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Canine fecal contamination in a metropolitan area (Milan, North-Western Italy): prevalence of intestinal parasites and evaluation of health risks.

1. Introduction

Dogs are likely to transmit several zoonotic infections, among which those caused by intestinal helminths and protozoa can be of public concern [1, 2]. People living in urban areas, as cities or large metropolitan areas, are exposed to zoonotic parasites of canine source. Among the nematode species, Toxocara canis represents the major concern because it is well known to cause even severe infection in humans [3, 4]. Other zoonotic helminths, though often neglected, such as hookworms (Ancylostoma caninum and Uncinaria stenocephala) and Trichuris vulpis, are frequently recorded in dogs [5]. Moreover, dogs can harbor either host specific (C, D, F) or zoonotic assemblages (A and B) of Giardia duodenalis, the most frequent parasite affecting domestic carnivores in the last years [6-8]. Additionally, recent molecular-based surveys have shown that a few genotypes of Cryptosporidium spp. are responsible for most human cryptosporidiosis cases, including C. canis (dog type) [9, 10]. Nowadays, intestinal parasites of dogs represent an important concern for humans due to the increasing presence of these pets mainly in urban areas. The parasitic risks for humans are mostly posed by environmental fecal contamination. In fact, parasitic elements (eggs, larvae, cysts, and oocysts) excreted via canine fecal route can survive and be infective in the environment over a long time at different conditions [11]. Thus, not only can dog faeces deposited on public soil, parks, or gardens of cities represent an inconvenience, but it can be mostly a health risk as previously demonstrated [12-15].

Lombardy is the region of north-western Italy with the largest population of companion dogs, representing about 15% of their overall presence in Italy (data from National Companion Registry http://www.salute.gov.it/anagcaninapublic_new/AdapterHTTP). From 2003 to 2010, 834, 075 dogs in Lombardy and approximately 100, 000 of them in the city of Milan were recorded. High environmental fecal contamination still occurs in this area in spite of the fact that public parks now include off-leash fenced areas for a better control of the issue.

Major goal of this survey was to determine the prevalence of canine intestinal parasites in faeces spread on the ground of a large metropolitan area of north-western Italy (Milan) and deriving sanitary risks for humans. Further, differences in parasites prevalence among areas of the city were explored by a geographical information system (GIS) based approach and influences of some factors, such as human density and sizes of green and dog areas, were also considered.

2. Materials and Methods

2.1. Study Area and Sampling. The survey was carried out in Milan, a large metropolitan city located in the north-western Italian region of Lombardy (latitude: 45[degrees]40'N; longitude: 9[degrees]30'E). Milan covers an area of 183, 77 [km.sup.2] populated by 1, 299, 633 inhabitants (ISTAT 2010). The city presents a continental climate (temperature min-max: -4.015.6[degrees]C in the coldest month and min-max: 14.5-37.1[degrees]C in the warmest month) with an annual rainfall of 1, 251 mm (average daily rainfall min-max: 0.50-6.45 mm) (ARPA, http://www.arpalombardia.it/arpa_splash/splash.asp). Milan has more than 21 million square meters of green urban areas organized in public parks presenting very different sizes (the biggest urban area reaches 6.4 million square meters) and is divided into 9 administrative districts (district area extension min-max: 967-3134 h). A GIS by the cadastral maps (1:1000) of the city of Milan (SIT, Cartographic Office of Milan Town Hall) was constructed, and a grid approach followed by transect sampling was used [13]. Then, the territory of Milan was divided into 157 equal, rectangular subareas of 1.6 km x 800 m; in each subarea, a 1-kilometer straight transect was identified along which a veterinary practitioner was instructed to collect 4 faecal samples. Each sampling point was georeferenced and maps with distribution of infected samples were created (ArcGIS 8.3). Further, the administrative district for each faecal sample was identified.

Out of 157 subareas only 138 could be investigated, 19 being inaccessible. The study was conducted between March and November 2010 and a total of 463 faecal samples were all collected in the early morning (before 9 am). All the samples collected derived from dog faeces (there are no foxes in urban Milan) and were fresh deposited (not more than a day).

