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VOLUME: 10, Special Issue 02, (IC-IMAF-2023) Paper id-IJIERM-X-II, January 2023 176

UTILIZATION OF FLORAL WASTE IN VERMICOMPOSTING AT VARIOUS TEMPLES OF DHAR CITY

Simran Suryavanshi1, Gurudutt Sharma2

1Research Scholar, Devi Ahilya University, Indore (M.P)

2Professor & Head of Department, PMB Gujarati Science College, Indore (M.P)

Abstract - Flowers are an important part of worship in temples of India. After worship, a huge number of flowers becomes waste. It generates pollution around the temples.

Vermicomposting is used as an ecofriendly method to manage the floral waste. The floral waste was collected from around 10 temples of Dhar city and was utilized in the process of vermicomposting. Factors like moisture content, temperature are considered very important during entire period. Earthworm species Eisenia fetida was used to prepare vermicompost.

Cow dung and floral waste were taken in a ratio of 30:70. Portable, UV stabilized, ecofriendly High-density Polyethylene (HDPE) Vermi beds were used for floral waste vermicomposting. Physico-chemical analysis of matured vermicompost was obtained as mentioned in Fertilizer Control Order,1985. The utilization of floral waste into vermicomposting resulted in an ecofriendly method of floral waste management. It was cost effective method and resulted as a source of income. Vermicompost can be sold at a rate of 10 rupees per kilogram.

Keywords: Vermicomposting, Earthworm, Floral waste, Eisenia fetida.

1 INTRODUCTION

India is a religious country. There are about 2 million temples in India. Nearly 20 million tons of floral waste is generated every day from various sectors including temples. This floral waste increases pollution of water, air, and land. The floral waste is organic in nature.

The organic nature of these wastes offers various biological management options such as vermicomposting instead of disposal to landfill sites, open dumping or any other environmentally risky waste management alternatives. (Sangwan et al 2002, Aalok et al 2008, Adhikary et al 2012). Vermicomposting is the process of conversion of organic wastes into finely degraded peat like substances using earthworms. Earthworm species convert this into better product and provide solution to the problem of organic waste degradation (Nagavallemma et al., 2006). There are about 40 temples in Dhar city and a lot of floral waste is generated around the temples which pollutes lake, ponds, other water resources and land near the temples. Vermicompost is a bio fertilizer enriched with all beneficial soil microbes and contains plant nutrients like N, P and K. It is a sustainable, cost effective, and ecological technology for efficient treatment of biodegradable wastes, and is thus widely adopted to recycle hazardous and worthless organic wastes into safe and valuable products (Garg et al. 2006). In this process, energy rich and complex organic substances have been bio-oxidized and transformed into stabilized products by combined action of earthworms and microorganisms (Edward et al, 1992). Vermicompost technology can be successfully applied in temples as a solid waste management strategy with flower as the major organic waste (Nisha,2016).

2 MATERIALS AND METHODS

A survey was done about the number of temples in Dhar. It was found that there are approximately 40 temples in Dhar. A regular visit to 10 selected temples was done for collecting primary data. A huge number of flowers are dumped as waste after worshiping.

This Floral waste was collected and used in vermicomposting. Physico-chemical analysis was done following Fertilizer Control Order (FCO) standards,1985.

2.1 Vermicomposting

2.1.1 Collection and Segregation of floral waste

The Floral Waste was collected from temples and non- biodegradable waste was removed from it. Only biodegradable waste such as flowers, leaves, coconut waste were segregated and shredded in small pieces.

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VOLUME: 10, Special Issue 02, (IC-IMAF-2023) Paper id-IJIERM-X-II, January 2023 177 2.2 Pre- Composting

The Segregated floral waste was then air dried for 3 days. The air-dried sample was then subjected to pre-composting for 8 days.

2.3 Collection of Cow dung

Cow dung was used as inoculant ( Adegunloye et. al 2007). Cow dung was collected from Lakshmi Gaushala, Dhar.

2.4 Experimental animal - Earthworm

Earthworm species Eisenia fetida was selected for vermicomposting. It was purchased from Krishi Vigyan Kendra (KVK), Dhar.

2.5 High-density Polyethylene (HDPE) Vermi bed

HPDE Vermi beds of size 12×4×2 was been set up at the backyard of temple. It is light weight, UV stabilized and water proof. It was supported with bamboo. Green shade was used for shading.

2.6 Experimental Design

For vermicomposting (VC), Cow dung and floral waste were mixed in 30:70 proportion. Each vermibed consists of 30% cow dung + 70% Floral waste + Earthworm (Eisenia fetida).

