Skip to main content
PLOS Neglected Tropical Diseases logoLink to PLOS Neglected Tropical Diseases
. 2014 Aug 28;8(8):e3090. doi: 10.1371/journal.pntd.0003090

Prevalence and Risk Factors for Echinococcal Infection in a Rural Area of Northern Chile: A Household-Based Cross-Sectional Study

Gerardo Acosta-Jamett 1,*,#, Thomas Weitzel 2,#, Belgees Boufana 3, Claudia Adones 4, Andrea Bahamonde 5, Katia Abarca 5, Philip S Craig 3, Ingrid Reiter-Owona 6
Editor: Mehmet Ali Ozcel7
PMCID: PMC4148223  PMID: 25167140

Abstract

Background

Hydatidosis is a zoonotic disease of worldwide distribution caused by Echinococcus granulosus. Our study aimed to determine the prevalence of human and canine echinococcosis as well as the associated risk factors in a rural area of the Limarí province in northern Chile.

Methodology/Principal Findings

A cross-sectional study was conducted between August and November 2009 using a stratified sampling design in each of the five districts of the province. In the selected villages, up to 10 households were sampled. Serum and fecal samples from an adult family member and a dog were collected from each participating household. Risk factors were assessed by standardized questionnaires. Seroprevalence was assessed using a multi-step approach: an ELISA for screening, IFA, IHA and western blot for confirmation of results, respectively. The prevalence of echinococcal infection in dogs was determined by coproantigen genus specific ELISA. Chi-square, Fisher tests and logistic regressions were used to assess risk factors for human seropositivity and dog copropositivity. A seroprevalence of 2.6% (10/403) and coproprevalence of 28% (26/93) was recorded for humans and dogs respectively. Contact with dogs and dog feces were risk factors for human seropositivity while dog copropositivity was associated with home slaughter of livestock (OR = 3.35; CI 90%: 1.16–6.85) and households de-worming dogs (OR = 2.82; CI 90%: 1.33–8.43).

Conclusions/Significance

Echinococcal infection of humans and their dogs is common in Limarí province. Risk factors for human seropositivity were related to contact with domestic dogs and their feces, whereas those for dogs were home slaughter of livestock and the practice of de-worming dogs.

Author Summary

Hydatidosis is a hyperendemic zoonotic disease in Chile caused by the dog tapeworm, Echinococcus granulosus. In Chile as in many other countries in South America, this disease has been largely neglected with few exceptions. Chile's growing economy and the interest of health authorities has lead to an increase in the number of studies investigating the epidemiology of echinococcosis and the factors related to infections of the main definitive host, the domestic dog and humans. In this study, we determined the prevalence of human and canine echinococcosis as well as the associated risk factors in a rural area of the Limarí province in northern Chile. We undertook a household questionnaire survey in rural areas of the five municipalities of the Limarí province in Coquimbo region. For each household serum of an adult family member and fecal samples from a dog were taken. Results of our study indicate that infection occurs in 2.6% of humans and 28% of dogs and is primarily due to feeding of dogs with contaminated offal and high dog-human contact. As a result of this study, the Chilean Ministry of Health instigated a control program aimed to control the infection in dogs and avoid new infections to humans.

Introduction

Hydatidosis or cystic echinococcosis (CE) is a chronic zoonotic parasitic disease of almost worldwide distribution caused by the cestode parasite Echinococcus granulosus. Cystic echinococcosis accounts for 95% of the estimated 2–3 million cases of human echinococcal infections worldwide and represents a major public health problem in many parts of the world [1]. It is listed by the World Health Organization as a neglected zoonotic disease since this disease mainly affects poor and marginalized populations in low-resource settings (www.who.int/neglected_diseases/zoonoses).

