Abstract
Molecular epidemiology of cryptosporidiosis is an active research area in China. The use of genotyping and subtyping tools in prevalence studies has led to the identification of unique characteristics of Cryptosporidium infections in humans and animals. Human cryptosporidiosis in China is exemplified by the high diversity of Cryptosporidium spp. at species and subtype levels, with dominant C. hominis and C. parvum subtypes being rarely detected in other countries. Similarly, preweaned dairy calves, lambs, and goat kids are mostly infected with non-pathogenic Cryptosporidium species (C. bovis in calves and C. xiaoi in lambs and goat kids), with C. parvum starting to appear in dairy calves as a consequence of concentrated animal feeding operations. The latter Cryptosporidium species is dominated by IId subtypes, with IIa subtypes largely absent from the country. Unlike elsewhere, rodents in China appear to be commonly infected with C. parvum IId subtypes, with identical subtypes being found in these animals, calves, other livestock, and humans. In addition to cattle, pigs and chickens appear to be significant contributors to Cryptosporidium contamination in drinking water sources, as reflected by the frequent detection of C. suis, C. baileyi, and C. meleagridis in water samples. Chinese scientists have also made significant contributions to the development of new molecular epidemiological tools for Cryptosporidium spp. and improvements in our understanding of the mechanism involved in the emergence of hyper-transmissible and virulent C. hominis and C. parvum subtypes. Despite this progress, coordinated research efforts should be made to address changes in Cryptosporidium transmission because of rapid economic development in China and to prevent the introduction and spread of virulent and zoonotic Cryptosporidium species and subtypes in farm animals.
Introduction
Cryptosporidiosis is a major cause of diarrhea and enteric disease in humans and farm animals. It has long been known as a primary cause of watery diarrhea in pre-weaned calves and lambs, responsible for significant morbidity and mortality (Holland, 1990; Naciri et al., 1999; Blanchard, 2012; Cho et al., 2013; Meganck et al., 2014). Even subclinical infection in older animals has been associated with reductions in growth, carcass weight and dressing efficiency (Jacobson et al., 2016). In zoo and pet snakes, gastric infection with Cryptosporidium serpentis is chronic and often fatal (Paiva et al., 2013). In birds, C. baileyi can cause respiratory and renal infections, resulting in high mortality (Santin, 2013). Recent human studies have implicated cryptosporidiosis as the second most important cause for moderate-to-severe diarrhea in young children in developing countries (Kotloff et al., 2013; Platts-Mills et al., 2015). Several Cryptosporidium species from mammals and birds, such as C. parvum, C. meleagridis, C. canis, C. felis, and C. ubiquitum, are important zoonotic pathogens, causing animal contact-associated or waterborne and foodborne cryptosporidiosis in humans (Xiao, 2010).
Because of the clinical, economic, and public health importance of Cryptosporidium spp., cryptosporidiosis has attracted the attention of many Chinese scientists, especially in recent years. They have made significant contributions to improved characterizations of Cryptosporidium spp. at species and subtype levels and understanding of their biology and transmission. These studies have led to the identification of unique characteristics of Cryptosporidium transmission in humans and animals in China.
Molecular epidemiologic tools
Molecular epidemiology of cryptosporidiosis in humans and animals is the most active area of Cryptosporidium research within China. In these studies, genotyping and subtyping tools are widely used in the identification of infection sources and assessment of cross-species transmission of Cryptosporidium spp. (Xiao, 2010). Chinese scientists, in collaborations with scientists in other countries, have played a major role in developing some recent molecular epidemiologic tools for Cryptosporidium spp. For example, the PCR-RFLP analysis of the small subunit (SSU) rRNA gene using SspI and MboII developed by Chinese scientists (Feng et al., 2007b) has become the most popular genotyping tool for rapid differentiation of common Cryptosporidium species in ruminants (C. parvum, C. bovis, C. ryanae, and C. andersoni in cattle and C. parvum, C. ubiquitum, and C. xiaoi in sheep and goats). Several subtyping tools targeting the 60 kDa glycoprotein (gp60) gene have been developed for the assessment of the importance of zoonotic infections with several emerging human-pathogenic Cryptosporidium species such as C. ubiquitum and Cryptosporidium chipmunk genotype I (Li et al., 2014; Guo et al., 2015a). Their use in comparative analyses of human, animal, and water samples has led to the identification of host adaptation in C. ubiquitum and differences in the role of ruminants and rodents in human infections among geographic areas (Li et al., 2014). This was substantiated recently by multilocus sequence type (MLST) analysis of C. ubiquitum isolates (Tang et al., 2016). An MLST tool has also been developed for C. andersoni and C. muris (Feng et al., 2011a), and used by Chinese scientists in population genetic characterizations of gastric Cryptosporidium species in various areas (Wang et al., 2012; Zhao et al., 2013, 2014; Du et al., 2015; Zhao G. H. et al., 2015; Qi et al., 2016; Deng et al., 2017). It was shown that while the population structure of C. andersoni was clonal in Shaanxi and Heilongjiang provinces (Zhao et al., 2013, 2014), it was epidemic in Xinjiang and other regions (Wang et al., 2012; Qi et al., 2016).