2.2. Faecal Examination. Macroscopic examination was firstly performed for the detection of proglottids of cestodes. Subsequently, each faecal sample was blended and divided into two aliquots. In order to detect parasite eggs and oocysts one aliquot was subjected to qualitative microscopic analysis by centrifugation-flotation technique with sucrose and sodium nitrate solution (specific gravity: 1360) [16]. The parasite eggs were differentiated according to their morphologic characteristics. The second aliquot was used to detect coproantigens of G. duodenalis and Cryptosporidium by enzyme linked immunosorbent assay (ELISA). For this purpose commercially available kits (RIDASCREEN Giardia and RIDASCREEN Cryptosporidium, R-BiopharmAG, Germany) were used following the manufacturer's recommended procedures. The negative and positive controls contained in the kits were used. Optical density (OD) of each sample was measured at 450 nm utilizing a microplate reader (Multiskan Ascent, Thermo Labsystems, Helsinki, Finland). OD values more than 10% above the calculated cutoff were considered positive. Sensitivity and specificity, respectively, were 100.0% and 99.6% for Giardia kit and 100.0% and 97.3% for Cryptosporidium kit.

2.3. Statistical Analysis. We defined prevalence according to Bush et al. [17]. Since prevalence of single taxa was too low for a risk factor analysis, data on infection with helminths and/or protozoa were also combined to the purpose. A sample was considered positive if tested positive for at least one species of parasites. Preliminary univariate logistic regression was performed considering the following independent variables: administrative district, human population density (inhabitant/[km.sup.2]), green area and dog area sizes ([m.sup.2]), percentage of green and dog areas calculated with respect to the administrative district size, and the number of dog areas for each administrative district. Data were inferred from ISTAT (2010) and Statistics Office of Milan Town Hall. Variables showing a P value <0.20 were included in the multivariate regression model. Backward elimination was used to determine which variables entered the final model, setting at 0.05 the level of significance to be included in the model. All statistical analysis was performed using SPSS v.19.0 (IBM Corp., Armonk, NY, USA).

3. Results

Dog faecal samples (n = 463) were found and collected from 120 (86.8%) out of the 138 surveyed subareas. In most subareas (n = 110) 4 faecal samples were obtained from each (overall 440); in 5 subareas, 3 faecal samples (overall 15), and in 2 subareas, 2 faecal samples (overall 6). Finally, in 2 subareas, only 1 faecal sample in each (overall 2) was detected (Figure 1).

As shown in Table 1, both zoonotic and non zoonotic parasites were observed. Zoonotic parasites were the most frequent, though. As regards helminths, the following prevalences were found: Trichuris vulpis (3.7%), Toxocara canis (1.72%), Strongyloides spp. (0.86%), Ancylostomatidae (0.43%), and Dipylidium caninum (0.43%). In regard to protozoa, 11.06% of the samples showed coproantigens of Giardia and 11.10% were positive to Cryptosporidium coproantigens. Non zoonotic parasites, such as Toxascaris leonina and Cystoisospora with a prevalence of 0.64 and 0.21%, respectively, were also found. Mixed infections were detected in 11 faecal sample (2.4%, 95% CI = 1.3%, 4.2%); in all these samples Giardia was associated with T. canis (n = 2), T.vulpis (n = 7), and T. leonina (n = 2). Out of the 120 subareas considered, 57 (47.5%) were positive to parasitic elements. G. duodenalis was the most prevalent species detected (42 positive subareas). T. vulpis eggs were found in faecal samples from 16 subareas (13.3%). T. caniseggs were obtained in 6 subareas (5%); three of them were located in the center of Milan. In general, the spatial distribution of parasitic stages found in dog faeces did not show any correlation with particular areas of the city (Figure 2).

Results from the logistic regression analysis showed that the size of green areas present in each administrative district expressed by the proportion of green areas with respect to the administrative district area was the variable entered in the final multivariable model; then, the odds of a faecal sample being contaminated by parasitic elements increased by a multiplicative factor of 1.084 with a one percentage point increase of the green areas proportion in the administrative district (Table 2).

4. Discussion

The study demonstrated a widespread faecal contamination of Milan soil, being canine faecal samples found in 86.8% of the surveyed subareas. Further, as previously set during the study design, in most subareas (110 out of 138, i.e., 79.7%) four faecal samples could be collected. The intestinal parasites traced are consistent with the canine parasitic fauna and with the results obtained by previous surveys carried out in Italy [13, 18-21]. Most faecal samples contained elements of zoonotic parasites. Among nematodes, the most frequent zoonotic species were Toxocara canis and Trichuris vulpis; the former is worldwide known as triggering a mostly asymptomatic human infection or the larval migrans syndrome, a severe disease involving the SNC and/or the eye [4]. The latter can sustain a zoonosis of minor importance even though several cases have been described since 1956 when the first case in a child was reported by Hall and Sonnenberg [22]. In general, T. vulpis causesan unapparent disease, but symptomatic infections were also reported in humans [2325]. Other parasites diffusing less relevant zoonoses were found, such as Ancylostomatidae and Dipylidium caninum.

