In this study, the overall prevalence of Cryptosporidium spp. was 2.2% (11/498), with 2.5% in Himalayan marmots, and 1.0% in Alashan ground squirrels. Other studies reported much higher prevalence of Cryptosporidium spp. in wild rodent species in China than this study, including in house mice (3.2%, 1/31), long-tailed rats (3.6%, 4/111 and 55.3%, 21/38), brown rats (6.3%, 4/64; 9.1%, 22/242 and 28.6%, 16/56), wild plateau pikas (6.3%, 4/64), Qinghai voles (8.9%, 8/90), Asian house rats (18.0%, 21/117; 18.2%, 6/33 and 73.9%, 4/46), Brandt’s voles (18.7%, 127/678), Muridae (40.0%, 4/10)[19, 26–31]. The prevalence in this study was also lower than that in some pet rodent species, including in bamboo rats (3.3%, 3/92), Siberian hamsters (7.8%, 4/51), red squirrels (8.6%, 27/314 and 26.3%, 5/19), Chichillas (9.3%, 26/280), chinchillas (10.0%, 14/140), campbell hamsters (10.0%, 3/30 and 22.2%, 6/27), Siberian chipmunks (30.0%, 6/20), gold hamsters (32.0%, 16/50), chipmunks (50.0%, 1/2 and 75.0%, 3/4 ), guinea pigs (52.3%, 162/310 and 85.0%, 34/40), Roborovski dwarf hamsters(100.0%,1/1), and higher than that in pet red-bellied tree squirrels (1.4%, 4/287) [28, 32–37]. In addition, there was difference between prevalence in different farmed and laboratory rodent species, including farmed bamboo rats (2.1%, 9/435 and 29.5%, 209/709), farmed brown rat (7.1%, 12/168), experimental brown rats (0.6%, 2/355), laboratory mouse (1.7%, 4/229), laboratory rat (4.0%, 1/25) [26, 28, 38–40]. These variations in the prevalence of Cryptosporidium spp. in different studies may be explained by many factors, including the population densities, health status of hosts, management systems, experimental method and source region [41].
Altogether, four Cryptosporidium genotypes were identified in this study. One known horse genotype was originally isolated from a Prezewalski wild horse at the Prague Zoo in Czech Republic, and commonly detected in horses and donkeys, occasionally found in neonatal calves and hedgehogs [42, 43]. It has also been found in human patients with diarrhea in the UK and USA, suggesting its zoonotic potential [44–46]. In the present study, horse genotype was identified in rodents for the first time, indicating it has a broader range of host range than initially anticipated. Horse genotype isolated from Alashan ground squirrels was further identified as novel subtype VIbA10. Currently, two subtype families are recognized within the Cryptosporidium horse genotype by sequence analysis targeting gp60 gene: VIa subtype family in animals (horses, donkeys and a calf, etc.) and VIb subtype family in humans and hedgehogs.
In addition, three novel Cryptosporidium genotypes (marmot genotype I, marmot genotype II and marmot genotype III) were also detected. To date, a total of 13 Cryptosporidium spp. species and 19 genotypes have been detected in 16 studies of various rodents in China, including those obtained in this study (Table 2) [19, 26–36, 38–40]. Among them, 11 species have been detected in humans: C. parvum, C. muris, C. ubiquitum, C. andersoni, C. occultus, C. viatorum, C. canis, C. suis, C. erinaceid, C. tyzzeri and horse genotype 4. Indicating rodent species may play an important role in the transmission of zoonotic cryptosporidiosis.
Table 2
Cryptosporidium species/genotypes in rodents in China.
