Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater

doi:10.1016/S1671-2927(00)8666

Journal of Integrative Agriculture ›› 2012, Vol. 12 ›› Issue (8): 1354-1364.DOI: 10.1016/S1671-2927(00)8666

Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater

XUE Yan-dong, YANG Pei-ling, LUO Yuan-pei, LI Yun-kai, REN Shu-mei, SU Yan-ping, NIU Yongtao

1.College of Water Resources and Civil Engineering, China Agricultural University, Beijing 100083, P.R.China
2.Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences, Beijing 100081, P.R.China

收稿日期:2011-06-10 出版日期:2012-08-01 发布日期:2012-09-09
通讯作者: Correspondence YANG Pei-ling, Tel/Fax: +86-10-62737866, E-mail: yangpeiling@126.com
基金资助:
The study was funded by the National Natural Science Foundation of China (50979107).

Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater

XUE Yan-dong, YANG Pei-ling, LUO Yuan-pei, LI Yun-kai, REN Shu-mei, SU Yan-ping, NIU Yongtao

1.College of Water Resources and Civil Engineering, China Agricultural University, Beijing 100083, P.R.China
2.Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences, Beijing 100081, P.R.China

Received:2011-06-10 Online:2012-08-01 Published:2012-09-09
Contact: Correspondence YANG Pei-ling, Tel/Fax: +86-10-62737866, E-mail: yangpeiling@126.com
Supported by:
The study was funded by the National Natural Science Foundation of China (50979107).

摘要/Abstract

摘要： The reuse of treated wastewater in agricultural systems could partially help alleviate water resource shortages in developing countries. Treated wastewater differs from fresh water in that it has higher concentrations of salts, Escherichia coli and presence of dissolved organic matter, and inorganic N after secondary treatment, among others. Its application could thus cause environmental consequences such as soil salinization, ammonia volatilization, and greenhouse gas emissions. In an incubation experiment, we evaluated the characteristics and effects of water-filled pore space (WFPS) and N input on the emissions of nitrous oxide (N2O) and carbon dioxide (CO2) from silt loam soil receiving treated wastewater. Irrigation with treated wastewater (vs. distilled water) significantly increased cumulative N2O emission in soil (117.97 μg N kg-1). Cumulative N2O emissions showed an exponentially increase with the increasing WFPS in unamended soil, but the maximum occurred in the added urea soil incubated at 60% WFPS. N2O emissions caused by irrigation with treated wastewater combined with urea-N fertilization did not simply add linearly, but significant interaction (P<0.05) caused lower emissions than the production of N2O from the cumulative effects of treated wastewater and fertilizer N. Moreover, a significant impact on cumulative CO2 emission was measured in soil irrigated with treated wastewater. When treated wastewater was applied, there was significant interaction between WFPS and N input on N2O emission. Hence, our results indicated that irrigation with treated wastewater should cause great concern for increasing global warming potential due to enhanced emission of N2O and CO2.

关键词: treated wastewater, nitrous oxide, carbon dioxide, water-filled pore space, urea

Abstract: The reuse of treated wastewater in agricultural systems could partially help alleviate water resource shortages in developing countries. Treated wastewater differs from fresh water in that it has higher concentrations of salts, Escherichia coli and presence of dissolved organic matter, and inorganic N after secondary treatment, among others. Its application could thus cause environmental consequences such as soil salinization, ammonia volatilization, and greenhouse gas emissions. In an incubation experiment, we evaluated the characteristics and effects of water-filled pore space (WFPS) and N input on the emissions of nitrous oxide (N2O) and carbon dioxide (CO2) from silt loam soil receiving treated wastewater. Irrigation with treated wastewater (vs. distilled water) significantly increased cumulative N2O emission in soil (117.97 μg N kg-1). Cumulative N2O emissions showed an exponentially increase with the increasing WFPS in unamended soil, but the maximum occurred in the added urea soil incubated at 60% WFPS. N2O emissions caused by irrigation with treated wastewater combined with urea-N fertilization did not simply add linearly, but significant interaction (P<0.05) caused lower emissions than the production of N2O from the cumulative effects of treated wastewater and fertilizer N. Moreover, a significant impact on cumulative CO2 emission was measured in soil irrigated with treated wastewater. When treated wastewater was applied, there was significant interaction between WFPS and N input on N2O emission. Hence, our results indicated that irrigation with treated wastewater should cause great concern for increasing global warming potential due to enhanced emission of N2O and CO2.