The life cycle of this helminth includes carnivores, mostly dogs, as definitive hosts and herbivores such as sheep and goats as intermediate hosts. Humans become infected after accidental ingestion of eggs excreted with carnivore feces. Cystic echinococcosis in humans and animals is characterized by the development of metacestode larval stages in the liver and other organs. Known key factors of persistence, emergence or re-emergence of hydatid disease in a given human population are among others (i) the presence of large numbers of dogs harbouring E. granulosus worms, (ii) access of dogs to infected offal (iii) inadequate facilities for slaughter and destruction of infected viscera, (iv) slaughtering of livestock in homesteads [2], [3]. The practice of feeding dogs with infected offal is by far one of the most important factors for the persistence of this disease [4]. The age of dogs is another relevant factor, since young dogs eliminate higher numbers of echinococcal eggs in their feces than older dogs [5][7]. In addition, restrictions regarding dog ownership are of epidemiological influence, since street dogs have an increased risk of acquiring E. granulosus infection through uncontrolled access to infected carcasses [7]. Other factors include the lack of regular deworming of dogs and the absence of knowledge pertaining to infection and disease [5][7].

Echinococcus granulosus is hyperendemic in the southern parts of South America, e.g. Argentina, Chile, Peru, and Uruguay, where it has an important economic and public health impact [8]. Sheep are the main intermediate host for the G1 genotype of E. granulosus, which has a worldwide distribution including South America [9]; to the best of our knowledge no studies of the genetic strain circulating in Chile has yet been published. The epidemiological situation in South America is complex and not fully understood and comprehensive epidemiological data is lacking. In Chile, echinococcosis mostly affects humans and their livestock in rural and poorly developed areas. According to national surveillance data, the surgical incidence has remained stable at around 2 cases per 100,000 inhabitants since the early 1990s [10], [11].

Although in Chile hydatid disease is a relevant public health problem, data regarding local distribution and risk factors is limited. One study carried out in the Coquimbo region which assessed risk factors for the presence of E. granulosus eggs in dog feces revealed that juvenile dogs from households performing home slaughter, which had not been de-wormed in the two previous months, were at highest risk of contracting echinococcosis [12]. To the best of our knowledge, epidemiological studies of E. granulosus infection in both humans and dogs at a household level, which are essential to implement control programs, have not been carried out in Chile and are rarely reported elsewhere [eg. 13], [14], [15]. Our study aimed to determine the prevalence of human echinococcosis as well as the associated risk factors including canine echinococcosis in rural areas of the Limarí province of the Coquimbo region in northern Chile.

Materials and Methods

Study Design

A cross-sectional study was conducted from August to November 2009 within the Limarí province of the Coquimbo region in northern Chile (Figure 1). Stratified sampling depended on the number of rural villages in each of the five municipalities. To estimate sample sizes, we used an echinococcosis prevalence of 3% in humans [16] and 28% in dogs [17]. For target values of 90% for confidence intervals and ±2.5% and ±4% for errors of human and dog populations, respectively, a sample size of 480 human samples was estimated using Epi Info 6.0 (wwwn.cdc.gov/epiinfo/). This number was approximated to 500 samples, of which 84, 67, 46, 217, and 86 were assigned to the municipalities of Ovalle, Punitaqui, Rio Hurtado, Monte Patria, and Combarbalá, respectively, according to the proportion of villages of each municipality and the overall number of villages in the province. In each village/settlement, ten households were randomly selected to be visited. During field visits epidemiological data was collected by a standardized questionnaire and blood samples were obtained from one adult per household (keeping an even sex ratio of the total samples). Furthermore, a fecal sample was collected from one dog per household in randomly selected households of two municipalities.

Figure 1. Study site in the Coquimbo region of Chile.

Figure 1

Down right: Coquimbo region of Chile (grey); Left: Limarí province within the Coquimbo region with its five municipalities (grey), where the household-based study was performed. Up: Map of the Limarí province. In black dots are interviewed households in the five municipalities across the study area.

Ethical Approval

The study was approved by the Institutional Review Board (IRB) of the Ministry of Health at the Coquimbo region. Information regarding the study was initially communicated to potential participants prior to their signing an informed consent.

Data Collection

The study included a questionnaire survey to determine the potential risk factors for transmission of E. granulosus in humans and dogs [eg. 5], [12]. The questionnaire included basic demographical data of the dog owner and his household, data on education and occupation, living standards including waste management and water supply as well as slaughtering practices and knowledge of the disease (using graphic material). Furthermore, the questionnaire covered data about the sampled dogs, dog-keeping practices, such as contact with dogs (i.e. high: grooming, petting, sleeping with dogs, dogs allowed to enter into the house; low: dogs sleeping outside the household with close contact on few occasions) and other factors that could influence contact between humans and the parasite. Complex questions were asked as open format questions to reduce bias. The questionnaire took between 30–40 minutes to complete.

