MATERIALS AND METHODS

The experiment was carried out in 2009-2010.Worms (Eisenia foetida Savigny) were reared in three reactors viz., rice straw and cow dung (RC) 2:1 ratio, sugarcane trash and cow dung (SC) 2:1 ratio and vegetable waste and cow dung (VC) 2:1 ratio. The reactors were mixed well and moistened with water up to 40% moisture contents. These treatment groups were investigated in two replicates; the reactor were placed in fiber bins and kept in natural environment to maintain favorable temperature for worms, as they are highly sensitive to temperature fluctuations. Two hundred mature earthworms were introduced into the bins containing 20 kg reactors each.

The treatment groups of different composition were allowed to stabilize for 70 days. Samples from the entire units were taken out, monthly, to measure the biomass of individuals. The worms were washed with distilled water and were weighed. After weighing, they were immediately placed in bins to prevent their desiccation.

During stabilization process of the reactors, five earthworms were collected and washed with sterile water to remove the surface microbial flora from its outer skin. The earthworms were then sacrificed by freezing and their whole body was dissected. The gut region approximately (3-5 cm) was taken for analysis for the reason the higher glutamic activity favours the microbial growth as reported by Edwards (1998) and Lavelle et al. (1998). Microbial analysis was carried out immediately following Lavelle et al. (1998).

For microbial analysis of castings, worms were collected from all the experimental units and rinsed thoroughly in sterile water. The worms were then placed in petriplates containing tissue paper for 5 min. The fresh casts deposited were analyzed for different microbial count.

The castings were analyzed at interval of 30 days. The total nitrogen, total potassium and total organic carbon measured by following Shaw and Beadle (1949), Pearson (1952) and Walkey and Black (1934), respectively.

Statistical analysis: Results are the means of three replicates. One way Analysis of Variance (ANOVA) was done using the INDOSTAT programme. The objective was to determine any significant differences among the parameters analyzed in different reactors during the stabilization process.

RESULTS

General: The average body weight (g) of earthworm was monitored on 30th and 60th days of vermistabilization (Table 1). No mortality was observed throughout experiment. The biomass (weight) increased from 0.64±0.02 to 1.2±0.02 in RC and SC and 0.64±0.02 to 0.84±0.02 in VC reactor. The readily available nutrients in RC and SC might have enhanced the feeding activity of worms (Kumar and Shweta, 2011) in present study.

Chemical analysis
Total organic carbon: During the process of stabilization process worms bio-transform waste constituents into a more useful fertilizer by grinding and digesting organic wastes with the help of aerobic and anaerobic micro flora. The percentage of organic carbon was remarkably decreased from 34.42±0.01 to 32.93±0.01 in RC; 36.39±0.05 to 32.82±0.02 in SC; 36.41±0.05 to 32.39±0.04 in VC at 30th day and remains ±30% at 60th day in all reactor. The total organic carbon was metabolized into CO₂ by various micro-floras present in gut of worm and in reactor, involved in the vermistabilization (Table 2).

Table 1:	Biomass (weight) of worms during stabilization process of reactors
All values are mean and standard deviation of the replicates. *Significant (p<0.01)

Table 2:	Chemical analysis of reactors during vermistabilization
All values are mean and standard deviation of the replicates. *Significant (p<0.01), RC: Rice straw+cow dung, SC: sugarcane trash+cow dung, VC: Vegetable waste+cow dung

Total kjeldahl nitrogen (TKN): The total nitrogen content of the vermicompost increased with time due to rapid mineralization of organic nitrogenous compounds (Table 2). However, the nitrogen content of the final produce depends on the initial nitrogen concentration of the reactor (Kumar and Shweta, 2011). The percentage of nitrogen significantly increased in all reactors viz. 0.73±0.02 to 1.00±0.02 in RC and from 0.76-0.86±0.02 to 1.44±0.02 in SC and VC at the end of vermistabilization. Their enhanced decomposition resulted in lowering of C:N ratio (Talashilkar et al., 1999).

