Article(id=1321169806561231707, tenantId=1146029695717560320, journalId=1319373219989389464, issueId=1321169735128043598, articleNumber=null, orderNo=null, doi=10.11847/zgggws1146582, pmid=null, cstr=null, oa=null, hot=null, price=null, onlineType=0, articleFormat=0, articleType=null, articleTypeStr=null, receivedDate=1735833600000, receivedDateStr=2025-01-03, revisedDate=1739462400000, revisedDateStr=2025-02-14, acceptedDate=1744387200000, acceptedDateStr=2025-04-12, onlineDate=1792921028031, onlineDateStr=2026-10-25, pubDate=1752076800000, pubDateStr=2025-07-10, doiRegisterDate=null, doiRegisterDateStr=null, onlineIssueDate=1792921028031, onlineIssueDateStr=2026-10-25, onlineJustAcceptDate=null, onlineJustAcceptDateStr=null, onlineFirstDate=null, onlineFirstDateStr=null, sourceXml=null, magXml=null, createTime=1792921028031, creator=13701087609, updateTime=1792921028031, updator=13701087609, issue=Issue{id=1321169735128043598, tenantId=1146029695717560320, journalId=1319373219989389464, year='2025', volume='41', issue='7', pageStart='769', pageEnd='896', issueExtLink='null', onlineDate='null', pubDate='1752076800000', pubDateStr='2025-07-10', beforeIssueId=null, nextIssueId=null, price=null, status=1, issueComplete=1, articleOrder=1, issueType=-1, specialIssue=null, createTime=1792921011000, creator='13701087609', updateTime=1792921011000, updator='13701087609', preIssue=null, nextIssue=null, articleTotal=null, ext=null, issueFiles=null, downloadFileDto=null}, startPage=841, endPage=847, ext={EN=ArticleExt(id=1321169806754169692, articleId=1321169806561231707, tenantId=1146029695717560320, journalId=1319373219989389464, language=EN, title=Construction of a public health risk assessment index system for emergency water pollution incidents, columnId=1320427686514770171, journalTitle=Chinese Journal of Public Health, columnName=Survey and Report, runingTitle=null, highlight=null, articleAbstract=
Objective To construct a public health risk assessment index system for sudden water pollution incidents to provide a reference tool for conducting public health risk assessments of such incidents.
Methods An initial index list was established through literature review and group discussions. A two-round Delphi expert consultation method was employed to evaluate and screen the indicators, and a comprehensive integration empowerment method was used to calculate indicator weights.
Results The expert positive coefficients for the two rounds of consultation were 83.33% and 100.00%, respectively, and the authority coefficients were (0.79 ± 0.11) and (0.82 ± 0.08), respectively. The overall Kendall′s W values were 0.250 and 0.460 (both P < 0.001). Finally, 4 first-level indicators, 17 second-level indicators, and 66 third-level indicators were established. The top three third-level indicators by weight were the speed of emergency resource allocation (0.049 9), regular monitoring of drinking water quality by the jurisdictional water quality supervision department with monitoring items covering the conventional indicators listed in GB 5749 - 2022 (0.044 4), and the professional and technical level of emergency personnel (0.039 1).
Conclusions The constructed public health risk assessment index system for sudden water pollution incidents provides a reference for the health emergency response to water pollution incidents.