Considering only helminth infections, prevalence (6.7%) of intestinal parasites in canine faecal samples collected from soil in Milan was similar to prevalence reported in a previous survey where eggs were found in 7% of dog faeces from public places, including parks, in Milan [18]. However, in both cases prevalence is lower than findings on pets sampled at Veterinary Clinics of Milan or in central Italy [20, 21]. As stated by Zanzani et al. [21], the difference in prevalence could be due to the kind of faecal samples collected from city soil that mainly included droppings voided by old dogs typically showing lower infection values than young ones. The currently reported prevalence rates of dog helminths are slightly different from those reported in a similar survey carried out in Naples (16.9%), a city in the south of Italy where stray dogs appear more widespread than in northern Italy (data from Italian Health Ministry, http://www.salute.gov.it/) [13]; nonetheless they are consistent with data from other investigated Italian urban areas even though differences in sampling must be considered [15, 26-28].

According to other authors T. canis eggs showed a low prevalence (1.72%) in faeces collected from soil [13, 14], whereas in the aforementioned survey carried out in Milan a prevalence of 5% and 5.5% was found in soil and faecal samples, respectively [18]. In contrast, 16.4% of soil samples collected in public parks of Madrid were demonstrated infected with Toxocara eggs by Dado et al. [14].

As regards protozoa, G. duodenalis was the most prevalent parasite according to other surveys [7, 14, 19, 29]. However, other data obtained by different analytical methods recorded lower prevalence values [18, 30-32]. Further, this protozoan seems largely spread among subareas of Milan unlike Cryptosporidium whose coproantigens were found in a very low number of samples and subareas. The prevalence value of Cryptosporidium is lower than those recently found in Spain varying from 9% throughout 17.6% [14]. Regarding sanitary risks posed by these protozoa, in dogs from Lombardy G. duodenalis assemblages C and D (i.e., Giardia canis) were previously isolated, but zoonotic assemblages can be hosted by dogs [8, 21]. Moreover, both C. canis and C. parvum were identified in the faeces of two dogs from Milan and underwent clinical examination (Manfredi et al., unpublished data). Accordingly, veterinarians should pay more attention to these potentially zoonotic protozoa and improve both their diagnostic and control levels using appropriate methods and due treatments.

Finally, the main risk factor associated with the presence of parasitic stages in dog faecal samples resulted to be the extension occupied by green areas within an administrative district area. In fact, faecal samples collected from administrative districts characterized by a large proportion of green are as were more positive than faeces from administrative districts whose territory showed a smaller proportion of green areas. Therefore, it can be inferred that green areas may contribute to maintain environmental contamination of public areas by canine faeces and deriving health risks posed by dog parasites. In order to prevent sanitary risks for humans, off-leash fenced areas for dogs to be set in public parks, small gardens, or traffic islands have been claimed in each district. However, the presence of fenced areas, as onlycontrol measure of dog parasites, is not able to eradicate the problem since any reserved areas can reasonably become a reservoir of parasites for dogs soiling it as no appropriate treatments are available to free them from parasites. Nowadays a regular control of dog parasites coupled with an appropriate laboratory diagnosis is needed in order to prevent the diffusion of zoonotic parasites in public areas. Owner should be educated to collect dropping voided by their own pets on public areas and to check the parasitic status of their dogs regularly. Other important risk factors associated with endoparasites in dogs from different urban areas resulted to be both animal age and their sharing the same house with other dogs. Thus, there is a strong need for parasitic monitoring of dogs younger than 12 months and of those living with other pets [21, 3335]. Particularly, younger dogs are more exposed to Toxocara canis infections that they can acquire by several routes such as transplacental and transmammary routes by migrating larvae, ingestion of embryonated eggs from the environment or finally by somatic larvae via paratenic hosts. It should be further considered that even though dogs older than 12 months show a parasitic spectrum slightly different from that of younger animals, they themselves may be infected by zoonotic parasites [21]. Last, but not least, owners should be helped to properly consider canine zoonotic parasites. As demonstrated by a survey carried out in Lombardy, a large part of them (50.8%) are not aware about the fact that gastrointestinal (GI) parasites of their dogs do represent a risk to human health [21, 36]. Veterinarians should be more determined in playing their key role in this educational step and in submitting dogs to periodic coprological examination as stated by the international guidelines for control of canine parasites (ESCAAP) as well as more careful in improving the diagnosis of GI parasites in the consideration that they infect nearly 45% of dogs presenting GI signs which urges a differential diagnosis [21, 36].

