Decontamination by anaerobic stabilisation of the environment contaminated with enteronematode eggs Toxocara canis and Ascaris suum.

Investigations were carried out under operating conditions of Field Composting Factory in Brezno (Slovak Republic) to determine the effect of anaerobic stabilization of organic wastes from public areas on the survival of model helminth Toxocara canis and Ascaris suum eggs. Due to anaerobic conditions, low temperature, low C:N ratio and changes in physical and chemical properties of organic waste, less than 64% of A. suum eggs remained viable after 150 days of stabilisation. The anaerobic stabilisation had a greater effect on the viability of T. canis eggs than on A. suum eggs. The infectivity of T. canis eggs was confirmed by a follow-up experiment in laboratory mice. A small number of T. canis larvae were found in their brain and muscles on day 28 after infection. The results refer to the risks of dissemination, survival and potential spread of endoparasitic developmental stages in the environment through organic wastes subjected to low temperature stabilisation.

Evolution of temperature and chemical parameters during composting of the pig slurry solid fraction amended with natural zeolite.

A 3-month experiment was conducted at a 300 kg scale to observe decomposition processes in pig slurry solids amended with two different doses of natural Slovak zeolite-clinoptilolite (substrates S1 and S2, 1% and 2% of zeolite by weight, respectively) in comparison with the control (unamended solids). The experimental and control substrates were stored outdoors in sheltered static piles at ambient temperatures ranging from 8.0 to 34.7 degrees C. The solid fraction (SF) of pig slurry was obtained by separation on vibration sieves prior to slurry treatment with activated sludge. The initial water content of the SF was 77.1% and no water was added to the piles during the storage. The temperature in the core of the piles was recorded throughout the experiment. By day 3 and 5 of storage (1% and 2% zeolite, resp.), the temperature in the substrates S1 and S2 exceeded 55 degrees C and remained above this level for 15 days while the highest temperature recorded in the control during the experiment was 29.8 degrees C. Samples from the core of the piles were taken periodically to determine pH, dry matter at 105 degrees C (DM), ash (550 degrees C/4 h), ammonia nitrogen (N-NH(4)(+)), nitrate nitrogen (N-NO(3)(-)), total nitrogen (N(t)), total phosphorus (P(t)); total organic carbon (TOC) was computed. The results showed that pH levels in S1 and S2 remained below that in the control for most of the thermophilic stage. This may be related to water-soluble ammonia and the affinity of zeolites to ammonium ions. A significant decrease in the level of ammonia nitrogen in water extracts from S1 and S2 was observed between days 5 and 35 in comparison with the control. The values of ash also differed and corresponded to the intensity of the decomposition processes in the respective substrates.

The effect of summer and winter seasons on the survival of Salmonella typhimurium and indicator micro-organisms during the storage of solid fraction of pig slurry.

AIMS: Investigations were carried out to observe the influence of winter/spring and summer periods on the survival of Salmonella typhimurium and indicator bacteria (psychrophilic, mesophilic, coliform and faecal coliform bacteria and faecal streptococci) in the solid fraction of pig slurry from agricultural wastewater treatment plant. METHODS AND RESULTS: Leather squares and PVC bottles with openings served as test carriers. They were inoculated with broth culture of Salm. typhimurium and introduced directly into the solid fraction. During the experiment, quantitative and qualitative examinations were carried out to determine the presence of Salm. typhimurium and observe the dynamics of indicator bacteria in the solid fraction. CONCLUSIONS: Salmonella typhimurium survived for 26 d in summer and for 85 d in winter/spring. The T90 values of indicator bacteria in summer ranged from 35.44 d (coliform bacteria) up to 100.29 d (mesophilic bacteria). The winter T90 values of indicator bacteria ranged from 74.58 d (faecal coliform bacteria) to 233.07 d (coliform bacteria). SIGNIFICANCE AND IMPACT OF THE STUDY: The present study demonstrated that it is necessary to pay increased attention to the manipulation of slurry solid fraction.

Effect of natural zeolite (clinoptilolite) on microbial decomposition processes in stored pig-slurry solids.

The solid fraction (SF) of pig slurry obtained in the first stage of aerobic slurry treatment was amended with 1 and 2% zeolite (clinoptilolite) and stored for 12 weeks under anaerobic conditions or with turning after 3 and 6 weeks of storage. In addition to that SF was mixed with 2% zeolite, 50% (V/V) sawdust, and both sawdust and zeolite, and stored for 6 weeks with turning after 1 and 3 weeks. Plate counts of psychrophilic, mesophilic, coliform and fecal coliform bacteria, determined during the storage, corresponded to the development of temperature in the core of the substrates. An effect of amendment of SF with zeolite and sawdust on plate counts of selected bacteria was observed, dependent on the zeolite dose. The thermophilic phase was not reached in any of the investigated substrates. The populations of fecal coliforms in the substrate amended with 1% zeolite and turned after 3 and 6 weeks decreased after 11 weeks down to 500 CFU/g substrate.