Madras was one of 22 urban places in India where centrally sponsored urban malaria control schemes were introduced in 1971-1972. Yet since 1970, malaria cases have actually registered a significant increase in Madras. This paper deals with some critical environmental issues facing malaria control schemes. The overall spatial trends and patterns of malaria incidence are illustrated through maps for the years 1975-1981. Areas of high incidence are shown in the northern part of the city which is also traditionally an endemic area. The City Corporation has identified 17 high risk divisions accounting for 75% of the total registered cases in the city. High risk areas were found to be related to environmentally deteriorating areas such as high density, older, residential areas, slums and squatter settled areas along stretches of two rivers and a canal which traverse the city, and the low-lying poorly drained areas scattered over many parts of the city. The typical breeding grounds and sources of major vectors (anophelines and culicines) are presented. A relationship exists between the density of breeding sources (of Anopheles stephensi), such as private and public wells (in use and in disuse), overhead tanks and cisterns, and malaria cases. Field observations were made in detail in four selected high risk areas. Each area presents different environmental, epidemiological and human (social) factors in understanding malaria resurgence situation and demand different types of control measures. The problems of implementation of urban control schemes are found to be political, administrative, economic, social as well as environmental in nature. The persistence of malaria problems in the city has been attributed to slackening of malaria eradication measures, rapid urban growth and deteriorating environmental conditions with sewage, drainage and sanitation programmes lagging far behind the plans. The advantages and drawbacks of various antimalaria (mostly larval) measures in practice are presented. Biological and chemical control methods of malaria seem to provide only temporary control of the vectors. Some of the problems and constraints faced by Madras City Corporation in enforcing public health measures are discussed. The study also points out that environmental improvement, management techniques and health education, including raising the public awareness and cooperation, involvement and participation at neighbourhood/community levels in a meaningful way, have a long way to go in achieving permanent vector control and eliminating the reservoir of infection.
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Malar J
January 2025
RBM Partnership Vector Control Working Group, Chem du Pommier 40, 1218, Le Grand-Saconnex, Switzerland.
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Department of Global Public Health, Karolinska Institutet, Stockholm, Sweden.
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ITC Faculty Geo-Information Science and Earth Observation, University of Twente, Enschede, the Netherlands.
Malaria remains a public health concern in Kenya where children and pregnant women are vulnerable groups. The common interventions in place to fight malaria include using insecticide-treated bed nets (ITNs), knowledge and awareness about malaria, and intake of malaria anti-malaria drugs. Despite the availability of these interventions, Kenya still records more than 10,000 clinical cases annually.
View Article and Find Full Text PDFParasite Epidemiol Control
February 2025
School of Medical laboratory Sciences, Hawassa University, Hawassa, Ethiopia.
Background: As Sub-Saharan African country urban malaria is potential catastrophe in Ethiopia, particularly in relation to rapidly growing small towns, which requires updating the epidemiology of malaria. There was lack of information regarding the study area, hence this study was designed to determine the prevalence of malaria and associated risk factors in Damboya town.
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Trop Med Health
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Department of Vector Biology and Control of Diseases, School of Public Health, Tehran University of Medical Sciences, Tehran, Iran.
Background: The Anopheles culicifacies complex is one of the most important malaria vectors in Southeast Asia and Southeastern Iran. Although the sibling species within this complex are morphologically indistinguishable, they differ significantly in their disease transmission potential, blood-feeding behaviour, and other biological traits. Cytogenetic and chromosomal studies have identified five sibling species within this complex: A, B, C, D, and E.
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