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Iranian Journal of Environmental Health, Science and Engineering
Iranian Association of Environmental Health (IAEH)
ISSN: p-ISSN: 1735-1979
Vol. 2, Num. 4, 2005, pp. 251-254
Untitled1

Iranian Journal of Environmental Health Science & Engineering, Vol. 2, No. 4, 2005, pp. 251-254

COMBINED COMPOST AND VERMICOMPOSTING PROCESS IN THE TREATMENT AND BIOCONVERSION OF SLUDGE

*1H. Alidadi, 2A. R. Parvaresh, 2M. R. Shahmansouri and 2H. Pourmoghadas

1Dept of Environmental Health, Faculty of Health, Mashhad University of Medical Sciences, Iran
2Dept of Environmental Health, Faculty of Public Health, Isfahan University of Medical Sciences, Iran

*Corresponding author: Tel: +98 511 7672124, Fax: +98 511 7628088, E-mail: halidadi @yahoo.com

Received 3 January 2005;
revised 22 May 2005;
accepted 26 June 2005

Code Number: se05036

ABSTRACT

Traditional thermophillic composting is commonly for treatment of sludge. A related technique as vermicomposting process, using earthworms to breakdown sludge, is also becoming popular. These two techniques have their inherent advantages and disadvantages. The combined approach suggested in this study to enhance the overall process and improve the products qualities. Two systems,vermicomposting and combined compost vermicomposting processes, have been investigated in this study. The sludge used in this study was obtained from the drying beds of South Isfahan wastewater treatment plant.The sludge mixed with sawdust to provide C/N ratio of 25/1. Eisenia fetida was the species of earthworms used in the vermicomposting processes.The results obtained indicates reduction in the amount of volatile solids,total carbon and C/N ratio with the vermicompost age,which indicates the reduction in the biodegradable organic content and mineralization of sludge. Also increase in phosphorus concentration by the end process because of mineralization of organic matter.
The results indicate that, a system that combines the two mentioned processes not only shortens stabilization time, but also improves the products quality. Combining the two systems resulted in a product that was more stable and homogenous; the product could meet the pathogen reduction requirements.

Key words: Sludge, vermicomposting process, eisenia fetida, combined process

INTRODUCTION

There are large amounts of sludge produced continuously in most wastewater treatment operations. The produced sludge needs to be deal with carefully. Stabilization and disposal of domestic sludge produced from wastewater treatment plants is especially critical (USEPA, 1994). The importance of biological processes in the management of sludge has been widely recognized. Within the broad range of bioprocesses available, composting and vermicomposting are the most efficient for converting sludge into useful products. The sludge obtained from municipal wastewater treatment plants is usually suitable for compost and vermicompost because of the huge amounts of organic matter available (Fair, 1998). The composting is an accelerated biooxidation of organic matter passing through a thermophilic stage (45 to 65 ºC), where microorganisms such as bacteria,
fungi and actinomycetes liberate heat, carbon dioxide and water. Hence, during the composting process kill of pathogens (Dominguez, 1997). The heterogeneous organic material is transformed into homogeneous and stabilized humus like product through turning or aeration. The major problems associated with thermophilic composting are the long duration of the process, loss of nutrients during the prolonged composting process and the frequency of turning of the material.

In recent times, interest in the use of a closely related technique, known as vermicomposting has increased (Logsdon, 1994 and Edwards, 1996). The vermicomposting is a low cost technology system that uses earthworms in the treatment of organic wastes. The earthworms fragment the organic waste substances; simulate microbial activity greatly and increase rates of mineralization, rapidly converting the wastes into humus like substances with a finer structure than compost (Elvira, 1996 and Atiyeh, 2000). The earthworm's roles of turning and maintaining the material in aerobic condition in the vermicompost. The major drawback in the vermicomposting process is that it must be maintained at temperatures below 35 ºC and exposure of worms to temperatures above this will kill them.The vermicomposting process temperature is not high enough for acceptable pathogen kill and hence the product does not pass EPA rules for pathogen reduction.

An integrated system from both the thermophilic composting process and the vermicomposting process would be necessary to provide a product free of pathogens, and product with desirable characteristics at a faster rate than either of the individual processes. In England, (Logsdon, 1994) reported successful addition of worms after the heat of the initial decomposition subsides. The worms worked well in this situation and shortened the time for curing and stabilization of the compost. Furthermore, combining composting with vermicomposting also accelerated the composting process thus reducing the time required for composting (Frederickson et al., 1997; Nedgwa and Thompson, 2001). The objectives of the present study included investigation of the vermicompost and combining compost vermicompost in the stabilization of dewatered sludge and comparison of two methods for chemical and biological characteristics.

MATERIALS AND METHODS

Preparation of the pilot

This study was conducted during the period from December 2003 to April 2004. The sludge used in this study was obtained from the drying beds of South Isfahan wastewater treatment plant. The methods of investigation were vermicomposting and combine compost vermicomposting processes. The earthworms were used in this study collected in Mazandaran province in the North of Iran. Eisenia foetida was the species of earthworms used in the vermicomposting process. The ratio of sludge used was 3 kg of 80 percent moisture content mixed by 1 kg of sawdust of 5 percent moisture content to provide a suitable C/N ratio of 25. The vermicompost experiments were performed in two plastic worm bins of 1.1´0.9´0.5 m3 (Lengthwidth´depth). These plastic bins provide one m2 of exposed top surface. From preliminary studies (Nedegwa et al, 1999), an optimal worm sticking density of 1.6 Kg worms/m2 and an optimal feeding rate of 0.75 Kg feed/Kg worm/day were used in this experiment. The Eight hundred pieces of adult Eisenia foetida between 0.4 to 0.5 g were placed in the vermicompost plastic bin, to provide the optimal sticking density. The biomass loading was 1.6 kg. The experiments lasted two months; hence, we needed 72 kg of the substrate.

