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2. MATERIAL AND METHODS<br />

2.1 Feedstock Preparation<br />

<strong>Solid</strong> waste used in <strong>th</strong>is study was collected from Taklong municipality dumpsite, Pa<strong>th</strong>um<strong>th</strong>ani,<br />

Thailand. The representative waste sample was manually segregated to retain <strong>th</strong>e organic fr<strong>ac</strong>tion<br />

and was subjected to particle size reduction (10 mm) by mechanical shredding. During <strong>th</strong>e start-up<br />

phase <strong>of</strong> <strong>th</strong>e process, 20% <strong>of</strong> total waste loaded during <strong>th</strong>e start-up was added as inoculums. The<br />

inoculum consisted <strong>of</strong> cow dung, anaerobic sludge, digested waste and matured le<strong>ac</strong>hate obtained<br />

from previous study (Adhikari, 2006). The experiments were carried out in <strong>th</strong>ermophilic (55°C)<br />

condition. The chemicals and physical analyses <strong>of</strong> samples were carried out for every collection in<br />

triplicate. Char<strong>ac</strong>teristic <strong>of</strong> <strong>th</strong>e solid waste is presented in Table 1.<br />

Table1. Feedstock Char<strong>ac</strong>teristics<br />

Parameters Value Parameters (mg/kg TS) Value<br />

Moisture content (MC) (%WW) 88-91 Cadmium (Cd) 0.3<br />

Total solid (TS) (%WW) 9-12 Lead (Pb) Not Detectable<br />

Volatile solid (VS) (%TS) 82.3-83.7 Zinc (Zn) 72.2<br />

Fixed solid (FS) (%TS) 17.7-16.3 Copper (Cu) 15.3<br />

N (% DM) 3.0 Chromium (Cr) 7.3<br />

P (% DM) 0.2 Nickel (Ni) 4.1<br />

K (% DM) 0.2 Manganese (Mn) 88.1<br />

C (%) 45.7 Mercury (Hg) 0.04<br />

C/N 15.0<br />

2.2 Experimental Set-up<br />

The experiments were performed in a stainless steel horizontal re<strong>ac</strong>tor wi<strong>th</strong> working volume <strong>of</strong><br />

600 L. The re<strong>ac</strong>tor’s feeding system consists <strong>of</strong> cover plate att<strong>ac</strong>hed wi<strong>th</strong> a movable shaft and a 2 m<br />

piston annexed to <strong>th</strong>e upper left <strong>of</strong> re<strong>ac</strong>tor. At <strong>th</strong>e o<strong>th</strong>er side (lower right) an outlet for <strong>th</strong>e digested<br />

waste and <strong>th</strong>e le<strong>ac</strong>hate is provided <strong>th</strong>at is fitted wi<strong>th</strong> movable paddle. Optimum <strong>th</strong>ermophilic<br />

condition (55°C) was maintained by a digital temperature controller wherein hot water from water<br />

ba<strong>th</strong> is circulating <strong>th</strong>rough <strong>th</strong>e double walled j<strong>ac</strong>ket <strong>of</strong> <strong>th</strong>e re<strong>ac</strong>tor. The gas outlet <strong>of</strong> <strong>th</strong>e re<strong>ac</strong>tor was<br />

connected a gas meter. Additionally, <strong>th</strong>e re<strong>ac</strong>tor is well insulated to minimize <strong>th</strong>e heat loss. Figure 1<br />

shows <strong>th</strong>e experimental set-up.<br />

2.3 Analytical Me<strong>th</strong>ods<br />

The parameters analyzed for <strong>th</strong>e char<strong>ac</strong>terization <strong>of</strong> OFMSW include Moisture Content (MC),<br />

Total <strong>Solid</strong> (TS), and Volatile <strong>Solid</strong> (VS) and selected heavy metals such as Cadmium (Cd), Lead<br />

(Pb), Zinc (Zn), Copper (Cu), Chromium (Cr), Nickel (Ni), Manganese (Mn), and Mercury (Hg).<br />

Nutrients analysis was also conducted by following ASTM standards (1993). Le<strong>ac</strong>hate was<br />

analyzed daily for <strong>th</strong>e following parameters, pH, alkalinity, VFA, NH3-N, TKN using Standard<br />

Me<strong>th</strong>od for Examination <strong>of</strong> Water and <strong>Waste</strong>water (APHA, AWWA, and WEF, 1998).<br />

2

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