More recently, procedures have been developed to facilitate whole genome sequencing (WGS) and advanced typing of human-pathogenic Cryptosporidium spp. (Guo et al., 2015b). The WGS and MLST tools have been used by Chinese scientists in studies of virulent and hypertransmissible C. hominis and C. parvum subtypes. Genetic recombination has been identified as a major mechanism for the emergence of these subtypes (Feng et al., 2013, 2014; Li et al., 2013; Guo et al., 2015c). WGS analysis of Cryptosporidium spp. has further indicated that copy number variation in two subtelomeric gene families encoding secreted MEDLE proteins and insulinase-like peptidases is involved in differences in host specificity between C. parvum and C. hominis and among host-adapted C. parvum subtype families (Guo et al., 2015c; Liu et al., 2016; Feng et al., 2017).
Although, molecular characterization of Cryptosporidium spp. is a recent development in China (Chen and Huang, 2007; Wang et al., 2008a,b,c), genotyping and subtyping tools are now widely used in the characterization of Cryptosporidium spp. in various animals (Karim et al., 2014; Liu et al., 2014a,b, 2015a,b; Ma et al., 2014, 2015; Qi et al., 2014, 2015a,b,d, 2016; Wang L. et al., 2014; Ye et al., 2014; Zhao et al., 2014; Du et al., 2015; Li J. et al., 2015, 2017; Liu A. et al., 2015; Li W. et al., 2015, 2017; Qi, M. Z., et al., 2015; Wang et al., 2015a,b; Zhang et al., 2015a,b; Zhao G. H. et al., 2015; Zhao Z. et al., 2015; Jian et al., 2016; Li F. et al., 2016; Li P. et al., 2016; Li Q. et al., 2016; Peng et al., 2016; Taylan-Ozkan et al., 2016; Xu et al., 2016; Yang et al., 2016; Zhang S. et al., 2016; Deng et al., 2017; Gong et al., 2017; Zou et al., 2017). The use of molecular diagnostic tools in prevalence studies has led to the identification of significant differences in the transmission of Cryptosporidium spp. between China and other countries.
Characteristics and distribution of Cryptosporidium hominis subtypes in China
Molecular surveillance of Cryptosporidium spp. in untreated urban wastewater indicates that like other developing countries, C. hominis is the major Cryptosporidium species in humans in China (Feng et al., 2009; Li et al., 2012; Huang et al., 2017). The common C. hominis subtype families found in humans in developing countries, including Ia, Ib, Id, Ie, and If, are present in wastewater in Shanghai (Feng et al., 2009). However, several Ib subtypes that are rarely found elsewhere in the world, including IbA19G2, IbA20G2, and IbA21G2, are dominant C. hominis subtypes in wastewater. The occurrence of diverse C. hominis subtype families and divergent Ib subtypes in humans in China has been confirmed by subtype analysis of clinical specimens from pediatric patients (Table 1). Elsewhere in developing countries, humans are commonly infected with two C. hominis subtypes of the virulent Ib subtype family: IbA10G2 and IbA9G3, which have not been found in China (Xiao, 2010).
