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Soil Organic Carbon Pools under Terminalia chebula Retz. based Agroforestry Systemin Himalayan Foothills, Indiax


Affiliations
1 Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
2 Forest Ecology and Climate Change Division, Forest Research Institute, Dehradun 248 006, India
3 ICAR-Indian Institute of Soil and Water Conservation, Dehradun 248 001, India
 

Knowledge of carbon (C) pools in soils is helpful in devising practices for efficient carbon management in intensive cropping systems. Carbon fractions of soil organic carbon are used asan indicator for land-use induced change in soil quality. The present study evaluated carbon pools under Terminalia chebula(chebulic myrobalan) based agroforestry system supplied with different nutrient sources, viz. farmyard manure, poultry manure, vermicompost, wheat straw and inorganic fertilizer (NPK @ 100:80:60). Carbon fractions, viz. very labile (C1 frac), labile (C2 frac), less labile (C3 frac) and non-labile (C4 frac), were analysed at 0–15 and 15–30 cm soil depth. The higher value of C1 frac (13.8%), C2 frac (4.8%), C3 frac (8.3%) and C4 frac(11.1%) were recorded under agroforestry as compared to open system. Among the nutrient sources, all the carbon fractions were higher under 100% integrated nutrient sources as compared to controlled treatment. Microbial biomass carbon (MBC) was recorded higher (298.31 μg g–1 ) under agroforestry system compared to the open system (290.63 μg g–1 ) at 0–15 cm. Among the different nutrient sources, higher MBC (458.66 μg g–1 ) at 0–15 cm and lower (340.59 μg g–1 ) at 15–30 cm soil depth was recorded in 100% integrated treatment.Thus, agroforestry-based land-use types and integrated nutrient management are more efficient for soil health and carbon management in Himalayan foothills.