, authors=Yanjun REN, Hong XU, Tao JIN, Ye LYU, Shanshan XU, Bing GAO, Chaokang LI, authorsList=Yanjun REN, Hong XU, Tao JIN, Ye LYU, Shanshan XU, Bing GAO, Chaokang LI, authorCompany=null, correspAuthors=Hong XU, authorNote=null, correspAuthorsNote=
, copyrightStatement=Copyright © 2025 Chinese Journal of Public Health. All rights reserved., copyrightOwner=null, extLink=null, articleAbsUrl=null, sourceXml=null, magXml=null, pdfUrl=null, pdf=null, pdfFileSize=null, pdfExtLink=null, richHtmlUrl=null, mobilePdfUrl=null, reviewReport=null, pdfFirstPage=null, abstractGraph=null, abstractGraphContent=null, abstractVideo=null, citation=null, cebUrl=null, magXmlContent=null, mapNumber=null, fund=null), CN=ArticleExt(id=1321169807144239965, articleId=1321169806561231707, tenantId=1146029695717560320, journalId=1319373219989389464, language=CN, title=突发水污染事件公共卫生风险评估指标体系构建, columnId=1320427686770622717, journalTitle=中国公共卫生, columnName=调查报告与分析, runingTitle=null, highlight=null, articleAbstract=
目的 构建突发水污染事件公共卫生风险评估指标体系，为开展突发事件的公共卫生风险评估提供参考工具。
方法 通过文献研究和小组讨论建立指标清单，采用两轮德尔菲专家咨询法评价和筛选指标，利用综合集成赋权法计算指标权重。
结果 两轮咨询的专家积极系数分别为83.33%和100.00%，权威系数分别为（0.79±0.11）和（0.82±0.08），总体Kendall′s W分别为0.250和0.460（均P<0.001）。最终确立4个一级指标、17个二级指标和66个三级指标。指标权重居前3位的三级指标依次是应急资源调配速率（0.049 9）、辖区水质监管部门定期开展生活饮用水水质监测且监测项目覆盖GB 5749—2022所列的常规指标（0.044 4）和应急人员专业技术水平（0.039 1）。
结论 构建的突发水污染事件公共卫生风险指标体系为水污染事件的卫生应急处置提供参考依据。
, authors=任艳军, 徐虹
*, *, 金涛, 吕烨, 徐珊珊, 高兵, 李朝康, authorsList=任艳军, 徐虹, 金涛, 吕烨, 徐珊珊, 高兵, 李朝康, authorCompany=null, correspAuthors=徐虹, authorNote=
任艳军（1980—），主任医师，硕士，研究方向：疾病预防与控制
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Degree of concentration and coordination of expert opinions in two rounds
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| 指标 | 条目数 | 重要性 | | 可行性 | | 敏感性 |
|---|
| 均数 | 变异系数 | Kendall′s W | | 均数 | 变异系数 | Kendall′s W | | 均数 | 变异系数 | Kendall′s W |
|---|
| 第1轮 | | | | | | | | | | | | |
| 一级指标 | 4 | 8.47～8.93 | 0.12～0.14 | 0.087a | | 7.40～8.53 | 0.14～0.28 | 0.199 | | 7.87～8.60 | 0.13～0.18 | 0.120 |
| 二级指标 | 18 | 7.47～9.00 | 0.09～0.21 | 0.400 | | 7.00～9.00 | 0.12～0.32 | 0.470 | | 7.07～8.87 | 0.13～0.22 | 0.327 |
| 三级指标 | 81 | 5.93～9.00 | 0.11～0.53 | 0.259 | | 6.20～9.07 | 0.10～0.51 | 0.298 | | 5.29～8.93 | 0.11～0.56 | 0.262 |
| 合计 | 103 | 5.93～9.00 | 0.09～0.53 | 0.276 | | 6.20～9.07 | 0.10～0.51 | 0.314 | | 5.29～8.93 | 0.11～0.56 | 0.261 |
| 第2轮 | | | | | | | | | | | | |
| 一级指标 | 4 | 8.27～9.07 | 0.03～0.09 | 0.421 | | 7.73～8.80 | 0.10～0.12 | 0.448 | | 7.80～8.67 | 0.07～0.12 | 0.430 |
| 二级指标 | 17 | 7.67～9.20 | 0.04～0.11 | 0.684 | | 7.20～9.00 | 0.06～0.17 | 0.602 | | 7.33～9.00 | 0.06～0.12 | 0.588 |
| 三级指标 | 66 | 7.40～9.20 | 0.04～0.13 | 0.434 | | 7.40～9.07 | 0.05～0.15 | 0.469 | | 7.13～9.00 | 0.05～0.13 | 0.485 |
| 合计 | 87 | 7.40～9.20 | 0.03～0.13 | 0.478 | | 7.20～9.07 | 0.10～0.17 | 0.499 | | 7.13～9.00 | 0.05～0.13 | 0.495 |
), ArticleFig(id=1321169813964178321, tenantId=1146029695717560320, journalId=1319373219989389464, articleId=1321169806561231707, language=CN, label=表1, caption=
两轮专家咨询意见的集中程度和协调程度
, figureFileSmall=null, figureFileBig=null, tableContent=
| 指标 | 条目数 | 重要性 | | 可行性 | | 敏感性 |
|---|
| 均数 | 变异系数 | Kendall′s W | | 均数 | 变异系数 | Kendall′s W | | 均数 | 变异系数 | Kendall′s W |
|---|
| 第1轮 | | | | | | | | | | | | |
