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DC Field | Value | Language |
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dc.contributor.author | Rajendra Hegde, Ramesh Kumar, S.C., K.V. Niranjana, S. Srinivas, M.Lalitha, B.A. Dhanorkar, R.S. Reddy and S.K. Singh | en_US |
dc.date.accessioned | 2020-08-25T05:15:37Z | - |
dc.date.available | 2020-08-25T05:15:37Z | - |
dc.date.issued | 2019-12-31 | - |
dc.identifier.citation | Rajendra Hegde, Ramesh Kumar, S.C., K.V. Niranjana, S. Srinivas, M.Lalitha, B.A. Dhanorkar, R.S. Reddy and S.K. Singh (2019). “Land Resource Inventory and Socio- Economic Status of Farm Households for Watershed Planning and Development of Babulgaon-2 (4E6E2D2e) Microwatershed, Humnabad Taluk, Bidar District, Karnataka”, ICAR-NBSS&LUP Sujala MWS Publ.66, ICAR – NBSS & LUP, RC, Bangalore. p.93 & 29. | en_US |
dc.identifier.issn | Not Available | - |
dc.identifier.uri | http://krishi.icar.gov.in/jspui/handle/123456789/40169 | - |
dc.description | Not Available | en_US |
dc.description.abstract | The land resource inventory of Babulgaon-2 microwatershed was conducted using village cadastral maps and IRS satellite imagery on 1:7920 scale. The false colour composites of IRS imagery were interpreted for physiography and these physiographic delineations were used as base for mapping soils. The soils were studied in several transects and a soil map was prepared with phases of soil series as mapping units. Random checks were made all over the area outside the transects to confirm and validate the soil map unit boundaries. The soil map shows the geographic distribution and extent, characteristics, classification and use potentials of the soils in the microwartershed. The present study covers an area of 404 ha in Babulgaon-2 microwatershed in Humnabad taluk of Bidar district, Karnataka. The climate is semiarid and categorized as drought- prone with an average annual rainfall of 811 mm, of which about 609 mm is received during south–west monsoon, 109 mm during north-east and the remaining 93 mm during the rest of the year. An area of about 97 per cent is covered by soils and three per cent is covered by waterbodies, settlements and others. The salient findings from the land resource inventory are summarized briefly below. The soils belong to 9 soil series and 34 soil phases (management units) and 4 land use classes. The length of crop growing period is about 150 days starting from the 1st week of June to 2nd week of October. From the master soil map, several interpretative and thematic maps like land capability, soil depth, surface soil texture, soil gravelliness, available water capacity, soil slope and soil erosion were generated. Soil fertility status maps for macro and micronutrients were generated based on the surface soil samples collected at every 250 m grid interval. Land suitability for growing major agricultural and horticultural crops were assessed and maps showing degree of suitability along with constraints were generated. Entire area is suitable for agriculture. About 87 per cent of the soils are moderately deep to deep and very deep (75- >150 cm) and 10 per cent are shallow (25-50 cm) soils. An area of 75 per cent has clayey soils at the surface and 22 per cent soils are loamy at the surface. About 80 per cent of the area has non-gravelly soils and 17 per cent gravelly to very gravelly (15-60% gravel) soils. About 18 per cent of the area are very high (>200mm/m), 32 per cent medium (100- 150 mm/m) and 47 per cent low (50-100 mm/m) to very low (<50 mm/m) in available water capacity. About 48 per cent is nearly level (0-1%), 38 per cent very gently sloping (1-3%), about 4 per cent area is gently (3-5%) sloping lands and 6 per cent moderately sloping (5-10%) lands. An area of about 70 per cent has soils that are slightly eroded (e1), 17 per cent moderately eroded (e2) and 9 per cent severely eroded (e3). An area of about 15 per cent has soils that are slightly acid (pH 6.0 to 6.5), about 38 per cent is neutral (pH 6.5-7.3) and about 44 per cent area is slightly to strongly alkaline soils (pH 7.3-9.0). The Electrical Conductivity (EC) of the soils are dominantly <2 dsm-1indicating that the soils are non-saline. An area about 91 per cent area is high (>0.75%) in organic carbon and 5 per cent medium (0.5-0.75%) in organic carbon. Major area of 85 per cent has soils that are low (<23 kg/ha), 10 per cent medium (23- 57 kg/ha) in available phosphorus and high (>57 kg/ha) in about 2 per cent area. About 30 per cent area is low (<145 kg/ha), 60 per cent medium (145-337 kg/ha) and 6 per cent high (>337 kg/ha) in available potassium. Available sulphur is low (<10 ppm) in about 60 per cent area, medium (10-20 ppm) in 36 per cent and 2 per cent high (>20 ppm). Available boron is low (<0.5 ppm) in about 93 per cent area and 4 per cent medium (0.5-1.0 ppm). About 93 per cent area is sufficient (>4.5 ppm) and 4 per cent is deficient in available iron. Available manganese and copper are sufficient in all the soils. About 27 per cent area has soils that are deficient (<0.6 