Abstract:The present study investigated the optimum time and temperature for inactivation of bacteria and parasites in cow dung and pit faecal sludge, a forthcoming fertilizer. Samples were collected from different areas of Bangladesh and were examined through modified centrifugal flotation and conventional culture techniques to isolate parasites and bacteria respectively. A cow dung sample from Gopalganj and a pit sample from Dohar that were found to be the most contaminated among the samples tested were heated to ann… Show more
“…However, it fails to consider the contents of pathogenic helminth eggs, which are of great concern due to their harmful effects on public health. Helminth eggs and pathogenic protozoa can be considered as the most difficult microbiological pathogens to inactivate in wastewater and sludge treatment [37]. Moreover, previous investigations of Tunisian treated wastewater showed the predominance of protozoan in sludge [38][39][40][41][42].…”
Wastewater sludge represents an important resource for reuse in agriculture. However, potentially harmful pathogens are a main threat in this context. Thus, the aim of this study was to examine the presence of helminth ova and protozoan cysts in dried sewage sludge samples collected from ten wastewater treatment plants (WWTPs) located in eight governorates in Tunisia. Based on morphological criteria, protozoan cysts of Giardia spp., Entamoeba histolytica/dispar/moshkovskii, and Entamoeba coli, were detected in all dried sludge composite samples (N = 116) from the investigated WWTPs. The mean concentration ranged from 1.4 to 10.7 cysts per 100 g dry matter (DM). The identified helminth eggs were Ascaris spp., Strongyles, Taeniid eggs, Hymenolepis nana, Enterobius vermicularis, and hookworm species. Ascaris spp. and Taeniid eggs were detected in 56.9 and 74.1% of analyzed samples, respectively. The presence of Trichuris spp., Hymenolepis diminuta, and Toxocara spp. eggs in dried sewage sludge samples was low (0.9, 1.7, and 2.6%, respectively). The mean concentration of helminth eggs during the three-year study was less than 1 egg/100 g DM. All examined dried sewage sludge sample contents were below the WHO (2006) and US EPA (2003) recommendations, and thus, the sludge can potentially be reused in agriculture.
“…However, it fails to consider the contents of pathogenic helminth eggs, which are of great concern due to their harmful effects on public health. Helminth eggs and pathogenic protozoa can be considered as the most difficult microbiological pathogens to inactivate in wastewater and sludge treatment [37]. Moreover, previous investigations of Tunisian treated wastewater showed the predominance of protozoan in sludge [38][39][40][41][42].…”
Wastewater sludge represents an important resource for reuse in agriculture. However, potentially harmful pathogens are a main threat in this context. Thus, the aim of this study was to examine the presence of helminth ova and protozoan cysts in dried sewage sludge samples collected from ten wastewater treatment plants (WWTPs) located in eight governorates in Tunisia. Based on morphological criteria, protozoan cysts of Giardia spp., Entamoeba histolytica/dispar/moshkovskii, and Entamoeba coli, were detected in all dried sludge composite samples (N = 116) from the investigated WWTPs. The mean concentration ranged from 1.4 to 10.7 cysts per 100 g dry matter (DM). The identified helminth eggs were Ascaris spp., Strongyles, Taeniid eggs, Hymenolepis nana, Enterobius vermicularis, and hookworm species. Ascaris spp. and Taeniid eggs were detected in 56.9 and 74.1% of analyzed samples, respectively. The presence of Trichuris spp., Hymenolepis diminuta, and Toxocara spp. eggs in dried sewage sludge samples was low (0.9, 1.7, and 2.6%, respectively). The mean concentration of helminth eggs during the three-year study was less than 1 egg/100 g DM. All examined dried sewage sludge sample contents were below the WHO (2006) and US EPA (2003) recommendations, and thus, the sludge can potentially be reused in agriculture.
“…The feces were pressed out from the intestine and was introduced into a specimen container, it was emulsified with a saline water, sieved into a container, then introduced into a centrifuge tube, and was centrifuged under 3500rpm for 10minutes. After centrifugation, the precipitate was filtered out from the sediment, the sediment was dropped on a slide with a drop of iodine and was covered with a cover slip, it was then view with microscope under the magnification of X40 for parasitological examination [9][10][11][12].…”
Section: Laboratory Examination For Parasitic Infectionmentioning
Lizards (Agama agama) are the most widely distributed reptiles and has shown to be a means of transport and reservoir host to a number of protozoan and helminth parasites. The aim of this study is to determine the association between parasitic infection of Agama agama and selected characteristics (age and sex). The observational study was carried out at Otuoke community where 50 Agama agama comprising both male and females were randomly obtained. The lizards were sacrificed and their feaces were collected from their intestines and studied in the laboratory for parasite presence using light microscope. The results showed the identification of four parasites in the lizards namely; nematode (Strongyluris brevicaudata and Parapharyngodon colonensis), cestode (Oochoristica truncate), trematode (Mesocoelium monas) and Conoidasida (Toxoplasma gondii). There was no association between age (described as length of the animal) and prevalence of parasitic infection. Also, there was no association between sex and prevalence of the parasitic infection and finally, there was no association between weight and prevalence of the parasitic infection. This study has shown that although parasites are present in Agama agama, there was no gender, age and weight variations or dependence of the rate of their infection.
“…It has a more stable operation but a lower biogas production rate compared to other types of AD. In contrast, the higher temperature process (T-AD) reduces pathogen numbers even further and provides more rapid reaction rates than M-AD (Mahmud et al, 2016). Process parameters such as temperature, pH, hydraulic retention time, organic loading rate, carbon-nitrogen ratio and free ammonia presence can also have a significant influence on pathogen inactivation (Sakar et al, 2009;Abbasi et al, 2012;Manyi-Loh et al, 2013).…”
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