Response of Rice Cultivars to Elevated Air Temperature and Soil Amendments: Implications towards Climate Change Adaptations and Mitigating Global Warming Potentials
Global mean surface air temperature is expected to increase 1.1?C - 6.4?C by the end of 21st century which may affect rice productivity and methane emissions in the future climate. This experiment was conducted to investigate the response of rice cultivars to elevated air temperature (+1.5?C higher than ambient) and soil amendments in regards to rice yield, yield scaled methane emissions and global warming potentials. The experimental findings revealed that replacement of inorganic fertilizers (20% - 40% of recommended NPKS) with Vermicompost, Azolla biofertilizer, enriched sugarcane pressmud, rice husk biochar and silicate fertilization increased rice yield 13.0% - 23.0%, and 11.0% - 19.0% during wet aman and dry boro season, respectively. However, seasonal cumulative CH4 fluxes were decreased by 9.0% - 25.0% and 5.0% - 19.0% during rainfed wet aman and irrigated dry boro rice cultivation, respectively with selected soil amendments. The maximum reduction in seasonal cumulative CH4 flux (19.0% - 25.0%) was recorded with silicate fertilization and azolla biofertilizer amendments (9.0% - 13.0%), whereas maximum grain yield increment 10.0 % - 14.0% was found with Vermicompost and Sugarcane pressmud amendments compared to chemical fertilization (100% NPKS) treated soils at ambient air temperature. However, rice grain yield decreased drastically 43.0% - 50.0% at elevated air temperature (3?C higher than ambient air temperature), eventhough accelerated the total cumulative CH4 flux as well as GWPs in all treatments. Maximum seasonal mean GWPs were calculated at 391.0 kg CO2 eq·ha?1 in rice husk biochar followed by sugarcane pressmud (mean GWP 387.0 kg CO2 eq·ha?1), while least GWPs were calculated at 285 - 305 kg CO2 eq·ha?1 with silicate fertilizer and Azolla biofertilizer amendments. Rice cultivar BRRI dhan 87 revealed comparatively higher seasonal cumulative CH4 fluxes, yield scaled CH4 flux and GWPs than BRRI dhan 71 during wet aman rice growing season; while BRRI dhan 89 showed higher cumulative CH4 flux and GWPs than BINA dhan 10 during irrigated boro rice cultivation. Conclusively, inorganic fertilizers may be partially (20% - 40% of the recommended NPKS) replaced with Vermicompost, azolla biofertilizer, silicate fertilizer and enriched sugarcane pressmud compost for sustainable rice production and decreasing GWPs under elevated air temperature condition.
References
[1]
Adhya, T. K., Rath, A. K., Gupta, P. K., Rao, V. R., Das, S. N., Parida, K. M. et al. (1994). Methane Emission from Flooded Rice Fields under Irrigated Conditions. Biology and Fertility of Soils, 18, 245-248. https://doi.org/10.1007/bf00647675
[2]
Akter, S., Rahman, M. Z., Rahman, M. M., Nasreen, S. S., Chowdhury, Z. J., & Ali, M. A. (2017). Effect of Different Levels of Silicon on Yield and Yield Attributes of Rice. International Journal of Natural Sciences, 6, 120-122.