ppm) in available zinc and 70 per cent sufficient (>0.6 ppm). The land suitability for 19 major crops grown in the microwatershed were assessed and the areas that are highly suitable (S1) and moderately suitable (S2) are given below. It is however to be noted that a given soil may be suitable for various crops but what specific crop to be grown may be decided by the farmer looking to his capacity to invest on various inputs, marketing infrastructure, market price and finally the demand and supply position. Land suitability for various crops in the microwatershed Crop Suitability Area in ha (%) Crop Suitability Area in ha (%) Highly suitable (S1) Moderately suitable (S2) Highly suitable (S1) Moderately suitable (S2) Sorghum 71 (18) 185 (46) Sapota 23 (6) 212(53) Maize - 185 (46) Jackfruit 97 (24) 151 (38) Red gram - 256 (64) Jamun 97 (24) 222 (55) Sunflower 71 (18) 185 (46) Musambi 23 (6) 296 (74) Cotton 65 (16) 187 (46) Lime 23 (6) 296 (74) Sugarcane - 185 (46) Cashew 103 (25) 136 (34) Soybean 71 (18) 200(50) Custard apple 181 (45) 144 (36) Bengalgram 71 (18) 185 (46) Amla 178 (44) 147 (36) Guava 23 (6) 212(52) Tamarind 97(24) 89 (22) Mango - 100 (25) Apart from the individual crop suitability, a proposed crop plan has been prepared for the 4 identified LUCs by considering only the highly and moderately suitable lands for different crops and cropping systems with food, fibre and horticulture crops that helps in maintaining the ecological balance in the microwatershed. Maintaining soil-health is vital to crop production and conserve soil and land resource base for maintaining ecological balance and to mitigate climate change. For this, several ameliorative measures have been suggested to these problematic soils like saline/alkali, highly eroded, sandy soils etc., Soil and water conservation treatment plan has been prepared that would help in identifying the sites to be treated and also the type of structures required. As part of the greening programme, several tree species have been suggested to be planted in marginal and submarginal lands, field bunds and also in the hillocks, mounds and ridges that would help in supplementing the income, provide fodder and fuel and generate lot of biomass. This helps in maintaining an ecological balance and also helps in mitigating the climate change.Baseline socioeconomic characterisation is prerequisite to prepare action plan for program implementation and to assess the project performance before making any changes in the watershed development program. The baseline provides appropriate policy direction for enhancing productivity and sustainability in agriculture. Methodology: Babulgaon-2 micro-watershed (Raipalli sub-watershed, Humnabad taluk, Bidar district) is located in between 17040’ – 17042’ North latitudes and 77014’ – 77016’ East longitudes, covering an area of about 404 ha, bounded by Mustari, Udbal, Bannahalli and Bilkhera villages with length of growing period (LGP) 120-150 days. We used soil resource map as basis for sampling farm households to test the hypothesis that soil quality influence crop selection, and conservation investment of farm households. The level of technology adoption and productivity gaps and livelihood patterns were analyses. The cost of soil degradation and ecosystem services were quantified for each watershed. Results: The socio-economic outputs for the Babulgaon-2 micro-watershed in Raipalli sub-watershed, Humnabad taluk and Bidar district are presented here. Social Indicators; Male and female ratio is 68.1 to 31.9 per cent to the total sample population. Younger age group of 18 to 30 populations is around 57.5 per cent to the total population. Literacy population is around 85.1 per cent. Social groups belong to other backward caste (OBC) is around 50 per cent. Fire wood and liquefied petroleum gas is the source of energy for a cooking among 70 per cent. About 40 per cent of households have a yashaswini health card. About 30 percent of farm households are having MGNREGA card for rural employment. Dependence on ration cards for food grains through public distribution system are among all households. Swach bharath program providing closed toilet facilities, among all these study area household are not having toilet facilities. Women participation in decisions making are around 90 per cent of households were found. Economic Indicators; The average land holding is 0.63 ha indicates that majority of farm households are belonging to marginal and small farmers. The total cultivated area by dry land condition of among all sample households. 