2 research outputs found

    Influence of water depth and soil amelioration on greenhouse gas emissions from peat soil columns

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    <p>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 (CO<sub>2</sub>), methane (CH<sub>4</sub>) and nitrous oxide (N<sub>2</sub>O) from the soil columns were measured weekly. There was a linear relationship between water depth and CO<sub>2</sub> emissions. No significant difference was observed in the CH<sub>4</sub> emissions in response to water depth and amelioration. The ameliorations influenced the CO<sub>2</sub> and N<sub>2</sub>O emissions from the peat soil. The application of biochar+compost enhanced the CO<sub>2</sub> and N<sub>2</sub>O emissions but reduced the CH<sub>4</sub> emission. Moreover, the application of steel slag+compost increased the emissions of all three gases. The highest CO<sub>2</sub> and N<sub>2</sub>O 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 CO<sub>2</sub>, CH<sub>4</sub> and N<sub>2</sub>O fluxes. Experiments for monitoring water depth and amelioration should be developed using peat soil as well as peat soil–crop systems.</p

    Effects of steel slag applications on CH<sub>4</sub>, N<sub>2</sub>O and the yields of Indonesian rice fields: a case study during two consecutive rice-growing seasons at two sites

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    <div><p></p><p>The increasing human population requires greater rice production. However, rice cultivation contributes to global warming through greenhouse gas (GHG) emissions. Technologies for reducing GHG emissions in concert with the increased rice production from rice fields are needed. The objectives of this study were to evaluate the effects of steel slag applications on methane (CH<sub>4</sub>) and nitrous oxide (N<sub>2</sub>O) emissions and rice yields. Two study sites were established at the experimental farm belonging to Indonesian Agricultural Environment Research Institute (IAERI) in Jakenan and a farmer’s field in Wedarijaksa sub-district, Indonesia. Both field trials were conducted during the dry season (DS) of 2009 and the rainy season (RS) of 2009/2010. During the DS, a randomized block design was arranged with two treatments (a control and a steel slag application at 1 Mg ha<sup>−1</sup>), which were replicated five times. During the RS, the experimental plot with 1 Mg ha<sup>−1</sup> of steel slag treatment was split into two small sub-plots to accommodate the additional 1 and 2 Mg ha<sup>−1</sup> steel slag treatments. The results showed that there was a decreasing tendency in the CH<sub>4</sub> emissions at both sites and during both seasons after steel slag applications, although there was no statistical significance. During the RS in Jakenan, steel slag applications at rates of 1 and 2 Mg ha<sup>−1</sup> decreased the CH<sub>4</sub> emissions by 9.1 and 10.7%, respectively. In Wedarijaksa, steel slag applications at rates of 1 and 2 Mg ha<sup>−1</sup> decreased the CH<sub>4</sub> emissions by 12.6 to 18.7%, respectively. The N<sub>2</sub>O emissions were decreased by 34 and 38% following slag applications at the 2 Mg ha<sup>−1</sup> rate during the RS in Jakenan and Wedarijaksa, respectively. The iron content of steel slag could be used to reduce not only CH<sub>4</sub> but also N<sub>2</sub>O emissions. Increased level of electron acceptors suppresses CH<sub>4</sub> and N<sub>2</sub>O emissions. The application of steel slag at 1 and 2 Mg ha<sup>−1</sup> increased rice grain yields by approximately 4.8–5.6% in Jakenan and 0.3–4.7% in Wedarijaksa. It might be better to apply steel slag at higher rates for more than two growing seasons to reach reduction in CH<sub>4</sub> and N<sub>2</sub>O emissions.</p></div
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