[3]
Ali, M. A., Kim, P. J., & Inubushi, K. (2015). Mitigating Yield-Scaled Greenhouse Gas Emissions through Combined Application of Soil Amendments: A Comparative Study between Temperate and Subtropical Rice Paddy Soils. Science of the Total Environment, 529, 140-148. https://doi.org/10.1016/j.scitotenv.2015.04.090
[4]
Ali, M. A., Oh, J. H., & Kim, P. J. (2008). Evaluation of Silicate Iron Slag Amendment on Reducing Methane Emission from Flood Water Rice Farming. Agriculture, Ecosystems & Environment, 128, 21-26. https://doi.org/10.1016/j.agee.2008.04.014
[5]
Ali, M. A., Sattar, M. A., Islam, M. N., & Inubushi, K. (2014). Integrated Effects of Organic, Inorganic and Biological Amendments on Methane Emission, Soil Quality and Rice Productivity in Irrigated Paddy Ecosystem of Bangladesh: Field Study of Two Consecutive Rice Growing Seasons. Plant and Soil, 378, 239-252. https://doi.org/10.1007/s11104-014-2023-y
[6]
Ali, M., Farouque, M., Haque, M., & Ul Kabir, A. (2012). Influence of Soil Amendments on Mitigating Methane Emissions and Sustaining Rice Productivity in Paddy Soil Ecosystems of Bangladesh. Journal of Environmental Science and Natural Resources, 5, 179-185. https://doi.org/10.3329/jesnr.v5i1.11574
[7]
Allison, L. E. (1965). Organic Carbon. In C. A. Black, D. D. Evans, J. L. White, L. E. Ensminger, & F. E. Clark (Eds.), Methods of Soil Analysis, Part 2 (pp. 1367-1376). American Society of Agronomy.
[8]
Aulakh, M. S., Bodenbender, J., Wassmann, R., & Rennenberg, H. (2000). Methane Transport Capacity of Rice Plants: Influence of Methane Concentration and Growth Stage Analyzed with an Automated Measuring System. Nutrient Cycling in Agroecosystems, 58, 357-366. https://doi.org/10.1023/a:1009831712602
[9]
Bharati, K., Mohanty, S. R., Singh, D. P., Rao, V. R., & Adhya, T. K. (2000). Influence of Incorporation or Dual Cropping of Azolla on Methane Emission from a Flooded Alluvial Soil Planted to Rice in Eastern India. Agriculture, Ecosystems & Environment, 79, 73-83. https://doi.org/10.1016/s0167-8809(99)00148-6
[10]
Borrell, A., Garside, A., & Fukai, S. (1997). Improving Efficiency of Water Use for Irrigated Rice in a Semi-Arid Tropical Environment. Field Crops Research, 52, 231-248. https://doi.org/10.1016/s0378-4290(97)00033-6
[11]
Chaturvedi, A. K., Bahuguna, R. N., Shah, D., Pal, M., & Jagadish, S. V. K. (2017). High Temperature Stress during Flowering and Grain Filling Offsets Beneficial Impact of Elevated CO2 on Assimilate Partitioning and Sink-Strength in Rice. Scientific Reports, 7, Article No. 8227. https://doi.org/10.1038/s41598-017-07464-6
[12]
Chen, J., Xuan, J., Du, C., & Xie, J. (1997). Effect of Potassium Nutrition of Rice on Rhizosphere Redox Status. Plant and Soil, 188, 131-137. https://doi.org/10.1023/a:1004264411323
[13]
Conrad, R. (2002). Control of Microbial Methane Production in Wetland Rice Fields. Nutrient Cycling in Agroecosystems, 64, 59-69. https://doi.org/10.1023/a:1021178713988
[14]
FAO (2023). World Food and Agriculture, Statistical Yearbook 2023. https://doi.org/10.4060/cc8166en
[15]
Gogoi, N., Baruah, K. K., Gogoi, B., & Gupta, P. K. (2005). Methane Emission Characteristics and Its Relations with Plant and Soil Parameters under Irrigated Rice Ecosystem of Northeast India. Chemosphere, 59, 1677-1684. https://doi.org/10.1016/j.chemosphere.2004.11.047
[16]
Inubushi, K., Hori, K., Matsumoto, S., & Wada, H. (1997). Anaerobic Decomposition of Organic Carbon in Paddy Soil in Relation to Methane Emission to the Atmosphere. Water Science and Technology, 36, 523-530. https://doi.org/10.2166/wst.1997.0632
[17]
IPCC (2007). The Physical Science Basis. Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. Working Paper No.57. Cambridge University Press.