Table 1
| Host | Location | Sample size | Cryptosporidium positive (%) | C. hominis | C. parvum | Other species (No.) | References | ||
|---|---|---|---|---|---|---|---|---|---|
| No. positive | Subtype (No.) | No. positive | Subtype (No.) | ||||||
| Human | Tianjin | – | 5 | 5 | IbA22G2 (1), IdA14 (1), IeA13G3T3 (1) | – | – | – | Peng et al., 2001 |
| Human | Shanghai | 6,284 | 102 (1.6%) | 92 | IaA14R4 (36), IaA18R4 (1), IdA19 (37), IdA14 (1), IbA19G2 (1), IgA14 (1) | – | – | C. meleagridis (6), C. canis (2), C. felis (2) | Feng et al., 2012 |
| Human | Shanghai | 252 | 34 (13.5%) | – | – | – | – | C. andersoni (34) | Liu H. et al., 2014 |
| Human | Jiangsu | 232 | 23 (9.9%) | 2 | – | – | – | C. andersoni (21) | Jiang et al., 2014 |
| Human | Henan | 1,366 | 11 (0.8%) | 3 | IbA19G2 (2), IeA12G3T3 (1) | 2 | IIdA19G1 (2) | C. meleagridis (5), C. suis (1) | Wang et al., 2013b |
| Human | Henan | – | 10 | 9 | IbA20G2 (3), IbA19G2 (2), IbA16G2 (1), IdA21 (2), IaA9R3 (1) | – | – | C. felis (1) | Wang et al., 2011c; Zhu et al., 2012 |
| Human | Hubei | 500 | 10 (2.0) | – | – | – | – | C. meleagridis (10) | Wang et al., 2017 |
| Rhesus monkey | Guizhou | 411 | 45 (10.9) | 39 | IdA20 (13), IeA11G3T3 (13), IaA13R8 (8), IaA13R7 (3), IaA14R7 (2), IfA16G2 (1) | 5 | IIcA5G3a (5) | C. felis (1) | Ye et al., 2012 |
| Rhesus monkey | Shaanxi | 86 | 6 (7.0) | – | – | 1 | IIdA15G1* (1) | C. andersoni (5) | Du et al., 2015 |
| Crab-eating macaques | Guangxi | 205 | 1 | 1 | IdA14 (1) | – | – | – | Ye et al., 2014 |
| Nonhuman primates | Guangdong, Guangxi, Shanghai, Henan | 266 | 19 (0.7) | 14 | IbA12G3 (7), IiA17 (1) | – | – | C. muris (5) | Karim et al., 2014 |
| Squirrel monkey | Sichuan | – | 1 | 1 | IkA7G4 (1)** | – | – | – | Liu et al., 2015a |
Cryptosporidium species and subtypes in humans and nonhuman primates in China.
Misidentified as IIdA15G2R1 in the report (KJ917586).
This subtype was assigned to the wrong subtype family, as it differed significantly from KJ941148 (IkA15G1), which has priority over this sequence (KP314263).
In addition to Ib subtypes, Ia and Id appear to be common in China (Table 1), and two of the Ia and Id subtypes, IaA14R4 and IdA19, were the cause of a cryptosporidiosis outbreak in a pediatric ward in Shanghai that lasted >14 months (Feng et al., 2012). In this outbreak, only IaA14R4 was associated with the occurrence of diarrhea. As these patients were orphans from a welfare institute, poor hygiene by patients and caregivers was implicated as the cause of the outbreak. This was supported by concurrent augment in the transmission of several other enteric pathogens, including Giardia duodenalis, Enterocytozoon bieneusi, and Clostridium difficile (Wang et al., 2013a).
The occurrence these common C. hominis subtype families in humans in China is also supported by studies of Cryptosporidium spp. in captive nonhuman primates. Four of the five C. hominis subtype families, including Ia, Id, Ie, and If, have been found at high frequency in rhesus monkeys in a popular park in Guizhou, where humans and animals interact with each other closely (Ye et al., 2012). Divergent Ib subtypes, have been found in nonhuman primates in other studies (Table 1). Although, the source of C. hominis in nonhuman primates is not clear, these animals clearly can serve as potential reservoirs for this pathogen, and some of the C. hominis subtypes in nonhuman primates have been found in lake water frequented by these animals (Ye et al., 2012).
