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Query: UMLS:C0271276 (Hudson)
 1,066 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

A large quantity of chromate chemical production waste, containing hexavalent chromium, has been used as fill at over 150 sites in Hudson County, New Jersey. One site is in a state park, and several other sites are adjacent to the park. Blood and urinary chromium levels were compared between 17 employees at the Hudson County park and 35 employees from two other state parks. A limited number of soil and personal air samples were also taken. Urinary and RBC chromium levels between the two groups were similar, even after adjusting for potentially confounding variables. The air sampling results demonstrated slightly higher chromium levels at Hudson County, but these were still very low level in nature (mean = 0.18 micrograms/m3). These results call into question the utility of chromium biomonitoring under environmental exposure conditions.
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PMID:Chromium exposure assessment of outdoor workers in Hudson County, NJ. 152 99

Chromite ore processing residue occurs at over 130 sites in Hudson County, New Jersey. Many of these sites are in urban residential areas. This waste is a result of 70 years of chromate and bichromate chemical manufacturing. At least 15% of the sites contain total chromium concentrations greater than 10,000 mg/kg, with hexavalent content ranging from about 1 to 50%. Continuing leaching of this waste results in yellow-colored surface water runoff and yellow deposits on the soil surface and inside basement walls. The chemistry, environmental fate, health effects, and human exposure potentials for this waste are described.
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PMID:Chromite ore processing residue in Hudson County, New Jersey. 193 43

An estimated two million tons of chromate production waste pollution has caused a major environmental and public health concern in Hudson County, New Jersey. As part of an occupational exposure assessment, urinary and red blood cell (RBC) chromium measurements were performed on 52 state employees who worked either near a contaminated site or elsewhere. Samples were collected so as to minimize contamination, and they were analyzed using sensitive techniques. These workers also completed a questionnaire that addressed potentially important third variables. Individual analyses suggested that exercise, drinking beer, past employment in chromium-related occupations, and diabetic status had an important effect on urinary chromium levels. These variables were entered into a regression model and were all found to be significant predictors of urinary chromium level (p less than .10). Some variables were also examined for their influence on RBC chromium level, but none had a measurable effect.
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PMID:Biological markers in chromium exposure assessment: confounding variables. 206 32

Chromate resistance of Pseudomonas fluorescens LB300, isolated from chromium-contaminated sediment in the upper Hudson River, was found to be plasmid specified. Loss of the plasmid (pLHB1) by spontaneous segregation or mitomycin C curing resulted in a simultaneous loss of chromate resistance. Subsequent transformation of such strains with purified pLHB1 plasmid DNA resulted in a simultaneous re-acquisition of the chromate resistance phenotype and the plasmid. When pLHB1 was transferred by conjugation to Escherichia coli, the plasmid still conferred chromate resistance.
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PMID:Chromate resistance plasmid in Pseudomonas fluorescens. 630 41

Hudson County, New Jersey, was a major center for the processing of chromium ore. After processing, some of the ore residue that contained low concentrations of chromium became distributed in population centers throughout the county. There now exists concern in the county about possible health effects from chromium exposure. Our previous research suggested that immune-function assays would make useful biomarkers for chromate exposure in humans. Blood samples were drawn from 46 individuals who lived and/or worked in Hudson County and from 47 controls. Only one of the immune-associated assays performed on these samples showed any statistically significant differences between the Hudson County and control groups. The mean level of IL-6 produced by pokeweed mitogen-stimulated mononuclear cells isolated from the Hudson County group was 64% of the control value--a highly significant decrease (p<.001). There was also a significant correlation between the proliferative responses of the mononuclear cells to pokeweed mitogen and the levels of IL-6 produced by these cells. No differences were detected in the IL-6 responses that resulted from age, gender, or smoking status. The reliability of the IL-6 assay was found to be 90%. To our knowledge, there have been no reports, until now, that describe reduced production of any cytokine in individuals who are exposed to chromate.
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PMID:Reduced IL-6 levels among individuals in Hudson County, New Jersey, an area contaminated with chromium. 862 59

A simple and sensitive assay for DNA-protein cross-links has been used as a biomarker of chromate exposure and early carcinogenic effects. Pilot studies of DNA-protein cross-links in peripheral blood lymphocytes have been conducted with individuals who had higher exposure to chromate, including welders, and with individuals who had lower levels of exposure such as residents living in a chromium-contaminated area in Jersey City, New Jersey. Studies were also conducted in two Bulgarian cities (Jambol and Burgas) with different levels of air pollution and Cr(VI) exposure and in chrome platers in Bulgaria who had high exposure to chromate. DNA-protein cross-links in U.S. welders and in individuals living in Hudson County, New Jersey around chromium-contaminated areas were significantly higher compared to matched controls. Although blood and urinary levels of chromium were not extensively studied in these populations, we were able to obtain these measurements in the Bulgarian population. Chromium levels in red blood cells of controls living in Burgas were in the order of 1 to 2 ppb chromium, and these individuals had the lowest levels of DNA-protein cross-links. However, the chromium levels in Jambol ranged from about 2 to 7 ppb in red blood cells of city residents to about 22 ppb in chrome platers. DNA-protein cross-links were saturated at about 7 to 8 ppb chromium in the red blood cells, and cross-links correlated well only with chromium levels in red blood cells. Urinary chromium levels did not correlate well with either DNA-protein cross-links or chromium levels in with red blood cells.
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PMID:Monitoring human lymphocytic DNA-protein cross-links as biomarkers of biologically active doses of chromate. 893 34

