Centre for Animal Production and Health, Murdoch University, Perth, 6150, Australia.
Centre for Animal Production and Health, Murdoch University, Perth, 6150, Australia.
Vet Parasitol. 2020 Dec;288:109281. doi: 10.1016/j.vetpar.2020.109281. Epub 2020 Oct 25.
Cryptosporidium and Giardia infections can negatively impact livestock health and reduce productivity, and some species and genotypes infecting livestock have zoonotic potential. Infection occurs via the faecal-oral route. Waterborne infections are a recognised source of infection for humans, but the role of livestock drinking water as a source of infection in livestock has not been described. This study aimed to determine whether contaminated drinking water supplies, such as farm dams, are a likely transmission source for Cryptosporidium and Giardia infections for extensively managed sheep. Dam water samples (n = 47) were collected during autumn, winter and spring from 12 farm dams located on six different farms in south west Western Australia, and faecal samples (n = 349) were collected from sheep with access to these dams. All samples were initially screened for Cryptosporidium spp. at the 18S locus and Giardia spp. at the gdh gene using qPCR, and oocyst numbers were determined directly from the qPCR data using DNA standards calibrated by droplet digital PCR. Cryptosporidium-positive sheep faecal samples were typed and subtyped by sequence analysis of 18S and gp60 loci, respectively. Giardia-specific PCR and Sanger sequencing targeting tpi and gdh loci were performed on Giardia- positive sheep faecal samples to characterise Giardia duodenalis assemblages. To identify Cryptosporidium and Giardia spp. in dam water samples, next-generation sequencing analysis of 18S and gdh amplicons were performed, respectively. Two species of Cryptosporidium (Cryptosporidium xiaoi and Cryptospordium ubiquitum (subtype family XIIa)) were detected in 38/345 sheep faecal samples, and in water from 9/12 farm dams during the study period, with C. xiaoi the species most frequently detected in both faeces and dam water overall. Giardia duodenalis assemblages AI, AII and E were detected in 36/348 faecal samples and water from 10/12 farm dams. For dam water samples where oo/cysts were detected by qPCR, Cryptosporidium oocyst concentration ranged from 518-2429 oocysts/L (n = 14), and Giardia cyst concentration ranged from 102 to 1077 cysts/L (n = 17). Cryptosporidium and Giardia with zoonotic potential were detected in farm dam water, including C. ubiquitum, C. hominis, C. parvum, C. cuniculus, C. xiaoi, and G. duodenalis assemblages A, B and E. The findings suggest that dam water can be contaminated with Cryptosporidium species and G. duodenalis assemblages that may infect sheep and with zoonotic potential, and farm dam water may represent one source of transmission for infections.
隐孢子虫和贾第鞭毛虫感染会对牲畜健康产生负面影响,降低生产力,一些感染牲畜的物种和基因型具有人畜共患潜力。感染通过粪-口途径发生。水生感染是人类感染的一个公认来源,但牲畜饮用水作为牲畜感染源的作用尚未描述。本研究旨在确定受污染的饮用水供应(如农场水坝)是否是广泛管理的绵羊感染隐孢子虫和贾第鞭毛虫的可能传播源。在澳大利亚西南部的六个不同农场的 12 个农场水坝中,在秋季、冬季和春季采集了水坝水样(n=47),并从可进入这些水坝的绵羊中采集了粪便样本(n=349)。所有样本均在 18S 基因座使用 qPCR 对隐孢子虫 spp.和 gdh 基因对贾第鞭毛虫 spp.进行初步筛查,并使用通过液滴数字 PCR 校准的 DNA 标准直接从 qPCR 数据中确定卵囊数量。对隐孢子虫阳性绵羊粪便样本进行 18S 和 gp60 基因座的序列分析,分别对其进行分型和亚型分析。对贾第鞭毛虫阳性绵羊粪便样本进行针对 tpi 和 gdh 基因的 Giardia 特异性 PCR 和 Sanger 测序,以表征十二指肠贾第鞭毛虫组合。为了在水坝水样中识别隐孢子虫和贾第鞭毛虫 spp.,分别对 18S 和 gdh 扩增子进行下一代测序分析。在 38/345 份绵羊粪便样本和研究期间的 9/12 个农场水坝中检测到两种隐孢子虫(微小隐孢子虫和隐孢子虫 ubiquitum(亚型家族 XIIa)),在粪便和水坝水中均最常检测到微小隐孢子虫。在 36/348 份粪便样本和 10/12 个农场水坝中检测到十二指肠贾第鞭毛虫组合 AI、AII 和 E。对于通过 qPCR 检测到 oo/cysts 的水坝水样,隐孢子虫卵囊浓度范围为 518-2429 卵囊/L(n=14),贾第鞭毛虫囊浓度范围为 102-1077 囊/L(n=17)。在农场水坝水中检测到具有人畜共患潜力的隐孢子虫和贾第鞭毛虫,包括 C. ubiquitum、C. hominis、C. parvum、C. cuniculus、C. xiaoi 和 G. duodenalis 组合 A、B 和 E。研究结果表明,水坝水可能受到感染绵羊的隐孢子虫物种和 G. duodenalis 组合的污染,并且具有人畜共患潜力,农场水坝水可能是感染的传播源之一。