Keywords

Active Pool, Carbon Fractions, Labile, Nonlabile, Nutrient Sources, Passive Pool.
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  • Johl, S. S., Singh, S., Dev, D. S., Nijjar, G. S., Sidhu, A. S. and Grewal, S. S., Report of the expert committee on diversification of agriculture in Punjab, submitted to the Govt of Punjab, 1986, vol.165.
  • Albrecht, A. and Kandji, S. T., Carbon sequestration in tropical agroforestry systems. Agric. Ecosyst. Environ., 2003, 99(1–3), 15– 27.
  • Yadav, R. P., Gupta, B., Bhutia, P. L., Bisht, J. K. and Pattanayak, A., Biomass and carbon budgeting of land use types along elevation gradient in Central Himalayas. J. Clean Prod., 2019, 211, 1284–1298.
  • Nierenstein, M. and Potter, J., The distribution of myrobalanitannin. Biochem. J., 1945, 39(5), 390–392.
  • Chen, H., Hou, R., Gong, Y., Li, H., Fan, M. and Kuzyakov, Y., Effects of 11 years of conservationtillage on soil organic matter fractions in wheat monoculture in Loess Plateau of China. Soil Till. Res., 2009, 106(1), 85–94.
  • Haynes, R. J., Labile organic matter fractions as central components of the quality of agricultural soils: an overview. Adv. Agron., 2005, 85, 221–268.
  • Duval, M. E., Galantini, J. A., Iglesias, J. O., Canelo, S., Martinez, J. M. and Wall, L., Analysis of organic fractions as indicators of soil quality under natural and cultivated systems. Soil Till. Res., 2013, 131, 11–19.
  • Sherrod, L. A., Peterson, G. A., Westfall, D. G. and Ahuja, L. R., Soil organic carbon pools after 12 years in no-till dry land agroecosystems. Soil Sci. Soc. Am. J., 2005, 69(5), 1600–1608.
  • Baah-Acheamfour, M., Chang, S. X., Carlyle, C. N. and Bork, E. W., Carbon pool size and stability are affected by trees and grass-land cover types within agroforestry systems of western Canada. Agric, Ecosyst. Environ., 2015, 213, 105–113.
  • Nyaga, J., Muthuri, C. W., Barrios, E., Oborn, I. and Sinclair, F. L., Enhancing maize productivity in agroforestry systems through managing competition: lessons from smallholders’ farms, Rift valley, Kenya. Agroforest. Syst., 2017, 93(2), 1–16.
  • Del Galdo, I., Six J., Peressotti, A. and Cotrufo, M. F., Assessing the impact of land-use change onsoil C sequestration in agricultural soils by means of organic matter fractionation and stable C isotopes. Glob. Change Biol., 2003, 9, 1204–1213.
  • Six, J., Callewaert, P., Lenders, S., De Gryze, S., Morris, S. J., Gregorich, E. G. and Paustian, K., Measuring and understanding carbon storage in afforested soils by physical fractionation. Soil Sci. Soc. Am. J., 2002, 66(6), 1981–1987.
  • Hesse, P. R., A Text Book of Soil Chemical Analysis, CBS, New Delhi, India, 2002.
  • Chan, K. Y., Bowman, A. and Oates, A., Oxidizible organic carbon fractions and soil quality changes in oxicpaleustalf under different pasture leys. Soil Sci., 2001, 166, 61–67.
  • Ghosh, S., Wilson, B. R., Mandal, B., Ghoshal, S. K. and Growns, I., Changes in soil organic carbon pool in three long-term fertility experiments with different cropping systems and inorganic and organic soil amendments in the eastern cereal belt of India. Aus. J. Soil Res., 2010, 48, 413–420.
  • Jackinson, D. S. and Powlson, D. S., The effects of biological treatments on metabolism in soil. A method for measuring soil biomass. Soil Biol. Func., 1976, 8, 209–213.
  • Voroney, R. P., Winter, J. and Beyert, R. P., Soil microbial bio-mass C and N. In Soil Sampling and Methods of Analysis(eds Carter, M. R. and Gregoric, E. G.), 1993, vol. 27, pp. 277–286.
  • Munoz, F. and Beer, J., Fine ischolar_main dynamics of shaded cacao plantations in Costa Rica. Agroforest Syst., 2001, 51, 119–130.
  • Blevines, R. L. and Frye, W. W., Conservation tillage: an ecological approach in soil management. Adv. Agron., 1993, 51, 33–78.
  • Yadav, R. P. and Bisht, J. K., Litter fall and potential nutrient returns from pecan nut (Caryaillinoinensis) in agroforestry system in Indian Himalaya. Int. J. Herb. Med., 2014, 2(1), 51–52.
  • Singh, G., Carbon sequestration under an agri-silvicultural system in the arid region. Indian Forest, 2005, 147, 543–552.
  • Seneviratne, G., Litter quality and nitrogen release in tropical agriculture. Biol. Fert. Soils, 2000, 3(1), 60–64.
  • Kaur, T., Brar, B. S. and Dhillon, N. S., Soil organic matter dynamics as affected by long-term use of organic and inorganic fertilizers under maize-wheat cropping system. Nutr. Cycl. Agro-ecosyst., 2008, 81, 159–180.
  • Mandal, B. et al., Potential of cropping systems and soil amendments for carbon sequestration in soils under long-term experiments in sub-tropical India. Glob. Change Biol., 2008, 3, 357–369.
  • Yadav, R., Yadav, B., Chhipa, B., Dhyani, S. and Ram, M., Soil biological properties under different tree based traditional agro-forestry systems in a semiarid region of Rajasthan, India. Agro-forest. Syst., 2011, 81(3), 195–202.
  • Mahmood, T., Azam, F., Hussain, F. and Malik, K. A., Carbon availability and microbial biomass in soil under an irrigated wheat–maize cropping system receiving different fertilizer treatments. Biol. Fert. Soils, 1997, 25, 63–68.
  • Graham, M. H., Haynes, R. J. and Meyers, J. H., Soil organic matter content and quality: effects of fertilizer applications, burning and trash retention on long-term sugarcane experiment in South Africa. Soil Biol. Biochem., 2002, 34, 93–102.
  • Insam, H., Mitchell, C. C. and Dormaar, J. F., Relationship of soil microbial biology and activity withfertilization practices and crop yield of three ultisols. Soil Biol. Biochem., 1991, 23, 459–464.
  • Simek, M., Hopkins, D. W., Kalcik, J., Picek, T., Santruckova, H., Stana, J. and Travnik, K., Biological and chemical properties of arable soils affected by long-term organic and inorganic fertilizer applications. Biol. Fert. Soils, 1999, 29, 300–308.
  • Whitbread, A. M., Lefroy, R. D. B. and Blair, G. J., A survey of the impact of cropping on soil physical and chemical properties in north-western New South Wales. Aus. J. Soil Res., 1998, 36, 669– 681.
  • Addiscott, T., Entropy and sustainability. Eur. J. Soil Sci., 1995, 46, 161–168.
  • Majumder, B., Mandal, B., Bandyopadhyay, P. K., Gangopadhyay, A., Mani, P. K., Kundu, A. L. and Mazumdar, D., Organic amendments influence soil organic carbon pools and rice–wheat productivity. Soil Sci. Soc. Am. J., 2008, 72(3), 775–785.
  • Tirol-Padre, A. and Ladha, J. K., Assessing the reliability of permanganate-oxidizable carbon as an index of soil labile carbon. Soil Sci. Soc. Am. J., 2004, 68(3), 969–978.
  • Blair, N., Faulkner, R. D., Till, A. R. and Poulton, P. R., Long-term management impacts on soil C, N and physical fertility: part I: broadbalk experiment. Soil Till. Res., 2006, 91(1–2), 30–38.