C. hominis has been recently found as a dominant Cryptosporidium species in horses and donkeys in China (Jian et al., 2016; Deng et al., 2017). The subtypes involved, however, mostly belong to the rare C. hominis subtype family Ik (Jian et al., 2016). Elsewhere in the world, Ik subtypes have been identified in horses in Algeria and Brazil (Laatamna et al., 2015; Inacio et al., 2017), indicating this subtype family is a host-adapted C. hominis with only limited public health significance. This was supported recently by WGS analysis of a human Ik isolate from Sweden, which showed that it has a much more divergent genome compared with common C. hominis subtypes (Sikora et al., 2016).
Characteristics of Cryptosporidium parvum transmission in China
There are some substantial differences in the transmission of C. parvum between China and other countries, especially in preweaned dairy calves. Two large scale studies in Henan showed that although the distribution of Cryptosporidium species in postweaned dairy cattle was similar to the one observed in industrialized nations, preweaned dairy calves were mainly infected with C. bovis instead of C. parvum (Wang et al., 2011a,b). This was supported by subsequent studies in Heilongjiang, Shaanxi, Gansu, Ningxia, and Shanghai (Zhang et al., 2013a, 2015a; Qi, M. Z., et al., 2015; Cai et al., 2017), although in some other areas C. parvum was shown to be common in preweaned dairy calves, especially on large farms or farms experiencing diarrhea outbreaks (Cui et al., 2014; Huang et al., 2014; Qi et al., 2015c; Li F. et al., 2016). Elsewhere in the world, C. parvum is the dominant Cryptosporidium species in preweaned dairy calves (Xiao, 2010), and the common occurrence of C. bovis in this age group has only been reported in a few studies in Sweden and Malaysia (Silverlas et al., 2010; Muhid et al., 2011). In contrast, C. bovis is a common species in preweaned beef cattle, which are usually maintained in less extensive animal management systems (Ng et al., 2011; Rieux et al., 2013a,b, 2014; Bjorkman et al., 2015). The short history of concentrated animal feeding operations in China could be responsible for the low occurrence of C. parvum in preweaned dairy calves.
Subtyping of C. parvum in bovine studies identified the exclusive occurrence of IId subtypes in dairy calves in China, mostly IIdA15G1 and IIdA19G1 (Table 2). One study identified the exclusive occurrence of a few IIa subtypes in yaks in Qinghai (Mi et al., 2013), but this was not supported by data from other studies conducted in the same area (Qi et al., 2015a; Li P. et al., 2016). In contrast, preweaned dairy calves in other countries are mostly infected with C. parvum IIa subtypes, especially IIaA15G2R1, with IId subtypes common only in some areas in Sweden, Romania, Egypt, and Malaysia (Amer et al., 2010, 2013; Muhid et al., 2011; Silverlas et al., 2013; Bjorkman et al., 2015; Vieira et al., 2015; Ibrahim et al., 2016). The source of C. parvum IId subtypes in dairy cattle is not clear (Wang et al., 2014b). The two dominant subtypes in cattle, IIdA15G1 and IIdA19G1, are apparently common in various rodents in China (Table 3). Elsewhere in the world, rodents are seldom infected with C. parvum (Feng et al., 2007a), and when infected, mostly with IIa subtypes (Danisova et al., 2017). Cross-species transmission of IId subtypes is apparently common in China, as other grazing animals such as goats, horses, donkeys, and takins are also known to be infected with IId subtypes (Mi et al., 2014; Qi et al., 2015a; Zhao G. H. et al., 2015; Jian et al., 2016; Peng et al., 2016). The two dominant IId subtypes have been further identified in humans and nonhuman primates in China, suggesting the potential occurrence of zoonotic transmission of C. parvum (Wang et al., 2013b; Du et al., 2015).
