Book of Extended summaries ISDA
Book of Extended summaries ISDA Book of Extended summaries ISDA
International Conference on Reimagining Rainfed Agro-ecosystems: Challenges & Opportunities during 22-24, December 2022 at ICAR-CRIDA, Hyderabad Methodology The productivity, profitability, energy security, and environmental sustainability of four Integrated Organic Farming System models (viz., IOFS -I, mono-cropping+livestock; IOFS - II, diversified cropping+livestock; IOFS -III, diversified cropping+livestock+poultry, and IOFS -IV, diversified cropping+ livestock+ poultry+ piggery) were assessed in Meghalaya region of Indian Himalayas. The system productivity of different systems was evaluated to assess their production capacity. For a meaningful comparison of different production systems, all products were converted into the rice equivalent yield i.e. system productivity. Energy auditing explores an efficiency edge between an input-output relationship in different production systems. Carbon footprint both at a spatial scale and yield scale and eco-efficiency considering energy input and emission of GHG per unit of economic gain were assessed to compare the environmental competency of integrated production systems. General Linear Model version SAS 9.4 was used to test the statistical significance of data obtained from diverse production systems. The least significant difference (LSD) and standard error of the mean was employed for valid comparison of data among the different IOFS models. Results All the integrated organic farming systems had higher energy profitability and substantially reduced greenhouse gas intensity (GHGI) over IOFS-I. IOFS -IV recorded considerably higher net profit (US$. 2828.5 y -1 ), energy productivity (0.22 kg MJ -1 ), and the lowest GHGI (0.33 kg CO 2eq kg -1 food production) over other production systems. GHG (kg -1 production) emissions of IOFS-IV were also 1.7 times lower than that of IOFS -I. Furthermore, IOFS -IV had recycled 81.1, 68.2, and 68.8% higher N, P, and K over the IOFS-1, respectively. Thus, the study suggested that IOFS -IV could be a profitable, energy-efficient, environmentally friendly, and economically viable sustainable production system for the Indian Himalayan region. References Babu Subhash, Mohapatra, K.P., Das, A., Yadav, G.S., Singh, R., Chandra, P., Avasthe, R. K., Kumar Amit, Thoithoi Devi, M., Singh, V. K. and Panwar, A. S. 2021. Integrated Farming Systems: Climate-Resilient Sustainable Food Production System in the Indian Himalayan Region. In: Exploring Synergies and Trade-offs Between Climate Change and the Sustainable Development Goals, V. Venkatramanan, Shachi Shah and Ram Prasad (Eds.): 119-143. https://doi.org/10.1007/978-981-15-7301-9_6 Lal, R. 2009. Soil degradation as a reason for inadequate human nutrition. Food Secur. 1(1): 45-57. DOI:10.1007/s12571-009-0009-z. Lu, S., Bai, X., Li, W., Wang, N. 2019. Impacts of climate change on water resources and grain production. Technol. Forecast. Soc. Change. 143:76-84. DOI:10.1016/j.techfore.2019.01.015 442 | Page Sustainable soil management for resilient rainfed agro-ecosystem: conservation agriculture, organic farming, INM, soil-microorganisms-plant interactions
International Conference on Reimagining Rainfed Agro-ecosystems: Challenges & Opportunities during 22-24, December 2022 at ICAR-CRIDA, Hyderabad Martínez M.L., Intralawan A., Vázquez G., Pérez-Maqueo O., Sutton P., Landgrave R. 2007. The coasts of our world: Ecological, economic and social importance. Ecol. Econ. 63(2-3): 254- 272. https://doi.org/10.1016/j.ecolecon.2006.10.022. T4-04R-1217 Impact of Long- Term Fertilization and Manuring on Aggregate Stability and Biochemical Characterization of Aggregate Associated C in the Alfisols Suvana Sukumaran 1* , T. J. Purakayastha 2 , Bidisha Chakrabarti 2 , K. K. Bandyopadhyay 2 , ThulasiViswanathe 3 , K. K. Rout 4 , K. Sammi Reddy 1 and A.K. Indoria 1 1 ICAR-Central Research Institute for Dryland Agriculture, Hyderabad, India, 2 ICAR- Indian Agricultural research Institute, New Delhi, 3 Regional Agricultural Research Station, Pattambi, Kerala, 4 Orissa University of Agriculture and Technology, Bhubaneswar, Odisha * suvana.sukumaran@icar.gov.in Different land use and land cover management practices affect soil aggregation, which inturn affect soil C retention. The SOC in the profile can be stabilised by three mechanisms mainly- physical protection by organo-mineral complexes, biochemical stability to decomposition and chemical protection by adsorption to clay surfaces. The decomposition rate of C is directly proportional to the size of aggregates. Chemical association of SOC with silt and clay particles can also impose a limit to the soil’s C stabilization potential due to a limit in the surface area of the silt-plus-clay fraction in a given soil. Biochemical stabilization of SOM in the soil matrix is a strong function of the inherent chemical and structural stability of the organic biomolecules. Soil aggregate dynamics and SOM decomposition are closely linked. The present study was undertaken to study the effect of long-term manuring and fertilization on the physical and biochemical stability of aggregates and the associated carbon in the ricerice cropping system of the Alfisols of Bhubaneswar (BHNS) and Pattambi (PTMB). Methodology This study was carried out in two long term fertilizer experiments continuing in Bhubaneswar (Orissa) and Pattambi (Kerala), where rice- rice was the main cropping system. The experimental site at Bhubaneswar has tropical and sub-humid climate, whereas that at Pattambi has perhumid. The soils at Bhubaneswar were acidic sandy loam and at Pattambi were acidic sandy clay loam. The following treatments were considered for the study:T1- control, T2- 50 % NPK, T3- 100%NPK, T4- 150 % NPK, T5- 100%NPK+ FYM ( 10 t ha -1 ), T6- 100%NPK + Lime. The soil samples were collected from 0-15 and 15-30 cm depth. The aggregate size distribution was done using wet sieving method. The total carbon content in the sample was determined by dry combustion in CHNS analyser (Eurovector, model Euro Sustainable soil management for resilient rainfed agro-ecosystem: conservation agriculture, organic farming, INM, soil-microorganisms-plant interactions 443 | Page
- Page 404 and 405: International Conference on Reimagi
- Page 406 and 407: International Conference on Reimagi
- Page 408 and 409: International Conference on Reimagi
- Page 410 and 411: International Conference on Reimagi
- Page 412 and 413: International Conference on Reimagi
- Page 414 and 415: International Conference on Reimagi
- Page 416 and 417: International Conference on Reimagi
- Page 418 and 419: International Conference on Reimagi
- Page 420 and 421: International Conference on Reimagi
- Page 422 and 423: International Conference on Reimagi
- Page 424 and 425: International Conference on Reimagi
- Page 426 and 427: International Conference on Reimagi
- Page 428 and 429: International Conference on Reimagi
- Page 430 and 431: International Conference on Reimagi
- Page 432 and 433: International Conference on Reimagi
- Page 434 and 435: International Conference on Reimagi
- Page 436 and 437: International Conference on Reimagi
- Page 438 and 439: International Conference on Reimagi
- Page 440 and 441: International Conference on Reimagi
- Page 442 and 443: International Conference on Reimagi
- Page 444 and 445: International Conference on Reimagi
- Page 446 and 447: International Conference on Reimagi
- Page 448 and 449: International Conference on Reimagi
- Page 450 and 451: International Conference on Reimagi
- Page 452 and 453: International Conference on Reimagi
- Page 456 and 457: International Conference on Reimagi
- Page 458 and 459: International Conference on Reimagi
- Page 460 and 461: International Conference on Reimagi
- Page 462 and 463: International Conference on Reimagi
- Page 464 and 465: International Conference on Reimagi
- Page 466 and 467: International Conference on Reimagi
- Page 468 and 469: International Conference on Reimagi
- Page 470 and 471: International Conference on Reimagi
- Page 472 and 473: International Conference on Reimagi
- Page 475 and 476: International Conference on Reimagi
- Page 477 and 478: International Conference on Reimagi
- Page 479 and 480: International Conference on Reimagi
- Page 481 and 482: International Conference on Reimagi
