Dreyfuss G, Vignoles P, Rondelaud D
UPRES EA n degrees 3174, Facultés de Pharmacie et de Médecine, 2 rue du Docteur Raymond Marcland, 87025, Limoges, France.
Parasitol Res. 2003 Dec;91(6):458-61. doi: 10.1007/s00436-003-0892-8. Epub 2003 Oct 17.
As larval forms of Fasciola hepatica have periodically been detected in Omphiscola glabraafter their collection from watercress beds or from meadows since 1995, field investigations in 37 populations of O. glabra were carried from 1996 to 2002. This was done in order to determine the changes in prevalences and intensities of these natural infections with F. hepatica in relation to the type of snail habitat and the year of snail collection. Snails infected with F. hepatica were found in all samples made in swampy meadows and roadside ditches in all years. In fenced pools and walled gardens, snail infections were only found from 1998 and 1999 onwards, respectively. In the four types of habitats, the prevalences of F. hepatica infections increased slightly over time (0.8-2.1% for snails sampled in swampy meadows, for example) but this increase varied with the habitat. The mean shell heights of infected snails (6.2-7.8 mm) were similar whatever the type of habitat. The numbers of cercariae-containing rediae counted in snails sampled in swampy meadows, roadside ditches, and fenced pools significantly increased over time. Significant numerical variation between these redial burdens was also observed in relation to snail habitat. As the larval development of F. hepatica is facilitated by the presence of another trematode larval form ( Paramphistomum daubneyi), the finding of some naturally infected O. glabra in watering places known to have no contact with domestic or wild large mammals might be explained by the development of P. daubneyi in small mammals such as lagomorphs. However, a progressive adaptation of F. hepatica miracidia to O. glabra over time, which would permit the infection of snails at sizes larger than 2 mm, could not be excluded.
自1995年以来,在从水田芥床或草地采集的光滑双脐螺中定期检测到肝片吸虫的幼虫形态,因此在1996年至2002年期间对37个光滑双脐螺种群进行了实地调查。这样做是为了确定这些肝片吸虫自然感染的流行率和感染强度相对于蜗牛栖息地类型和蜗牛采集年份的变化。在所有年份的沼泽草地和路边沟渠采集的所有样本中都发现了感染肝片吸虫的蜗牛。在围栏水池和围墙花园中,蜗牛感染分别仅从1998年和1999年开始出现。在这四种栖息地类型中,肝片吸虫感染的流行率随时间略有增加(例如,在沼泽草地采集的蜗牛中为0.8%-2.1%),但这种增加因栖息地而异。无论栖息地类型如何,感染蜗牛的平均壳高(6.2-7.8毫米)相似。在沼泽草地、路边沟渠和围栏水池采集的蜗牛中,含尾蚴雷蚴的数量随时间显著增加。在这些雷蚴负荷之间,也观察到与蜗牛栖息地相关的显著数值差异。由于另一种吸虫幼虫形态(道氏腹袋吸虫)的存在有利于肝片吸虫的幼虫发育,在已知与家养或野生大型哺乳动物无接触的水域中发现一些自然感染的光滑双脐螺,可能是由于道氏腹袋吸虫在小型哺乳动物(如兔形目动物)中的发育。然而,不能排除肝片吸虫毛蚴随着时间的推移逐渐适应光滑双脐螺,从而使大于2毫米的蜗牛受到感染的可能性。