2 Agriculture is the main occupation among 19.1per cent and agriculture is the main and agriculture labour is subsidiary occupation for 42.6 per cent of sample households. The average value of domestic assets is around Rs. 20229 per household. Mobile and television are popular media mass communication. The average value of livestock is around Rs.42667 per household; about 66.9 per cent of household are having livestock. The average per capita food consumption is around 827grams (1879 kilo calories) against national institute of nutrition recommendation at 827 gram. Around 82.9 per cent of sample households are consuming less than the NIN recommendation. The annual average income is around Rs.31803 per household. Among all farm households are comes under the below poverty line. The per capita average monthly expenditure is around Rs. 2039. Environmental Indicators-Ecosystem Services; The value of ecosystem service helps to support investment to decision on soil and water conservation and in promoting sustainable land use. The onsite cost of different soil nutrients lost due to soil erosion is around Rs. 1406 per ha/year. The total cost of annual soil nutrients is around Rs. 548361 per year for the total area of 403 ha. The average value of ecosystem service for food grain production is around Rs. 22424/ ha/year. Per hector food grain production services is maximum in redgram (Rs. 35746) followed by sugarcane (Rs. 26202) and maize (Rs. 5324). The data on water requirement for producing one quintal of grain is considered for estimating the total value of water required for crop production. The per hectare value of water used and value of water was maximum in sugarcane (Rs. 146532) followed by redgram (Rs.63166) and maize (Rs. 25152). Economic Land Evaluation; The major cropping pattern is maize (17.3 %) followed by redgram (53.8%) sugarcane (25.5 %). In Babulgaon-2 micro watershed, major soils of Babulgoan (BGN) series are having very soil depth cover around 17.7 % of area. On this soil farmers are presently growing redgram. Mudhanal (MNL) are also having deep soil depth cover around 3.7 % of area, major crops are redgram. Muthangi (MTN) soil series having moderately soil depth cover around 19.7 % of areas, crops are sugarcane. Mustarwadi (MWD) and soil series having very deep soil depth cover 24.7 % of areas crops are maize (29 %) and redgram (71%). 3 The total cost of cultivation and benefit cost ratio (BCR) in study area for redgram ranges between Rs. 66484/ha in MNL soil (with of BCR of 0.83) and Rs. 41914/ha in MWD soil (with of BCR 1.15). In sugarcane the cost of cultivation in MTN soil is Rs. 123820/ha (with of BCR 1.21). In maize the cost of cultivation Rs. 23492/ha in MWD soil (with BCR of 1.23) The land management practices reported by the farmers are crop rotation, tillage practices, fertilizer application and use of farm yard manure (FYM). Due to higher wages farmer are following labour saving strategies is not prating soil and water conservation measures. Less ownership of livestock limiting application of FYM. It was observed soil quality influences on the type and intensity of land use. More fertilizer applications in deeper soil to maximize returns. Suggestions; Involving farmers is watershed planning helps in strengthing institutional participation. The per capita food consumption and monthly income is very low. Diversifying income generation activities from crop and livestock production in order to reduce risk related to drought and market prices. Majority of farmers reported that they are not getting timely support/extension services from the concerned development departments. By strengthing agricultural extension for providing timely advice improved technology there is scope to increase in net income of farm households. By adopting recommended package of practices by following the soil test fertiliser recommendation, there is scope to increase yield in redgram (2.7 to 48%) followed by sugarcane (10.7%) and maize (75.2%). | en_US |
dc.description.sponsorship | Watershed Development Department, Government of Karnataka (World Bank Funded) Sujala –III Project | en_US |
dc.language.iso | English | en_US |
dc.publisher | ICAR::National Bureau of Soil Survey and Land Use Planning, Regional Centre, Bengaluru & Watershed Development Department, Government of Karnataka (Sujala-III Project) | en_US |
dc.relation.ispartofseries | 66; | - |
dc.subject | Details of Soil Survey, Soil constraints, Soil and Water Conservation, Soil Suitability, Economic Land Evaluation, Watershed Planning, Sujala – III Project | en_US |
dc.title | LAND RESOURCE INVENTORY AND SOCIO-ECONOMIC STATUS OF FARM HOUSEHOLDS FOR WATERSHED PLANNING AND DEVELOPMENT BABULGAON-2 (4E6E2D2e) MICROWATERSHED Humnabad Taluk, Bidar District, Karnataka | en_US |
dc.title.alternative | Not Available | en_US |
dc.type | Project Report | en_US |
dc.publication.projectcode | Not Available | en_US |
dc.publication.journalname | Not Available | en_US |
dc.publication.volumeno | Not Available | en_US |
dc.publication.pagenumber | p.93 & 29. | en_US |
dc.publication.divisionUnit | ICAR::National Bureau of Soil Survey and Land Use Planning, Regional Centre, Bengaluru | en_US |
dc.publication.sourceUrl | Not Available | en_US |
dc.publication.authorAffiliation | ICAR::National Bureau of Soil Survey and Land Use Planning | en_US |
dc.ICARdataUseLicence | http://krishi.icar.gov.in/PDF/ICAR_Data_Use_Licence.pdf | en_US |
Appears in Collections: | NRM-NBSSLUP-Publication |
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