Journals / Atmospheric Pollution Research / 2020 / Cilt: 11 - Sayı: 11

Projected background nitrous oxide emissions from cultivable maize and rice farmland in China

Pages
1982–1990
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

The results indicated that thespatio-temporal variation of BNE was dominated by temperature and the interaction effect of temperature andprecipitation may also play an important role.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Climate change is expected to have a major impact on agriculture in China.
📊
Key Findings & Data:Therefore, using projections of future climate derived from a multi-modelensemble under three representative concentration pathway scenarios (RCP2.6, RCP4.5, and RCP8.5), a gridbased spatial analysis was conducted to investigate the agricultural BNE by empirical statistical models andsimulated suitable cultivation areas of rice and maize in China for 2006–2100.
💡
Conclusion & Impact:The results indicated that thespatio-temporal variation of BNE was dominated by temperature and the interaction effect of temperature andprecipitation may also play an important role.
🔬Design:Modeling & Simulation
📍Scope:2006 Verileri
⚙️Variables:Domain Parameters

Özet

Climate change is expected to have a major impact on agriculture in China. It affects agricultural backgroundnitrous oxide emissions (BNE) through warming or cooling and precipitation changes, but the related mechanisms remain poorly understood. Therefore, using projections of future climate derived from a multi-modelensemble under three representative concentration pathway scenarios (RCP2.6, RCP4.5, and RCP8.5), a gridbased spatial analysis was conducted to investigate the agricultural BNE by empirical statistical models andsimulated suitable cultivation areas of rice and maize in China for 2006–2100. The results indicated that thespatio-temporal variation of BNE was dominated by temperature and the interaction effect of temperature andprecipitation may also play an important role. Under the high-emission scenario (RCP8.5), the greater warmingcaused the potential BNE area of maize and rice to slightly migrate northward and the high-emission area wasconcentrated in southeastern China. The total BNE showed an increasing trend over time, from 120.59 ± 0.69to 142.42 ± 0.78 Gg N a−1during the 21st century, driven by the synthetic action of these climatic factors. Thefindings of this study may provide reference for predicting future agricultural BNE and formulating appropriatemeasures to mitigate global warming.

🔖

Cite This Article

ZHANG, Y., NIU, H. (2020). Projected background nitrous oxide emissions from cultivable maize and rice farmland in China. Atmospheric Pollution Research, Cilt: 11 - Sayı: 11, 1982–1990. https://ajindex.com/articles/351316

References (10)

  1. Aliyu, G., Sanz-Cobena, A., Müller, C., Zaman, M., Luo, J., Liu, D., Yuan, J., Chen, Z., Niu, Y., Arowolo, A., Ding, W., 2018. A meta-analysis of soil background N2O emissions from croplands in China shows variation among climatic zones. Agric. Ecosyst. Environ. 267, 63–73.
  2. Allen, R.G., Pereira, L.S., Raes, D., Smith, M., 1998. Crop Evapotranspiration-Guidelines for Computing Crop Water Requirements. FAO Irrigation and Drainage Paper 56, Rome. Bouwman, A., Boumans, L., Batjes, N., 2002. Emissions of N2O and NO from fertilized fields: summary of available measurement data. Global Biogeochem. Cycles 16, 1058. https://doi.org/10.1029/2001GB001811.
  3. Bouwman, A., Taylor, J., 1996. Testing high-resolution nitrous oxide emission estimates against observations using an atmospheric transport model. Global Biogeochem. Cycles 10, 307–318.
  4. Butterbach-Bahl, K., Baggs, E.M., Dannenmann, M., Kiese, R., Zechmeister-Boltenstern, S., 2013. Nitrous oxide emissions from soils: how well do we understand the processes and their controls? Philosophical Transactions of the Royal Society B 368, 20130122. https://doi.org/10.1098/rstb.2013.0122.
  5. Chen, X.J., Cao, G.C., Jia, Y.S., Wu, D.B., Chen, J., Yu, Y.X., Li, W., Li, J., 2009. Influence of elevation on growth duration of maize (Zea mays L.). Chin. J. Eco-Agric. 17, 527–532.
  6. Deryng, D., Elliott, J., Folberth, C., Müller, C., Pugh, T., Boote, K., Conway, D., Ruane, A., Gerten, D., Jones, J., Khabarov, N., Olin, S., Schaphoff, S., Schmid, E., Yang, H., Rosenzweig, C., 2016. Regional disparities in the beneficial effects of rising CO2 concentrations on crop water productivity. Nat. Clim. Change 6, 786–790.
  7. Duan, J.Q., Zhou, G.S., 2011. Potential distribution of rice in China and its climate characteristics. Acta Ecol. Sin. 31, 6659–6668.
  8. Duan, J.Q., Zhou, G.S., 2012a. Climatic suitability of single cropping rice planting region in China. Chin. J. Appl. Ecol. 23, 426–432.
  9. Duan, J.Q., Zhou, G.S., 2012b. Climatic suitability of double rice planting regions in China. Sci. Agric. Sin. 45, 218–227. FAO, 2014. FAOSTAT: Asia and Pacific agriculture. Rome, Italy: food and agriculture organization of the united nations. Available online at: http://faostat.fao.org.
  10. Gerber, J., Carlson, K., Makowski, D., Mueller, N., de Cortazar-Atauri, I., Havlík, P., Herrero, M., Launay, M., O'Connell, C., Smith, P., West, P., 2016. Spatially explicit estimates of N2O emissions from croplands suggest climate mitigation opportunities from improved fertilizer man