Key words: treated wastewater, nitrous oxide, carbon dioxide, water-filled pore space, urea

XUE Yan-dong, YANG Pei-ling, LUO Yuan-pei, LI Yun-kai, REN Shu-mei, SU Yan-ping, NIU Yongtao. Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater[J]. Journal of Integrative Agriculture, 2012, 12(8): 1354-1364.

参考文献

[1]Aarnio T, Martikainen P J. 1996. Mineralization of carbon and nitrogen, and nitrification in scots pine forest soil treated with fast-and slow-release nitrogen fertilizers. Biology and Fertility of Soils, 22, 214-220.

[2]Adrover M, Farrús E, Gabriel M, Vadell J. 2010. Chemical properties and biological activity in soils of Mallorca following twenty years of treated wastewater irrigation. Journal of Environmental Management, doi:10.1016/j. jenvman.2010.08.017 Akiyama H, Tsuruta H. 2003. Nitrous oxide, nitric oxide, and nitrogen dioxide fluxes from soils after manure and urea application. Journal of Environmental Quality, 32, 423-431.

[3]© 2012, CAAS. All rights reserved. Published by Elsevier Ltd. Bateman E J, Baggs E M. 2005. Contributions of nitrification and denitrification to N2O emissions from soils at different water-filled pore space. Biology and Fertility of Soils, 41, 379-388.

[4]Bowman W D, Steltzer H. 1998. Positive feedbacks to anthropogenic nitrogen deposition in rocky mountain alpine tundra. Ambio, 27, 514-517.

[5]Brzezinska M, Tiwari S, Stepniewska Z, Nosalewicz M, Bennicelli R, Samborska A. 2006. Variation of enzyme activities, CO2 evolution and redox potential in an eutric histosol irrigated with wastewater and tap water. Biology and Fertility of Soils, 43, 131-135.

[6]Chen W, Wu L, Frankenberger W, Chang T C A. 2008. Soil enzyme activities of long-term reclaimed wastewaterirrigated soils. Journal of Environmental Quality, 37, 36-42.

[7]Ciarlo E, Conti M, Bartoloni N, Rubio G. 2007. The effect of moisture on nitrous oxide emissions from soil and the N2O/(N2O+N2) ratio under laboratory conditions. Biology and Fertility of Soils, 43, 675-681.

[8]Conen F, Dobbie K E, Smith K A. 2000. Predicting N2O emissions from agricultural land through related soil parameters. Global Change Biology, 6, 417-426.

[9]Del Prado A, Merino P, Estavillo J, Pinto M, González-Murua C. 2006. N2O and NO emissions from different N sources and under a range of soil water contents. Nutrient Cycling in Agroecosystems, 74, 229-243.

[10]Dittert K, Lampe C, Gasche R, Butterbach-Bahl K, Wachendorf M, Papen H, Sattelmacher B, Taube F. 2005. Short-term effects of single or combined application of mineral N fertilizer and cattle slurry on the fluxes of radiatively active trace gases from grassland soil. Soil Biology and Biochemistry, 37, 1665-1674.

[11]Dobbie K E, Smith K A. 2001. The effects of temperature, water-filled pore space and land use on N2O emissions from an imperfectly drained gleysol. European Journal of Soil Science, 52, 667-673.

[12]Dobbie K E, Smith K A. 2003. Nitrous oxide emission factors for agricultural soils in Great Britain: the impact of soil water-filled pore space and other controlling variables. Global Change Biology, 9, 204-218.