Sampling and Laboratory Analysis

After each interview, a blood sample was taken from each participant by peripheral venipuncture. Specimens were centrifuged on the same day using a portable centrifuge (Mobilspine, Vulcon Technologies, Richmond, USA), serum was separated and kept at −20°C until further analysis. Additionally, a fresh fecal sample from one dog within each household was collected either rectally or from the ground as previously described [14]. A small amount (approx. 1 gram) of feces was placed in 5% phosphate-buffered saline formalin and thoroughly mixed. The supernatant was transferred into Eppendorf tubes and maintained at 4°C until further analysis [5].

Human serum samples were all screened by a commercial enzyme-linked immunosorbent assay (ELISA) detecting IgG antibodies against E. granulosus antigens (Echinococcus IgG ELISA classic, Serion Immundiagnostica, Würzburg, Germany). Positive or indeterminate samples were retested at the Institute of Medical Microbiology, Immunology and Parasitology, Bonn, Germany, by additional serological techniques such as indirect hemagglutination assay (IHA) and immunofluorescence assay (IFA), which have been described elsewhere [18]. Samples with positive or borderline results in either in-house assay were confirmed by Western Blot (WB) (Echinococcus Western Blot IgG, LDBIO Diagnostics, Lyon, France). Seropositivity was defined by means of a WB positive result. To diagnose echinococcal infections in dogs, an Echinococcus genus-specific coproantigen ELISA was used (Cestode Zoonoses Research Group, University of Salford), as previously described [19], [20].

Data Analysis

Data was analyzed using Stata 10.0 (Stata Corporation, Texas, USA). To compare frequencies of confirmed seropositive human samples between municipalities, a Fisher exact test was used. Additionally, risk factors associated with seropositivity to E. granulosus in people inhabiting rural areas of the Limarí province was assessed by two tailed Fisher or Chi-square tests. To determine risk factors for canine echinococcosis, fixed effect logistic regression analyses were performed, using adjustment by sample numbers in each municipality. For risk analysis, univariate logistic regression was carried out to select variables with p values≤0.250, which were included in further multivariate models.

Results

Questionnaire Survey

A total of 393 households were visited (Figure 1). An overall of 3.5 persons and 2.2 dogs per household were included, with a ratio of 1.7 human per each dog per household. Livestock herding was the occupation reported by 23% of interviewees. Only 64% of interviewees reported to have finished their primary education and 52% of them said to have potable water. In 3% of all households, at least one member reported to suffer from hydatid disease. High contact rates with dogs and regular contact with dog feces were reported by 41% and 43% of the participants, respectively. The majority of individuals (75%) stated that they had never dewormed their dogs with antiparasitic drugs. Home slaughter or purchase of undisemboweled animals for consumption was reported in 63% of households, of which 75% had noticed the presence of fluid-filled structures compatible with hydatid cysts. Furthermore, 61% reported the presence of household dogs during slaughter or disembowelment of livestock, 50% reported feeding of dogs with viscera, and 34% feeding of dogs with hydatid cysts. Regarding the knowledge of zoonotic diseases, 55% of participants quoted that they knew of diseases transmitted from animals to humans, however only 17% had heard about human hydatidosis (Table 1).

Table 1. Demographic features and behavioral and educational characteristics regarding variables that could be factors for echinococcal infection in the Limarí province, Chile.

Variables Overall 90% CI
Persons per household 3.5 3.3–3.7
Dogs per household 2.2 2.1–2.3
Human per dog at household 1.7 1.6–1.8
Livestock herding 23% 20%–27%
Primary education 64% 60%–67%
Potable water 52% 48%–57%
Hydatidosis at household 3% 2%–5%
High rate of dog contacts 41% 37%–45%
Collection of dog feces 43% 39%–47%
De-worming of dogs 25% 22%–29%
Home slaughter 63% 59%–67%
Cysts seen in carcasses 75% 71%–78%
Dogs present at slaughter 61% 57%–65%
Feeding dogs with viscera 50% 46%–54%
Feeding dogs with cysts 34% 31%–38%
Zoonotic diseases known 55% 51%–59%
Hydatidosis known 17% 14%–21%

Overall and 90% Confidence intervals are given for each variable.