Host species (Latin name) | No. positive (%) | Species/genotype (n) | Sample source | Ref |
Alashan ground squirrel (Spermophilus alaschanicus) | 1/99 (1.0) | horse genotype (1) | wild | this study |
Asian house rat (Rattus tanezumi) | 6/33 (18.2) | C. parvum (3), C. muris (3) | wild | 26 |
Asian house rat (Rattus tanezumi) | 6/33 (18.2) | C. tyzzer (1), rat genotype II (1), rat genotype III (1), C. tyzzer + rat genotype II (1), C. tyzzer + rat genotype III (1) | wild | 28 |
Asian house rat (Rattus tanezumi) | 34/46 (73.9) | rat genotype IV (24), rat genotype III (8), C. occultus (1), C. erinacei (1) | wild | 31 |
bamboo rats (Rhizomys sinensis) | 9/435 (2.1) | bamboo rat genotype I (5), C. parvum (2), C. occultus (1), bamboo rat genotype II (1) | farmed | 39 |
bamboo rats (Rhizomys sinensis) | 3/92(3.3) | C. parvum (3) | pet | 33 |
bamboo rats (Rhizomys sinensis) | 209/709 (29.5) | C. ubiquitum-like (85), C. parvum (78), C. parvum-like (45), C. occultus (1), | farmed | 40 |
Brandt's vole (Lasiopodomys brandtii) | 127/678 (18.7) | C. suis, muskrat genotype II, Brandt's voles genotype I | wild | 30 |
brown rats (Rattus norvegicus) | 4/64 (6.3) | C. tyzzer (3), C. tyzzer + rat genotype III (1) | wild | 28 |
brown rat (Rattus norvegicus) | 12/168 (7.1) | C. parvum (9), C. muris (3) | farmed | 26 |
brown rats (Rattus norvegicus) | 22/242 (9.1) | C. ratti (14), rat genotype IV (6), C. occultus (1) | wild | 29 |
brown rat (Rattus norvegicus) | 16/56 (28.6) | rat genotype IV (13), C. muris (1), C. occultus (1), rat genotype III (1) | wild | 31 |
Campbell hamster (Phodopus campbelli) | 3/30 (10.0) | C. parvum (1), C. andersoni (1), C. muris + C. parvum (1) | pet | 28 |
Campbell hamster (Phodopus campbelli) | 6/27 (22.2) | hamster genotype (4), C. andersoni (2) | pet | 37 |
Chichillas (Chinchilla lanigera) | 26/280 (9.3) | C. ubiquitum (23), C. parvum (2), chipmunk genotype V (1) | pet | 37 |
Chipmunk (Eutamias asiaticus) | 1/2 (50.0) | ferret genotype (1) | pet | 36 |
Chipmunk (Eutamias asiaticus) | 3/4 (75.0) | ferret genotype (2), chipmunk genotype V (1) | pet | 37 |
Edward's long-tailed rat (Leopoldamys edwardsi) | 21/38 (55.3) | rat genotype IV (13), rat genotype III (1), C. muris (1), C. occultus (1) | wild | 31 |
experimental brown rats (Ruttus norvegicus) | 2/355 (0.6) | C. ubiquitum (1), undetermined Cryptosporidium genotype (1) | laboratory | 38 |
gold hamster (Mesocricetu auratus) | 16/50(32.0) | C. muris (6), C. andersoni (5), C. parvum (2), C. muris + C. parvum (1), C. andersoni + C. parvum (1) | et | 28 |
guinea pig (Cavia porcellus) | 162/310 (52.3) | C. wrairi (129), C. homai (32), C. muris (1) | pet | 37 |
guinea pig (Cavia porcellus) | 34/40 (85.0) | C. wrairi (30) | pet | 28 |
Himalayan marmot (Marmota himalayana) | 10/399 (2.5) | Himalayan marmot genotype I (7), Himalayan marmot genotype II (2), Himalayan marmot genotype III (1) | wild | this study |
house mouse (Mus musculus) | 1/31 (3.2) | C. muris (1) | wild | 26 |
laboratory mouse (Mus musculus) | 4/229 (1.7) | C. tyzzer (4) | laboratory | 28 |
laboratory rat (Rattus norvegicus) | 1/25 (4.0) | C. tyzzer (1) | laboratory | 28 |
long-tailed rats (Leopoldamys edwardsi) | 4/111 (3.6) | C. viatorum (4) | wild | 27 |
Muridae (Niviventer fulvescens) | 4/10 (40.0) | rat genotype III (2), rat genotype IV (2) | wild | 31 |
pet chinchillas (Chinchilla lanigera) | 14/140 (10.0) | C. ubiquitum (13), C. parvum (1) | pet | 35 |
Qinghai vole (Microtus fuscus) | 8/90 (8.9) | C. parvum (3), Qinghai vole genotype (3), C. canis (1), C. ubiquitum (1) | wild | 19 |
red-bellied tree squirrels (Callosciurus erythraeus) | 4/287 (1.4) | rat genotype II (2), C. parvum (1), C. wrairi (1) | pet | 32 |
red squirrels (Sciurus vulgaris) | 27/314 (8.6) | rat genotype II (8), ferret genotype (8), chipmunk genotype III (5), C. ratti (4), C. parvum (2) | pet | 34 |
red squirrel (Sciurus vulgaris) | 5/19 (26.3) | ferret genotype (5) | pet | 28 |
Roborovski dwarf hamster (Phodopus roborovskii) | 1/1 (100) | C. muris (1) | pet | 37 |
Siberian chipmunk (Tamias sibiricus) | 6/20 (30.0) | ferret genotype (3), ferret genotype + C. parvum (1), C. muris + C. parvum + chipmunk genotype III (1) | pet | 28 |
Siberian flying squirrel (Pteromys volans) | 1/1 (100) | C. ubiquitum (1) | pet | 37 |
Siberian hamster (Phodopus sungorus) | 4/51 (7.8) | C. muris (1), C. parvum (1), C. andersoni + C. parvum (1), hamster genotype (1) | pet | 28 |
Siberian hamster (Phodopus sungorus) | 32/37 (86.5) | hamster genotype (26),C. andersoni (6) | pet | 37 |
Syrian hamster (Mesocricetus auratus) | 26/30 (86.7) | C. andersoni (26) | pet | 37 |
white-toothed rat (Berylmys bowersi) | 21/117 (18.0) | C. viatorum (21) | wild | 27 |
wild plateau pika (Ochotona curzoniae) | 4/64 (6.3) | C. parvum (2), pika genotype (2) | wild | 19 |
Note: Plus signs indicate that the sample was co-infected with different Cryptosporidium species/genotypes. |
The present study detected the infection of two pathogens in two wild rodent species of the genus Marmota and genus Spermophilus. Further, eight previous studies have reported the occurrence of Cryptosporidium species/genotypes in other three species of the genus Marmota and other four species of genus Spermophilus : including C. ubiquitum in woodchuck (Marmota monax) in the USA [47, 48]; C. parvum in yellow-bellied marmot (Marmota flaviventris) in the USA[49]; C. andersoni in Bobak marmot (Marmota bobac) in the Czech Republic[42]; C. rubeyi in California ground squirrels (Spermophilus beecheyi) in the USA, Belding's ground squirrels (Spermophilus beldingi) and golden-mantled ground squirrels (Spermophilus lateralis) in the USA [50–52]; ground squirrel genotype I and ground squirrel genotype III in thirteen-lined ground squirrels (Spermophilus tridecemlineatus) in USA [53].
