毛琦,孙彩英,黎安琪,等.2007—2023年上海市松江区钉螺监测结果及趋势分析[J].上海预防医学,2024,36(5):444-447.. DOI: 10.19428/j.cnki.sjpm.2024.23635
引用本文: 毛琦,孙彩英,黎安琪,等.2007—2023年上海市松江区钉螺监测结果及趋势分析[J].上海预防医学,2024,36(5):444-447.. DOI: 10.19428/j.cnki.sjpm.2024.23635
MAO Qi,SUN Caiying,LI Anqi,et al.Surveillance and trend analysis of snails in Songjiang District of Shanghai from 2007 to 2023[J].Shanghai Journal of Preventive Medicine,2024,36(05):444-447.. DOI: 10.19428/j.cnki.sjpm.2024.23635
Citation: MAO Qi,SUN Caiying,LI Anqi,et al.Surveillance and trend analysis of snails in Songjiang District of Shanghai from 2007 to 2023[J].Shanghai Journal of Preventive Medicine,2024,36(05):444-447.. DOI: 10.19428/j.cnki.sjpm.2024.23635

20072023年上海市松江区钉螺监测结果及趋势分析

Surveillance and trend analysis of snails in Songjiang District of Shanghai from 2007 to 2023

  • 摘要:
    目的 分析2007—2023年上海市松江区钉螺监测结果及变化趋势,为今后开展监测工作提供参考依据。
    方法 收集2007—2023年松江区钉螺监测相关数据,包括螺点的发现地点、调查框数、调查面积、有螺面积、有螺框数、捕螺总数、最高密度、钉螺解剖数,并计算活螺密度和活螺框出现率等指标。
    结果 2007—2023年松江区累计在4个镇、22个行政村监测发现螺点158个,其中新螺点131个(82.91%),复现螺点27个(17.09%);累计有螺面积175 980 m2,有螺框数10 061个,捕获钉螺33 302个,最高密度260只/0.11 m2,解剖钉螺15 662个,未发现阳性钉螺,平均活螺密度0.60只/0.11 m2,平均活螺框出现率17.99%。不同地区有螺面积:叶榭镇126 000 m2(71.60%),泖港镇26 470 m2(15.04%),新浜镇17 040 m2(9.68%),石湖荡镇6 470 m2(3.68%)。不同地区平均活螺密度:叶榭镇0.89只/0.11 m2,泖港镇0.65只/0.11 m2,石湖荡镇0.26只/0.11 m2,新浜镇0.24只/0.11 m2;不同螺点环境类型有螺面积:林地151 250 m2(85.95%),河道13 810 m2(7.85%),沟渠6 910 m2(3.93%),田滩地4 010 m2(2.28%);不同螺点环境类型平均活螺密度:沟渠1.01只/ 0.11 m2,田滩地0.86只/0.11 m2,林地0.57只/0.11 m2,河道0.40只/0.11 m2;不同地区及不同螺点环境类型活螺框出现率均呈下降趋势且差异有统计学意义。
    结论 虽然松江区有螺面积、平均活螺密度和平均活螺框出现率等螺情监测指标仍处于历史较低水平,但平均活螺密度和平均活螺框出现率与其他地区或全国平均水平相比处于较高水平。应重点关注黄浦江上游及支流地区,特别是苗木移植重点地区,应加强监测监管,降低钉螺输入风险。

     

    Abstract:
    Objective To analyze the monitoring results and trends of Oncomelania in Songjiang District of Shanghai from 2007 to 2023, and to provide reference for future monitoring work.
    Methods The data of snail monitoring in Songjiang District from 2007 to 2023 were collected, including the location of snail spots, the number of survey frames, the area with snails, the number of frames with snails, the total number of snails, etc. The density of living snails and the occurrence rate of living snail frames were calculated.
    Results From 2007 to 2023, a total of 158 snail spots were found in 22 administrative villages in 4 towns in Songjiang District, including 131 emerging snail habitats (82.91%) and 27 reemerging snail habitats (17.09%). The total snail area was 175 980 m2, the number of snail frames was 10 061, and 33 302 snails were captured. The highest density was 260/0.11 m2, and 15 662 snails were dissected. No positive snails were found. The average density of living snails was 0.60/0.11 m2 and the average occurrence rate of living snail frames was 17.99%. The snail areas in different areas were Yexie Town 126 000 m2 (71.60%), Maogang Town 26 470 m2 (15.04%), Xinbang Town 17 040 m2 (9.68%), and Shihudang Town 6 470 m2 (3.68%). The average density of living snails in different areas was 0.89/0.11 m2 in Yexie Town, 0.65/0.11 m2 in Maogang Town, 0.26/0.11 m2 in Shihudang Town and 0.24/0.11 m2 in Xinbang Town. The snail areas of different snail habitats were as follows: woodland 151 250 m2(85.95%), river 13 810 m2(7.85%), ditch 6 910 m2(3.93%), farmland 4 010 m2(2.28%). The average density of living snails in different snail habitats: ditch 1.01/0.11 m2, beach 0.86/0.11 m2, woodland 0.57/0.11 m2, river 0.40/0.11 m2. The occurrence rate of living snail frames in different regions and different snail environment types showed a downward trend and the difference was statistically significant.
    Conclusion Although the snail monitoring indicators such as snail area, average living snail density and average living snail frame occurrence rate in Songjiang District are still at its historically low level, the average living snail density and average living snail frame occurrence rate are still high compared with other regions or the national average. We should focus on the upper reaches and tributaries of the Huangpu River, especially the key areas of seedling transplantation, and strengthen monitoring and supervision to reduce the risk of snail input.

     

/

返回文章
返回