The windrow composting size was approximately 1.2 m in height and 1.5 m in width and 2.5 m length. The sludge used in the study have 80 percent moisture content, sludge mixed with the sawdust to control and adjust the moisture content to 60 percent and increased C/N ratio to 25/1 . The windrow turning was done manually. The windrow was turned to ensure availability of sufficient amount of oxygen to be utilized by microorganisms at the start of the composting cycle. The windrow was turned five times, until temperature of compost reach to 55 ºC, then substrate was cooled and introduce of vermicompost plastic bin. The temperature were measured by thermometer. The temperature was measured at two thirds of the elevation of the windrow, at about eighty centimeters from surface of the windrow. The substrate material was maintained temperature by spraying the surface with water.

Measured parameters

The composite samples were taken from about three different points of bin for examination. The moisture content of the vermicompost samples was determined drying to a constant weight at 105 ºC for 24 h in oven. The ambient temperature and the plastic bins were measurements by thermometer. The determination of pH was made potentiometrically in a 1/10 suspension of the sample in deionized water; this suspension was placed on a mechanical shaker at 230 rpm for 30 minutes prior to pH measurement. Volatile solids (VS) were obtained by ashing the dried samples at 550 ºC for 30 minutes (APHA,1992). Total phosphorus using the ascorbic acid method, after digestion of the sample and reading at 880 nm on a Spectrophotometer (APHA,1992). Total nitrogen was extracted by the Kjeldhl digestion method where the sample is pretreated with salicylic acid and thiosulphate (Mulvaney, 1996). The NH4+ and NO3- using the KCL extraction method (Mulvaney, 1996). Fecal coliforms were determined using a most probable number (MPN) technique in accordance with part 9221E, Standard methods for examination of water and wastewater (APHA, 1992). The helminth eggs such as ascaris were determined using by Yanko method (Yanko, 1998).

Statistical analysis

All the reported results were expressed as mean of two replicates and all data were analyzed using of SPSS statistical analysis. The comparisons among means were made using the least significant difference test calculated at P-values.

RESULTS

The ambient and the plastic bins as measured daily varied between 8 to 15°C and between 10 to 17 º C, respectively. The moisture content in plastic bins of vermicompost varied between 70 to 75 percent, and the pH ranged between 5.8 to 7.6, a temperature range of 0 to 35°C , a moisture range of 60 to 90 percent and a pH range of 5 to 9 were utilized as suitable conditions for the growth of E,fetida. Thus, favorable growth conditions for the growth of earthworms E.fetida were provided in this study

The results of parameters (TC, TN, C/N ratio, VS, TP, FC, NH4/NO3 and Ascaris egg) of the dewatered sludge and the products from two systems are summarized in Table 1. The percentage changes of each parameter after 60 days of processing were calculated and are shown in Table 2, also the results of analysis of variance among the two systems are shown Table 2.

DISCUSSION

The results obtained indicates reduction in the amount of volatile solids with the vermicompost age, which indicates the reduction in the biodegradable organic content of sludge. The table 1 shown that the extent of reduction of volatile
solids in vermicomposting and combined compost-vermicomposting processes were decreased 26.68 and 33.48 percent, respectively. Higher reductions were observed in combine process than vermicomposting process. The decrease in volatile
solids was significantly different (a<0.05) between two systems. This finding indicates that the combined compost vermicomposting process is more efficient in stabilizing sludge than the vermicomposting process. our results confirmed the results of hassouneh et al., (1999).

The results obtained indicates reduction in the amount of total carbon with the vermicompost age, which indicates the mineralization of sludge, but decomposition of the sludge during vermicomposting process was slow as compared to combined compost-vermicomposting process. Also higher increase in the amount total nitrogen because the more microbial activity in the beginning of combined compost-vermicomposting than vermicomposting process, thus decreaseing the C/N ratio .The decrease in C/N ratio was significantly different (a<0.05) between two systems.our results confirmed the results of Eiland et al., 2001.

According to Table 1 , increase in phosphorus concentration by the end process possibly because of mineralization of organic matter. Higher increase were observed in combined process than vermicomposting process. The increase in phosporus was significantly different (a<0.05) between two systems. our results confirmed the results of Ndegwa et al., 2001.

The temperature during the composting phase in the combined systems reach to 55 oC ,to provide the temperature required for pathogen kill,thus it satisfy the EPA requirements for class A compost , but vermicomposting process satisfy the EPA requirements for class B compost. our results confirmed the results of hassouneh et al 1999.

The results presented above suggest that, the combined systems are better treatment options than the vermicomposting system because higher reductions of C/N ratio, volatile solids, NH4/NO3 and fecal coliforms observed. The higher reductions in volatile solids suggest that more stable products were obtained from combine system; it would be possible to achieve the required compost within a shorter time, thus effectively reducing the overall processing time for the combine system. In addition, the product from combine system seems to be better met the EPA criterion and was the most homogenous.

ACKNOWLEDGEMENTS

The authors would like to thank vice chancellor, Researches of Isfahan University of Medical Sciences for their financial support in this research. We would like to thank for helps of Isfahan Water and Wastewater Company and M.Mousavi for his contribution in this study.

REFERENCES

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  • Nedgwa, P. M. and Thompson, S. A., (2001). Effects of C to N ratio on vermicomposting of biosolids.Bioresource and Technology, 75:7-12.
  • USEPA (1994). Sludge handling and disposal, composting.Federal regulation,Washington,DC
  • Yanko, W. A., (1998). Occurrence of pathogens in distribution and marketing municipal sludges. Report No: EPA/600/1-87/014.

© 2005 Tehran University of Medical Sciences Publications


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