[18]
IPCC (2014). Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC.
[19]
Jackel, U., & Schnell, S. (2000). Suppression of Methane Emission from Rice Paddies by Ferric Iron Fertilization. Soil Biology and Biochemistry, 32, 1811-1814. https://doi.org/10.1016/s0038-0717(00)00094-8
[20]
Jagadeesh Babu, Y., Nayak, D. R., & Adhya, T. K. (2006). Potassium Application Reduces Methane Emission from a Flooded Field Planted to Rice. Biology and Fertility of Soils, 42, 532-541. https://doi.org/10.1007/s00374-005-0048-3
[21]
Jugsujinda, A., & Patrick, W. H. (1996). Methane and Water Soluble Iron Production under Controlled Soil Ph and Redox Conditions. Communications in Soil Science and Plant Analysis, 27, 2221-2227. https://doi.org/10.1080/00103629609369699
[22]
Keeney, D. R., & Nelson, D. W. (1982) Nitrogen—Inorganic Forms. In A. L. Page, R. H. Miller, & D. R. Keeney, (Eds.), Methods of Soil Analysis: Part 2 Chemical and Microbiological Properties (pp. 643-698). American Society of Agronomy, Madison. https://doi.org/10.2134/agronmonogr9.2.2ed.c33
[23]
Khosa, M. K., Sidhu, B. S., & Benbi, D. K. (2010). Effect of Organic Materials and Rice Cultivars on Methane Emission from Rice Field. Journal of Environmental Biology, 31, 281-285.
[24]
Kim, S. Y., Pramanik, P., Bodelier, P. L. E., & Kim, P. J. (2014). Cattle Manure Enhances Methanogens Diversity and Methane Emissions Compared to Swine Manure under Rice Paddy. PLOS ONE, 9, e113593. https://doi.org/10.1371/journal.pone.0113593
[25]
Kollah, B., Patra, A. K., & Mohanty, S. R. (2016). Aquatic Microphylla Azolla: A Perspective Paradigm for Sustainable Agriculture, Environment and Global Climate Change. Environmental Science and Pollution Research, 23, 4358-4369. https://doi.org/10.1007/s11356-015-5857-9
[26]
Kumar, S., Meena, R. S., Jinger, D., Jatav, H. S., & Banjara, T. (2017). Use of Press Mud Compost for Improving Crop Productivity and Soil Health. International Journal of Chemical Studies, 5, 384-389.
[27]
Lee, K., Nguyen, D., Choi, D., Ban, H., & Lee, B. (2015). Effects of Elevated Air Temperature on Yield and Yield Components of Rice. Korean Journal of Agricultural and Forest Meteorology, 17, 156-164. https://doi.org/10.5532/kjafm.2015.17.2.156
[28]
Lehmann, J., & Rondon, M. (2006). Bio-Char Soil Management on Highly Weathered Soils in the Humid Tropics. In N. T. Uphoff (Ed.), Biological Approaches to Sustainable Soil Systems (pp. 517-529). CRC Press. https://doi.org/10.1201/9781420017113.ch36
[29]
Liang, C., Zhu, X., Fu, S., Méndez, A., Gascó, G., & Paz-Ferreiro, J. (2014). Biochar Alters the Resistance and Resilience to Drought in a Tropical Soil. Environmental Research Letters, 9, Article ID: 064013. https://doi.org/10.1088/1748-9326/9/6/064013
[30]
Liu, J., Shen, J., Li, Y., Su, Y., Ge, T., Jones, D. L. et al. (2014). Effects of Biochar Amendment on the Net Greenhouse Gas Emission and Greenhouse Gas Intensity in a Chinese Double Rice Cropping System. European Journal of Soil Biology, 65, 30-39. https://doi.org/10.1016/j.ejsobi.2014.09.001
[31]
