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dc.contributor.authorMuneko Nishijoen_US
dc.contributor.authorYasushi Suwazonoen_US
dc.contributor.authorWerawan Ruangyuttikarnen_US
dc.contributor.authorKowit Nambunmeeen_US
dc.contributor.authorWitaya Swaddiwudhipongen_US
dc.contributor.authorKazuhiro Nogawaen_US
dc.contributor.authorHideaki Nakagawaen_US
dc.date.accessioned2018-09-04T09:56:38Z-
dc.date.available2018-09-04T09:56:38Z-
dc.date.issued2014-07-09en_US
dc.identifier.issn14712458en_US
dc.identifier.other2-s2.0-84903870725en_US
dc.identifier.other10.1186/1471-2458-14-702en_US
dc.identifier.urihttps://www.scopus.com/inward/record.uri?partnerID=HzOxMe3b&scp=84903870725&origin=inwarden_US
dc.identifier.urihttp://cmuir.cmu.ac.th/jspui/handle/6653943832/53724-
dc.description.abstractBackground: The aim of the present study was to estimate the benchmark doses (BMD) for renal effects for health risk assessment of residents living in Cd-polluted and non-polluted areas in a Thai population. Methods. The study participants consisted of inhabitants aged 40 years or older who lived in a non-polluted area (40 men and 41 women) and in the environmentally polluted Mae Sot District (230 men and 370 women) located in northwestern Thailand. We measured urinary and blood cadmium (Cd) as markers of long-term exposure and urinary β2-microglobulin (β2-MG) and N-acetyl-β-D-glucosaminidase (NAG) as renal tubular effect markers. An updated hybrid approach was applied to estimate the benchmark doses (BMD) and their 95% lower confidence limits (BMDL) of urinary and blood Cd for Cd-induced renal effects in these subjects. BMD and BMDL corresponding to an additional risk (BMR) of 5% were calculated with the background risk at zero exposure set to 5% after adjusting for age and smoking status. Results: The estimated BMDLs of urinary Cd for renal effect markers were 6.9 for urinary β2-MG and 4.4 for NAG in men and 8.1 for β2-MG and 6.1 for NAG μg/g creatinine (Creat) in women. These BMDLs of urinary Cd (μg/g Creat) for NAG were less than the geometric mean urinary Cd in the polluted area (6.5 in men and 7.1 in women). The estimated BMDLs of blood Cd (μg/L) were 6.2 for urinary β2-MG and 5.0 for NAG in men and 5.9 for β2-MG and 5.8 for NAG in women. The calculated BMDLs were similar or less compared with the geometric mean blood Cd (μg/L) in the polluted Thai area (6.9 in men and 5.2 in women). Conclusion: The BMDLs of urinary and blood Cd for renal effects were estimated to be 4.4 - 8.1 μg/g Creat and 4.4 - 6.2 μg/L in the Thai population aged ≥ 40 years old, suggesting that more than 40% of the residents were at risk of adverse renal effects induced by Cd exposure in Thailand. © 2014 Nishijo et al.; licensee BioMed Central Ltd.en_US
dc.subjectMedicineen_US
dc.titleRisk assessment for Thai population: Benchmark dose of urinary and blood cadmium levels for renal effects by hybrid approach of inhabitants living in polluted and non-polluted areas in Thailanden_US
dc.typeJournalen_US
article.title.sourcetitleBMC Public Healthen_US
article.volume14en_US
article.stream.affiliationsKanazawa Medical Universityen_US
article.stream.affiliationsChiba Universityen_US
article.stream.affiliationsChiang Mai Universityen_US
article.stream.affiliationsMae Fah Luang Universityen_US
article.stream.affiliationsMae Sot General Hospitalen_US
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