| 一级指标 | 4 | 8.47～8.93 | 0.12～0.14 | 0.087a | | 7.40～8.53 | 0.14～0.28 | 0.199 | | 7.87～8.60 | 0.13～0.18 | 0.120 |
| 二级指标 | 18 | 7.47～9.00 | 0.09～0.21 | 0.400 | | 7.00～9.00 | 0.12～0.32 | 0.470 | | 7.07～8.87 | 0.13～0.22 | 0.327 |
| 三级指标 | 81 | 5.93～9.00 | 0.11～0.53 | 0.259 | | 6.20～9.07 | 0.10～0.51 | 0.298 | | 5.29～8.93 | 0.11～0.56 | 0.262 |
| 合计 | 103 | 5.93～9.00 | 0.09～0.53 | 0.276 | | 6.20～9.07 | 0.10～0.51 | 0.314 | | 5.29～8.93 | 0.11～0.56 | 0.261 |
| 第2轮 | | | | | | | | | | | | |
| 一级指标 | 4 | 8.27～9.07 | 0.03～0.09 | 0.421 | | 7.73～8.80 | 0.10～0.12 | 0.448 | | 7.80～8.67 | 0.07～0.12 | 0.430 |
| 二级指标 | 17 | 7.67～9.20 | 0.04～0.11 | 0.684 | | 7.20～9.00 | 0.06～0.17 | 0.602 | | 7.33～9.00 | 0.06～0.12 | 0.588 |
| 三级指标 | 66 | 7.40～9.20 | 0.04～0.13 | 0.434 | | 7.40～9.07 | 0.05～0.15 | 0.469 | | 7.13～9.00 | 0.05～0.13 | 0.485 |
| 合计 | 87 | 7.40～9.20 | 0.03～0.13 | 0.478 | | 7.20～9.07 | 0.10～0.17 | 0.499 | | 7.13～9.00 | 0.05～0.13 | 0.495 |
), ArticleFig(id=1321169814064841618, tenantId=1146029695717560320, journalId=1319373219989389464, articleId=1321169806561231707, language=EN, label=Tab.2, caption=
Index adjustment of the two rounds of expert consultation
, figureFileSmall=null, figureFileBig=null, tableContent=
| 轮次 | 调整前指标 | 调整情况 | 调整后指标 | 修改依据 |
|---|
| 第1轮 | 经济损失 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 近1年水源水污染物浓度监测不合格率 | 删除 | | 重要性和敏感性评分不达标 |
| 慢性中毒 | 删除 | | 可行性和敏感性评分不达标 |
| 对睡眠质量的影响 | 删除 | | 重要性和可行性和敏感性评分均不达标 |
| 洪涝灾害后的心理和行为应激水平 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 水源种类复杂 | 删除 | | 可行性和敏感性评分不达标 |
| 人口流动性 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 辖区人口密度 | 删除 | | 重要性和可行性评分不达标 |
| 辖区预防相关疾病的疫苗接种率 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 人群受教育程度 | 删除 | | 可行性和敏感性评分不达标 |
| 水质信息公开制度及执行 | 删除 | | 可行性和敏感性评分不达标 |
| 饮用水不安全的担心、焦虑和恐惧 | 删除 | | 敏感性评分不达标，小组讨论后删除 |
| 水污染造成城市饮用水处理需付出的额外成本 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 城市居民因担心水污染影响健康而采用家庭自来水净化防护措施的成本 | 删除 | | 敏感性评分不达标，小组讨论后删除 |
| 水污染的应对技能 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 应急响应效率 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 应急资源共享整合能力 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 5年内发生水污染相关的投诉举报 | 删除 | | 专家认为投诉举报应经过核实，小组讨论后删除 |
| 当地近3年水源水污染物监测浓度的变化趋势 | 修改 | 当地近5年水源水污染物监测浓度的变化趋势 | 专家建议污染物浓度监测时限和外部反应性时限一致，
小组讨论后统一修改为5年 |
| 当地近3年生活饮用水污染物监测浓度的变化趋势 | 修改 | 当地近5年生活饮用水污染物监测
浓度的变化趋势 | 专家建议污染物浓度监测时限和外部反应性时限一致，
小组讨论后统一修改为5年 |
| 近1年生活饮用水污染物浓度监测不合格率 | 修改 | 近5年生活饮用水污染物浓度监测
不合格率 | 专家建议污染物浓度监测时限和外部反应性时限一致，小组讨论后统一修改为5年 |
| 二次供水消毒剂指标在线实时监测 | 修改 | 二次供水消毒剂指标在线实时监测且定期计量认证 | 专家认为在线监测仪需要定期计量认证，
小组讨论后修改 |
| 5年内发生突发水污染事件 | 修改 | 近5年内发生突发水污染事件的数量 | 专家认为5年内突发水污染事件的发生数量可以更好
反映极端天气事件如洪涝台风的影响程度和地区应对
能力，小组讨论后通过修改 |
| 健康宣教力度 | 修改 | 应急信息传播/发布力度 | 专家建议修改，小组讨论后修改 |
| 应急资源（人财物）储备情况 | 修改 | 应急资源储备情况 | 专家认为表述存在重复，小组讨论后修改 |
| | 增加 | 辖区人口数 | 专家建议增加，小组讨论通过 |
| | 增加 | 应急供水能力 | 专家认为应急供水能力是应急响应的重要环节，
建议增加，小组讨论通过 |
| 第2轮 | 二次供水消毒剂指标在线实时监测且定期计量认证 | 修改 | 二次供水消毒剂指标在线实时监测且定期检定校准 | 专家建议修改，小组讨论后修改 |
| | 排水管与污水管相连 | 修改 | 排水管与污水管不相连 | 专家建议修改，小组讨论后修改 |
), ArticleFig(id=1321169814152922003, tenantId=1146029695717560320, journalId=1319373219989389464, articleId=1321169806561231707, language=CN, label=表2, caption=
两轮专家咨询的指标调整情况
, figureFileSmall=null, figureFileBig=null, tableContent=
| 轮次 | 调整前指标 | 调整情况 | 调整后指标 | 修改依据 |
|---|
| 第1轮 | 经济损失 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 近1年水源水污染物浓度监测不合格率 | 删除 | | 重要性和敏感性评分不达标 |
