Effect of Bottom Ash and Cow Manure Compost on Chemical Properties of Soil at New-Established Rice Field

The conversion of dryland to rice field at Sumatra Island, Indonesia was generally developed on marginal lands with Ultisols and Oxisols soil types. Those soil types contained high iron (Fe) and aluminum (Al), but low phosphorus (P) and potassium (K). That is because the changes in the process resulted from submerging the soil. For example, the decrease of redox potential, ion reduction from Fe3+ to Fe2+, and Mn4+ into Mn2+.  Those compounds will be dissolved and can be absorbed by plants thus causing toxicity. The objective of the study was to assess the effects of bottom ash and cow manure compost at the various doses on soil chemical properties and rice yield on the new-established rice field. This research used factorial design with two factors in Completely Randomized Design. The factors were a dose of bottom ash and cow manure compost, with three replications. The results showed. The addition of bottom ash and cow manure compost at the dosage in this study was not able to reduce the levels of FeDTPA and MnDTPA at newly established rice fields.  However, the application of cow manure compost significantly increased soil pH,  exchangeable cation (K, Na, Ca), base saturation and decreased exchangeable-H. The addition of bottom ash does not affect paddy yield, while cow manure compost up to 10 tons ha-1 increased panicle and straw dry weight.

[1]  S. Utami,et al.  Perubahan Sifat Kimia Entisol Pada Sistem Pertanian Organik , 2020 .

[2]  M. Basir-Cyio EFEKTIVITAS BAHAN ORGANIK DAN TINGGI GENANGAN TERHADAP PERUBAHAN Eh, pH, DAN STATUS Fe, P, Al TERLARUT PADA TANAH ULTISOL , 2017 .

[3]  Rika Yayu Agustini,et al.  Respon Tanah Mineral Masam Dan Tanaman Caisim (Brassica Juncea) Terhadap Pemberian Abu Dasar (Bottom Ash) Dan Kompos Kotoran Sapi Sebagai Amelioran Tanah , 2016 .

[4]  R. Thring,et al.  Wood pellet fly ash and bottom ash as an effective liming agent and nutrient source for rye grass (Lolium perenne L.) and oats (Avena sativa). , 2012, Chemosphere.

[5]  A. Ivanov,et al.  MANGANESE AS ESSENTIAL AND TOXIC ELEMENT FOR PLANTS: TRANSPORT, ACCUMULATION AND RESISTANCE MECHANISMS , 2010 .

[6]  Iskandar,et al.  Pemanfaatan Bahan Amelioran Abu Terbang pada Lingkungan Tanah Gambut: Penglepasan Hara Makro , 2008 .

[7]  Asmar Asmar,et al.  POTENSI SENYAWA ORGANIK TIDAK TER-ION DALAM MENGURANGI KELARUTAN BESI (FE) UNTUK MENINGKATKAN PRODUKTIFITAS TANAH SAWAH BUKAAN BARU , 2007 .

[8]  N. Hue,et al.  Manganese Solubility and Phytotoxicity Affected by Soil Moisture, Oxygen Levels, and Green Manure Additions , 2004 .

[9]  W. H. Patrick,et al.  Evaluation of toxic conditions associated with oranging symptoms of rice in a flooded Oxisol in Sumatra, Indonesia , 1993, Plant and Soil.

[10]  M. H. Milford Soils and Their Environment , 1993 .

[11]  N. J. Sell,et al.  The agronomic landspreading of coal bottom ash: Using a regulated solid waste as a resource , 1989 .

[12]  A. Tanaka,et al.  INTERACTION BETWEEN IRON AND MANGANESE IN THE RICE PLANT , 1966 .

[13]  Francis Hamilton Redman Effect of submergence on several biological and chemical soil properties , 1965 .

[14]  C. A. Black Soil-Plant Relationships , 1958 .