Sturrock R F, Diaw O T, Talla I, Niang M, Piau J P, Capron A
Department of Infectious and Tropical Diseases, London School of Hygiene & Tropical Medicine, UK.
Parasitology. 2001;123 Suppl:S77-89. doi: 10.1017/s0031182001008125.
Irrigation for intensive sugar cultivation started in the early 1980s at Richard Toll, some 100 km from the mouth of the Senegal River. Infections with Schistosoma mansoni were first seen in late 1988. This study records quantitative snail surveys for over 3 years from 1992 at sites representing different habitats in and around the irrigation scheme. Populations of both Biomphalaria pfeifferi (the intermediate host of S. mansoni) and Bulinus spp. (mainly B. truncatus, the local host of S. boris) peaked in late 'spring' or early 'summer', depending on the habitat, and then remained low until the following spring', B. pfeifferi favoured smaller, man-made habitats with most transmission between May and August each year. The less abundant Bulinus spp. favoured larger natural and man-made habitats with most S. bovis transmission between April and July. S. mansoni infections were more, but S. bovis infections were less abundant than other trematodes in their respective snail hosts. Ecological changes in the early 1980s due to sugar irrigation pre-dated similar, more widespread changes in the late 1980s when the completion of dams across the Senegal River prevented seasonal rain fed floods and sea water intrusion. S. mansoni has since spread rapidly around Richard Toll. The incompatibility of the local S. haematobium strains with the dominant bulinid snails has so far prevented an epidemic of urinary schistosomiasis at Richard Toll, but the invasion of similar downstream habitats by susceptible B. globosus is worrying. The principal control measure, chemotherapy, given in the 'winter' would minimise the rate of reinfection. It could be reinforced by judicious mollusciciding within the sugar irrigation scheme but not elsewhere.
20世纪80年代初,在距离塞内加尔河河口约100公里的理查德托尔开始了集约化甘蔗种植灌溉。1988年末首次发现曼氏血吸虫感染。本研究记录了1992年起3年多来在灌溉区及其周边代表不同栖息地的地点进行的定量蜗牛调查。菲氏双脐螺(曼氏血吸虫的中间宿主)和泡螺属(主要是截形泡螺,牛血吸虫的本地宿主)的种群数量在“春季”末或“夏季”初达到峰值,具体取决于栖息地,然后一直保持在低水平直至次年“春季”。菲氏双脐螺偏好较小的人工栖息地,每年5月至8月间传播最为频繁。数量较少的泡螺属偏好较大的自然和人工栖息地,牛血吸虫的传播在4月至7月最为频繁。在各自的蜗牛宿主中,曼氏血吸虫感染更为常见,但牛血吸虫感染比其他吸虫更为少见。20世纪80年代初由于甘蔗灌溉导致的生态变化早于80年代末类似的、更广泛的变化,当时横跨塞内加尔河的水坝建成,阻止了季节性雨水洪水和海水入侵。此后,曼氏血吸虫在理查德托尔迅速传播。当地的埃及血吸虫菌株与占主导地位的泡螺不相容,迄今为止,这阻止了理查德托尔地区泌尿血吸虫病的流行,但易感的球泡螺侵入类似的下游栖息地令人担忧。主要的控制措施是在“冬季”进行化疗,这将使再感染率降至最低。可以通过在甘蔗灌溉区内明智地使用杀螺剂来加强控制,但在其他地方则不行。