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安庆市小环境改造工程灭螺效果评价OA

EVALUATION OF SNAIL CONTROL EFFECT IN ANQING SMALL ENVIRONMENT RENOVATION PROJECT

中文摘要英文摘要

目的 评估安庆市小环境改造工程灭螺效果,为山丘型血吸虫病流行区钉螺综合治理提供参考.方法 采用现场调查和回顾性调查,收集整理安庆市 35 个小环境改造工程调査表数据和控螺效果监测表,对环境改造基本情况、投入费用进行描述性分析.采用 Wilcoxon 符号秩和检验比较环改前后的螺情数据,Friedman 检验评估环改后数年的螺情变化情况,非参数独立样本检验比较不同环改方法、环境特征及工程区与对照区在环改效果上的差异.结果 2017-2023 年,安庆市环境改造共 35 处环境,其中沟渠 29 处、旱地 1 处、塘堰 5 处.环改方法主要有沟渠、塘堰硬化和翻耕套种.浆砌块石硬化平均投入费用最高(147.10 元/m2),翻耕套种投入费用最低(4.62 元/m2).环改前钉螺面积 7.89 万 m2,环改后钉螺面积1.81 万 m2,减少 77.06%.环改前后,在活螺密度和有螺框出现率指标上均有显著改善(P<0.001).对于沟渠环境,沟壁是否光滑及上游是否有螺对活螺密度下降率没有显著影响,但沟渠内侧有无开裂对活螺密度下降率存在显著影响(P<0.001).不同环改方法之间在活螺密度下降率及有螺框出现率下降率上均没有显著差异;砖砌、混泥土和浆砌块石环改方法灭螺效果显著优于药物灭螺(P<0.01),其他环改方法下的工程区在活螺密度下降率及有螺框出现率下降率上与药物灭螺对照区没有显著差异.结论 血防环境改造工程能有效杀灭山丘型有螺区域钉螺,需结合环境类型选择成本效益适配的改造方法,加强后期监测和维护,以进一步提升工作实效.

Objective The aim was to evaluate the effects of efforts directed toward controlling Oncomelania hupensis snails on small environmental modification projects in Anqing City to provide a reference for comprehensively controlling O.hupensis in hilly areas where schistosomiasis is endemic.Methods Field and retrospective surveys were conducted to collect data using questionnaires.The data from 35 questionnaires on small-scale environmental modification projects in Anqing City and the effects of snail obtained from monitoring forms were sorted.The data were descriptively analyzed using basic information on environmental modifications and investment costs.The Wilcoxon signed-rank test was used to compare snail status before and after environmental interventions.The Friedman test was applied to evaluate the changes in snail populations in the years after environmental intervention.Non-parametric independent sample tests were adopted to compare differences in the effects of different environmental interventions,environmental characteristics,and between project and control areas.Results A total of 35 environments altered from 2017 to 2023,including the creation of 29 ditches,1 dry land,and 5 pond-weirs.The main environmental interventions included hardening of ditches and pond-weirs as well as tilling with intercropping.The average investment costs of mortared rubble masonry hardening and tilling with intercropping were the highest(147.10 yuan/m2)and lowest(4.62 yuan/m2),respectively.The pre-intervention snail-infested area was 78 900 m2,which decreased to 18 100 m2,a decrease of 77.06%.After environmental intervention,the density and rate of living snails significantly decreased on frames with snails(P<0.001).In ditch environments,the smoothness of the ditch walls and the presence of snails in the upper reaches did not significantly decrease the living snail density;however,the presence of cracks on the inner side of the ditches significantly impacted the decline in the rate(P<0.001).No significant difference was found in the rates at which the living snail density or snail frame occurrence decreased among different environmental modification method.The effects of brick masonry,concrete,and mortared rubble masonry on snail control were significantly stronger than those of chemical snail control(P<0.01),whereas no significant difference was found in the decline in these two rates between project areas using other modification method and control areas using chemical snail control.Conclusions Schistosomiasis-prevention-oriented environmental interventions effectively eliminate snails from hilly snail-infested areas.Cost-effective modification method should be selected based on the environmental type,and post-modification monitoring and maintenance must be strengthened to further increase snail control effectiveness.

储琼;丁平;姚金付;王星

安庆市疾病预防控制中心,安徽 安庆 246001安庆市疾病预防控制中心,安徽 安庆 246001安庆市疾病预防控制中心,安徽 安庆 246001安庆市疾病预防控制中心,安徽 安庆 246001

医药卫生

钉螺环境改造安庆市血吸虫病

SnailsEnvironmental renovationAnqing CitySchistosomiasis

《寄生虫与医学昆虫学报》 2026 (1)

9-18,10

安徽省引江济淮工程血防科研项目(YJJHXF2021002)

10.3969/j.issn.1005-0507.2026.01.002

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