| 慢性中毒 | 删除 | | 可行性和敏感性评分不达标 |
| 对睡眠质量的影响 | 删除 | | 重要性和可行性和敏感性评分均不达标 |
| 洪涝灾害后的心理和行为应激水平 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 水源种类复杂 | 删除 | | 可行性和敏感性评分不达标 |
| 人口流动性 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 辖区人口密度 | 删除 | | 重要性和可行性评分不达标 |
| 辖区预防相关疾病的疫苗接种率 | 删除 | | 重要性、可行性和敏感性评分均不达标 |
| 人群受教育程度 | 删除 | | 可行性和敏感性评分不达标 |
| 水质信息公开制度及执行 | 删除 | | 可行性和敏感性评分不达标 |
| 饮用水不安全的担心、焦虑和恐惧 | 删除 | | 敏感性评分不达标，小组讨论后删除 |
| 水污染造成城市饮用水处理需付出的额外成本 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 城市居民因担心水污染影响健康而采用家庭自来水净化防护措施的成本 | 删除 | | 敏感性评分不达标，小组讨论后删除 |
| 水污染的应对技能 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 应急响应效率 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 应急资源共享整合能力 | 删除 | | 可行性评分不达标，小组讨论后删除 |
| 5年内发生水污染相关的投诉举报 | 删除 | | 专家认为投诉举报应经过核实，小组讨论后删除 |
| 当地近3年水源水污染物监测浓度的变化趋势 | 修改 | 当地近5年水源水污染物监测浓度的变化趋势 | 专家建议污染物浓度监测时限和外部反应性时限一致，
小组讨论后统一修改为5年 |
| 当地近3年生活饮用水污染物监测浓度的变化趋势 | 修改 | 当地近5年生活饮用水污染物监测
浓度的变化趋势 | 专家建议污染物浓度监测时限和外部反应性时限一致，
小组讨论后统一修改为5年 |
| 近1年生活饮用水污染物浓度监测不合格率 | 修改 | 近5年生活饮用水污染物浓度监测
不合格率 | 专家建议污染物浓度监测时限和外部反应性时限一致，小组讨论后统一修改为5年 |
| 二次供水消毒剂指标在线实时监测 | 修改 | 二次供水消毒剂指标在线实时监测且定期计量认证 | 专家认为在线监测仪需要定期计量认证，
小组讨论后修改 |
| 5年内发生突发水污染事件 | 修改 | 近5年内发生突发水污染事件的数量 | 专家认为5年内突发水污染事件的发生数量可以更好
反映极端天气事件如洪涝台风的影响程度和地区应对
能力，小组讨论后通过修改 |
| 健康宣教力度 | 修改 | 应急信息传播/发布力度 | 专家建议修改，小组讨论后修改 |
| 应急资源（人财物）储备情况 | 修改 | 应急资源储备情况 | 专家认为表述存在重复，小组讨论后修改 |
| | 增加 | 辖区人口数 | 专家建议增加，小组讨论通过 |
| | 增加 | 应急供水能力 | 专家认为应急供水能力是应急响应的重要环节，
建议增加，小组讨论通过 |
| 第2轮 | 二次供水消毒剂指标在线实时监测且定期计量认证 | 修改 | 二次供水消毒剂指标在线实时监测且定期检定校准 | 专家建议修改，小组讨论后修改 |
| | 排水管与污水管相连 | 修改 | 排水管与污水管不相连 | 专家建议修改，小组讨论后修改 |
), ArticleFig(id=1321169814249390996, tenantId=1146029695717560320, journalId=1319373219989389464, articleId=1321169806561231707, language=EN, label=Tab.3, caption=
Scoring and weighting of the public health risk assessment index system for emergency water pollution incidents
, figureFileSmall=null, figureFileBig=null, tableContent=
| 指标内容 | 重要性/分 | 可行性/分 | 敏感性/分 | 综合得分/分 | 专家评分权重 | 熵权法权重 | 综合权重 |
|---|
| 1 可能性 | 8.87 | 8.27 | 8.20 | 8.51 | 0.380 6 | 0.372 9 | 0.373 4 |
| 1.1 污染物监测浓度 | 9.00 | 8.67 | 8.67 | 8.85 | 0.046 0 | 0.052 0 | 0.052 8 |
| 1.1.1 当地近5年水源水污染物监测浓度的变化趋势 | 8.60 | 8.87 | 8.13 | 8.51 | 0.015 4 | 0.026 4 | 0.026 8 |
| 1.1.2 当地近5年生活饮用水污染物监测浓度的变化趋势 | 8.67 | 9.00 | 8.20 | 8.59 | 0.015 5 | 0.017 6 | 0.018 0 |
| 1.1.3 近5年生活饮用水污染物浓度监测不合格率 | 8.27 | 8.93 | 8.07 | 8.35 | 0.015 1 | 0.008 0 | 0.008 0 |
| 1.2 污染源 | 9.07 | 8.00 | 8.60 | 8.74 | 0.093 4 | 0.079 0 | 0.080 9 |
| 1.2.1 洪涝灾害引起水源污染物种类或数量增多 | 8.33 | 8.07 | 8.53 | 8.31 | 0.015 0 | 0.017 8 | 0.017 6 |
| 1.2.2 水源上游存在工农业和生活污染 | 9.00 | 8.53 | 8.53 | 8.76 | 0.015 8 | 0.017 7 | 0.018 4 |
| 1.2.3 水源受人为因素 (如投毒或交通事故)污染 | 9.00 | 8.40 | 8.60 | 8.80 | 0.015 9 | 0.015 6 | 0.016 3 |
1.2.4 水厂区30 m范围内存在污染源，生产区外围30米范围内有生活居住区、渗水厕所
和垃圾堆放场等 | 8.87 | 8.93 | 8.47 | 8.73 | 0.015 8 | 0.009 1 | 0.009 5 |
| 1.2.5 供水设施周围15米内存在污水井、化粪池等污染源 | 8.73 | 8.67 | 8.33 | 8.58 | 0.015 5 | 0.010 6 | 0.010 8 |
| 1.2.6 二次供水水箱/蓄水池10 m范围内存在污染源 | 8.60 | 8.53 | 8.40 | 8.52 | 0.015 4 | 0.008 2 | 0.008 3 |
| 1.3 水厂处理工艺 | 8.67 | 8.87 | 8.27 | 8.61 | 0.105 3 | 0.114 1 | 0.113 0 |
| 1.3.1 根据水源水质情况配置了适宜的净水工艺且设施工作正常 | 9.00 | 9.07 | 8.80 | 8.99 | 0.016 3 | 0.008 7 | 0.009 3 |
| 1.3.2 有消毒设备且能正常使用，正确选用消毒剂，并在供水期间连续投加且准确计量 | 8.87 | 9.07 | 8.53 | 8.81 | 0.015 9 | 0.017 9 | 0.018 8 |