5. Conclusions

According to the results of this survey, canine faecal samples from public areas in Milan show a relatively high presence of intestinal parasites, among which zoonotic parasites were found most frequently (T. canis, T. vulpis, Ancylostomatidae, and G. duodenalis). In spite of control measures against environmental faecal pollution recently set by local authorities, such as off-leash fenced dog areas within public green areas, the issue is still on. In fact, it requires further and continuous monitoring and control of gastrointestinal parasites in owned dogs to which veterinarians can contribute by properly informing and educating owners about a correct behavior in defense of the health of their pets and of other companion animals they can come in contact with in the urban scenarios.

http://dx.doi.org/10.1155/2014/132361

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

The authors are grateful to Ms/Professor Gigliola Canepa, University of Milan, for her support in editing their paper.

References

[1] P. A. M. Overgaauw, L. van Zutphen, D. Hoek et al., "Zoonotic parasites in fecal samples and fur from dogs and cats in the Netherlands," Veterinary Parasitology, vol. 163, no. 1-2, pp. 115-122, 2009.

[2] D. Traversa, "Pet roundworms and hookworms: a continuing need for global worming," Parasites and Vectors, vol. 5, no. 1, article 91, 2012.

[3] A. C. Y. Lee, P. M. Schantz, K. R. Kazacos, S. P. Montgomery, and D. D. Bowman, "Epidemiologic and zoonotic aspects of ascarid Infections indogsandcats, "Trends in Parasitology, vol. 26, no. 4, pp. 155-161, 2010.

[4] C. N. L. Macpherson, "The epidemiology and public health importance of toxocariasis: a zoonosis of global importance," International Journal for Parasitology, vol. 43, no. 12-13, pp. 999-1008, 2013.

[5] P.N. Achaand B. Szyfres, Zoonoses et maladies transmissibles communes a l'homme et auxanimaux, Office International des Epizooties, Paris, France, 1989.

[6] E. Claerebout, S. Casaert, A. C. Dalemans et al., "Giardia and other intestinal parasites in different dog populations in Northern Belgium," Veterinary Parasitology, vol. 161, no. 1-2, pp. 41-46, 2009.

[7] C. Epe, G. Rehkter, T. Schnieder, L. Lorentzen, and L. Kreienbrock, "Giardia in symptomatic dogs and cats in Europe-Results of a European study," Veterinary Parasitology, vol. 173, no. 1-2, pp. 32-38, 2010.

[8] U. Ryan and S. M. Caccio, "Zoonotic potential of Giardia" International Journal for Parasitology, vol. 43, no. 12-13, pp. 943-956, 2013.

[9] L. Xiao and Y. Feng, "Zoonotic cryptosporidiosis," FEMS Immunology & Medical Microbiology, vol. 52, no. 3, pp. 309-323, 2008.

[10] Y. Feng, "Cryptosporidium in wild placental mammals," Experimental Parasitology, vol. 124, no. 1, pp. 128-137, 2010.

[11] R. C. Anderson, Nematode Parasites of Vertebrates: Their Development and Transmission, CABI, Wallingford, UK, 2nd edition, 2000.

[12] A. Habluetzel, G. Traldi, S. Ruggieri et al., "An estimation of Toxocara canis prevalence in dogs, environmental egg contamination and risk of human infection in the Marche region of Italy," Veterinary Parasitology, vol. 113, no. 3-4, pp. 243-252, 2003.

[13] L. Rinaldi, A. Biggeri, S. Carbone et al., "Canine faecal contamination and parasitic risk in the city of Naples (southern Italy)," BMC Veterinary Research, vol. 2, article 29, 2006.

[14] D. Dado, F. Izquierdo, O. Vera et al., "Detection of zoonotic intestinal parasites in public parks of Spain. Potential epidemiological role of microsporidia," Zoonoses and Public Health, vol. 59, no. 1, pp. 23-28, 2012.

[15] D. Traversa, A. F. Di Regalbono, A. Di Cesare, F. La Torre, J. Drake, and M. Pietrobelli, "Environmental contamination by canine geohelminths," Parasites and Vectors, vol. 7, no. 1, article 67, 2014.