In this study, the overall prevalence of G. duodenalis was 1.6% (8/498), with 1.5% (6/399) for Himalayan marmots and 2.0% (2/99) for Alashan ground squirrels, which are lower than that reported in rodents in China: house mouse (3.2%, 1/31); Asian house rat (6.1%, 2/33); brown rat (6.6%, 11/168 and 9.3%, 33/355); pet chipmunks (8.6%, 24/279); bamboo rat (10.8%, 52/480); coypus (12.3%, 38/308); pet chinchillas (27.1%, 38/140)[26, 38, 54–57] (Table 3).
Table 3
G. duodenalis assemblages in rodents in China.
Host species (Latin name) | No. positive (%) | Assemblage (n) | Sample source | Ref |
bg | gdh | tpi |
Alashan ground squirrels (Spermophilus alashanicus) | 2/99 (2.0) | B (2) | B (2) | | wild | this study |
Asian house rat (Rattus tanezumi) | 2/33 (6.1) | G (2) | G (1) | G (1) | wild | 26 |
bamboo rat (Rhizomys sinensis) | 52/480 (10.8) | B (52) | B (27) | B (12) | farmed | 55 |
brown rat (Rattus norvegicus) | 11/168 (6·6) | G (11) | G (9) | G (10) | wild | 26 |
brown rat (Ruttus norvegicus) | 33/355 (9.3) | G (19) | G (20) | G (21) | laboratory | 20 |
coypus (Myocastor coypus) | 38/308 (12.3) | B (11), A (1) | B (10), A (1) | B (22), A (3) | farm | 57 |
Himalayan marmots (Marmota himalayana) | 6/399 (1.5) | A (1), B (3), E (1) | B (2), E (1) | - | wild | this study |
house mouse (Mus musculus) | 1/31 (3.2) | G (1) | - | G (1) | wild | 26 |
pet chinchillas (Chinchilla lanigera) | 38/140 (27.1) | A (4), B (8) | A (4), B (16) | A (3), B (3) | pet | 35 |
pet chipmunks (Eutamias asiaticus) | 24/279 (8.6) | G (11), A (13) | G (7), A (10) | G (4), A (13) | pet | 54 |
In this study, the sequences of amplicons from G. duodenalis-positive samples were determined to be assemblages A, B, and E, with assemblage B being more prevalent. Assemblages A, B and E were identified in Himalayan marmots and assemblage B in Alashan ground squirrels. G. duodenalis assemblages in Himalayan marmots were richer than Alashan ground squirrels. As we known, G. duodenalis infections in Chinese rodents were reported to be caused by assemblage A, B and G in previous studies [26, 38, 54–57]. Among them, assemblages A and B have a broad host range and commonly found in humans [55]. In fact, some recent studies in China also reported the occurrence of assemblage Ain pet chipmunks, coypus and pet chinchillas, while assemblage Bin bamboo rat, coypus and pet chinchillas [54–57]. These two assemblages detected in this study, suggesting that these two rodent species can play a role in the zoonotic dissemination of G. duodenalis. Assemblage E is commonly found in a range of hoofed livestock, it has also been found in human cases, indicating that this assemblage is of zoonotic significance [58]. And one recent study describes the occurrence of assemblage E in a rodent species long-tailed chinchillas in Romania [59]. And in the present study, we characterized the appearances of assemblages E in rodents in China for the first time, and identified a novel assemblage E sequence (GenBank: MZ494459), sequence comparison showed that this isolate had high homology with a known assemblages E sequence available on GenBank (GenBank: KY633473), with only 1 base differences.
In the investigated areas of QTPA, wild rodent species Himalayan marmots and Alashan ground squirrels have strong migration habits and often share pasture with humans, herbivorous animals and other wild animals. Results of this study suggest that the two wild rodent species may play an important role in the transmission of Cryptosporidium spp. oocysts and G. duodenalis cysts among humans, animals, water sources and fresh produce in QTPA grassland ecosystem, and pose a threat to grassland ecosystem and public health.