Mapping Land Used After Bricks Mining Area at Potorono Village Banguntapan Yogyakarta
International Journal of Applied Agricultural Sciences
Volume 4, Issue 1, January 2018, Pages: 21-27
Received: Nov. 13, 2017;
Accepted: Dec. 24, 2017;
Published: Jan. 19, 2018
Views 2429 Downloads 112
Susila Herlambang, Department of Soil Science, University Pembangunan Nasional Veteran Yogyakarta Indonesia, Yogyakarta, Indonesia
Purwono Budi Santosa, Department of Soil Science, University Pembangunan Nasional Veteran Yogyakarta Indonesia, Yogyakarta, Indonesia
The degradation on the soil after bricks mining was limited land used to agriculture plant in fields. The out put this research to know land used after mining in the various depths after bricks mining. The mapping was land used after bricks mining in the six villages mining at Potorono Banguntapan District of Yogyakarta in the 2016. The method of this research was used survey techniques and over lapping map land use. Mapping base was used satellite imagery map to determine the boundaries of operations, and then use the map was used various soil deeper in mining. The map of the plant is determining on the land use after the land was reclamation lands. The result of this research is mapping irrigated lands, settlements, gardens, and field moor at several debts after bricks mining. The pasca bricks mining will be restrict land use of agricultural. At mining on the depth about 100 cm was grown by paddy soil in land, while the mining of more than 200 cm, the wetland is unsuitable by paddy soil. The limited alternative of agriculture plants was determined by the level of decline fertility and organic matter in soil, add bulk density and sand content in the soil. In the former bricks mining can be planted with paddy soil is an area with good irrigation requirements with a production under 7 tones per hectare. While in the mining above 200 cm and nothing irrigation, the farmers will be grown crops with irrigation depends on the rain. The conclusion on the research is content of organic matter in the mining was important by nutrient storage soil. The amelioration to marginal soil was soil structure repaired by organic matter for water and nutrient storage. The nutrient was sufficient to determine on reclamation to growth of plants after the mining for sustainability agriculture. On the brick mining was allowed soil take at top soils, after mining it must be done as soon as possible for reclamation land towards sustainability agriculture.
Purwono Budi Santosa,
Mapping Land Used After Bricks Mining Area at Potorono Village Banguntapan Yogyakarta, International Journal of Applied Agricultural Sciences.
Vol. 4, No. 1,
2018, pp. 21-27.
Antonious, G. F., Turley, E. T., & Hill, R. R. (2014). Impact of soil amendments on metribuzin and DCPA half-lives and mobility into agricultural run off water. Journal of Environmental Science and Health, Part B, 49 (5), 313–323.
Barto, E. K., Alt, F., Oelmann, Y., Wilcke, W., & Rillig, M. C. (2010). Contributions of biotic and abiotic factors to soil aggregation across a land use gradient. Soil Biology and Biochemistry, 42 (12), 2316–2324.
Basso, B., Amato, M., Bitella, G., Rossi, R., Kravchenko, A., Sartori, L., Gomes, J. (2010). Two-dimensional spatial and temporal variation of soil physical properties in tillage systems using electrical resistivity tomography. Agronomy Journal, 102 (2), 440–449.
Costantini, E. A., & Lorenzetti, R. (2013). Soil degradation processes in the Italian agricultural and forest ecosystems. Italian Journal of Agronomy, 8 (4), 28.
DuPont, S. T., Culman, S. W., Ferris, H., Buckley, D. H., & Glover, J. D. (2010). No-tillage conversion of harvested perennial grassland to annual cropland reduces root biomass, decreases active carbon stocks, and impacts soil biota. Agriculture, Ecosystems & Environment, 137 (1), 25–32.
González-Peñaloza, F. A., Cerdà, A., Zavala, L. M., Jordán, A., Giménez-Morera, A., & Arcenegui, V. (2012). Do conservative agriculture practices increase soil water repellency? A case study in citrus-cropped soils. Soil and Tillage Research, 124, 233–239.
Grewal, S. S., Cheng, Z., Masih, S., Wolboldt, M., Huda, N., Knight, A., & Grewal, P. S. (2011). An assessment of soil nematode food webs and nutrient pools in community gardens and vacant lots in two post-industrial American cities. Urban Ecosystems, 14 (2), 181–194.
He, N., Zhang, Y., Dai, J., Han, X., Baoyin, T., & Yu, G. (2012). Land-use impact on soil carbon and nitrogen sequestration in typical steppe ecosystems, Inner Mongolia. Journal of Geographical Sciences, 22 (5), 859–873.
Jagadamma, S., & Lal, R. (2010). Distribution of organic carbon in physical fractions of soils as affected by agricultural management. Biology and Fertility of Soils, 46 (6), 543–554.
Johnson, M., Isakov, V., Touma, J. S., Mukerjee, S., & Özkaynak, H. (2010). Evaluation of land-use regression models used to predict air quality concentrations in an urban area. Atmospheric Environment, 44 (30), 3660–3668.
Kato, H., Onda, Y., & Teramage, M. (2012). Depth distribution of 137 Cs, 134 Cs, and 131 I in soil profile after Fukushima Dai-ichi Nuclear Power Plant accident. Journal of Environmental Radioactivity, 111, 59–64.
Koarashi, J., Atarashi-Andoh, M., Matsunaga, T., Sato, T., Nagao, S., & Nagai, H. (2012). Factors affecting vertical distribution of Fukushima accident-derived radiocesium in soil under different land-use conditions. Science of the Total Environment, 431, 392–401.
Laborde, D., & others. (2011). Assessing the land use change consequences of European biofuel policies. International Food Policy Institute (IFPRI). Retrieved from http://re.indiaenvironmentportal.org.in/files/file/biofuelsreportec2011.pdf.
Lenssen, A. W., Sainju, U. M., Jabro, J. D., Allen, B. L., & Evans, R. G. (2015). Management and tillage influence barley forage productivity and water use in dryland cropping systems. Agronomy Journal, 107 (2), 551–557.
Olson, N. C., Gulliver, J. S., Nieber, J. L., & Kayhanian, M. (2013). Remediation to improve infiltration into compact soils. Journal of Environmental Management, 117, 85–95.
Osman, K. T. (2014). Physical Deterioration of Soil. In Soil Degradation, Conservation and Remediation (pp. 45–67). Springer. Retrieved from http://link.springer.com/10.1007/978-94-007-7590-9_2
Virto, I., Barré, P., Burlot, A., & Chenu, C. (2012). Carbon input differences as the main factor explaining the variability in soil organic C storage in no-tilled compared to inversion tilled agrosystems. Biogeochemistry, 108 (1–3), 17–26.
Volchko, Y., Norrman, J., Bergknut, M., Rosén, L., & Söderqvist, T. (2013). Incorporating the soil function concept into sustainability appraisal of remediation alternatives. Journal of Environmental Management, 129, 367–376.
Wick, A. F., Daniels, W. L., Orndorff, Z. W., & Alley, M. M. (2013). Organic matter accumulation post-mineral sands mining. Soil Use and Management, 29 (3), 354–364.