| 1.3.3 按规定清洗和维护水处理设施和设备，并按要求更换水处理材料 | 8.67 | 8.80 | 8.33 | 8.65 | 0.015 6 | 0.025 1 | 0.025 8 |
| 1.3.4 水厂设计处理能力大于实际供水规模 | 7.80 | 8.27 | 7.60 | 7.84 | 0.014 2 | 0.020 5 | 0.019 2 |
| 1.3.5 涉水产品批件资质与许可 | 8.13 | 8.80 | 7.60 | 8.04 | 0.014 5 | 0.014 7 | 0.014 0 |
| 1.3.6 人员考核培训制度 | 8.13 | 8.40 | 7.20 | 7.81 | 0.014 1 | 0.010 7 | 0.009 9 |
| 1.3.7 具有备用水源 | 8.27 | 8.33 | 8.00 | 8.15 | 0.014 7 | 0.016 5 | 0.016 0 |
| 1.4 输配管网 | 8.60 | 8.47 | 8.20 | 8.39 | 0.060 5 | 0.067 7 | 0.068 0 |
| 1.4.1 输配水管选材适宜 | 8.33 | 8.93 | 7.80 | 8.31 | 0.015 0 | 0.014 9 | 0.014 7 |
| 1.4.2 输配管道定期巡查、检修和保养 | 8.40 | 8.60 | 7.80 | 8.27 | 0.015 0 | 0.020 5 | 0.020 3 |
| 1.4.3 配水管网漏损率低于20% | 8.13 | 8.40 | 7.87 | 8.09 | 0.014 6 | 0.010 3 | 0.009 9 |
| 1.4.4 排水管与污水管不相连 | 9.00 | 8.53 | 8.60 | 8.79 | 0.015 9 | 0.022 0 | 0.023 1 |
| 1.5 二次供水 | 8.67 | 8.87 | 8.33 | 8.57 | 0.075 4 | 0.060 1 | 0.058 7 |
| 1.5.1 二次供水水箱定期清洗消毒 | 9.13 | 8.93 | 8.67 | 9.00 | 0.016 3 | 0.007 0 | 0.007 5 |
| 1.5.2 二次供水消毒剂指标在线实时监测且定期校准维护 | 8.47 | 8.27 | 8.13 | 8.31 | 0.015 0 | 0.009 4 | 0.009 3 |
| 1.5.3 二次供水泵房环境状况 | 8.07 | 8.67 | 7.80 | 8.18 | 0.014 8 | 0.011 5 | 0.011 2 |
| 1.5.4 设有透气管、溢水管和泄水管并装有溢水孔网罩 | 8.40 | 8.80 | 8.00 | 8.36 | 0.015 1 | 0.009 5 | 0.009 5 |
| 1.5.5 清洗消毒人员持健康证上岗 | 8.07 | 8.53 | 7.20 | 7.84 | 0.014 2 | 0.022 7 | 0.021 2 |
| 2 危害性 | 9.07 | 8.80 | 8.67 | 8.93 | 0.105 0 | 0.081 0 | 0.081 1 |
| 2.1 水体感官异常 | 9.07 | 9.00 | 9.00 | 9.03 | 0.032 2 | 0.027 1 | 0.029 0 |
| 2.1.1 水源水出现浑浊、红虫、异味 | 8.67 | 8.80 | 8.67 | 8.70 | 0.015 7 | 0.010 4 | 0.010 8 |
| 2.1.2 龙头水出现浑浊、红虫、异味 | 9.20 | 9.07 | 9.00 | 9.13 | 0.016 5 | 0.016 7 | 0.018 2 |
| 2.2 水污染相关疾病 | 8.93 | 7.87 | 8.53 | 8.57 | 0.045 5 | 0.038 7 | 0.038 5 |
| 2.2.1 介水传染病病例数量 | 8.93 | 8.27 | 8.60 | 8.65 | 0.015 6 | 0.011 1 | 0.011 4 |
| 2.2.2 经皮肤急性中毒 | 8.60 | 7.47 | 8.27 | 8.20 | 0.014 8 | 0.015 7 | 0.015 3 |
| 2.2.3 经口急性中毒 | 8.80 | 7.47 | 8.40 | 8.33 | 0.015 1 | 0.011 9 | 0.011 8 |
| 2.3 人群心理健康 | 7.87 | 7.20 | 7.60 | 7.59 | 0.027 3 | 0.015 2 | 0.013 6 |
| 2.3.1 对突发水污染事件的接受程度 | 7.67 | 7.60 | 7.27 | 7.51 | 0.013 6 | 0.008 4 | 0.007 5 |
| 2.3.2 对政府处理事件能力的信任程度 | 8.00 | 7.53 | 7.20 | 7.57 | 0.013 7 | 0.006 8 | 0.006 1 |
| 3 脆弱性 | 8.27 | 7.73 | 7.87 | 8.01 | 0.178 1 | 0.149 6 | 0.144 6 |
| 3.1 监测能力 | 9.13 | 9.00 | 8.87 | 9.04 | 0.031 9 | 0.015 9 | 0.016 8 |
| 3.1.1 水污染物实时监测 | 9.07 | 8.60 | 8.87 | 8.94 | 0.016 2 | 0.008 5 | 0.009 1 |
| 3.1.2 常规污染物监测指标数量 | 8.60 | 8.93 | 8.47 | 8.67 | 0.015 7 | 0.007 4 | 0.007 7 |
| 3.2 污染物消除 | 9.20 | 8.27 | 8.80 | 8.93 | 0.031 9 | 0.026 9 | 0.028 2 |
| 3.2.1 水处理工艺能解决原水的主要污染物 | 9.00 | 8.80 | 8.67 | 8.91 | 0.016 1 | 0.009 8 | 0.010 4 |
| 3.2.2 在传统工艺基础上，增加深度净化处理工艺如混凝沉淀、臭氧活性炭等 | 8.73 | 8.47 | 8.60 | 8.72 | 0.015 8 | 0.017 1 | 0.017 8 |
| 3.3 外部反应性 | 7.73 | 7.53 | 7.73 | 7.81 | 0.042 2 | 0.048 0 | 0.044 2 |
| 3.3.1 近5年内发生突发水污染事件的数量 | 8.13 | 8.53 | 7.87 | 8.22 | 0.014 9 | 0.010 2 | 0.010 0 |
| 3.3.2 近5年内水污染相关的媒体新闻负面报道 | 7.60 | 7.93 | 7.33 | 7.62 | 0.013 8 | 0.029 8 | 0.027 1 |
| 3.3.3 近5年内水污染相关的行政处罚 | 7.40 | 7.93 | 7.13 | 7.44 | 0.013 5 | 0.008 0 | 0.007 1 |
| 3.4人群易感性 | 7.87 | 7.47 | 7.53 | 7.70 | 0.029 6 | 0.016 8 | 0.016 4 |
| 3.4.1.辖区脆弱人群（老年人、儿童、孕妇、慢性病人等）比例 | 8.47 | 7.87 | 7.80 | 8.14 | 0.014 7 | 0.006 0 | 0.005 8 |
| 3.4.2 辖区常住人口数 | 8.13 | 8.67 | 7.80 | 8.23 | 0.014 9 | 0.010 8 | 0.010 6 |