Loeppert, R. H., & Inskeep, W. P. (1996). Iron. In D. L. Sparks, A. L. Page, R. H. Loeppert, C. T. Johnston, M. E. Sumner, & J. M. Bigham, (Eds.), Methods of Soil Analysis: Part 3 Chemical Methods (pp. 639-664). Soil Science Society of America and American Society of Agronomy, Madison. https://doi.org/10.2136/sssabookser5.3.c23
[32]
Maniruzzaman, M., Biswas, J. C., Hossain, M. B., Haque, M. M., Naher, U. A., Choudhury, A. K. et al. (2018). Effect of Elevated Air Temperature and Carbon Dioxide Levels on Dry Season Irrigated Rice Productivity in Bangladesh. American Journal of Plant Sciences, 9, 1557-1576. https://doi.org/10.4236/ajps.2018.97114
[33]
Mon, W. W., Toma, Y., & Ueno, H. (2024). Combined Effects of Rice Husk Biochar and Organic Manures on Soil Chemical Properties and Greenhouse Gas Emissions from Two Different Paddy Soils. Soil Systems, 8, Article 32. https://doi.org/10.3390/soilsystems8010032
[34]
Mosier, A. R., Halvorson, A. D., Reule, C. A., & Liu, X. J. (2006). Net Global Warming Potential and Greenhouse Gas Intensity in Irrigated Cropping Systems in Northeastern Colorado. Journal of Environmental Quality, 35, 1584-1598. https://doi.org/10.2134/jeq2005.0232
[35]
Neue, H. U. (1993). Methane Emission from Rice Fields. Bioscience, 43, 466-474. https://doi.org/10.2307/1311906
[36]
Nisbet, E. G., Dlugokencky, E. J., Manning, M. R., et al. (2016). Rising Atmospheric Methane: 2007-2014 Growth and Isotopic Shift. Global Biogeochemical Cycles, 30, 1356-1370. https://doi.org/10.1002/2016GB005406
[37]
Prasanna, R., Kumar, V., Kumar, S., et al. (2002). Methane Production in Rice Soil Is Inhibited by Cyanobacteria. Microbiological Research, 157, 1-6. https://doi.org/10.1078/0944-5013-00124
[38]
Rolston, D. E. (1986). Gas Flux. In A. Klute (Ed.), Methods of Soil Analysis, Part 1: Physical and Mineralogical Methods, 2nd Edition (pp. 1103-1119). Wiley.
[39]
Singh, S., Singh, J. S., & Kashyap, A. K. (1999). Methane Flux from Irrigated Rice Fields in Relation to Crop Growth and N-Fertilization. Soil Biology and Biochemistry, 31, 1219-1228. https://doi.org/10.1016/S0038-0717(99)00027-9
[40]
van der Gon, H. A. C. D., & Neue, H. U. (1995). Influence of Organic Matter Incorporation on the Methane Emission from a Wetland Rice Field. Global Biogeochemical Cycles, 9, 11-22. https://doi.org/10.1029/94gb03197
[41]
Wassmann, R., & Aulakh, M. S. (2000). The Role of Rice Plants in Regulating Mechanisms of Methane Missions. Biology and Fertility of Soils, 31, 20-29. https://doi.org/10.1007/s003740050619
[42]
Zhang, A., Cui, L., Pan, G., Li, L., Hussain, Q., Zhang, X. et al. (2010). Effect of Biochar Amendment on Yield and Methane and Nitrous Oxide Emissions from a Rice Paddy from Tai Lake Plain, China. Agriculture, Ecosystems & Environment, 139, 469-475. https://doi.org/10.1016/j.agee.2010.09.003
[43]
Zheng, X. H., Zou, J. W., Huang, Y., & Wang, Y. S. (2007). Quantifying Direct N2O Emissions in Paddy Fields during Rice Growing Season in Mainland China: Dependence on Water Regime. Atmospheric Environment, 41, 8030-8042. https://doi.org/10.1016/j.atmosenv.2007.06.049