Human Seroprevalence and Risk Factors to E. granulosus

The initial ELISA screening revealed positive results in 47 out of 403 serum samples, resulting in a seroprevalence of 12% (90% CI 9–14%). When the 47 initially positive samples were retested by IHA, IFA, and WB 10 samples were confirmed positive by this multi-step analysis, resulting in a seroprevalence of 2.6% (90% CI 1.6–4.4%). Prevalence in different municipalities ranged from 0% to 6.8%, but remained without significant differences (Table 2). Statistical analyses revealed that a higher seropositivity was found in people from households reporting high dog contact, those that allowed dogs to defecate in orchards, and those that did not regularly collect their dog feces (Table 3). Due to the small number of positives it was not possible to run a multivariable analysis. A further study with a larger sample size is recommended.

Table 2. Seroprevalence of antibodies against E. granulosus in different municipalities of the Limarí province, Chile.

Municipality Total Positives Prevalence 90% CI
Combarbalá 60 1 1.7 0.6–6.3
Monte Patria 148 4 2.7 1.3–6.0
Ovalle 77 1 1.3 0.5–5.9
Punitaqui 59 4 6.8 3.3–14.6
Río Hurtado 40 0 0.0 0.0–7.0

ELISA test followed by confirmatory tests.

Table 3. Analysis of factors associated with seropositivity to E. granulosus in inhabitants of the Limarí province.

Factor Pos. result Neg. result % p
Sex
Male 5 125 3.8
Female 5 249 2.0 0.45
Age
18–40 years 4 118 3.3
>40 years 6 256 2.3 0.73
Contact with dogs
High rate 10 274 3.5
Low rate 0 97 0.0 0.07
Occupation
Workers 3 121 2.4
Housewife or retired 6 237 2.5 1.0
Education
Primary 4 185 2.1
Secondary 4 165 2.4 1.0
Knowledge of hydatidosis
No 10 311 3.2
Yes 0 63 0.0 0.38
Collection of dog feces
No 9 205 4.2
Yes 1 168 0.6 0.04
Dogs enter domestic area
No 6 190 3.1
Yes 4 184 2.1 0.75
Dogs sleep in domestic area
No 10 346 2.8
Yes 0 28 0.0 1.0
Dog defecates in backyard
No 4 307 1.3
Yes 6 67 8.2 <0.01
Regular veterinary care
No 8 293 2.7
Yes 2 77 2.6 0.73
Deworming of dogs
No 7 283 2.4
Yes 3 91 3.2 0.71
Home slaughter
No 4 129 3.0
Yes 6 245 2.4 0.74
Feeding dogs with viscera
No 5 153 3.2
Yes 4 220 1.8 0.50
Cysts seen in carcasses
No 4 150 2.6
Yes 5 219 2.2 1.0
Public water supply
No 2 156 1.3
Yes 8 198 3.9 0.20
Waste disposal
Within private property 6 185 3.1
Public collection 3 183 1.6 0.50
Number of dogs in household
1 4 141 2.8
>1 6 232 2.5 1.0

Analyses were carried out with Fisher exact test. p<0.1 was considered significant.

Dog Coproprevalence and Risk Factors to E. granulosus

A total of 93 canine fecal samples from the Combarbalá and Monte Patria municipalities were collected and analysed. Of those, 26 were positive resulting in an overall prevalence of 28% (90% CI 21–36%). The prevalence in the municipalities of Combarbalá and Monte Patria was 29% (15/52) and 27% (11/41), respectively.

Variables (n = 15) from the epidemiological questionnaire were tested for the risk of the presence of E. granulosus antigen in canine samples in the respective household using a univariable logistic regression analysis (see Table 4). Four variables were selected for further multivariable logistic regression model: ‘de-worming of dogs’, ‘regular veterinary care’, ‘home slaughter’, and ‘feeding dogs with viscera’ (selected variables in bold in Table 4). Final conditional regression analysis revealed that ‘dogs from households reporting home slaughter of livestock were 3.35 (90% CI 1.16–6.85) times more likely to shed E. granulosus antigen than those from households without home slaughter. Furthermore, dogs from households reporting de-worming of pets had a 2.82 (90% CI 1.33–8.43) times higher risk of carrying E. granulosus than dogs from households that did not de-worm their dogs.

