Perspect       Date:  1991-05       Impact factor: 9.031

10.  Chromite ore processing residue in Hudson County, New Jersey.

Authors:  T Burke; J Fagliano; M Goldoft; R E Hazen; R Iglewicz; T McKee
Journal:  Environ Health Perspect       Date:  1991-05       Impact factor: 9.031

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  2 in total

1.  A post-remediation assessment in Jersey City of the association of hexavalent chromium in house dust and urinary chromium in children.

Authors:  Kathleen Black; Michael Gochfeld; Paul J Lioy; Zhi-Hua Tina Fan; Chang Ho Yu; Chris Jeitner; Marta Hernandez; Stephanie A Einstein; Alan H Stern
Journal:  J Expo Sci Environ Epidemiol       Date:  2015-09-02       Impact factor: 5.563

2.  Two decades of exposure assessment studies on chromate production waste in Jersey City, New Jersey--what we have learned about exposure characterization and its value to public health and remediation.

Authors:  Alan H Stern; Michael Gochfeld; Paul J Lioy
Journal:  J Expo Sci Environ Epidemiol       Date:  2012-11-07       Impact factor: 5.563

  2 in total

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