Leathwick D M, Miller C M, Waghorn T S
AgResearch Grasslands, Private Bag 11008, Palmerston, North 4442 , New Zealand.
N Z Vet J. 2011 Nov;59(6):272-8. doi: 10.1080/00480169.2011.610273.
To measure the development of Teladorsagia (=Ostertagia) circumcincta and Trichostrongylus colubriformis eggs to third-stage infective larvae (L3) at different times of the year. Also, to measure the spatial distribution of L3 across herbage, soil and faeces, in order to assess whether spatial issues could be important in larval dynamics on pasture.
Field plots were contaminated with sheep faeces containing approximately 20,000 eggs of each of T. circumcincta and T. colubriformis on five separate occasions, viz 01 December 1996 (summer), 18 March 1998 (autumn), 17 June 1998 (winter), 15 October 1998 (spring), and 23 July 1999 (winter). Replicate plots (n=10) were harvested at intervals for up to 12 months after deposition of faeces, and the number and distribution of L3 were measured. Larvae were sampled from faeces (where these remained), herbage, and three soil zones to a depth of 145 mm.
There were large differences between contamination dates in the percentage of eggs that developed to L3. For both species the highest percentage development was for eggs deposited in December (7.8% and 25.9% for T. circumcincta and T. colubriformis, respectively) and the lowest for June (0.4% and 0.03% T. circumcincta and T. colubriformis, respectively). Development in winter was often delayed, and this was always associated with a low yield of larvae, probably due to compounding mortalities associated with long periods of exposure to low temperatures. The relative distribution of L3 present on herbage, in faeces or in the soil varied between sampling times. However, overall the most L3 were recovered from soil (74% and 66% for T.circumcincta and T. colubriformis, respectively, averaged over all samples), and the lowest recoveries were from the herbage.
Although the data are limited, the results indicated that the highest percentage of eggs developed to infective larvae in summer and only minimal development occurred in winter. The data do not support the view that substantial contamination of pastures with sheep parasites occurs over winter. Large numbers of larvae were recovered from soil, which indicates that, assuming they can subsequently migrate onto herbage, soil is a potentially important reservoir of infective larvae in New Zealand. Therefore, the spatial distribution of L3 on pasture may affect both the dynamics and transmission of parasite populations. Further work on both these issues is warranted.
测定环形泰勒虫(= 奥斯特他线虫)和蛇形毛圆线虫虫卵在一年中不同时间发育至感染性三期幼虫(L3)的情况。同时,测定L3在牧草、土壤和粪便中的空间分布,以评估空间因素在牧场幼虫动态中是否重要。
在五个不同时间,即1996年12月1日(夏季)、1998年3月18日(秋季)、1998年6月17日(冬季)、1998年10月15日(春季)和1999年7月23日(冬季),用含有约20000枚环形泰勒虫和蛇形毛圆线虫虫卵的绵羊粪便污染田间地块。在粪便沉积后长达12个月的时间里,每隔一段时间对重复地块(n = 10)进行收割,并测定L3的数量和分布。从粪便(若仍存在)、牧草以及深度达145毫米的三个土壤区域采集幼虫样本。
不同污染日期之间,发育至L3的虫卵百分比存在很大差异。对于这两个物种,发育百分比最高的是12月沉积的虫卵(环形泰勒虫和蛇形毛圆线虫分别为7.8%和25.9%),最低的是6月(环形泰勒虫和蛇形毛圆线虫分别为0.4%和0.03%)。冬季发育常常延迟,且这总是与幼虫产量低相关,可能是由于长时间暴露于低温导致的复合死亡率。在不同采样时间,牧草、粪便或土壤中L3的相对分布有所不同。然而,总体而言,从土壤中回收的L3最多(所有样本平均,环形泰勒虫和蛇形毛圆线虫分别为74%和66%),从牧草中回收的最少。
尽管数据有限,但结果表明,夏季发育至感染性幼虫的虫卵百分比最高,而冬季只有极少发育。数据不支持冬季绵羊寄生虫大量污染牧场的观点。从土壤中回收了大量幼虫,这表明,假设它们随后能迁移到牧草上,在新西兰土壤是感染性幼虫的一个潜在重要储存库。因此,L3在牧场上的空间分布可能会影响寄生虫种群的动态和传播。有必要对这两个问题进一步开展研究。