Table 4. Univariable logistic regression analysis of factors associated with E. granulosus infection of dogs in households within the Limarí province, Chile (n = 93).

Risk factor Infected Uninfected % OR p
Municipality
Combarbalá 15 37 29 1.00
Monte Patria 11 30 27 0.90 0.98
Dog's sex
Male 21 58 27 1.00
Female 5 9 36 1.53 0.71
Dog's age (months)
0–12 3 10 23 1.00
13–24 1 10 9 0.33 0.71
>24 22 47 32 1.56 0.53
Breed
No 25 59 30 1.00
Yes 1 8 11 0.30 0.44
Deworming
No 17 58 23 1.00
Yes 9 9 50 3.41 0.04
Own property
No 6 13 32 1.00
Yes 20 53 27 0.82 0.94
Owner's occupation
Rising livestock, farmer 7 12 37 1.00
Workers, office, unemployed 1 6 14 0.30 0.38
Housewife, retired 16 48 25 0.57 0.39
Education
Primary 14 35 29 1.00
Secondary 8 25 24 0.80 0.85
Graduate 4 6 40 1.67 0.48
Owner knows hydatidosis
No 18 55 25 1.00
Yes 8 12 40 2.04 0.28
Regular veterinary care
No 24 58 29 1.00
Yes 2 7 22 0.69 0.24
Home slaughter
No 6 31 16 1.00
Yes 20 36 36 2.87 0.04
Cysts seen in carcasses
No 10 26 18 1.00
Yes 15 41 18 0.95 0.92
Dogs present at slaughter
No 12 37 16 1.00
Yes 14 30 22 1.44 0.58
Feeding dogs with viscera
Yes 19 25 21 4.56 <0.01
Waste disposal
Within private property 18 41 23 1.00
Public collection 8 23 14 0.79 0.82

In bold are variables that were retained for the multivariable logistic regression analysis.

Discussion

Our study was designed to obtain an accurate picture of human and dog echinococcosis in rural areas of the Limarí province in the Coquimbo region through the stratification and random selection of villages and households in each municipality. Based on the seroprevalence of 2.6% it may be assumed that about 1560 individuals in this province would have been in contact with the parasite and could suffer from hydatidosis. This value is several orders of magnitude higher than that officially reported [21] and should be considered when planning control programs.

Our findings confirm that monitoring the seroprevalance by means of an ELISA which applies native, cyst fluid antigens of E. granulosus might easily over estimate human exposure to E. granulosus in areas where contact or infection with other helminths is possible. Using a one-step approach with an ELISA of low specificity, as done in many epidemiological studies, the seroprevalence rate would have increased to 12% in our population. Through the implementation of a combination of confirmatory techniques, we attempted to eliminate false positive results caused by cross-reactivity with other parasites [4], as suggested by the WHO [22].

Serological studies have been used to assess prevalence and risk factors of cystic echinococcosis in humans worldwide [eg. 14], [23], [24]. Still, this approach does not detect all cases of CE in a population due to its lower sensitivity compared to field studies using imaging techniques such as portable ultrasound [14], [25], [26]. Therefore, we were not able to calculate the number of false negative and positive individuals in this specific area. Future research on CE in the Coquimbo region should include those tests.

Using coproantigen testing we detected a 28% prevalence of canine infection in two municipalities of the Limarí province. A previous study reported a coproprevalence of 7.2% in dogs originating from both rural and urban settings from the Elqui province in the northern part of Coquimbo region [12]. These dogs could be at a lower risk of infection than those in this study and/or are regularly de-wormed by their owners. Nevertheless, the prevalence reported in this study is lower than that found in other rural areas in Latin America, for example in the central Andes of Perú (51%) [25] and in Río Negro in Argentina (42%) [27].