| 3.5人群适应性 | 7.67 | 7.27 | 7.33 | 7.51 | 0.042 5 | 0.042 0 | 0.039 0 |
| 3.5.1 生活饮水习惯 | 8.27 | 8.07 | 8.07 | 8.19 | 0.014 8 | 0.012 3 | 0.012 0 |
| 3.5.2 水污染危害知识的掌握情况 | 8.13 | 7.53 | 7.80 | 7.90 | 0.014 3 | 0.012 9 | 0.012 2 |
| 3.5.3 人群对安全防范体系的信赖程度 | 7.60 | 7.40 | 7.13 | 7.40 | 0.013 4 | 0.016 8 | 0.014 8 |
| 4 可控性 | 8.67 | 7.87 | 7.80 | 8.11 | 0.320 4 | 0.369 3 | 0.372 8 |
| 4.1 水质监管 | 9.07 | 8.80 | 8.27 | 8.78 | 0.091 0 | 0.100 9 | 0.101 4 |
| 4.1.1 划定水源一级防护区并有完善的巡查记录 | 8.53 | 8.93 | 7.93 | 8.43 | 0.015 3 | 0.026 2 | 0.026 4 |
| 4.1.2 1000 m3/d以上水厂具有水质实验室并定期开展水质检测 | 8.60 | 7.93 | 7.93 | 8.19 | 0.014 8 | 0.006 5 | 0.006 3 |
| 4.1.3 自检或小型水厂进行定期送样检测且采样、送检记录完整 | 8.53 | 8.20 | 7.93 | 8.20 | 0.014 8 | 0.005 6 | 0.005 5 |
| 4.1.4 辖区水质监管部门具有GB5749—2022所列常规和扩展项目的检测能力 | 8.47 | 8.67 | 8.20 | 8.39 | 0.015 2 | 0.010 6 | 0.010 6 |
4.1.5 辖区水质监管部门定期开展生活饮用水水质监测，监测项目覆盖
GB5749—2022所列的常规指标 | 8.53 | 8.53 | 8.27 | 8.48 | 0.015 3 | 0.044 0 | 0.044 4 |
| 4.1.6 饮用水污染物快速检测能力 | 8.87 | 8.27 | 8.40 | 8.62 | 0.015 6 | 0.008 0 | 0.008 2 |
| 4.2 预警体系 | 9.13 | 8.60 | 8.67 | 8.95 | 0.077 2 | 0.069 3 | 0.070 7 |
| 4.2.1 制定突发水污染事件的应急预案 | 8.87 | 8.80 | 8.53 | 8.73 | 0.015 8 | 0.026 7 | 0.027 8 |
| 4.2.2 预案可操作性、完整性和演练情况 | 8.80 | 8.40 | 8.40 | 8.59 | 0.015 5 | 0.009 2 | 0.009 4 |
| 4.2.3 对重点风险的主动监控力度 | 8.80 | 8.20 | 8.67 | 8.66 | 0.015 7 | 0.009 5 | 0.009 8 |
| 4.2.4 突发事件报告及时性、完整性和准确性 | 8.87 | 8.60 | 8.27 | 8.65 | 0.015 6 | 0.010 7 | 0.011 0 |
| 4.2.5 前期预报结果回溯评价 | 8.20 | 8.20 | 7.73 | 8.06 | 0.014 6 | 0.013 2 | 0.012 7 |
| 4.3 应急响应 | 8.87 | 8.60 | 8.47 | 8.70 | 0.090 6 | 0.078 0 | 0.077 6 |
| 4.3.1 突发水污染应急管理联动机制 | 8.87 | 8.40 | 8.47 | 8.67 | 0.015 7 | 0.021 7 | 0.022 5 |
| 4.3.2 事件性质研判时间效率 | 8.93 | 7.93 | 8.73 | 8.67 | 0.015 7 | 0.006 6 | 0.006 8 |
| 4.3.3 预案执行程度 | 8.67 | 8.00 | 8.13 | 8.36 | 0.015 1 | 0.008 3 | 0.008 3 |
| 4.3.4 群众疏散安置率 | 8.20 | 7.73 | 7.93 | 7.99 | 0.014 5 | 0.017 0 | 0.016 2 |
| 4.3.5 病患应急转运与救治能力 | 8.33 | 8.27 | 8.07 | 8.20 | 0.014 8 | 0.010 5 | 0.010 2 |
| 4.3.6 应急信息传播/发布力度 | 8.27 | 8.20 | 7.93 | 8.17 | 0.014 8 | 0.013 9 | 0.013 6 |
| 4.3.7 应急供水能力 | 8.93 | 8.20 | 8.40 | 8.58 | 0.015 5 | 0.027 3 | 0.027 9 |
| 4.4 资源保障 | 8.67 | 8.27 | 8.07 | 8.36 | 0.061 6 | 0.121 1 | 0.123 1 |
| 4.4.1 应急资源储备情况 | 8.93 | 8.87 | 8.40 | 8.73 | 0.015 8 | 0.020 5 | 0.021 3 |
| 4.4.2 应急资源调配速率 | 8.53 | 8.53 | 8.47 | 8.53 | 0.015 4 | 0.049 2 | 0.049 9 |
| 4.4.3 应急人员专业技术水平 | 8.60 | 8.53 | 8.33 | 8.53 | 0.015 4 | 0.038 5 | 0.039 1 |
| 4.4.4 法规政策保障情况 | 8.47 | 8.33 | 8.00 | 8.28 | 0.015 0 | 0.012 9 | 0.012 8 |
), ArticleFig(id=1321169814354248597, tenantId=1146029695717560320, journalId=1319373219989389464, articleId=1321169806561231707, language=CN, label=表3, caption=
突发水污染事件公共卫生风险评估指标体系的得分与权重
, figureFileSmall=null, figureFileBig=null, tableContent=
| 指标内容 | 重要性/分 | 可行性/分 | 敏感性/分 | 综合得分/分 | 专家评分权重 | 熵权法权重 | 综合权重 |
|---|
| 1 可能性 | 8.87 | 8.27 | 8.20 | 8.51 | 0.380 6 | 0.372 9 | 0.373 4 |
| 1.1 污染物监测浓度 | 9.00 | 8.67 | 8.67 | 8.85 | 0.046 0 | 0.052 0 | 0.052 8 |
| 1.1.1 当地近5年水源水污染物监测浓度的变化趋势 | 8.60 | 8.87 | 8.13 | 8.51 | 0.015 4 | 0.026 4 | 0.026 8 |
| 1.1.2 当地近5年生活饮用水污染物监测浓度的变化趋势 | 8.67 | 9.00 | 8.20 | 8.59 | 0.015 5 | 0.017 6 | 0.018 0 |
| 1.1.3 近5年生活饮用水污染物浓度监测不合格率 | 8.27 | 8.93 | 8.07 | 8.35 | 0.015 1 | 0.008 0 | 0.008 0 |
| 1.2 污染源 | 9.07 | 8.00 | 8.60 | 8.74 | 0.093 4 | 0.079 0 | 0.080 9 |