- Page 483 and 484: International Conference on Reimagi
- Page 485 and 486: International Conference on Reimagi
- Page 487 and 488: International Conference on Reimagi
- Page 489 and 490: International Conference on Reimagi
- Page 491 and 492: International Conference on Reimagi
- Page 493 and 494: International Conference on Reimagi
- Page 495 and 496: International Conference on Reimagi
- Page 497 and 498: International Conference on Reimagi
- Page 499 and 500: International Conference on Reimagi
- Page 501 and 502: International Conference on Reimagi
- Page 503 and 504: International Conference on Reimagi
International Conference on Reimagining Rainfed Agro-ecosystems: Challenges &<br />
Opportunities during 22-24, December 2022 at ICAR-CRIDA, Hyderabad<br />
Martínez M.L., Intralawan A., Vázquez G., Pérez-Maqueo O., Sutton P., Landgrave R. 2007. The<br />
coasts <strong>of</strong> our world: Ecological, economic and social importance. Ecol. Econ. 63(2-3): 254-<br />
272. https://doi.org/10.1016/j.ecolecon.2006.10.022.<br />
T4-04R-1217<br />
Impact <strong>of</strong> Long- Term Fertilization and Manuring on Aggregate Stability<br />
and Biochemical Characterization <strong>of</strong> Aggregate Associated C in the Alfisols<br />
Suvana Sukumaran 1* , T. J. Purakayastha 2 , Bidisha Chakrabarti 2 ,<br />
K. K. Bandyopadhyay 2 , ThulasiViswanathe 3 , K. K. Rout 4 , K. Sammi Reddy 1 and<br />
A.K. Indoria 1<br />
1 ICAR-Central Research Institute for Dryland Agriculture, Hyderabad, India,<br />
2 ICAR- Indian Agricultural research Institute, New Delhi,<br />
3 Regional Agricultural Research Station, Pattambi, Kerala,<br />
4 Orissa University <strong>of</strong> Agriculture and Technology, Bhubaneswar, Odisha<br />
* suvana.sukumaran@icar.gov.in<br />
Different land use and land cover management practices affect soil aggregation, which inturn<br />
affect soil C retention. The SOC in the pr<strong>of</strong>ile can be stabilised by three mechanisms mainly-<br />
physical protection by organo-mineral complexes, biochemical stability to decomposition and<br />
chemical protection by adsorption to clay surfaces. The decomposition rate <strong>of</strong> C is directly<br />
proportional to the size <strong>of</strong> aggregates. Chemical association <strong>of</strong> SOC with silt and clay<br />
particles can also impose a limit to the soil’s C stabilization potential due to a limit in the<br />
surface area <strong>of</strong> the silt-plus-clay fraction in a given soil. Biochemical stabilization <strong>of</strong> SOM in<br />
the soil matrix is a strong function <strong>of</strong> the inherent chemical and structural stability <strong>of</strong> the<br />
organic biomolecules. Soil aggregate dynamics and SOM decomposition are closely linked.<br />
The present study was undertaken to study the effect <strong>of</strong> long-term manuring and fertilization<br />
on the physical and biochemical stability <strong>of</strong> aggregates and the associated carbon in the ricerice<br />
cropping system <strong>of</strong> the Alfisols <strong>of</strong> Bhubaneswar (BHNS) and Pattambi (PTMB).<br />
Methodology<br />
This study was carried out in two long term fertilizer experiments continuing in Bhubaneswar<br />
(Orissa) and Pattambi (Kerala), where rice- rice was the main cropping system. The<br />
experimental site at Bhubaneswar has tropical and sub-humid climate, whereas that at<br />
Pattambi has perhumid. The soils at Bhubaneswar were acidic sandy loam and at Pattambi<br />
were acidic sandy clay loam. The following treatments were considered for the study:T1-<br />
control, T2- 50 % NPK, T3- 100%NPK, T4- 150 % NPK, T5- 100%NPK+ FYM ( 10 t ha -1 ),<br />
T6- 100%NPK + Lime. The soil samples were collected from 0-15 and 15-30 cm depth. The<br />
aggregate size distribution was done using wet sieving method. The total carbon content in<br />
the sample was determined by dry combustion in CHNS analyser (Eurovector, model Euro<br />
Sustainable soil management for resilient rainfed agro-ecosystem: conservation agriculture, organic farming,<br />
INM, soil-microorganisms-plant interactions<br />
443 | Page