Two risk factors for E. granulosus infection of dogs were identified. The first, home slaughter, has been previously reported in Chile [12] and elsewhere [28]. The second factor was previous de-worming of dogs in the respective households. The significance of this finding is unclear; one explanation could be that households which deworm dogs actually have higher risk of parasitic infections and that treatment was irregular and inadequate, e.g. by using pyrantel, which does not eliminate E.granulosus tapeworms. Further studies are required to verify this finding such as cross-sectional studies with a larger sample size or longitudinal studies using different de-worming strategies [eg. 29].

In most areas of our study, community level risk factors for the persistence of the parasite within the environment were present such as home slaughter (60%), feeding dogs with cysts (21–45%), and high rates of echinococcosis in dogs (28%). In an endemic area such as the Limarí province, where the main factors for seropositivity are those linked to contact with dogs, it is extremely important for intervention activities to prioritize on the interruption of the chain of infection from dog to human. Thus, strategies should be based on education to promote proper hygienic measures such the management of waste, waste handling, washing hands, the use of plastic gloves when cleaning homesteads, reduction of dog grooming to prevent contact in a highly polluted environment and regular deworming of dogs, repeated at least every 45 days to be effective against E. granulosus [1]. This latter strategy is rarely adapted mainly due to economic constraints. Therefore an important intervention would be to increase the frequency of antiparasitic treatment of dogs by governmental sponsored programs, according to international criteria. Still, only a comprehensive program that includes various measures including education and animal management would allow disruption of the cycle of the parasite [30]. Currently, the Chilean Ministry of Health has taken these recommendations into account and instigated a control program with a focus on public education and de-worming and sterilization of dog populations. This latter measure could reduce the contamination of the environment particularly by young dog populations that are known from previous studies to shed large numbers of echinococcal eggs [7].

The results of our questionnaire survey showed that the crucial factors for the maintenance of the life cycle of E. granulosus were widely present throughout the rural areas of the Limarí province. In the Coquimbo region, hydatid disease is endemic mainly by the existence of large numbers of goats and sheep maintained in rural areas [31]. Due to poverty and poor animal health management, these areas provide ideal conditions for the maintenance of the life cycle of this parasite. A general limitation of our analysis of risk factors was that the questionnaire did not clearly identify current and past practices, a fact which might confound our results and interpretations.

Cystic echinococcosis is a relevant public health and an economic problem worldwide [15], [32][34] as well as in many areas of South America [8] including Chile. [21]. However, due to the lack of solid epidemiological data, difficulties in diagnosis and the chronic nature of infection and the complicated treatment required, it often has low priority and is therefore part of the group of neglected diseases [22]. The epidemiology of human cystic echinococcosis is complex and depends on the presence of the parasite in zoonotic cycles. Prevention and control of infection therefore requires careful mapping of regional epidemiological data and risk factors to tailor intervention strategies to specific situations. Accordingly, this study provides epidemiological data on prevalence and risk factors to both human and canine echinococcal infection that were determined at the household level.

Supporting Information

Checklist S1

STROBE checklist.

(DOC)

Acknowledgments

We thank Galaxia Cortés for her assistance during field work and also to two anonymous reviewers that helped to improve this paper.

Data Availability

The authors confirm that all data underlying the findings are fully available without restriction. All relevant data are within the paper and its Supporting Information files.

Funding Statement

This study was funded by the Servicio Minsiterial de Salud, Coquimbo region. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.