| 1.2.1 洪涝灾害引起水源污染物种类或数量增多 | 8.33 | 8.07 | 8.53 | 8.31 | 0.015 0 | 0.017 8 | 0.017 6 |
| 1.2.2 水源上游存在工农业和生活污染 | 9.00 | 8.53 | 8.53 | 8.76 | 0.015 8 | 0.017 7 | 0.018 4 |
| 1.2.3 水源受人为因素 (如投毒或交通事故)污染 | 9.00 | 8.40 | 8.60 | 8.80 | 0.015 9 | 0.015 6 | 0.016 3 |
1.2.4 水厂区30 m范围内存在污染源，生产区外围30米范围内有生活居住区、渗水厕所
和垃圾堆放场等 | 8.87 | 8.93 | 8.47 | 8.73 | 0.015 8 | 0.009 1 | 0.009 5 |
| 1.2.5 供水设施周围15米内存在污水井、化粪池等污染源 | 8.73 | 8.67 | 8.33 | 8.58 | 0.015 5 | 0.010 6 | 0.010 8 |
| 1.2.6 二次供水水箱/蓄水池10 m范围内存在污染源 | 8.60 | 8.53 | 8.40 | 8.52 | 0.015 4 | 0.008 2 | 0.008 3 |
| 1.3 水厂处理工艺 | 8.67 | 8.87 | 8.27 | 8.61 | 0.105 3 | 0.114 1 | 0.113 0 |
| 1.3.1 根据水源水质情况配置了适宜的净水工艺且设施工作正常 | 9.00 | 9.07 | 8.80 | 8.99 | 0.016 3 | 0.008 7 | 0.009 3 |
| 1.3.2 有消毒设备且能正常使用，正确选用消毒剂，并在供水期间连续投加且准确计量 | 8.87 | 9.07 | 8.53 | 8.81 | 0.015 9 | 0.017 9 | 0.018 8 |
| 1.3.3 按规定清洗和维护水处理设施和设备，并按要求更换水处理材料 | 8.67 | 8.80 | 8.33 | 8.65 | 0.015 6 | 0.025 1 | 0.025 8 |
| 1.3.4 水厂设计处理能力大于实际供水规模 | 7.80 | 8.27 | 7.60 | 7.84 | 0.014 2 | 0.020 5 | 0.019 2 |
| 1.3.5 涉水产品批件资质与许可 | 8.13 | 8.80 | 7.60 | 8.04 | 0.014 5 | 0.014 7 | 0.014 0 |
| 1.3.6 人员考核培训制度 | 8.13 | 8.40 | 7.20 | 7.81 | 0.014 1 | 0.010 7 | 0.009 9 |
| 1.3.7 具有备用水源 | 8.27 | 8.33 | 8.00 | 8.15 | 0.014 7 | 0.016 5 | 0.016 0 |
| 1.4 输配管网 | 8.60 | 8.47 | 8.20 | 8.39 | 0.060 5 | 0.067 7 | 0.068 0 |
| 1.4.1 输配水管选材适宜 | 8.33 | 8.93 | 7.80 | 8.31 | 0.015 0 | 0.014 9 | 0.014 7 |
| 1.4.2 输配管道定期巡查、检修和保养 | 8.40 | 8.60 | 7.80 | 8.27 | 0.015 0 | 0.020 5 | 0.020 3 |
| 1.4.3 配水管网漏损率低于20% | 8.13 | 8.40 | 7.87 | 8.09 | 0.014 6 | 0.010 3 | 0.009 9 |
| 1.4.4 排水管与污水管不相连 | 9.00 | 8.53 | 8.60 | 8.79 | 0.015 9 | 0.022 0 | 0.023 1 |
| 1.5 二次供水 | 8.67 | 8.87 | 8.33 | 8.57 | 0.075 4 | 0.060 1 | 0.058 7 |
| 1.5.1 二次供水水箱定期清洗消毒 | 9.13 | 8.93 | 8.67 | 9.00 | 0.016 3 | 0.007 0 | 0.007 5 |
| 1.5.2 二次供水消毒剂指标在线实时监测且定期校准维护 | 8.47 | 8.27 | 8.13 | 8.31 | 0.015 0 | 0.009 4 | 0.009 3 |
| 1.5.3 二次供水泵房环境状况 | 8.07 | 8.67 | 7.80 | 8.18 | 0.014 8 | 0.011 5 | 0.011 2 |
| 1.5.4 设有透气管、溢水管和泄水管并装有溢水孔网罩 | 8.40 | 8.80 | 8.00 | 8.36 | 0.015 1 | 0.009 5 | 0.009 5 |
| 1.5.5 清洗消毒人员持健康证上岗 | 8.07 | 8.53 | 7.20 | 7.84 | 0.014 2 | 0.022 7 | 0.021 2 |
| 2 危害性 | 9.07 | 8.80 | 8.67 | 8.93 | 0.105 0 | 0.081 0 | 0.081 1 |
| 2.1 水体感官异常 | 9.07 | 9.00 | 9.00 | 9.03 | 0.032 2 | 0.027 1 | 0.029 0 |
| 2.1.1 水源水出现浑浊、红虫、异味 | 8.67 | 8.80 | 8.67 | 8.70 | 0.015 7 | 0.010 4 | 0.010 8 |
| 2.1.2 龙头水出现浑浊、红虫、异味 | 9.20 | 9.07 | 9.00 | 9.13 | 0.016 5 | 0.016 7 | 0.018 2 |
| 2.2 水污染相关疾病 | 8.93 | 7.87 | 8.53 | 8.57 | 0.045 5 | 0.038 7 | 0.038 5 |
| 2.2.1 介水传染病病例数量 | 8.93 | 8.27 | 8.60 | 8.65 | 0.015 6 | 0.011 1 | 0.011 4 |
| 2.2.2 经皮肤急性中毒 | 8.60 | 7.47 | 8.27 | 8.20 | 0.014 8 | 0.015 7 | 0.015 3 |
| 2.2.3 经口急性中毒 | 8.80 | 7.47 | 8.40 | 8.33 | 0.015 1 | 0.011 9 | 0.011 8 |
| 2.3 人群心理健康 | 7.87 | 7.20 | 7.60 | 7.59 | 0.027 3 | 0.015 2 | 0.013 6 |
| 2.3.1 对突发水污染事件的接受程度 | 7.67 | 7.60 | 7.27 | 7.51 | 0.013 6 | 0.008 4 | 0.007 5 |
| 2.3.2 对政府处理事件能力的信任程度 | 8.00 | 7.53 | 7.20 | 7.57 | 0.013 7 | 0.006 8 | 0.006 1 |
| 3 脆弱性 | 8.27 | 7.73 | 7.87 | 8.01 | 0.178 1 | 0.149 6 | 0.144 6 |
| 3.1 监测能力 | 9.13 | 9.00 | 8.87 | 9.04 | 0.031 9 | 0.015 9 | 0.016 8 |
| 3.1.1 水污染物实时监测 | 9.07 | 8.60 | 8.87 | 8.94 | 0.016 2 | 0.008 5 | 0.009 1 |
| 3.1.2 常规污染物监测指标数量 | 8.60 | 8.93 | 8.47 | 8.67 | 0.015 7 | 0.007 4 | 0.007 7 |
| 3.2 污染物消除 | 9.20 | 8.27 | 8.80 | 8.93 | 0.031 9 | 0.026 9 | 0.028 2 |