Table 2
| Area | No. positive/No. examined (%) | Species (No.) | C. parvum subtype (No.) | References |
|---|---|---|---|---|
| Henan | 172/801 (21.5) | C. bovis (65), C. parvum (54), C. ryanae (19), C. andersoni (12) | IIdA19G1 (67) | Wang et al., 2011b |
| Heilongjiang | 72/151 (47.7) | C. bovis (34), C. andersoni (26), C. ryanae (5), C. meleagridis (5), C. parvum (2) | IIdA19G1 (1) | Zhang et al., 2013a |
| Ningxia | 49/158 (31) | C. parvum (48), C. bovis (1) | IIdA15G1 (51) | Cui et al., 2014 |
| Ningxia | 19/186 (10.2) | C. parvum (15), C. bovis (4) | IIdA15G1 (15) | Huang et al., 2014 |
| Ningxia and Gansu | 122/877 (14.0) | C. bovis (62), C. ryanae (23), C. andersoni (19), C. parvum (18) | IIdA15G1 (18) | Zhang et al., 2015a |
| Xinjiang | 37/237 (15.6) | C. parvum (22), C. bovis (9), C. ryanae (1), C. andersoni (2) | IIdA15G1 (11), IIdA14G1 (4), | Qi et al., 2015c |
| Shaanxi | 46/186 (24.7) | C. bovis (22), C. andersoni (13), C. ryanae (11) | – | Qi, M. Z., et al., 2015 |
| Beijing | 14/404 (3.5)* | C. parvum (10), C. andersoni (4) | IIdA15G1 (4), IIdA19G1 (1), IIdA17G1 (1) | Li F. et al., 2016 |
| Shanghai | 303/818 | C. bovis (199), C. parvum (72), C. ryanae (38) | IIdA19G1 (66) | Cai et al., 2017 |
Common occurrence of Cryptosporidium bovis and dominance of Cryptosporidium parvum IId subtypes in preweaned dairy calves in China.
Animals < 1 year.
Table 3
| Animal | Location | Sample size | No. Cryptosporidium positive (%) | No. of C. parvum | Subtype | References |
|---|---|---|---|---|---|---|
| Golden hamster | Henan | 50 | 16 (32.0) | 4 | IIdA15G1 (4) | Lv et al., 2009 |
| Siberian hamster | Henan | 51 | 4 (7.8) | 2 | IIdA15G1 (2) | |
| Campbell hamster | Henan | 30 | 3 (10.0) | 2 | IIdA15G1 (2) | |
| Siberian chipmunk | Henan | 20 | 6 (30.0) | 2 | IIdA15G1 (2) | |
| Brown rat | Henan | 168 | 11 (6.6) | 9 | IIdA15G1 (9) | Zhao Z. et al., 2015 |
| Golden takin | Shaanxi | 191 | 15 (7.9) | 2 | IIdA19G1 (2) | Zhao G. H. et al., 2015 |
| Yak | Qinghai, Gansu, Sichuan, Tibet | 545 | 22 (4.0) | 12 | IIdA15G1 (3), IIdA19G1 (1), IIdA18G1 (1) | Qi et al., 2015a |
| Goat | Shanghai | 302 | 33 (10.9) | 11 | IIdA19G1 (8), IIaA17G2R1 (1), IIaA15G2R1 (1) | Mi et al., 2014 |
| Horse | Sichuan, Gansu, Inner Mongolia | – | 5 | 4 | IIdA19G1 (3) | Jian et al., 2016 |
| Donkey | Henan, Shandong | – | 82 | 18 | IIdA19G1 (18) | |
| Rhesus monkey | Shaanxi | 86 | 6 (7.0) | 1 | IIdA15G1 (1) | Du et al., 2015 |
Rodents and other animals as possible sources of Cryptosporidium parvum IId subtype family in dairy cattle in China.
Transmission of other zoonotic Cryptosporidium spp. in humans in China
In addition to C. hominis and C. parvum, several other Cryptosporidium species that are traditionally associated with animals, such as C. meleagridis, C. canis, and C. felis, have been found in humans in China (Table 1). This is not surprising considering the frequent reports of these pathogens in humans in other developing countries (Xiao, 2010). As these pathogens were identified in children in urban areas in the absence of C. parvum (Feng et al., 2012; Wang et al., 2017), anthroponotic transmission of these Cryptosporidium species cannot be ruled out. In contrast, C. andersoni has been identified at high frequency in humans in two urban studies in China (Table 1). The unusual high Cryptosporidium infection rates, especially in adult patients (Jiang et al., 2014), and the identification of the canine-specific assemblage C as the dominant G. duodenalis genotype in one of the studies (Liu H. et al., 2014) are some other unusual observations in these studies.