References

  • 1. Craig PS, McManus DP, Lightowlers MW, Chabalgoity JA, Garcia HH, et al. (2007) Prevention and control of cystic echinococcosis. Lancet Infect Dis 7: 385–394. [DOI] [PubMed] [Google Scholar]
  • 2. Battelli G, Mantovani A, Seimenis A (2002) Cystic echinococcosis and the Mediterranean Region: a long-lasting association. Parassitologia 44: 43–57. [PubMed] [Google Scholar]
  • 3. Todorov T, Boeva V (1999) Human echinococcosis in Bulgaria: a comparative epidemiological analysis. Bulletin of World Health Organization 77: 110–118. [PMC free article] [PubMed] [Google Scholar]
  • 4. Eckert J, Deplazes P (2004) Biological, epidemiological, and clinical aspects of echinococcosis, a zoonosis of increasing concern. Clin Microbiol Rev 17: 107–135. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5. Buishi I, Njoroge E, Zeyhle E, Rogan MT, Craig PS (2006) Canine echinococcosis in Turkana (north-western Kenya): a coproantigen survey in the previous hydatid-control area and an analysis of risk factors. Ann Trop Med Parasitol 100: 601–610. [DOI] [PubMed] [Google Scholar]
  • 6. Buishi I, Walters T, Guildea Z, Craig P, Palmer S (2005) Reemergence of canine Echinococcus granulosus infection, Wales. Emerg Infect Dis 11: 568–571. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7. Buishi IE, Njoroge EM, Bouamra O, Craig PS (2005) Canine echinococcosis in northwest Libya: assessment of coproantigen ELISA, and a survey of infection with analysis of risk-factors. Vet Parasitol 130: 223–232. [DOI] [PubMed] [Google Scholar]
  • 8. Moro P, Schantz PM (2006) Cystic echinococcosis in the Americas. Parasitol Int 55: S181–S186. [DOI] [PubMed] [Google Scholar]
  • 9. McManus DP, Thompson RCA (2003) Molecular epidemiology of cystic echinococcosis. Parasitology 127: S37–S51. [DOI] [PubMed] [Google Scholar]
  • 10. Schenone H, Contreras M, Salinas P, Sandoval L, Saavedra T, et al. (1999) Hidatidosis humana en Chile. Seroprevalencia y estimación del número de personas infectadas. Bol Chil Parasitol 54: 70–73. [PubMed] [Google Scholar]
  • 11. Martínez P (2011) Hidatidosis humana: antecedentes generales y situación epidemiológica en Chile, 2001–2009. Rev Chilena Infectol 28: 585–591. [PubMed] [Google Scholar]
  • 12. Acosta-Jamett G, Cleaveland S, Bronsvoort BMd, Cunningham AA, Bradshaw H, et al. (2010) Echinococcus granulosus infection in domestic dogs in urban and rural areas of the Coquimbo region, north-central Chile. Vet Parasitol 169: 117–122. [DOI] [PubMed] [Google Scholar]
  • 13. Himsworth CG, Jenkins E, Hill JE, Nsungu M, Ndao M, et al. (2010) Short Report: Emergence of Sylvatic Echinococcus granulosus as a Parasitic Zoonosis of Public Health Concern in an Indigenous Community in Canada. Am J Trop Med Hyg 82: 643–645. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14. Wang YH, Rogan MT, Vuitton DA, Wen H, Bartholomot B, et al. (2001) Cystic echinococcosis in semi-nomadic pastoral communities in north-west China. T Roy Soc Trop Med H 95: 153–158. [DOI] [PubMed] [Google Scholar]
  • 15. Yang YR, Cheng L, Yang SK, Pan X, Sun T, et al. (2006) A hospital-based retrospective survey of human cystic and alveolar echinococcosis in Ningxia Hui autonomous region, PR China. Acta Trop 97: 284–291. [DOI] [PubMed] [Google Scholar]
  • 16. Lorca M, Garrido M, Contreras M, Salinas P, Alvarez C, et al. (2006) Seroprevalencia de hidatidosis humana en la Región de Coquimbo. Chile. Parasitol Latinoam 61: 111–116. [Google Scholar]
  • 17.Sabelle C (2001) Diagnóstico Equinococosis canina en la región de Coquimbo. Unpublished report: SAG IV region. Ministerio de Agricultura. Chile.
  • 18. Reiter-Owona I, Grüner B, Frosch M, Hoerauf A, Kern P, et al. (2009) Serological confirmatory testing of alveolar and cystic echinococcosis in clinical practice: results of a comparative study with commercialized and in-house assays. Clinical Laboratory 55: 41–48. [PubMed] [Google Scholar]
  • 19. Craig PS, Gasser RB, Parada L, Cabrera P, Parietti S, et al. (1995) Diagnosis of canine echinococcosis-comparison of coproantigen and serum antibody tests with arecoline purgation in Uruguay. Vet Parasitol 56: 293–301. [DOI] [PubMed] [Google Scholar]