| 3.2.1 水处理工艺能解决原水的主要污染物 | 9.00 | 8.80 | 8.67 | 8.91 | 0.016 1 | 0.009 8 | 0.010 4 |
| 3.2.2 在传统工艺基础上，增加深度净化处理工艺如混凝沉淀、臭氧活性炭等 | 8.73 | 8.47 | 8.60 | 8.72 | 0.015 8 | 0.017 1 | 0.017 8 |
| 3.3 外部反应性 | 7.73 | 7.53 | 7.73 | 7.81 | 0.042 2 | 0.048 0 | 0.044 2 |
| 3.3.1 近5年内发生突发水污染事件的数量 | 8.13 | 8.53 | 7.87 | 8.22 | 0.014 9 | 0.010 2 | 0.010 0 |
| 3.3.2 近5年内水污染相关的媒体新闻负面报道 | 7.60 | 7.93 | 7.33 | 7.62 | 0.013 8 | 0.029 8 | 0.027 1 |
| 3.3.3 近5年内水污染相关的行政处罚 | 7.40 | 7.93 | 7.13 | 7.44 | 0.013 5 | 0.008 0 | 0.007 1 |
| 3.4人群易感性 | 7.87 | 7.47 | 7.53 | 7.70 | 0.029 6 | 0.016 8 | 0.016 4 |
| 3.4.1.辖区脆弱人群（老年人、儿童、孕妇、慢性病人等）比例 | 8.47 | 7.87 | 7.80 | 8.14 | 0.014 7 | 0.006 0 | 0.005 8 |
| 3.4.2 辖区常住人口数 | 8.13 | 8.67 | 7.80 | 8.23 | 0.014 9 | 0.010 8 | 0.010 6 |
| 3.5人群适应性 | 7.67 | 7.27 | 7.33 | 7.51 | 0.042 5 | 0.042 0 | 0.039 0 |
| 3.5.1 生活饮水习惯 | 8.27 | 8.07 | 8.07 | 8.19 | 0.014 8 | 0.012 3 | 0.012 0 |
| 3.5.2 水污染危害知识的掌握情况 | 8.13 | 7.53 | 7.80 | 7.90 | 0.014 3 | 0.012 9 | 0.012 2 |
| 3.5.3 人群对安全防范体系的信赖程度 | 7.60 | 7.40 | 7.13 | 7.40 | 0.013 4 | 0.016 8 | 0.014 8 |
| 4 可控性 | 8.67 | 7.87 | 7.80 | 8.11 | 0.320 4 | 0.369 3 | 0.372 8 |
| 4.1 水质监管 | 9.07 | 8.80 | 8.27 | 8.78 | 0.091 0 | 0.100 9 | 0.101 4 |
| 4.1.1 划定水源一级防护区并有完善的巡查记录 | 8.53 | 8.93 | 7.93 | 8.43 | 0.015 3 | 0.026 2 | 0.026 4 |
| 4.1.2 1000 m3/d以上水厂具有水质实验室并定期开展水质检测 | 8.60 | 7.93 | 7.93 | 8.19 | 0.014 8 | 0.006 5 | 0.006 3 |
| 4.1.3 自检或小型水厂进行定期送样检测且采样、送检记录完整 | 8.53 | 8.20 | 7.93 | 8.20 | 0.014 8 | 0.005 6 | 0.005 5 |
| 4.1.4 辖区水质监管部门具有GB5749—2022所列常规和扩展项目的检测能力 | 8.47 | 8.67 | 8.20 | 8.39 | 0.015 2 | 0.010 6 | 0.010 6 |
4.1.5 辖区水质监管部门定期开展生活饮用水水质监测，监测项目覆盖
GB5749—2022所列的常规指标 | 8.53 | 8.53 | 8.27 | 8.48 | 0.015 3 | 0.044 0 | 0.044 4 |
| 4.1.6 饮用水污染物快速检测能力 | 8.87 | 8.27 | 8.40 | 8.62 | 0.015 6 | 0.008 0 | 0.008 2 |
| 4.2 预警体系 | 9.13 | 8.60 | 8.67 | 8.95 | 0.077 2 | 0.069 3 | 0.070 7 |
| 4.2.1 制定突发水污染事件的应急预案 | 8.87 | 8.80 | 8.53 | 8.73 | 0.015 8 | 0.026 7 | 0.027 8 |
| 4.2.2 预案可操作性、完整性和演练情况 | 8.80 | 8.40 | 8.40 | 8.59 | 0.015 5 | 0.009 2 | 0.009 4 |
| 4.2.3 对重点风险的主动监控力度 | 8.80 | 8.20 | 8.67 | 8.66 | 0.015 7 | 0.009 5 | 0.009 8 |
| 4.2.4 突发事件报告及时性、完整性和准确性 | 8.87 | 8.60 | 8.27 | 8.65 | 0.015 6 | 0.010 7 | 0.011 0 |
| 4.2.5 前期预报结果回溯评价 | 8.20 | 8.20 | 7.73 | 8.06 | 0.014 6 | 0.013 2 | 0.012 7 |
| 4.3 应急响应 | 8.87 | 8.60 | 8.47 | 8.70 | 0.090 6 | 0.078 0 | 0.077 6 |
| 4.3.1 突发水污染应急管理联动机制 | 8.87 | 8.40 | 8.47 | 8.67 | 0.015 7 | 0.021 7 | 0.022 5 |
| 4.3.2 事件性质研判时间效率 | 8.93 | 7.93 | 8.73 | 8.67 | 0.015 7 | 0.006 6 | 0.006 8 |
| 4.3.3 预案执行程度 | 8.67 | 8.00 | 8.13 | 8.36 | 0.015 1 | 0.008 3 | 0.008 3 |
| 4.3.4 群众疏散安置率 | 8.20 | 7.73 | 7.93 | 7.99 | 0.014 5 | 0.017 0 | 0.016 2 |
| 4.3.5 病患应急转运与救治能力 | 8.33 | 8.27 | 8.07 | 8.20 | 0.014 8 | 0.010 5 | 0.010 2 |
| 4.3.6 应急信息传播/发布力度 | 8.27 | 8.20 | 7.93 | 8.17 | 0.014 8 | 0.013 9 | 0.013 6 |
| 4.3.7 应急供水能力 | 8.93 | 8.20 | 8.40 | 8.58 | 0.015 5 | 0.027 3 | 0.027 9 |
| 4.4 资源保障 | 8.67 | 8.27 | 8.07 | 8.36 | 0.061 6 | 0.121 1 | 0.123 1 |
| 4.4.1 应急资源储备情况 | 8.93 | 8.87 | 8.40 | 8.73 | 0.015 8 | 0.020 5 | 0.021 3 |
| 4.4.2 应急资源调配速率 | 8.53 | 8.53 | 8.47 | 8.53 | 0.015 4 | 0.049 2 | 0.049 9 |
| 4.4.3 应急人员专业技术水平 | 8.60 | 8.53 | 8.33 | 8.53 | 0.015 4 | 0.038 5 | 0.039 1 |
| 4.4.4 法规政策保障情况 | 8.47 | 8.33 | 8.00 | 8.28 | 0.015 0 | 0.012 9 | 0.012 8 |
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