RESUMO
The World Health Organization (WHO) has established as a criterion of parasitological quality for irrigation water, ≤ 1 helminth egg/liter, which guarantees the safety in agricultural products. In this study, the presence of parasites in surface water used for irrigation of crops (n = 96) and vegetables (celery and lettuce) (n = 120), from the Former La Ramada irrigation district, was evaluated using conventional and molecular parasitological methods. Our findings showed contamination of irrigation systems in the study area with domestic wastewater, demonstrated by the presence of Ancylostomatidae eggs, Ascaris spp., Hymenolepis spp., Trichuris spp., Capillaria spp., Giardia spp. cysts, and oocysts of Toxoplasma gondii and Cryptosporidium spp. A prevalence of 33% and 23.3% was calculated for helminths and protozoa, respectively in vegetables, representing a possible risk to human and animal health in relation to these parasites. These findings show the need for continuous monitoring of the water quality used for crop irrigation, as well as the safety of food, taking into account the values established in national and international regulations.
Assuntos
Irrigação Agrícola , Produtos Agrícolas , Verduras , Verduras/parasitologia , Colômbia , Animais , Parasitos , HumanosRESUMO
The accidental ingestion of treated recreational water is an important transmission route of waterborne protozoa worldwide. The present study aimed to provide the first evaluation of swimming pools in Brazil, analysing the presence of pathogenic protozoa (Toxoplasma gondii, Cryptosporidium spp. and Giardia spp.) by parasitological and molecular methods. A total of 57 samples were collected from 21 public swimming pools, either directly from the pool or filter backwash water and concentrated using the membrane filtration technique. Giardia cysts and Cryptosporidium oocysts were visualized by direct immunofluorescence assay after purification by immunomagnetic separation. Toxoplasma gondii oocysts were detected by autofluorescence visualization using the supernatant discarded during the purification step as a sample. Positive samples were submitted to molecular analysis. The molecular markers were used: SSU-rRNA, tpi, gdh and bg, for Giardia DNA amplification, and 18S rRNA gene fragment amplification was used for the Cryptosporidium oocysts. The 529-bp repeat element (REP529) fragment and the 35-fold repetitive B1 gene were employed as a target for T. gondii. Amplified products were submitted to sequencing and phylogenetic analysis. Giardia cysts were detected in 19.0% and Cryptosporidium oocysts in 9.5% of swimming pools. In one swimming pool (4.7%), both protozoa were detected on at least one occasion. Structures similar to T. gondii oocysts were detected in 33.3% of the samples, ranging from one to 23 per slide. Giardia was confirmed by DNA amplification in three swimming pools; Giardia duodenalis Assemblage A was identified by the phylogenetic positioning of the ß-giardin gene. Toxoplasma gondii DNA was detected in 14.2% of swimming pools. The present study represents the first report of the occurrence of T. gondii oocysts in swimming pools. Recreational activity in swimming pools contaminated by chlorine-resistant protozoa can represent a high risk of infection for bathers and swimmers.
Assuntos
Cryptosporidium/isolamento & purificação , Giardia/isolamento & purificação , Oocistos/isolamento & purificação , Piscinas , Toxoplasma/isolamento & purificação , Animais , Brasil , Imunofluorescência , Humanos , Fatores de Risco , Água/parasitologiaRESUMO
Giardia and Cryptosporidium have caused numerous outbreaks of diarrhea as a result of the ingestion of water contaminated with sewage. In Brazil, the efficiency of Giardia and Cryptosporidium removal by combined fixed-film systems has rarely been studied. The aims of the present study were therefore to verify the removal efficiency of Giardia and Cryptosporidium by a combined system (anaerobic/anoxic filter and aerated submerged biofilter) and to perform the genetic characterization of these parasites. The (oo)cysts were detected by centrifuge concentration and membrane filtration from raw sewage, effluents, adhered biomass, and sludge samples. Immunofluorescence assay and differential interference contrast microscopy were used for the visualization of the (oo)cysts. Nested PCR was applied to confirm Giardia and Cryptosporidium. Giardia and Cryptosporidium were detected in 27% and 5.5% of the 144 analyzed samples of raw sewage and effluents, respectively. A total of 33,000 cysts/L were recovered in the adhered biomass samples (n = 25) from different points of the aerated submerged biofilter, while 6000 oocysts/L were registered in a single point. An average of 11,800 cysts/L were found in the sludge samples (n = 5). The combined system exhibited a removal efficiency of Giardia cysts of 1.8 ± 1.0 log removal. The C and BIV assemblages of Giardia were identified in the raw sewage while AII was found in the treated effluent sample. It was not possible to calculate the removal efficiency of Cryptosporidium oocysts by the combined system. The combined system exhibited some potential as a suitable treatment for the removal of parasites from sewage.