Zoonotic infection appears to be important in cryptosporidiosis epidemiology in rural China, as indicated by the high ratio of zoonotic Cryptosporidium spp. (C. parvum, C. meleagridis, and C. suis) in HIV+ patients in a case-control study in Henan, which identified animal contact as a risk factor for cryptosporidiosis occurrence in the study population (Wang et al., 2013b). Subtype analysis identified the C. parvum as IIdA19G1, which is one of the two major C. parvum subtypes in calves, rodents, and other animals in China (see below).
Transmission of other Cryptosporidium spp. in animals in China
The transmission of Cryptosporidium spp. appears to be unique in sheep and goats. Although, initial studies in Henan and Sichuan indicated a frequent occurrence of the zoonotic pathogen C. ubiquitum in sheep (Wang Y. et al., 2010; Shen et al., 2011), more recent studies have shown a common occurrence of the non-pathogenic C. xiaoi in sheep in Inner Mongolia and Qinghai (Ye et al., 2013; Li P. et al., 2016). Goats in China are also mostly infected with these two Cryptosporidium species, although in some areas a few C. parvum and C. andersoni infections were detected (Mi et al., 2014; Wang et al., 2014a; Peng et al., 2016). Elsewhere in the world, sheep and goats in European countries are frequently infected with the pathogenic and zoonotic species C. parvum, whereas those in Americas are mainly infected with C. ubiquitum. All three Cryptosporidium species appear to be common in sheep in Australia (Ye et al., 2013; Ryan et al., 2014). Cryptosporidium xiaoi appears to be common in sheep and goats in Africa, where like in China animal management is less intensive (Soltane et al., 2007; Mahfouz et al., 2014; Parsons et al., 2015; Hijjawi et al., 2016).
There are quite a few molecular epidemiologic studies of Cryptosporidium spp. in pigs, but results obtained thus far are in agreement with observations in industrialized nations (Wang R. et al., 2010; Chen et al., 2011; Yin et al., 2011, 2013; Zhang et al., 2013b; Lin et al., 2015; Zou et al., 2017). As in other countries, pigs in China are mostly infected with C. suis and C. scrofarum, with different distribution of these two between piglets and adults. The former is preferentially found in preweaned piglets whereas the latter is mostly found in postweaned pigs (Wang R. et al., 2010; Yin et al., 2013; Zhang et al., 2013b), although in one study C. suis was also found in postweaned and adult pigs at high frequency (Lin et al., 2015). Cryptosporidium scrofarum has been identified in Eurasian wild boars in China (Li W. et al., 2017). In contrast, both C. suis and C. scrofarum are common in these animals in Europe (Garcia-Presedo et al., 2013; Nemejc et al., 2013).
Molecular characterizations of Cryptosporidium spp. in other animals are less systematic. There are a few studies on the distribution of Cryptosporidium spp. in dogs and cats in China, but likely in most other areas, only C. canis and C. felis were identified in these animals, respectively (Jian et al., 2014; Li W. et al., 2015; Xu et al., 2016). As expected, these two species have been also found in wild or captive canine and feline animals such foxes, raccoon dogs, and mauls (Felis manul) (Li J. et al., 2015; Zhang S. et al., 2016; Zhang X. X. et al., 2016). As expected, host-adapted Cryptosporidium genotypes have been identified in the a few wild mammals examined, such as minks, bats, and other rodents (Wang et al., 2008b; Lv et al., 2009; Wang W. et al., 2013; Zhao Z. et al., 2015; Li Q. et al., 2016; Zhang S. et al., 2016). Similarly, a new Cryptosporidium genotype related to the bear genotype has been identified in giant panda (Liu et al., 2013), although C. andersoni appears to be common in both giant and less panda (Wang et al., 2015a,b). Interestingly, C. ubiquitum has been identified in pet chinchillas and hedgehogs in China (Qi et al., 2015b; Li Q. et al., 2016). All 11 C. ubiquitum isolates from chinchillas belonged to the XIId subtype family previously identified in the United States. Two novel subtype families of C. ubiquitum related to XIId have been found in wastewater and storm water in Shanghai, indicating C. ubiquitum could be a human pathogen in China (Huang et al., 2017).
