Rieuwerts J S, Searle P, Buck R
School of Earth, Ocean and Environmental Sciences, University of Plymouth, Portland Square, North Hill, Plymouth, PL4 8AA, United Kingdom.
Sci Total Environ. 2006 Dec 1;371(1-3):89-98. doi: 10.1016/j.scitotenv.2006.08.039. Epub 2006 Oct 4.
Samples of household dust and garden soil were collected from twenty households in the vicinity of an ex-mining site in southwest England and from nine households in a control village. All samples were analysed by ICP-MS for pseudo-total arsenic (As) concentrations and the results show clearly elevated levels, with maximum As concentrations of 486 microg g(-1) in housedusts and 471 microg g(-1) in garden soils (and mean concentrations of 149 microg g(-1) and 262 microg g(-1), respectively). Arsenic concentrations in all samples from the mining area exceeded the UK Soil Guideline Value (SGV) of 20 microg g(-1). No significant correlation was observed between garden soil and housedust As concentrations. Bioaccessible As concentrations were determined in a small subset of samples using the Physiologically Based Extraction Test (PBET). For the stomach phase of the PBET, bioaccessibility percentages of 10-20% were generally recorded. Higher percentages (generally 30-45%) were recorded in the intestine phases with a maximum value (for one of the housedusts) of 59%. Data from the mining area were used, together with default values for soil ingestion rates and infant body weights from the Contaminated Land Exposure Assessment (CLEA) model, to derive estimates of As intake for infants and small children (0-6 years old). Dose estimates of up to 3.53 microg kg(-1) bw day(-1) for housedusts and 2.43 microg kg(-1) bw day(-1) for garden soils were calculated, compared to the index dose used for the derivation of the SGV of 0.3 microg kg(-1) bw day(-1) (based on health risk assessments). The index dose was exceeded by 75% (18 out of 24) of the estimated As doses that were calculated for children aged 0-6 years, a group which is particularly at risk from exposure via soil and dust ingestion. The results of the present study support the concerns expressed by previous authors about the significant As contamination in southwest England and the potential implications for human health.
从英格兰西南部一个旧矿区附近的20户家庭以及一个对照村庄的9户家庭采集了室内灰尘和花园土壤样本。所有样本均通过电感耦合等离子体质谱法(ICP-MS)分析了总砷(As)浓度,结果显示浓度明显升高,室内灰尘中砷的最高浓度为486微克/克,花园土壤中为471微克/克(平均浓度分别为149微克/克和262微克/克)。矿区所有样本中的砷浓度均超过了英国土壤指导值(SGV)20微克/克。花园土壤和室内灰尘中的砷浓度之间未观察到显著相关性。使用基于生理学的提取试验(PBET)在一小部分样本中测定了生物可利用砷浓度。对于PBET的胃部阶段,通常记录的生物可及性百分比为10%-20%。在肠道阶段记录到更高的百分比(通常为30%-45%),其中一个室内灰尘样本的最高值为59%。来自矿区的数据与污染土地暴露评估(CLEA)模型中土壤摄入率和婴儿体重的默认值一起,用于估算婴儿和幼儿(0-6岁)的砷摄入量。计算得出室内灰尘的剂量估算值高达3.53微克/千克体重/天,花园土壤为2.43微克/千克体重/天,相比之下,用于推导SGV的指数剂量为0.3微克/千克体重/天(基于健康风险评估)。在为0-6岁儿童计算的估计砷剂量中,75%(24个中有18个)超过了指数剂量,该年龄段的儿童特别容易因摄入土壤和灰尘而受到暴露。本研究结果支持了先前作者对英格兰西南部严重砷污染及其对人类健康潜在影响所表达的担忧。