| Literature DB >> 28862690 |
Maria Bernadeta Studzińska1, Marta Demkowska-Kutrzepa2, Anna Borecka3, Michał Meisner4, Krzysztof Tomczuk5, Monika Roczeń-Karczmarz6, Teresa Kłapeć7, Zahrai Abbass8, Alicja Cholewa9.
Abstract
Companion animals are an important aspect in human life. However, they may also be considered a source of pathogens. An example of zoonotic parasitoses is toxocarosis or cutaneous larva migrans (CLM). The aim of the study was to detect zoonotic nematodes of dogs living in different areas and the intensity of contamination in parasite polluted environments that are hazardous to human health. The fecal samples were examined using standard flotation and decantation methods as well as McMaster's quantitative technique. The soil samples in urban and rural areas were examined using a modified flotation method as described by Quinn et al. Statistical analyses were performed by IBM SPSS Statistics Version 23. The overall prevalence of parasites in dogs was 38%, 17.02% and 56.60% from urban and rural areas, respectively. The percentage values of nematodes important for human health (Toxocaracanis, Ancylostomatidae, Trichurisvulpis) remained at the same level (16%). The infected dogs were dominated by a single parasite species, the main was T.canis (28.95%). In total, 54.30% of the soil samples were contaminated with parasite eggs. The contamination of urban and rural sandpits was 40% and 60%, respectively. The molecular examinations of soil samples using LAMP (loop-mediated isothermal amplification) confirmed the presence of nematode eggs of the species T.canis in all samples previously classified as positive.Entities:
Keywords: Ancylostomatidae; LAMP; Toxocara canis; dog; environment; zoonosis
Mesh:
Substances:
Year: 2017 PMID: 28862690 PMCID: PMC5615540 DOI: 10.3390/ijerph14091003
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Prevalence of parasites in dogs.
| Number of Dogs Examined | Number of Dogs Infected | |||||
|---|---|---|---|---|---|---|
| Total | Infested | |||||
| 100 | 38 (38%) | 16 (16%) | 3 (3%) | 16 (16%) | 16 (16%) | 5 (5%) |
Eggs per 1 g of feces (EPG) in canine feces from various environments.
| No. of Dogs Infested | EPG Mean | Urban Area | Rural Area | |||
|---|---|---|---|---|---|---|
| No. of Dogs Infested | EPG Mean (Min–Max) | No. of Dogs Infested | EPG Mean (Min–Max) | |||
| 16 | 852.81 | 4 | 300 | 12 | 1037 | |
| 3 | 383.33 | 1 | 50 | 2 | 500 | |
| 16 | 584.38 | 2 | 700 | 14 | 568 | |
| 16 | 134.38 | 1 | 50 | 15 | 137 | |
| 5 | 60 | 0 | 0 | 5 | 60 | |
The number of infected dogs from various environments with different levels of EPG.
| EPG | Ancylostomatidae | ||||||||
|---|---|---|---|---|---|---|---|---|---|
| Total | Urban | Rural | Total | Urban | Rural | Total | Urban | Rural | |
| <100 | 2 | 1 | 1 | 5 | 1 | 4 | 8 | 1 | 7 |
| 101–500 | 7 | 2 | 5 | 8 | 0 | 8 | 8 | 0 | 8 |
| 501–1000 | 3 | 1 | 2 | 1 | 0 | 1 | 0 | 0 | 0 |
| >1000 | 4 | 0 | 4 | 2 | 1 | 1 | 0 | 0 | 0 |
The presence of eggs of intestinal parasites in sandpits in the city of Lublin and rural areas.
| Sampling Site | Total | No of Positive Samples (%) | No. of Invasions | ||||
|---|---|---|---|---|---|---|---|
| Single | Mixed | ||||||
| T | A | T/A | |||||
| urban area | sandpits | surface | 15 | 2 (13.3) | 2 | 0 | 0 |
| depth 30 cm | 4 (26.7) | 4 | 0 | 0 | |||
| home zone pathways | surface | 10 | 0 | 0 | 0 | 0 | |
| depth 30 cm | 1 | 0 | 1 | 0 | |||
| surface + depth | 6 | 3 | 0 | 3 | |||
| rural areas | sandpits | surface | 10 | 1 (10) | 1 | 0 | 0 |
| depth 30 cm | 5 (50) | 3 | 2 | 0 | |||
T—Toxocara canis, A—Ancylostomatidae, T/A—Toxocara canis/Ancylostomatidae.
Figure 1Effect of LAMP (loop-mediated isothermal amplification) reaction for T. canis and T. cati: Lane M—pUC Mix marker; Lanes 1 and 4—a negative control, Lane 2—a standard for T. canis, Lane 3—the product of reaction of LAMP DNA isolated from selected environmental samples (recovered from soil), Lane 5—standard for T. cati, Lane 6—no product of reaction of LAMP DNA isolated from the environmental samples.