It has been known for a number of years that chromium-containing mine slags were used as landfill in residential areas of Hudson County, New Jersey. Since one of the major lesions induced in intact cells by chromate is the DNA-Protein crosslink, we have used this lesion as a biomarker of biological effect of chromium (Cr) exposure. We have previously developed a sensitive and easy-to-perform assay to detect DNA-Protein crosslinks, based on the selective K SDS precipitation of DNA associated with protein. We examined the levels of DNA-Protein crosslinks in peripheral blood mononuclear cells of 33 individuals determined to be at risk for chromium exposure by virtue of their residence in Hudson County and their urinary Cr levels. These data were compared to the levels of DNA-Protein crosslinks among 49 controls who resided in noncontaminated areas. A complete clinical examination and urine analysis did not show any Cr-related abnormalities among the exposed population. The mean DNA-Protein crosslink level in the lymphocytes of the exposed group was 1.3 +/- 0.5% (SD), whereas the unexposed group had 0.8 +/- 0.4% (p < 0.001), after adjustment for age, gender, race, smoking, and weight. Further studies in this population are needed to confirm the possible association between the high levels of DNA-Protein crosslink and Cr exposure.
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PMID:Increased DNA-protein crosslinks in lymphocytes of residents living in chromium-contaminated areas. 896 89

During much of this century, Hudson County, New Jersey, was a major center for the processing of chromium ore. Some of the residue from this processing was used in landfills and in construction materials throughout the county and, in some cases, in highly populated areas. Given that it is widely accepted that exposure to hexavalent chromium compounds poses a risk for the development of respiratory-tract cancer, concerns were raised that individuals who worked or resided in chromium-contaminated areas might be at increased risk for the development of respiratory cancer. To address these concerns, we evaluated a Hudson County soil sample-heavily contaminated with chromium ore residue (Cr(+6) concentration at 5 895 mg/kg)-with respect to its carcinogenic potential to the respiratory tract of Sprague-Dawley rats. Groups of animals were given repeated intratracheal exposures to one of four materials: (1) Hudson County chromium-contaminated soil (CCS), (2) CCS augmented with calcium chromate (CaCrO4), (3) CaCrO4 alone, or (4) control soil. Nominal total doses of Cr(+6) for each respective group were 324 microg/kg, 7,975 microg/kg, 8,700 microg/kg, and 0.02 microg/kg. Incidences of malignant tumors and nephritis were not elevated in any group. Four primary lung tumors appeared in animals that received CCS + CaCrO4, and one primary lung tumor appeared in the group treated with CaCrO4 alone. These incidences were not significant statistically, but the rare spontaneous occurrence of these tumors in Sprague-Dawley rats suggested that they were treatment related. No primary lung tumors appeared in the control or CCS-treated groups.
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PMID:An assessment of the tumorigenic properties of a Hudson County soil sample heavily contaminated with hexavalent chromium. 916 33

Batch leaching tests, qualitative and quantitative x-ray powder diffraction (XRPD) analyses, and geochemical modeling were used to investigate the leaching mechanisms of Cr(VI) from chromite ore processing residue (COPR) samples obtained from an urban area in Hudson County, New Jersey. The pH of the leaching solutions was adjusted to cover a wide range between 1 and 12.5. The concentration levels for total chromium (Cr) and Cr(VI) in the leaching solutions were virtually identical for pH values >5. For pH values <5, the concentration of total Cr exceeded that of Cr(VI) with the difference between the two attributed to Cr(III). Geochemical modeling results indicated that the solubility of Cr(VI) is controlled by Cr(VI)-hydrocalumite and Cr(VI)-ettringite at pH >10.5 and by adsorption at pH <8. However, experimental results suggested that Cr(VI) solubility is controlled partially by Cr(VI)-hydrocalumite at pH >10.5 and by hydrotalcites at pH >8 in addition to adsorption of anionic chromate species onto inherently present metal oxides and hydroxides at pH <8. As pH decreased to <10, most of the Cr(VI) bearing minerals become unstable and their dissolution contributes to the increase in Cr(VI) concentration in the leachate solution. At low pH ( <1.5), Cr(III) solid phases and the oxides responsible for Cr(VI) adsorption dissolve and release Cr(III) and Cr(VI) into solution.
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PMID:Leaching mechanisms of Cr(VI) from chromite ore processing residue. 1894 66