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dc.contributor.author | Dlamini, Jerry Celumusa![]() |
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dc.contributor.author | Cardenas, L. M.![]() |
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dc.contributor.author | Tesfamariam, Eyob Habte![]() |
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dc.contributor.author | Dunn, R. M.![]() |
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dc.contributor.author | Evans, J.![]() |
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dc.contributor.author | Hawkins, J. M. B.![]() |
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dc.contributor.author | Blackwell, M. S. A.![]() |
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dc.contributor.author | Collins, A. L.![]() |
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dc.date.accessioned | 2022-11-02T11:04:19Z | |
dc.date.available | 2022-11-02T11:04:19Z | |
dc.date.issued | 2022-04-11 | |
dc.description.abstract | Purpose Nitrous oxide (N2O) and methane (CH4) are some of the most important greenhouse gases in the atmosphere of the 21st century. Vegetated riparian bufers are primarily implemented for their water quality functions in agroecosystems. Their location in agricultural landscapes allows them to intercept and process pollutants from adjacent agricultural land. They recycle organic matter, which increases soil carbon (C), intercept nitrogen (N)-rich runof from adjacent croplands, and are seasonally anoxic. Thus processes producing environmentally harmful gases including N2O and CH4 are promoted. Against this context, the study quantifed atmospheric losses between a cropland and vegetated riparian bufers that serve it. Methods Environmental variables and simultaneous N2O and CH4 emissions were measured for a 6-month period in a replicated plot-scale facility comprising maize (Zea mays L.). A static chamber was used to measure gas emissions. The cropping was served by three vegetated riparian bufers, namely: (i) grass riparian bufer; (ii) willow riparian bufer and; (iii) woodland riparian bufer, which were compared with a no-bufer control. Results The no-bufer control generated the largest cumulative N2O emissions of 18.9 kg ha−1 (95% confdence interval: 0.5–63.6) whilst the maize crop upslope generated the largest cumulative CH4 emissions (5.1±0.88 kg ha−1 ). Soil N2O and CH4-based global warming potential (GWP) were lower in the willow (1223.5±362.0 and 134.7±74.0 kg CO2-eq. ha−1 year−1 , respectively) and woodland (1771.3±800.5 and 3.4±35.9 kg CO2-eq. ha−1 year−1 , respectively) riparian bufers. Conclusions Our results suggest that in maize production and where no riparian bufer vegetation is introduced for water quality purposes (no bufer control), atmospheric CH4 and N2O concerns may result. | en_US |
dc.description.department | Plant Production and Soil Science | en_US |
dc.description.librarian | dm2022 | en_US |
dc.description.sponsorship | The Department of Higher Education and Training (New Generation Gap of Academics Program) and National Research Foundation-Thuthuka. | en_US |
dc.description.uri | https://www.springer.com/journal/11104 | en_US |
dc.identifier.citation | Dlamini, J.C., Cardenas, L.M., Tesfamariam, E.H. et al. Soil N2O and CH4 emissions from fodder maize production with and without riparian buffer strips of differing vegetation. Plant Soil 477, 297–318 (2022). https://doi.org/10.1007/s11104-022-05426-0. | en_US |
dc.identifier.issn | 1573-5036 (online) | |
dc.identifier.issn | 0032-079X (print) | |
dc.identifier.other | 10.1007/s11104-022-05426-0 | |
dc.identifier.uri | https://repository.up.ac.za/handle/2263/88104 | |
dc.language.iso | en | en_US |
dc.publisher | Springer | en_US |
dc.rights | © The Author(s) 2022. Open Access. This article is licensed under a Creative Commons Attribution 4.0 International License. | en_US |
dc.subject | Nitrous oxide | en_US |
dc.subject | Methane | en_US |
dc.subject | Maize | en_US |
dc.subject | Vegetated riparian buffer strips | en_US |
dc.title | Soil N2O and CH4 emissions from fodder maize production with and without riparian buffer strips of differing vegetation | en_US |
dc.type | Article | en_US |