Sources of Cryptosporidium contamination in water
Because water exposure is frequently associated with human cryptosporidiosis in industrialized nations, extensive efforts have been made to understand the transport of Cryptosporidium oocysts in environment. The host-adapted nature of most Cryptosporidium spp. has led to the use of genotyping tools to assess the source and human-infective potential of Cryptosporidium oocysts in water (Xiao et al., 2000). Due to cost issues, these types of studies are largely restricted to industrialized nations. With the implementation of new Standards for Drinking Water Quality (GB 5749-2006) (http://www.iwa-network.org/filemanager-uploads/WQ_Compendium/Database/Selected_guidelines/016.pdf) in China in July 2012, Cryptosporidium spp. and G. duodenalis are now among six microbial parameters in the national drinking water quality standard, which has generated increased interest in monitoring for Cryptosporidium oocysts in drinking water and source water, as China is the major source for point and nonpoint Cryptosporidium emission to surface water (Hofstra et al., 2012; Hofstra and Vermeulen, 2016). Currently, the cost of Cryptosporidium detection per water sample in China is >10,000 RMB (>$1,500). As a result, regulatory testing of water samples for Cryptosporidium spp. is, in essence, restricted to large utilities and special events, and genotyping of Cryptosporidium spp. in water remains a research effort only in a few elite academic laboratories.
Procedures have been developed in China to genotype Cryptosporidium spp. in source water using oocyst concentration by flocculation instead of by expensive cartridge filtration and immunomagnetic separation, and detection of Cryptosporidium spp. by PCR instead of immunofluorescence microscopy (Feng et al., 2011b). Compared with the USEPA Method 1623 (USEPA, 2012), the new test cannot provide accurate quantitative data on the contamination level, but is much less expensive and can assess the source and human-infective potential of Cryptosporidium oocysts. This technique has also been used effectively in assessing the human-infective potential of Cryptosporidium spp. in treated urban wastewater (Ma et al., 2016). The recent development of three real-time PCR assays for genotyping and source tracking Cryptosporidium spp. in water could further promote research on Cryptosporidium contamination in drinking source watershed (Li N. et al., 2015).
The use of genotyping tools in the analysis of source water has led to the identification of C. andersoni and C. suis as the dominant Cryptosporidium species in Huangpu River, suggesting that cattle and pigs are major contributors to Cryptosporidium contamination for this drinking water source (Feng et al., 2011b). Similar observations have also been made in other areas in China using other approaches. In these studies, two poultry Cryptosporidium species, C. baileyi and C. meleagridis, also appear in source water in China at higher frequencies than in other countries (Table 4). In other countries, C. suis, C. baileyi, and C. meleagridis are rarely identified in drinking water sources.
Table 4
| Area | Sample size | No. positive (%) | Cryptosporidium species | References |
|---|---|---|---|---|
| Shanghai | 50 | 17 (34.0)* | C. andersoni (14), C. suis (7), C. baileyi (2), C. meleagridis (1), C. hominis (1) | Feng et al., 2011b |
| Shanghai | 178 | 67 (37.6)** | C. andersoni (38), C. suis (27), C. baileyi (16), C. scrofarum (8), C. meleagridis (4), C. parvum (3), C. hominis (2), C. ryanae (1), C. cuniculus (1), C. fragile (1), rat genotype IV (1), avian genotype II (1), avian genotype III (1) | Hu et al., 2014 |
| Chongqing | 66 | 19 (28.8) | C. andersoni (9), C. hominis (6), C. suis (5), C. bovis (3), C. meleagridis (1), C. baileyi (1) | Xiao et al., 2013 |
| Zhejiang | 47 | 37 (78.7) | C. suis (2), avian genotype III (2), C. scrofarum (1), C. ubiquitum (1), C. fragile (1) | Xiao et al., 2012 |
Cryptosporidium species in drinking source water in China.
