Effects of irrigation, fertilization and crop straw management on nitrous oxide and nitric oxide emissions from a wheat–maize rotation field in northern China

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Abstract

One-year winter wheat–summer maize rotation is the most popular double cropping system in north-central China, and this highly productive system is an important source of nitrous oxide (N2O) and nitric oxide (NO) emissions due to the high fertilizer N and irrigation water inputs. To sustain the high crop production and mitigate the detrimental impacts of N2O and NO emissions, improved management practices are extensively applied. The aim of this study is therefore to evaluate the effects of an improved management practice of irrigation, fertilization and crop straw on grain yield and N2O and NO emissions for a wheat–maize rotation field in northern China. Using automated and manual chamber measuring systems, we monitored N2O and NO fluxes for the conventional (CT, 2007–2008), improved (IT, 2007–2008), straw-amended (WS, 2008–2009), straw-not-amended (NS, 2008–2009), and no N-fertilizer treatments (WS–NN, 2008–2009), respectively, for one rotation-year. The grain yields were determined for CT and IT for three rotation-years (2005–2008) and for WS, NS and WS–NN for one rotation-year (2008–2009). The improved management of irrigation and fertilization reduced the annual N fertilization rate and irrigation amount by 17% and 30%, respectively; increased the maize yield by 7–14%; and significantly decreased the N2O and NO emissions by 7% (p < 0.05) and 29% (p < 0.01), respectively. The incorporation of wheat straw increased the cumulative N2O and NO emissions in the following maize season by 58% (p < 0.01) and 13%, respectively, whereas the effects of maize straw application were not remarkable. The N2O and NO emission factors of applied N were 2.32 ± 2.32% and 0.42 ± 1.69% for wheat straw and 0.67 ± 0.23% and 0.54 ± 0.15% for chemical N-fertilizers, respectively. Compared to conventional management practices using high application rates of irrigation water and chemical N-fertilizer as well as the field burning of crop straw, the improved management strategy presented here has obvious environmentally positive effects on grain yield and mitigation of N2O and NO emissions.

Research highlights

▶ We investigated the crop yield and N2O/NO fluxes for different management practice. ▶ The improved irrigation, fertilization and crop straw management increased crop yield. ▶ The improved management also reduced water and fertilizer inputs and N2O/NO emissions.

Introduction

Nitrous oxide (N2O) plays an important role in the recent global warming trend and participates in the destruction of stratospheric ozone (O3) (IPCC, 2007). In contrast, nitric oxide (NO) is a precursor of tropospheric O3, which contributes to global warming (IPCC, 2007). Fertilized agricultural fields are important sources of atmospheric N2O and NO (Bouwman et al., 2002). In most agricultural soils, both gases are formed biologically via nitrification and denitrification, and these microbial processes are strongly affected by natural conditions and agricultural management (Ludwig et al., 2001, Snyder et al., 2009).