[16] Ministry of Agriculture; Fisheries and Food (MAAF), Manual of Veterinary Parasitological Laboratory Techniques, HMSO, London, UK, 1986.

[17] A. O. Bush, K. D. Lafferty, J. M. Lotz, and A. W. Shostak, "Parasitology meets ecology on its own terms: margolis et al. revisited," Journal of Parasitology, vol. 83, no. 4, pp. 575-583, 1997.

[18] M. Genchi, E. Ferroglio, G. Traldi, S. Passera, G. Mezzano, and C. Genchi, "Fecalizzazione ambientale e rischio parassitario nelle cittao di Milanoe Torino, "Professione Veterinaria, vol. 41, pp. 15-17, 2007.

[19] L. Rinaldi, M. P. Maurelli, V. Musella et al., "Giardia and Cryptosporidium in canine faecal samples contaminating an urban area," Research in Veterinary Science, vol. 84, no. 3, pp. 413-415, 2008.

[20] F. Riggio, R. Mannella, G. Ariti, and S. Perrucci, "Intestinal and lung parasites in owned dogs and cats from central Italy," VeterinaryParasitology, vol. 193, no. 1-3, pp. 78-84, 2013.

[21] S. A. Zanzani, A. L. Gazzonis, P. Scarpa, F. Berrilli, and M. T. Manfredi, "Intestinal parasites of owned dogs and cats from metropolitan and micropolitan areas: prevalence, zoonotic risks, and pet owner awareness in northern Italy," BioMed Research International, vol. 2014, Article ID 696508, 10 pages, 2014.

[22] J. E. Hall and B. Sonnenberg, "An apparent case of human infection withthe whipworm of dogs, Trichurisvulpis (Froelich, 1789)," The Journal of parasitology, vol. 42, no. 2, pp. 197-199, 1956.

[23] Y. Masuda, T. Kishimoto, H. Ito, and M. Tsuji, "Viscerallarva migrans caused by Trichuris vulpis presenting as a pulmonary mass," Thorax, vol. 42, no. 12, pp. 990-991, 1987.

[24] J. J. Dunn, S. T. Columbus, W. E. Aldeen, M. Davis, and K. C. Carroll, "Trichuris vulpis recovered from a patient with chronic diarrhea and five dogs," Journal of Clinical Microbiology, vol. 40, no. 7, pp. 2703-2704, 2002.

[25] A. Marquez-Navarro, G. Garcia-Bracamontes, B. E. Alvarez-Fernandez et al., "Trichuris vulpis (Froelich, 1789) infection in a child: a case report," Korean Journal of Parasitology, vol. 50, no. 1, pp. 69-71, 2012.

[26] R. Lia, C. la Montanara, N. Leone, N. Pantone, A. Lazzari, and V. Puccini, "Canine helminthic fauna and environmental faecalization in the town of Bari (Apulia region, Southern Italy)," Parassitologia, vol. 44, p. 92, 2002.

[27] A. L. Risitano, E. Brianti, G. Gaglio, M. Ferlazzo, and S. Giannetto, "Environmental contamination by canine feces in the city of Messina: parasitological aspects and zoonotic hazards," in Proceedings of 61st Congress of the Italian Society for Veterinary Science (S.I.S.Vet.). Salsomaggiore Terme, pp. 135-136, Parma, Italy, 2007.

[28] A. Scala, G. Garippa, and D. Pintus, "Environmental contamination by canine feces in the city of Alghero (SS): parasitological aspects and zoonotic hazards," in Proceedings of the 63rd Congress of the Italian Society for Veterinary Science (S.I.S.Vet. '09), pp. 180-182, Udine, Italy, 2009.

[29] D. Barutzki and R. Schaper, "Results of parasitological examinations of faecal samples from cats and dogs in Germany between 2003 and 2010," Parasitology Research, vol. 109, no. 1, pp. S45-S60, 2011.

[30] F. Berrilli, D. Di Cave, C. De Liberato, A. Franco, P. Scaramozzino, and P. Orecchia, "Genotype characterisation of Giardia duodenalis isolates from domestic and farm animals by SSU-rRNA gene sequencing," Veterinary Parasitology, vol. 122, no. 3, pp. 193-199, 2004.

