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Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns
Authors:Helena Lina Susilawati  Prihasto Setyanto  Miranti Ariani  Anggri Hervani  Kazuyuki Inubushi
Institution:1. Graduate School of Horticulture, Chiba University, Matsudo 648, Matsudo-shi 271-8510, Japan;2. Division of GHG Emission and Absorption, Indonesian Agricultural Environment Research Institute, Jl. Jakenan-Jaken Km 5 Pati, Central Java, 59182, Indonesia;3. Division of GHG Emission and Absorption, Indonesian Agricultural Environment Research Institute, Jl. Jakenan-Jaken Km 5 Pati, Central Java, 59182, Indonesia
Abstract:Recently, large areas of tropical peatland have been converted into agricultural fields. To be used for agricultural activities, peat soils need to be drained, limed and fertilized due to excess water, low nutrient content and high acidity. Water depth and amelioration have significant effects on greenhouse gas (GHG) production. Twenty-seven soil samples were collected from Jabiren, Central Kalimantan, Indonesia, in 2014 to examine the effect of water depth and amelioration on GHG emissions. Soil columns were formed in the peatland using polyvinyl chloride (PVC) pipe with a diameter of 21 cm and a length of 100 cm. The PVC pipe was inserted vertically into the soil to a depth of 100 cm and carefully pulled up with the soil inside after sealing the bottom. The treatments consisting of three static water depths (15, 35 and 55 cm from the soil surface) and three ameliorants (without ameliorant/control, biochar+compost and steel slag+compost) were arranged using a randomized block design with two factors and three replications. Fluxes of carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO2 emissions. No significant difference was observed in the CH4 emissions in response to water depth and amelioration. The ameliorations influenced the CO2 and N2O emissions from the peat soil. The application of biochar+compost enhanced the CO2 and N2O emissions but reduced the CH4 emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO2 and N2O emissions occurred in response to the biochar+compost treatment followed by the steel slag-compost treatment and without ameliorant. Soil pH, redox potential (Eh) and temperature influenced the CO2, CH4 and N2O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems.
Keywords:Biochar  CO2  N2O  steel slag  water tables
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