Introduction
Cysticercus fasciolaris is the larval stage of the adult tapeworm Taenia taeniaeformis (Cestoda), a parasite that presents a global distribution and develops mainly in the small intestine of domestic (Felis cattus) and wild felines (e.g., Felis rufus, Felis silvestris, and Panthera pardus).1,2 Felines get infected naturally by consuming contaminated livers from intermediate hosts.3 However, infection has also been identified in domestic (Canis lupus familiaris) and wild canines, such as red foxes (Vulpes vulpes), and coyotes (Canis latrans).4,5 Laboratory animals that have been experimentally infected with C. fasciolaris have a prepatent period of 34-80 days (41.1 ± 5.9), at the end of which the ingested larvae has developed and become fully infectious.6 An adult T. taeniaeformis tapeworm produces close to 12,000 partially developed eggs (called oncospheres) daily, which are released from the proglottids of the parasite, and shed into the environment with infected host feces.7 Intermediate hosts of T. taeniaeformis are mainly small rodents and lagomorphs, which can become infected by consuming food or water contaminated with viable oncospheres.8 Under experimental conditions, one-month old white mice can get infected with low numbers of eggs (200-500), and develop 11-250 metacestodes in the liver.9,10
Taenia taeniaeformis eggs lose their membrane in the stomach or intestine of intermediate hosts soon after being ingested, releasing larvae that pass through the intestinal wall. Larvae then migrate via the hepatic portal system, reach the liver and develop into C. fasciolaris metacestodes (also known as Hydatigera fasciolaris, Strobilocercus fasciolaris, or Taenia crassicolis). The Taenia taeniaeformis life cycle is completed when a definitive host (feline) ingests an infected intermediate host.3,11
Taenia taeniaeformis is a parasite with zoonotic significance because humans can act as accidental hosts. Adult parasites and metacestodes (C. fasciolaris) have been detected in intestines and liver of people from Argentina, Czech Republic, Denmark, Taiwan, and Sri Lanka.12-14
Synanthropic species such as Rattus norvegicus, Rattus rattus, and Mus musculus are the main intermediate hosts of this parasite, with prevalence ranging from 4.3%15 to 67.7%.16Cysticercus fasciolaris infection has been reported in urban and wild rodents from Brazil,17 Korea,18 Egypt,19 India,20 Malaysia,21 Thailand,22 and Mexico.23-25
Rodents from the R. rattus and M. musculus species have been found infected with C. fasciolaris, in Yucatan.25 It is still unknown however if wild indigenous rodent species also act as intermediate hosts. This study aimed to determine if infection with C. fasciolaris occurs naturally in synanthropic and/or wild rodents, captured in a rural environment in Yucatan, Mexico.
Materials and methods
Study site
A rural tropical community in Cenotillo, Yucatan, Mexico (20º57’N, 88º36’W), with an annual average temperature and rainfall of 25.8 °C and 1,180 mm, respectively, was chosen for this study. The region has a rural settlement with neighboring areas of low deciduous forest, and small extensions of medium-highland forest.26,27
Rodent capture
Rodents were captured from June to December 2016, in dwellings from the study locality and in two undisturbed small areas of low deciduous forest, located 9 km away from the rural settlement. Animal capture followed the guidelines of the American Society of Mammalogists (ASM).28 Both capture and sampling were approved by the Bioethics and Animal Welfare Committees of the Autonomous University of Yucatan (Biological and Agricultural Sciences Campus) (Registry: CB-CCBA M-2016-004) and of the Ministry of Environment and Natural Resources of Mexico (Registry: SGPA/DGVS/00867/17).
Synanthropic rodents were captured by dividing the study locality in four quadrants, by tracing two perpendicular axes that crossed the center of the community, according to the methodology described by Torres-Castro et al29,30 Ten dwellings (40 in total) were sampled in each quadrant over two consecutive nights and in two different weeks within one month. Twelve Sherman traps of 8 × 9 × 23 cm (HB Sherman traps Inc®, Florida, USA) were placed inside the household and throughout the backyard, close to areas where there was evidence of or suspected rodent activity and near potential sources of food or/and lodging.
For wild rodent capture, 100 Sherman traps were distributed along 10 linear transects through the low deciduous forest extensions. Ten traps were placed per transect at 5-6 m intervals. Traps were checked with similar periodicity as that followed and previously described for dwelling quadrants.
All traps were placed in the morning and checked the following day. Bait was a mixture of oat flakes and artificial vanilla flavoring. Species identification of captured rodents was performed by veterinarians, based on the guidelines described in “A Field Guide to the Mammals of Central America and Southeast Mexico”.31
Biological sampling
Captured rodents were transported alive to the parasitology laboratory of the Biological and Agricultural Sciences Campus at the Autonomous University of Yucatan. Animals were anesthetized upon arrival by intraperitoneal sodium pentobarbital injection (130 mg/kg) and euthanized by cervical dislocation, according to American Veterinary Medical Association guidelines.32 Species identification, biometry sex, and age of individuals were determined post mortem.
Abdominal cavity and liver of all rodents were macroscopically inspected to determine the presence of fasciolaris cysts. The larval capsule of found cysts was opened, metacestodes were extracted and preserved in 70% ethanol for morphological identification.