China is one of the major agricultural countries in the world. To increase grain yield and soil fertility, many new management practices, including fertilization, irrigation, crop straw application, and double- and triple-cropping are applied in intensive cropland areas of China. The 1-year winter wheat–summer maize rotation is the most popular double-cropping system and has been adopted across a wide range of climate zones in north-central China. The highly productive double-cropping system relies on inputs of irrigation water (90–690 mm year−1, Wang et al., 2008) and chemical fertilizer (500–700 kg N ha−1 year−1, Zhen et al., 2006, Ju et al., 2009) that far exceed the optimum or recommended water and fertilizer inputs (127–350 kg N ha−1 year−1, Liu et al., 2003, Zhao et al., 2006, He et al., 2009, Wang et al., 2010). The overuse of irrigation water and chemical N-fertilizer has been ubiquitous and triggered many environmental problems, such as water pollution, drawdown of groundwater table, soil salination, soil acidification and emission of gaseous N (Zhen et al., 2006, Ju et al., 2009). To mitigate the detrimental effects, improved management practices need to be fully evaluated and popularized. Many studies have been carried out to estimate the impacts of improved irrigation and fertilization management on crop yield, nutrient use efficiency, N leaching, soil organic matter and N accumulation in deeper soil layers in the wheat–maize rotation fields of China (Liu et al., 2003, Mack et al., 2005, Xu et al., 2006, He et al., 2009, Wang et al., 2010). However, to date, no study has been carried out to clarify the role of these improved management practices in the mitigation of N2O and NO emissions. Furthermore, the application of wheat and maize straws has become popular because the Chinese government has banned the field burning of crop straws. The combined application of chemical fertilizer and crop straw is thought to be beneficial for improving soil fertility and nutrient utilization. On the other hand, it may increase or decrease soil N2O and NO emissions depending on the type, mode, timing and quantity of the chemical fertilizer application and the quantity and quality of the incorporated straws (Baggs et al., 2003, Garcia-Ruiz and Baggs, 2007). The complex interactive influences of chemical fertilizer and wheat/maize straw on soil N2O and NO emissions have not been adequately surveyed. Therefore, we investigated the N2O and NO fluxes as well as the crop yields for conventional, improved, straw-amended, straw-not-amended, and no N-fertilizer treatments in a typical irrigated wheat–maize rotation field in northern China. The objectives of this study were (a) to quantify the effects of improved irrigation and fertilization management on crop yield and N2O and NO emissions; (b) to characterize the combined effects of wheat/maize straw and chemical N-fertilizer applications on the cumulative emissions of both gases; and, (c) to calculate the emission factors of both gases for applied N in the form of crop straw and chemical N-fertilizer.

Section snippets

Experimental site

The experimental site (34°55.51′N, 110°42.59′E) is situated within the Dong Cun Farm near Yongji, Shanxi Province, northern China. The area is 348 m above sea level and has a temperate continental climate. The annual mean air temperature and precipitation were 14.8 °C and 562 mm, respectively, during 2000–2008 (National Climatic Data Center, http://www.ncdc.noaa.gov/oa/ncdc.html). The soil of the experimental field is a cinnamon soil (National Soil Survey Office, 1998) with 31.8 ± 0.9% clay (<0.002 

Crop yields

The rates of fertilizer N application were 430 and 360 kg N ha−1 year−1 for CT and IT, respectively, in the first and second rotation-years (from October 15th, 2005 to October 28th, 2007). After the high-fertilizer N inputs for 2 years, the application rates were reduced to 295 and 240 kg N ha−1, respectively, for CT and IT in the third rotation-year (between October 29th, 2007 and October 10th, 2008). The 16–19% reduction in N-fertilizer application rates did not affect the wheat yield but increased

Effects of irrigation and fertilization management

We observed the significantly high N2O and NO emission period that started after the fertilization on July 19th, 2008 and lasted for 41 days. The cumulative N2O and NO emissions during the period were 2.8 ± 0.3 and 1.5 ± 0.2 kg N ha−1 for CT, and 1.9 ± 0.2 and 0.8 ± 0.1 kg N ha−1 for IT, respectively, which accounted 40% and 62% (CT), and 29% and 47% (IT) for the annual total emissions. The higher annual N2O and NO emissions for CT were primarily attributed to the significantly higher emissions of both gases

Conclusions

We investigated the grain yields (2005–2009) and N2O/NO emissions (2007–2009) for conventional (CT), improved (IT), straw-amended (WS), straw-not-amended (NS) and no N-fertilizer treatments (WS–NN) in an irrigated wheat–maize rotation field in northern China. The average fertilization rate and irrigation amount were 17% and 30%, respectively, lower for IT than for CT during the three rotation-years between 2005 and 2008. However, the maize yields were 7–14% higher for IT due to the improved

Acknowledgements

This study was supported by the Ministry of Agriculture of the P.R. China (200803036, 2003-Z53), the Ministry of Science and Technology of the P.R. China (2008BAD95B13), the National Natural Science Foundation of China (40711130636), and the Australian Center for International Agricultural Research (LWR/2003/039). Special thanks go to Guangren Liu, Yinghong Wang, Pushan Zheng, Bingwen Hao, Tingyu Wang, Ming Li, Wangguo Liang and Rui Wang for their technical support and help during field

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