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  • Soil Organic Carbon Pools under Terminalia chebula Retz. based Agroforestry Systemin Himalayan Foothills, Indiax

Abstract Views: 246  |  PDF Views: 88

Authors

Amit Kumar
Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
G. K. Dwivedi
Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
Salil Tewari
Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
Jaipaul
Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
V. K. Sah
Agroforestry Section, College of Agriculture, G.B. Pant University of Agriculture and Technology, Pantnagar, U.S. Nagar 243 145, India
Hukum Singh
Forest Ecology and Climate Change Division, Forest Research Institute, Dehradun 248 006, India
Parmanand Kumar
Forest Ecology and Climate Change Division, Forest Research Institute, Dehradun 248 006, India
Narendra Kumar
Forest Ecology and Climate Change Division, Forest Research Institute, Dehradun 248 006, India
Rajesh Kaushal
ICAR-Indian Institute of Soil and Water Conservation, Dehradun 248 001, India

Abstract


Knowledge of carbon (C) pools in soils is helpful in devising practices for efficient carbon management in intensive cropping systems. Carbon fractions of soil organic carbon are used asan indicator for land-use induced change in soil quality. The present study evaluated carbon pools under Terminalia chebula(chebulic myrobalan) based agroforestry system supplied with different nutrient sources, viz. farmyard manure, poultry manure, vermicompost, wheat straw and inorganic fertilizer (NPK @ 100:80:60). Carbon fractions, viz. very labile (C1 frac), labile (C2 frac), less labile (C3 frac) and non-labile (C4 frac), were analysed at 0–15 and 15–30 cm soil depth. The higher value of C1 frac (13.8%), C2 frac (4.8%), C3 frac (8.3%) and C4 frac(11.1%) were recorded under agroforestry as compared to open system. Among the nutrient sources, all the carbon fractions were higher under 100% integrated nutrient sources as compared to controlled treatment. Microbial biomass carbon (MBC) was recorded higher (298.31 μg g–1 ) under agroforestry system compared to the open system (290.63 μg g–1 ) at 0–15 cm. Among the different nutrient sources, higher MBC (458.66 μg g–1 ) at 0–15 cm and lower (340.59 μg g–1 ) at 15–30 cm soil depth was recorded in 100% integrated treatment.Thus, agroforestry-based land-use types and integrated nutrient management are more efficient for soil health and carbon management in Himalayan foothills.

Keywords


Active Pool, Carbon Fractions, Labile, Nonlabile, Nutrient Sources, Passive Pool.

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DOI: https://doi.org/10.18520/cs%2Fv118%2Fi7%2F1098-1103