Seven samples (41.2%) contained more than one Cryptosporidium species, including six samples containing two species and one containing three species.
Including unspecified number of samples with mixed Cryptosporidium species/genotypes.
The importance of pigs in Cryptosporidium contamination in source water in China was supported by results of the investigation of a pig carcass incident in March 2013, in which more than 16,000 pig carcasses that had been dumped in Jiaxing, Zhejiang Province reached Shanghai via the upper Huangpu River. Much higher Cryptosporidium detection rates were obtained in Huangpu River samples collected upstream of Shanghai during and shortly after the carcass incident, especially the occurrence of C. suis and C. scrofarum, another Cryptosporidium species in pigs (Hu et al., 2014). This was further supported by data on the occurrence of pig-adapted E. bieneusi genotypes in the river water samples.
Challenges and opportunities of Cryptosporidium research in China
Despite recent progress in Cryptosporidium research in China, there remain some challenges. Most studies in this area have used established molecular diagnostic tools (SSU rRNA-based PCR-RFLP tool for species identification and gp60-based PCR-sequencing for subtyping) in prevalence studies. There is a lack of integrated usage of advanced molecular diagnostic tools and sophisticated epidemiological design in field studies of cryptosporidiosis. Studies are urgently needed to address public health issues related to the rapid economic development in China, such as changes in incidence and epidemiology of cryptosporidiosis in humans, impacts of concentrated animal feeding operations on Cryptosporidium transmission and environmental contamination, and potential introduction and dispersal of virulent and zoonotic Cryptosporidium species and subtypes from the Belt and Road countries. Efforts also could be made to substantiate some unusual molecular epidemiologic observations of cryptosporidiosis in China by research teams, such as the finding of C. tyzzeri and C. serpentis in several species of farm animals (Chen and Huang, 2007, 2012; Chen and Qiu, 2012) and the unexpectedly high occurrence of C. andersoni in urban human populations (Jiang et al., 2014; Liu H. et al., 2014). These observations are in stark contrast to other reports, and have important public health and regulatory implications.
For young scientists new to research, now may be the best time to conduct research on Cryptosporidium spp. In the past few years, the identification of cryptosporidiosis as a major cause for moderate-to-severe diarrhea in young infants in developing countries, the increasing occurrence of waterborne cryptosporidiosis in industrialized nations because of the chlorine–resistant nature of the parasite, and the lack of effective treatment and vaccines have attracted the attention of funding agencies. With new research investments and involvements of scientists from other research areas, major advances have been made in basic research on Cryptosporidium spp., including in vitro cultivation, cryopreservation, WGS, genetic manipulation, and drug development (Guo et al., 2015b; Vinayak et al., 2015; Morada et al., 2016; Hulverson et al., 2017; Manjunatha et al., 2017). They likely will promote research in pathogen biology of Cryptosporidium spp. and improve the depth of molecular epidemiological studies of Cryptosporidium spp. With these developments, Chinese Cryptosporidium research may be able to broaden its scope and increase its impact.
Statements
Author contributions
YF and LX conducted data collection and analysis and prepared the report.
Acknowledgments
This work was supported by the National Natural Science Foundation of China (31425025 and 31630078). The findings and conclusions in this report are those of the authors and do not necessarily represent the views of the U.S. Centers for Disease Control and Prevention.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest. The reviewer MY and handling Editor declared their shared affiliation.
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Summary
Keywords
cryptosporidiosis, Cryptosporidium, molecular epidemiology, zoonosis, China
Citation
Feng Y and Xiao L (2017) Molecular Epidemiology of Cryptosporidiosis in China. Front. Microbiol. 8:1701. doi: 10.3389/fmicb.2017.01701
Received
28 April 2017
Accepted
23 August 2017
Published
06 September 2017
Volume
8 - 2017
Edited by
Wei Hu, Fudan University, China
Reviewed by
Mingbo Yin, Fudan University, China; Jiaxu Chen, National Institute of Parasitic Diseases, China
Updates
Copyright
© 2017 Feng and Xiao.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Yaoyu Feng yyfeng@scau.edu.cn
This article was submitted to Infectious Diseases, a section of the journal Frontiers in Microbiology
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