Alternate layers of Floral waste and cow dung are placed in vermi bed. This mixture was left for pre-composting. The moisture was maintained to 70 % for pre- composting.

After 10 days of pre-composting, adult Earthworms (Eisenia fetida) were released in the HDPE Vermi bed at the rate of 2.6 kg worms per square meter. Water was sprinkled to maintain moisture content up to 70% throughout the process of vermicomposting. Watering was stopped on 45th day when the Vermicompost seems to be ready notified by a dark brown layer. The prepared vermicompost was sun dried for 3 days. After drying up to 20%, the vermicompost was sieved through 4.0 mm sieve tube. The earthworm was removed manually by hand sorting. The ready vermicompost was air dried by spreading in layers at floor.

Total weight and ime taken to prepare vermicompost is given in table 1 2.7 Physico-chemical analysis of vermicompost

The matured vermicompost sample of about 1 kg was collected in a polybag for Physico- chemical analysis according to Fertilizer Control Order (FCO,1985) parameters for vermicompost testing.

FCO standards are given in Table 2.

Physico-chemical analysis of prepared vermicompost (VC) is given in Table 3.

The Electrical Conductivity (EC), although this parameter is not incorporated in the FCO standard, the FCO standard schedule in city compost has been specified to be 4.0 ds/m. Estimation of total carbon was done following FCO standard (table 2). Estimation of total nitrogen was done as mentioned under Schedule – II, Part-B, 3 (v) of FCO,1985.

3 USE OF VERMICOMPOST

The vermicompost was used as bio fertilizer in plants of temple.

4 RESULTS AND DISCUSSION

In the present study the prepared vermicompost appeared dark brown which indicated that the floral waste has decomposed successfully, as the earthworms consume the floral waste very rapidly. (Lakshmi Prabha et al, 2014). The dark brown color of test sample is similar with the FCO standard (Table 2) for the required color of vermicompost. There was no foul smell during the process of vermicomposting because of the oxygen rich hemoglobin circulation through earthworm’s skin. (Jadhav et al, 2013). More than 90% of the prepared vermicompost passed through 4.0mm sieve tube. (FCO, 1985). The moisture was maintained at 70% by regular sprinkling of water. In summer seasons there was much fluctuation noted in moisture content. Similarly, the temperature was maintained below

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VOLUME: 10, Special Issue 02, (IC-IMAF-2023) Paper id-IJIERM-X-II, January 2023 178

34°C as the maximum temperature which earthworms can survive is below 35°C. (Taiwo and Oso ,2004). The study showed high bulk density (Table 2) because the porosity was increased. (Bhargava et al,1993). The bulk density of test sample was 0.88 g/cm3 (Table 3).

The pH value of tested sample was found to be 6.9, which was nearly neutral (FCO standard). The Electrical Conductivity (EC) was determined in a compost water sample and was noted to 3 34 dsm-1. The increase in Organic carbon was found which is beneficial for growth and productivity for plants (Nelson and Sommers 1982). The availability of Nitrogen was found significant due to presence of nitrogen fixing bacteria. (Parmelle et al, 1988, Tiwari et al, 1989). In the tested sample C/N ratio was found significant. The loss of carbon through microbial respiration lowered the C/N ratio. (Dash and Senapati 1986). In the test sample an average amount of phosphorus was present as P2O5 in worm’s Verm cast’s total potassium (K2O) was found quite high as compared to FCO standard, it was in good amount (Table 3). (Mackay et al 1982).

5 CONCLUSION

The present study proved that the vermicompost prepared with the utilization of floral waste with cow dung at 70:30 is a standard vermicompost. It not only helped in managing the temple’s floral waste but also proved as an example of best out of waste. It is cost effective. Temple floral waste can be successfully utilized in vermicomposting and results in a high value vermicompost for the use in plants as an organic fertilizer.

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Table 1

Prepared Vermicompost

Table 2

Fertilizer Control Board Standards for Vermicompost:

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VOLUME: 10, Special Issue 02, (IC-IMAF-2023) Paper id-IJIERM-X-II, January 2023 180 Table 3

Physico-chemical Analysis of Floral Waste Vermicompost (VC) and its comparison with standard parameters of vermicompost testing.

Fig.1. Segregation of Floral waste

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VOLUME: 10, Special Issue 02, (IC-IMAF-2023) Paper id-IJIERM-X-II, January 2023 181

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