Total potassium: Potassium is an essential micronutrient for both animals and plants. It plays a significant role in food metabolism and maintenance of cellular organization. It activates the enzymes in protein and carbohydrate metabolism. The percentage of potassium were found maximum in VC (0.85±0.003) followed by SC (0.83±0.03) and a slight decrease in RC (0.65±0.03) treatment (Table 2) at 60th day (Table 2).

Microbiomics of gut of worms during stabilization: At the initial stage of stabilization process various pathogens viz. Salmonella, Shigella, Escherichia and Flexibacter were found to be dominant in the gut of worm but during the subsequent days their level decreased significantly (Table 3). However, Pseudomonas and Streptosporangium count increased from 12-16x10⁴±0.05 to 18-22x10⁵±10.0 cfu g^-1. The microbial population of Salmonella decreased from 12x10³±0.05 to 4x10³±0.05 cfu g^-1 in RC, 13x10³±0.02 to 0.00±0.02 cfu g^-1 in SC, 17x10³±0.02 to 0.00±0.05 cfu g^-1 in VC reactor at 60th day of vermistabilization.

Table 3:	Microbiomics of gut of worm during stabilization process of reactors
All values are mean and standard deviation of the replicates and expressed in cfu g-1. *Significant (p<0.01)

Table 4:	Microbiomics in castings of worm during stabilization of reactors
All values are mean and standard deviation of the replicates and expressed in cfu g-1. *Significant (p<0.01)

Similarly, Escherichia count decreases from 8x10²±0.02 to 1x10¹±0.05 cfu g^-1 in RC, 8x10²±0.03 to 0.00±0.05 cfu g^-1 in SC and VC reactor at the 60th day. The reduction in Shigella and Flexibacter recorded at earlier (30th day of stabilization) stage. Shigella decreased from 3-5x10²±0.04 to 0.00-1x10¹±0.05 cfu g^-1 in all reactors at 30th day and completely removed at 60th day. Flexibacter sp. observed only in RC reactor (8x10²±0.05 cfu g^-1) at 30th day of stabilization while, in others completely removed at the same point of time. Population of Pseudomonas gradually increased from 14x10⁴±0.05 to 22x10⁵±1.0 cfu g^-1 in RC, 16x10⁴±0.05 to 22x10⁵±1.0 cfu g^-1 in SC, 13x10⁴±0.05 to 18x10⁵±1.0 cfu g^-1 in VC reactor. The microbial population of Streptosporangium also significantly increased from 12x10⁴±0.05 to 20x10⁵±1.0 cfu g^-1 in SC, 12x10⁴±0.05 to 18x10⁵±1.0 cfu g^-1 in VC and 14x10⁴±0.05 to 15x10⁵±1.0 cfu g^-1 RC reactor.

Microbiomics of cast during stabilization: The casting analysis did not show much difference with microbial count of gut. However, Shigella and Flexibacter were not recorded in any reactor at 30th day of vermistabilization. Salmonella sp. was completely removed out in all reactors except in RC (2x10³±0.02 cfu g^-1) at 60th day. Similarly, Escherichia was also not recorded in any reactor at same point of time. The significant increase in Pseudomonas (16x10⁴±0.05 to 28x10⁵±1.0 cfu g^-1 in RC, 16x10⁴±0.05 to 28x10⁵±1.0 cfu g^-1 in SC, 13x10⁴±0.05 to 20x10⁵±1.0 cfu g^-1 in VC) and Streptosprangium (15x10⁴±0.05 to 17x10⁵±1.0 cfu g^-1 in RC, 14x10⁴±0.05 to 20x10⁵±1.0 cfu g^-1 in SC, 14x10⁴±0.05 to 18x10⁵±1.0 cfu g^-1 in VC were recorded in castings of all reactors (Table 4).