[31] P. Bianciardi, R. Papini, G. Giuliani, and G. Cardini, "Prevalence of Giardia antigeninstool samples fromdogs and cats," Revue de Medecine Veterinaire, vol. 155, no. 8-9, pp. 417-421, 2004.

[32] G. Capelli, A. Frangipane di Regalbono, R. Iorio, M. Pietrobelli, B. Paoletti, and A. Giangaspero, "Giardia species and other intestinal parasites in dogs in north-east and central Italy," VeterinaryRecord, vol. 159, no. 13, pp. 422-424, 2006.

[33] M. C. Gates and T. J. Nolan, "Endoparasite prevalence and recurrence across different age groups of dogs and cats," VeterinaryParasitology, vol. 166, no. 1-2, pp. 153-158, 2009.

[34] M. C. Gates and T. J. Nolan, "Risk factors for endoparasitism in dogs: retrospective case-control study of 6578 veterinary teaching hospital cases," Journal of Small Animal Practice, vol. 50, no. 12, pp. 636-640, 2009.

[35] F. D. Uehlinger, S. J. Greenwood, J.T.McClure, G.Conboy, R. O'Handley, and H. W. Barkema, "Zoonotic potentialof Giardia duodenalis and Cryptosporidium spp. and prevalence of intestinal parasites in young dogs from different populations on Prince Edward Island, Canada," Veterinary Parasitology, vol. 196, no. 3-4, pp. 509-514, 2013.

[36] S. Katagiri and T. C. G. Oliveira-Sequeira, "Prevalence of dog intestinal parasites and risk perception of zoonotic infection by dog owners in Sao Paulo State, Brazil," Zoonoses and Public Health, vol. 55, no. 8-10, pp. 406-413, 2008.

Sergio Aurelio Zanzani, (1) Anna Rita Di Cerbo, (1) Alessia Libera Gazzonis, (1) Marco Genchi, (1) Laura Rinaldi, (2) Vincenzo Musella, (2) Giuseppe Cringoli, (2) and Maria Teresa Manfredi (1)

(1) Department of Veterinary Science and Public Health, Universita degli Studi di Milano, 20143Milan, Italy

(2) Department of Veterinary Medicine and Animal Productions, Universita degli Studi di Napoli "Federico II", 80137 Naples, Italy

Correspondence should be addressed to Maria Teresa Manfredi; mariateresa.manfredi@unimi.it

Received 31 July 2014; Accepted 30 October 2014; Published 17 November 2014

Academic Editor: Adriano Casulli

TABLE 1: Prevalence (%) and 95% confidence interval (CI) of
intestinal parasites in 463 dog faecal samples and 120 subareas in
Milan (north-western Italy).

                          Faecal samples          Subareas

                     n    % (95 CI)          n    % (95 CI)
Toxocara canis       8    1.72               6    5.00
                          (0.88-3.37)             (2.05-11.02)
Toxascaris leonina   3    0.64               3    2.50
                          (0.22-1.89)             (0.65-7.68)
Ancylostomatidae          0.43 (0.12-1.56)   2    1.67 (0.29-6.5)
Trichuris vulpis     17   3.67 (2.22-5.93)   16   13.33 (8.05-21.04)
Strongyloides spp.   4    0.86 (0.28-2.35)   4    3.33 (1.07-8.82)
Dipylidium           2    0.43               2    1.67
caninum                   (0.12-1.56)             (0.29-6.5)
Cystoisospora sp.    1    0.21 (0.04-1.22)   1    0.83 (0.04-5.23)
Giardia duodenalis   50   11.06              42   35.00
                          (8.49-14.29)            (26.67-44.30)
Cryptosporidium      5    1.10               3    2.50
sp.                       (0.47-2.55)             (0.65-7.68)

Overall prevalence   77   16.63              57   47.50
                          (13.52-20.29)           (38.38-56.78)

TABLE 2: Final multivariate analysis of risk factors associated with
intestinal parasites in dog faecal samples collected in public areas
of Milan (north-western Italy).

Variable   Riskfactor         Cases    Odd     95% CI *     P value
                                      ratio
Green      Proportion of
areas      territory of the
           administrative     463     1.084   1.030-1.140   0.002
           district
           occupied by
           green areas

* Confidence interval.
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Title Annotation:Research Article
Author:Zanzani, Sergio Aurelio; Di Cerbo, Anna Rita; Gazzonis, Alessia Libera; Genchi, Marco; Rinaldi, Laur
Publication:The Scientific World Journal
Article Type:Report
Date:Jan 1, 2014
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