  • 20. Allan JC, Craig PS, Noval JG, Mencos F, Liu D, et al. (1992) Coproantigen detection for immunodiagnosis of Echinococcosis and Taeniasis in dogs and humans. Parasitology 104: 347–355. [DOI] [PubMed] [Google Scholar]
  • 21. Acosta-Jamett G, Cleaveland S, Bronsvoort BMd, Cunningham AA, Bradshaw H, et al. (2010) Echinococcus granulosus infection in human and livestock in the Coquimbo region, north-central Chile. Vet Parasitol 169: 102–110. [DOI] [PubMed] [Google Scholar]
  • 22.WHO (2011) Report of the WHO Informal Working Group on cystic and alveolar echinococcosis surveillance, prevention and control, with the participation of the Food and Agriculture Organization of the United Nations and the World Organisation for Animal Health. Geneva, Switzerland. [Google Scholar]
  • 23. Schantz PM, Wang H, Qiu J, Liu FJ, Saito E, et al. (2003) Echinococcosis on the Tibetan Plateau: prevalence and risk factors for cystic and alveolar echinococcosis in Tibetan populations in Qinghai Province, China. Parasitology 127: S109–S120. [PubMed] [Google Scholar]
  • 24. Yang YR, Sun T, Li ZZ, Zhang JZ, Teng J, et al. (2006) Community surveys and risk factor analysis of human alveolar and cystic echinococcosis in Ningxia Hui Autonomous Region, China. B World Health Organ 84: 714–721. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25. Moro PL, Lopera L, Bonifacio N, Gonzales A, Gilman RH, et al. (2005) Risk factors for canine echinococcosis in an endemic area of Peru. Vet Parasitol 130: 99–104. [DOI] [PubMed] [Google Scholar]
  • 26. Macpherson CN, Bartholomot B, Frider B (2003) Application of ultrasound in diagnosis, treatment, epidemiology, public health and control of Echinococcus granulosus and E. multilocularis . Parasitology 127: S21–S35. [DOI] [PubMed] [Google Scholar]
  • 27. Larrieu E, Costa MT, Cantoni G, Labanchi JL, Bigatti R, et al. (2000) Rate of infection and of reinfection by Echinococcus granulosus in rural dogs of the province of Rio Negro, Argentina. Vet Parasitol 87: 281–286. [DOI] [PubMed] [Google Scholar]
  • 28. Watson-Jones DL, Craig PS, Badamochir D, Rogan MT, Wen H, et al. (1997) A pilot, serological survey for cystic echinococcosis in north-western Mongolia. Annals of tropical medicine and parasitology 91: 173–177. [DOI] [PubMed] [Google Scholar]
  • 29. Yang YR, McManus DP, Huang Y, Heath DD (2009) Echinococcus granulosus Infection and Options for Control of Cystic Echinococcosis in Tibetan Communities of Western Sichuan Province, China. Plos Neglect Trop D 3 [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30. Acosta-Jamett G, Cleaveland S, Cunningham A, Bronsvoort M (2010) Demography of domestic dogs in rural and urban areas in Coquimbo region of Chile and its implication for diseases transmission. Preventive Veterinary Medicine 94: 272–281. [DOI] [PubMed] [Google Scholar]
  • 31.INE (2005) Instituto Nacional de Estadísticas. Censo 2002. Resultados población y vivienda. Santiago, Chile.
  • 32. Banks DJ, Copeman DB, Skerratt LF, Molina EC (2006) Echinococcus granulosus in northern Queensland. 1. Prevalence in cattle. Aust Vet J 84: 303–307. [DOI] [PubMed] [Google Scholar]
  • 33. Bekele J, Butako B (2011) Occurrence and financial loss assessment of cystic echinococcosis (hydatidosis) in cattle slaughtered at Wolayita Sodo municipal abattoir, Southern Ethiopia. Trop Anim Health Prod 43: 221–228. [DOI] [PubMed] [Google Scholar]
  • 34. Getaw A, Beyene D, Ayana D, Megersa B, Abunna F (2010) Hydatidosis: prevalence and its economic importance in ruminants slaughtered at Adama municipal abattoir, Central Oromia, Ethiopia. Acta Trop 113: 221–225. [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Checklist S1

STROBE checklist.

(DOC)

Data Availability Statement

The authors confirm that all data underlying the findings are fully available without restriction. All relevant data are within the paper and its Supporting Information files.


Articles from PLoS Neglected Tropical Diseases are provided here courtesy of PLOS

RESOURCES