[13]Fernández-Luqueño F, Reyes-Varela V, Cervantes-Santiago F, Gómez-Juárez C, Santillán-Arias A, Dendooven L. 2010. Emissions of carbon dioxide, methane and nitrous oxide from soil receiving urban wastewater for maize (Zea mays L.) cultivation. Plant and Soil, 331, 203-215.

[14]Groffman P M, Tiedje J M, Robertson G P, Christensen S. 1988. Denitrification at different temporal and geographical scales: proximal and distal controls. In: Wilson J R, ed., Advances in Nitrogen Cycling in Agricultural Systems. Commonwealth Agricultural Bureau. International, Wallingford, UK. pp. 174-192.

[15]Grosso S J D, Parton W J, Mosier A R, Ojima D S, Kulmala A E, Phongpan S. 2000. General model for N2O and N2 gas emissions from soils due to dentrification. Global Biogeochemical Cycles, 14, 1045-1060.

[16]Guo X, Drury C F, Yang X, Zhang R. 2010. Influence of constant and fluctuating water contents on nitrous oxide emissions from soils under varying crop rotations. Soil Science Society of America Journal, 74, 2077-2085.

[17]Hofman G, van Cleemput O. 2004. Soil and Plant Nitrogen. International Fertilizer Industry Association (IFA), Paris. Hou A, Akiyama H, Nakajima Y, Sudo S, Tsuruta H. 2000. Effects of urea form and soil moisture on N2O and NO emissions from Japanese Andosols. Chemosphere-Global Change Science, 2, 321-327.

[18]IPCC. 2007. Climate Change 2007: The Physical Science Basis. Cambridge University, Cambridge, UK. Keller M, Reiners W A. 1994. Soil-atmosphere exchange of nitrous oxide, nitric oxide, and methane under secondary succession of pasture to forest in the Atlantic lowlands of costa rica. Global Biogeochemical Cycles, 8, 399-409.

[19]Khalil M, Rosenani A, van Cleemput O, Boeckx P, Shamshuddinc J, Fauziah C. 2002. Nitrous oxide production from an ultisol of the humid tropics treated with different nitrogen sources and moisture regimes. Biology and Fertility of Soils, 36, 59-65.

[20]Li C, Frolking S, Frolking T A. 1992a. A model of nitrous oxide evolution from soil driven by rainfall events: 1. model structure and sensitivity. Journal of Geophysical Research, 97, 9759-9776.

[21]Li C, Frolking S, Frolking T A. 1992b. A model of nitrous oxide evolution from soil driven by rainfall events: 2. model applications. Journal of Geophysical Research, 97, 9777-9783.

[22]Maljanen M, Liikanen A, Silvola J, Martikainen P J. 2003. Nitrous oxide emissions from boreal organic soil under different land-use. Soil Biology and Biochemistry, 35, 689-700.

[23]Master Y, J L R, Shavit U, Stevens R J, Shaviv A. 2003. Gaseous nitrogen emissions and mineral nitrogen transformations as affected by reclaimed effluent application. Journal of Environmental Quality, 32, 1204-1211.

[24]Master Y, Laughlin R J, Stevens R J, Shaviv A. 2004. Nitrite formation and nitrous oxide emissions as affected by reclaimed effluent application. Journal of Environmental Quality, 33, 852-860.

[25]McSwiney C P, Robertson G P. 2005. Nonlinear response of N2O flux to incremental fertilizer addition in a continuous maize (Zea mays L.) cropping system. Global Change Biology, 11, 1712-1719.

[26]Meli S, Porto M, Belligno A, Bufo S A, Mazzatura A, Scopa A. 2002. Influence of irrigation with lagooned urban wastewater on chemical and microbiological soil parameters in a citrus orchard under mediterranean condition. Science of the Total Environment, 285, 69-77.

[27]Monnett G T, Reneau R B, Hagedorn C. 1995. Effects of domestic wastewater spray irrigation on denitrification rates. Journal of Environmental Quality, 24, 940-946.

