Specialist Group on Use of Macrophytes in Water Pollution ... - IWA
Specialist Group on Use of Macrophytes in Water Pollution ... - IWA
Specialist Group on Use of Macrophytes in Water Pollution ... - IWA
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APPLICATION OF CONSTRUCTED WETLAND FOR CONTROLLING<br />
LEACHATE POLLUTION FROM SOLID WASTE DISPOSAL<br />
Chart Chiemchaisri<br />
Department <strong>of</strong> Envir<strong>on</strong>mental Eng<strong>in</strong>eer<strong>in</strong>g/Nati<strong>on</strong>al Center <strong>of</strong> Excellence for Envir<strong>on</strong>mental<br />
and Hazardous Waste Management, Faculty <strong>of</strong> Eng<strong>in</strong>eer<strong>in</strong>g, Kasetsart University, Bangkok<br />
10900, Thailand<br />
An <strong>in</strong>vestigati<strong>on</strong> <strong>in</strong> Thailand is focus<strong>in</strong>g <strong>on</strong> the applicati<strong>on</strong> <strong>of</strong> c<strong>on</strong>structed wetland for direct<br />
treatment <strong>of</strong> leachate at municipal solid waste disposal site. The ma<strong>in</strong> purpose <strong>of</strong> treatment<br />
was to reduce the organic c<strong>on</strong>centrati<strong>on</strong> <strong>in</strong> leachate to an acceptable c<strong>on</strong>centrati<strong>on</strong> so that it<br />
can be further utilize for irrigati<strong>on</strong> <strong>on</strong> the landfill top soil. Two c<strong>on</strong>figurati<strong>on</strong>s <strong>of</strong> c<strong>on</strong>structed<br />
wetland were tested, i.e. horiz<strong>on</strong>tal sub-surface flow (HSF, Figure 1) and vertical flow (VF)<br />
types. Cattail was used as the vegetati<strong>on</strong> <strong>in</strong> both systems. They were applied for primary<br />
treatment <strong>of</strong> young leachate as well as post treatment for stabilized leachate. In each case, the<br />
hydraulic load<strong>in</strong>g rate (HLR) is varied between 0.01-0.056 m 3 /m 2 .d, equivalent to hydraulic<br />
retenti<strong>on</strong> time (HRT) <strong>in</strong> range <strong>of</strong> 28 and 5 days.<br />
Pollutant removal efficiencies <strong>in</strong> c<strong>on</strong>structed wetland<br />
Applied leachate had COD c<strong>on</strong>centrati<strong>on</strong> <strong>of</strong> about 3,000-5,000 mg/l with BOD/COD ratio <strong>of</strong><br />
0.6-0.7 and 0.05-0.1 for young and stabilized leachate respectively. In HSF and VF systems<br />
treat<strong>in</strong>g young leachate, high organic removal <strong>of</strong> more than 90% was achieved up to HLR <strong>of</strong><br />
0.028 m 3 /m 2 .d. In stabilized leachate case, moderate organic removal efficiencies were<br />
achieved. TKN removal was higher <strong>in</strong> VF (60-70%) as compared to HSF system (40-50%).<br />
Temporal accumulati<strong>on</strong> <strong>of</strong> oxidized nitrogen was observed at high nitrogen load<strong>in</strong>g c<strong>on</strong>diti<strong>on</strong><br />
(from stabilized leachate) caus<strong>in</strong>g some death <strong>of</strong> plant (Figure 2). Moderate nitrogen removal<br />
efficiencies was achieved at HLR up to 28 m 3 /m 2 .d for stabilized leachate where <strong>in</strong>fluent<br />
TKN c<strong>on</strong>centrati<strong>on</strong> was c<strong>on</strong>trolled at about 100-300 mgL -1 .<br />
Gravel<br />
Influent<br />
Coarse sand<br />
Figure 1 Schematic <strong>of</strong> HSF c<strong>on</strong>structed wetland system<br />
____________________________________________________________________________________________________<br />
<strong>IWA</strong> <str<strong>on</strong>g>Specialist</str<strong>on</strong>g> <str<strong>on</strong>g>Group</str<strong>on</strong>g> <strong>on</strong> <strong>Use</strong> <strong>of</strong> <strong>Macrophytes</strong> <strong>in</strong> <strong>Water</strong> Polluti<strong>on</strong> C<strong>on</strong>trol: Newsletter No. 35 15<br />
3 m<br />
Effluent<br />
0.40 m<br />
0.8 m<br />
1.3 m