Metacestodes were stained with Semichon’s acetic carmine, mounted on slides with Canada balsam medium and observed under a conventional stereoscope (OLYMPUS-SZ51, Tokyo, Japan). Characterization was performed according to morphological traits described by Bowman et al33 and Malsawmtluangi et al 20
Results and discussion
A total of 153 rodents from seven different species were captured. Most individuals (107, 69.9%) were captured in households and backyards. From these, R. rattus species was the most abundant (63/107, 58.9%), followed by M. musculus (43/107, 40.2%), and Peromyscus yucatanicus (1/107, 0.9%). For rodents captured in low deciduous forest areas (46, 30.1%), the most abundant species was Heteromys gaumeri (22/46, 47.8%), followed by Ototylomys phyllotis (11/46, 23.9%), P. yucatanicus (8/46, 17.4%), R. rattus (2/46, 4.3%), Peromyscus leucopus (1/46, 2.2%), Sigmodon hispidus (1/46, 2.2%), and M. musculus (1/46, 2.2%).
The overall infection was 7.8% (12/153). Cysticercus fasciolaris cysts were found only in animals of the R. rattus species captured in households. Frequency of infection in R. rattus captured both in households and forest patches was 18.5% (12/65), from which 91.7% of the animals (11/12) presented with a single cyst and 8.3% (1/12) with two cysts. Of these 12 infected R. rattus, 75% (9/12) were females and 25% (3/12) males; 58.3% (7/12) were juveniles and 41.7% (5/12) adults.
All C. fasciolaris cysts were almost white and slightly adhered to the liver parenchyma (Fig. 1). Each cyst presented a fibrous capsule of variable thickness, surrounding a slightly coiled white larva, suspended in an opalescent fluid. Extracted larvae measured between 2 and 11 cm in length.
Larvae were morphologically characterized by identifying a large extruded scolex with four lateral suckers and two rows of hooks (larger and smaller hooks in outer and inner rows respectively; Fig. 2). Also, pseudo-segmentations were detected along the strobila (which is found posterior to the scolex and includes the proglottids), and a relatively small terminal bladder was seen. Cysticercus fasciolaris is the only metacestode in which the scolex is not invaginated at the bladder but rather attached to it by the strobile.33
The distribution of Taenia taeniaeformis and C. fasciolaris (larval stage) is ubiquitous. Adult parasites located in intestines of definitive hosts rarely cause clinical signs; however, evidence of disease can relate to the degree of infection, age, body condition, and even host species.33 In contrast, intermediate hosts infected with C. fasciolaris tend to develop more signs and lesions.34
Two transmission cycles have been described for C. fasciolaris: an urban cycle, in which domestic cats and synanthropic rodents are definitive and intermediate hosts, respectively; and a wild cycle, in which a large variety of wild canines and felines, as well as various species of rodents, can be involved. Indeed, Theis and Schwab,35 reported a 3.4% prevalence of T. taeniaeformis in Peromyscus maniculatus from California, and Wanas et al19 found the parasite in Gerbillus gerbillus (33.3%), Acomys cahirinus (16.6%), and Arvicanthis niloticus (7.2%).Moreover, the presence of C. fasciolaris was established in R. rattus wild populations in bamboo forests from Mizoram, India.20
None of the rodents captured from wild environments in this study were positive for C. fasciolaris infection. Absence of a wild transmission cycle that includes rodents may be due to the presence of five indigenous wild feline species that can act as final hosts: Herpailurus yagouaroundi, Leopardus pardalis, Leopardus wiedii, Puma concolor, and Panthera onca. Also, rodent relative population dispersion and density, associated with habitat loss, can adversely impact the efficacy of parasite life cycle maintenance in the region.36-39 Nonetheless, wild rodents from the Yucatan area can be infected by C. fasciolaris as documented for species such as P. yucatanicus, H. gaumeri, and O. phyllotis, that passthrough households located in rural communities that are associated with secondary forest patches.40 These rodents could have become infected by consuming contaminated food or water contaminated with domestic cat feces parasitized with T. taeniaeformis. However, further studies are necessary to conclude this causal association.
Contrary to our findings, in which none of the sampled mice (M. musculus) were positive to infection. Cysticercus fasciolaris has been previously found in this species in a rural community in Yucatan.24 This discrepancy between results could relate to genetic variations of the C. fasciolaris populations and their inherent ability to infect intermediate hosts. In effect, Brandt and Sewell reported distinct infectivity of four T. taeniaeformis isolates in mice and rats.41 Moreover, Nonaka et al observed that C. fasciolaris cysts did not develop in rats, mice, or gerbils infected with T. taeniaeformis eggs derived from a metacestode isolated from a grey red-backed vole mouse (Clethrionomys rufocanus bedfordiae, currently Myodes rufocanus).42
Other factors that affect C. fasciolaris transmission dynamics between intermediate (rodents) and definitive hosts (felids) are: 1) relative population density of hosts; 2) seasonal changes in host and parasite abundance; 3) seasonal vulnerability of parasite eggs due to changes of environmental conditions; 4) host sex; and 5) host age.24,35 Moreover, antibodies against T. taeniaeformis can be transmitted to the offspring of infected rats via colostrum43. However, pups between 25 and 30 days of age seem to be more susceptible to experimental infection than adults or other age groups.44,45
Stability and resilience of parasite eggs to changing environmental conditions may also impact infection prevalence in rodents since contaminated food and/or water sources can be constantly available for individuals geographically associated with definite hosts.24
Conclusions
Results from this study confirm that synanthropic rodents in rural areas of the Yucatan region in Mexico are susceptible to C. fasciolaris infection. An infected Rattus rattus individual could hence contribute to maintain the parasite’s life cycle as an intermediate host, potentially disseminating the infection to domestic cats. There was no evidence of a transmission cycle with wild rodent species.