中华流行病学杂志
中華流行病學雜誌
중화류행병학잡지
CHINESE JOURNAL OF EPIDEMIOLOGY
2010年
2期
163-166
,共4页
李源培%王海银%周艺彪%何忠%万伟%姜杰%姜庆五
李源培%王海銀%週藝彪%何忠%萬偉%薑傑%薑慶五
리원배%왕해은%주예표%하충%만위%강걸%강경오
湖区%钉螺孳生地%微生态环境%钉螺分布%广义相加模型
湖區%釘螺孳生地%微生態環境%釘螺分佈%廣義相加模型
호구%정라자생지%미생태배경%정라분포%엄의상가모형
Lake area%Snail habitats%Micro-ecological environment%Distribution of Snails%General additive model
目的 探索微生态环境因素与钉螺密度之间的关系.方法 在2007年10月至2008年10月选择湖南省岳阳市君山区洞庭湖区的草滩为现场,系统抽样查螺并测量部分框的植被盖度、土壤温度,同时采集约30 g土壤样本.实验室压螺鉴定死活并分框记数,测量土壤含水量、土壤pH值.首先描述钉螺及各影响因素的分布情况,再用广义相加模型拟合分析多种环境因素与钉螺密度之间的关系.结果 微生态环境因素共查104框,pH值为4.70~7.92,植被盖度为1%~96%,土壤温度为14.5~32.7℃,土壤含水量为0.07~2.00.环境相关因素的广义相加模型拟合发现湖区植被盖度没有统计学意义,其他因素均有统计学意义(P<0.001).各微环境因素与钉螺密度间表现为非线性关系.结论 各微环境因素与钉螺密度间为平滑函数关系,应考虑用广义相加模型对钉螺分布与其影响因素间的关系进行研究,从而采取适宜策略来改变钉螺生态,进而遏制钉螺的繁殖和扩散.
目的 探索微生態環境因素與釘螺密度之間的關繫.方法 在2007年10月至2008年10月選擇湖南省嶽暘市君山區洞庭湖區的草灘為現場,繫統抽樣查螺併測量部分框的植被蓋度、土壤溫度,同時採集約30 g土壤樣本.實驗室壓螺鑒定死活併分框記數,測量土壤含水量、土壤pH值.首先描述釘螺及各影響因素的分佈情況,再用廣義相加模型擬閤分析多種環境因素與釘螺密度之間的關繫.結果 微生態環境因素共查104框,pH值為4.70~7.92,植被蓋度為1%~96%,土壤溫度為14.5~32.7℃,土壤含水量為0.07~2.00.環境相關因素的廣義相加模型擬閤髮現湖區植被蓋度沒有統計學意義,其他因素均有統計學意義(P<0.001).各微環境因素與釘螺密度間錶現為非線性關繫.結論 各微環境因素與釘螺密度間為平滑函數關繫,應攷慮用廣義相加模型對釘螺分佈與其影響因素間的關繫進行研究,從而採取適宜策略來改變釘螺生態,進而遏製釘螺的繁殖和擴散.
목적 탐색미생태배경인소여정라밀도지간적관계.방법 재2007년10월지2008년10월선택호남성악양시군산구동정호구적초탄위현장,계통추양사라병측량부분광적식피개도、토양온도,동시채집약30 g토양양본.실험실압라감정사활병분광기수,측량토양함수량、토양pH치.수선묘술정라급각영향인소적분포정황,재용엄의상가모형의합분석다충배경인소여정라밀도지간적관계.결과 미생태배경인소공사104광,pH치위4.70~7.92,식피개도위1%~96%,토양온도위14.5~32.7℃,토양함수량위0.07~2.00.배경상관인소적엄의상가모형의합발현호구식피개도몰유통계학의의,기타인소균유통계학의의(P<0.001).각미배경인소여정라밀도간표현위비선성관계.결론 각미배경인소여정라밀도간위평활함수관계,응고필용엄의상가모형대정라분포여기영향인소간적관계진행연구,종이채취괄의책략래개변정라생태,진이알제정라적번식화확산.
Objective To explore the relationships between micro-ecological environmental factors and the density of Snails so as to provide information for the elimination of Snails and control of Schistosomiasis disease,under ecological methods.Methods A bottomland close to Junshan Park in Yueyang city,Hunan province was selected as the field for survey during 10,2007-10,2008,and a systematic sampling method was applied to determine the specific sites of Snail investigation.All the Snails in each frames were collected and the soil surface temperature and vegetation coverage in several frames were measured.30 g soil sample in each selected frames were also collected simultaneously.The number of live Snails in each frame was counted by dissection,and soil measured pH value and soil moisture were tested in the laboratory.The distribution of Snails and microecological environmental factors,fitted general additive model for the relationship of these factors and the Snail density were described.Results 104 frames were surveyed,with pH value as between 4.70-7.92,vegetation coverage as in 1% to 96%,soil surface temperature as in 14.5-32.7℃,the soil moisture as in 0.07-2.00.Under General additive model,data showed that there was no significant difference for vegetation coverage.However,other factors were all significantly different(P<0.001).It was found that a nonlinear relationship was existing between these factors and the Snail density.Conclusion Smoothing function relationship was noticed between the Snail density and micro-ecological environmental factors.It's suggested to fit general additive model to study the relationship between the distribution of Snails and its influencing factors,so as to adopt appropriate measures to change the related ecology to control the diffusion and reproduction of Snails.