DISCUSSION

Earthworms routinely devour on the protozoa, bacteria and fungus as food in any substrate where they inhabit (Sinha et al., 2010). They seem to realize instinctively those anaerobic bacteria and fungi are undesirable and so feed upon them preferentially, thus arresting their proliferation. More recently, Sinha et al. (2010) has found in her research that worms living in pathogen-rich materials (e.g., sewage and sludge), when dissected show no evidence of pathogens beyond 5 mm of their gut (Sinha et al., 2009a). The experimental results of microbiomics of gut and casting in present study proved the reduction/removal of Salmonella, Shigella, Escherichia and Flexibacter in all reactors. These results corroborate with the findings of Edwards and Bohlen (1996a), Bohlen and Edwards (1995) who have reported that earthworm’s food source include microorganism and can digest them selectively. Kumar and Sekaran (2005) also reported removal of Salmonella and Escherichia in 35 days in municipal solid wastes by Lampito mauritii.

Bajsa et al. (2003) reported the removal of faecal Coliform, Salmonella, enteric viruses; helminths ova from sewage and sludge appear to be much more rapid when they are processed by E. foetida. In another study Bajsa et al. (2004) reported the pathogen die-off in vermicomposting of sewage-sludge stipends with E. coli and E. faecalis at the 1.6-5.4x10⁶ cfu g^-1 and 3- 4x10⁴ cfu g^-1, respectively and achieved a safe product in 4-5 months of vermicomposting and the product remained the same quality without much reappearance of pathogens after in the remaining month of the test, confirming the observation of present study. Other studies (Singleton et al., 2003; Safawat et al., 2002) also confirmed significant human pathogen reduction in biosolids, vermicomposted by earthworms.

Increase in population of Streptosporangium and Pseudomonas in present study corroborates the findings of Sidhu et al. (2001) who described the role of Streptosporangium in the suppression of pathogenic bacterial population in earthworm. Kumar and Sekaran (2005), Masciandaro et al. (2000) and Sidhu et al. (2001) also proved that the indigenous micro-flora play a significant role in the suppression of pathogenic bacterial population growth in composted sludge. This confirms the role of Streptosporangium and Pseudomonas in suppression of pathogens in present study. However, there are conflicting observations relative to the proliferation of specific bacterial group in earthworm gut micro flora; indeed passage through the gut may selectively decrease the number of certain microbes such as Shigella and Escherichia (Edwards and Bohlen, 1996b).

Vinceslas-Apka and Loquet (1997) and Lavelle et al. (1998) have reported that organic carbon is metabolized into CO₂ and the various microflora present in the gut of worm and in reactor are involved in the degradation of organic carbon. The total nitrogen content of the reactors increased with time, due to rapid mineralization of organic nitrogen compounds. Present results have supported the findings of Bansal and Kapoor (2000) which have shown increase in the nitrogen content as a result of carbon loss in vermicomposting of crop residues and cattle dung. In the present study C:N ratio of reactors lowered because of enhanced decomposition, agreeing to the earlier observations of Talashilkar et al. (1999).

Nevertheless, the removal of pathogens may be due to release of antibiotics by earthworms, responsible to kill pathogenic organisms inhabit and render it virtually sterile (Sinha et al., 2009a). The worms also release the coelomic fluids that have anti-bacterial properties which may destroy all pathogen in reactors (Pierre et al., 1982). Further, there is some thing inside the worms which destroys the pathogens and makes their excreta pathogen free needed to be explored. However, absolute removal of pathogens is difficult to achieve, some may survives even after vermistabilization.

CONCLUSION

The study suggests that the worm selectively inhibits the growth of pathogens in reactors. The presence of pathogenic organisms Salmonella, Shigella, Escherichia and Flexibacter was observed at initial stage of stabilization process but after vermistabilization these were reduced to zero concentration. This amply demonstrates that these pathogens have been eliminated as they entered in food chain of worms. And for this, Pseudomonas, Streptosporangium seems to be responsible for reduction of pathogens and metabolization of reactors. However, it may not be possible to remove pathogens completely but at least worms change the ‘microbial make-up’ of reactors to make it harmless to the soil and enable its use as a nutritive organic fertilizer.

ACKNOWLEDGMENTS

The authors are thankful to the Department of Biotechnology, Ministry of Science and Technology, Government of India, New Delhi, for financial assistance.