[28]Mosier A, Schimel D, Valentine D, Bronson K, Parton W. 1991. Methane and nitrous oxide fluxes in native, fertilized and cultivated grasslands. Nature, 350, 330-332.

[29]Ndour N, Baudoin E, Guissé A, Seck M, Khouma M, Brauman A. 2008. Impact of irrigation water quality on soil nitrifying and total bacterial communities. Biology and Fertility of Soils, 44, 797-803.

[30]Neeteson J J, Carton O T. 2001. The environmental impact of nitrogen in field vegetable production. Acta Horticulturae, 563, 21-28.

[31]Parton W J, Mosier A R, Ojima D S, Valentine D W, Schimel D S, Weier K, Kulmala A E. 1996. Generalized model for N2 and N2O production from nitrification and denitrification. Global Biogeochemical Cycles, 10, 401-412.

[32]Ramirez-Fuentes E, Lucho-Constantino C, Escamilla-Silva E, Dendooven L. 2002. Characteristics, and carbon and nitrogen dynamics in soil irrigated with wastewater for different lengths of time. Bioresource Technology, 85, 179-187.

[33]Ravishankara A R, Daniel J S, Portmann R W. 2009. Nitrous oxide (N2O): the dominant ozone-depleting substance emitted in the 21st century. Science, 326, 123-125.

[34]Rosso D, Stenstrom M K. 2008. The carbon-sequestration potential of municipal wastewater treatment. Chemosphere, 70, 1468-1475.

[35]Ruser R, Flessa H, Russow R, Schmidt G, Buegger F, Munch J C. 2006. Emission of N2O, N2 and CO2 from soil fertilized with nitrate: effect of compaction, soil moisture and rewetting. Soil Biology and Biochemistry, 38, 263-274.

[36]Rutkowski T, Raschid-Sally L, Buechler S. 2007. Wastewater irrigation in the developing world-two case studies from the Kathmandu Valley in Nepal. Agricultural Water Management, 88, 83-91.

[37]Silva C C, Guido M L, Ceballos J M, Marsch R, Dendooven L. 2008. Production of carbon dioxide and nitrous oxide in alkaline saline soil of texcoco at different water contents amended with urea: a laboratory study. Soil Biology and Biochemistry, 40, 1813-1822.

[38]Skiba U, Smith K A. 2000. The control of nitrous oxide emissions from agricultural and natural soils. Chemosphere Global Change Science, 2, 379-386.

[39]Smith K A, Ball T, Conen F, Dobbie K E, Massheder J, Rey A. 2003. Exchange of greenhouse gases between soil and atmosphere: interactions of soil physical factors and biological processes. European Journal of Soil Science, 54, 779-791.

[40]Stark J M, Firestone M K. 1995. Mechanisms for soil moisture effects on activity of nitrifying bacteria. Applied and Environmental Microbiology, 61, 218-221.

[41]Stevens R J, Laughlin R J, Burns L C, Arah J R M, Hood R C. 1997. Measuring the contributions of nitrification and denitrification to the flux of nitrous oxide from soil. Soil Biology and Biochemistry, 29, 139-151.

[42]Xu M, Qi Y. 2001. Soil-surface CO2 efflux and its spatial and temporal variations in a young ponderosa pine plantation in northern California. Global Change Biology, 7, 667-677.

[43]Yadav R K, Goyal B, Sharma R K, Dubey S K, Minhas P S. 2002. Post-irrigation impact of domestic sewage effluent on composition of soils, crops and ground water-a case study. Environment International, 28, 481-486.

[44]Zhang F S, Chen X P, Chen Q. 2009. China’s Major Crops Fertilization Guide. China Agricultural Univeristy Press, Beijing, China. (in Chinese)

[45]Zou J, Liu S, Qin Y, Pan G, Zhu D. 2009. Sewage irrigation increased methane and nitrous oxide emissions from rice paddies in southeast China. Agriculture Ecosystems and Environment, 129, 516-522.

Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater

Characteristics and Driven Factors of Nitrous Oxide and Carbon Dioxide Emissions in Soil Irrigated with Treated Wastewater

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