Ecology and Environment ›› 2024, Vol. 33 ›› Issue (4): 645-654.DOI: 10.16258/j.cnki.1674-5906.2024.04.015
• Research Article [Environmental Sciences] • Previous Articles Next Articles
JIANG Hao1,2(), WU Qitang1,*(
)
Received:
2024-01-12
Online:
2024-04-18
Published:
2024-05-31
Contact:
WU Qitang
通讯作者:
吴启堂
作者简介:
蒋皓(1990年生),男,博士,研究方向为污染场地风险评估和修复。E-mail: xpyhydhm@gmail.com
基金资助:
CLC Number:
JIANG Hao, WU Qitang. Probabilistic Analysis of the Health Risk Screening Errors in a Petroleum Hydrocarbon Contaminated Sensitive Site[J]. Ecology and Environment, 2024, 33(4): 645-654.
蒋皓, 吴启堂. 石油烃污染敏感场地健康风险筛选误差的概率方法分析[J]. 生态环境学报, 2024, 33(4): 645-654.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2024.04.015
参数 | 总石油烃 (C10‒C40) | |
---|---|---|
采样深度/m | 表层 (<1.0) | 下层 (>1.0) |
采集样品数 | 10 | 37 |
检出最大质量分数/(mg·kg-1) | 4123 | 1440 |
检出平均质量分数//(mg·kg-1) | 912 | 200 |
变异系数 | 1.66 | 1.43 |
Table 1 Statistics of detected contaminant in the test site
参数 | 总石油烃 (C10‒C40) | |
---|---|---|
采样深度/m | 表层 (<1.0) | 下层 (>1.0) |
采集样品数 | 10 | 37 |
检出最大质量分数/(mg·kg-1) | 4123 | 1440 |
检出平均质量分数//(mg·kg-1) | 912 | 200 |
变异系数 | 1.66 | 1.43 |
石油烃碳段 | 质量分数/% |
---|---|
脂肪烃C13‒C16 | 0.162 |
脂肪烃C17‒C21 | 0.342 |
脂肪烃C22‒C40 | 0.115 |
芳香烃C10‒C12 | 0.01 |
芳香烃C13‒C16 | 0.04 |
芳香烃C17‒C21 | 0.224 |
芳香烃C22‒C40 | 0.092 |
Table 2 Mass fractions of the hypotheses of petroleum hydrocarbons
石油烃碳段 | 质量分数/% |
---|---|
脂肪烃C13‒C16 | 0.162 |
脂肪烃C17‒C21 | 0.342 |
脂肪烃C22‒C40 | 0.115 |
芳香烃C10‒C12 | 0.01 |
芳香烃C13‒C16 | 0.04 |
芳香烃C17‒C21 | 0.224 |
芳香烃C22‒C40 | 0.092 |
参数 | 说明及单位 | 最可能值 | 区间 | 分布 |
---|---|---|---|---|
EDa | 成人暴露期, a | 24 | 对数正态 | |
EDc | 儿童暴露期, a | 6 | 对数正态 | |
EFa | 成人暴露频率, d·a-1 | 182‒350 | 均匀 | |
EFc | 儿童暴露频率, d·a-1 | 130‒315 | 均匀 | |
BWa | 成人平均体质量, kg | 61.8 | 对数正态 | |
BWc | 儿童平均体质量, kg | 19.2 | 对数正态 | |
DAIRa | 成人每日空气呼吸量, m3·d-1 | 14.5 | 对数正态 | |
DAIRc | 儿童每日空气呼吸量, m3·d-1 | 7.5 | 对数正态 | |
OSIRa | 成人每日摄入土壤量, mg·d-1 | 100 | 对数正态 | |
OSIRc | 儿童每日摄入土壤量, mg·d-1 | 120 | 对数正态 | |
Ev | 每日皮肤接触事件频率 | 1 | 对数正态 | |
SERa | 成人暴露皮肤所占体表面积比 | 0.32 | 对数正态 | |
SERc | 儿童暴露皮肤所占体表面积比 | 0.36 | 对数正态 | |
LB | 室内空间体积与气态污染物 入渗面积之比 (层高), cm | 300 | 280‒450 | 三角 |
ER | 室内空气交换速率, d-1 | 20 | 12‒28 | 三角 |
τ | 气态污染物入侵持续时间, a | 25 | 20‒30 | 三角 |
Table 3 List of exposure parameters containing ranges of uncertainties in the test site
参数 | 说明及单位 | 最可能值 | 区间 | 分布 |
---|---|---|---|---|
EDa | 成人暴露期, a | 24 | 对数正态 | |
EDc | 儿童暴露期, a | 6 | 对数正态 | |
EFa | 成人暴露频率, d·a-1 | 182‒350 | 均匀 | |
EFc | 儿童暴露频率, d·a-1 | 130‒315 | 均匀 | |
BWa | 成人平均体质量, kg | 61.8 | 对数正态 | |
BWc | 儿童平均体质量, kg | 19.2 | 对数正态 | |
DAIRa | 成人每日空气呼吸量, m3·d-1 | 14.5 | 对数正态 | |
DAIRc | 儿童每日空气呼吸量, m3·d-1 | 7.5 | 对数正态 | |
OSIRa | 成人每日摄入土壤量, mg·d-1 | 100 | 对数正态 | |
OSIRc | 儿童每日摄入土壤量, mg·d-1 | 120 | 对数正态 | |
Ev | 每日皮肤接触事件频率 | 1 | 对数正态 | |
SERa | 成人暴露皮肤所占体表面积比 | 0.32 | 对数正态 | |
SERc | 儿童暴露皮肤所占体表面积比 | 0.36 | 对数正态 | |
LB | 室内空间体积与气态污染物 入渗面积之比 (层高), cm | 300 | 280‒450 | 三角 |
ER | 室内空气交换速率, d-1 | 20 | 12‒28 | 三角 |
τ | 气态污染物入侵持续时间, a | 25 | 20‒30 | 三角 |
误差种类 | 性质 | 健康风险影响 | 经济效益影响 |
---|---|---|---|
“敏感/非敏感” 用地界定 | 误差A (低估) | 遗留健康风险 | 可能使场地调查 提前结束 |
非居住性敏感用地按居住用地评估 | 误差B (高估) | 较小 | 可能造成过度修复 |
复杂有机物组分 | 误差B (高估) | 较小 | 可能造成过度修复 |
Table 4 Characteristics of the typical errors in the health risk assessment of contaminated site
误差种类 | 性质 | 健康风险影响 | 经济效益影响 |
---|---|---|---|
“敏感/非敏感” 用地界定 | 误差A (低估) | 遗留健康风险 | 可能使场地调查 提前结束 |
非居住性敏感用地按居住用地评估 | 误差B (高估) | 较小 | 可能造成过度修复 |
复杂有机物组分 | 误差B (高估) | 较小 | 可能造成过度修复 |
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