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Article: Nitrogen flow patterns in the food system among cities within urban agglomeration: A case study of the Pearl River Delta region

TitleNitrogen flow patterns in the food system among cities within urban agglomeration: A case study of the Pearl River Delta region
Authors
KeywordsFood system
Nitrogen
Resource recovery
Scenario analysis
Substance flow analysis
Urban agglomeration
Issue Date2020
Citation
Science of the Total Environment, 2020, v. 703, article no. 135506 How to Cite?
AbstractHuman activities along the entire food supply-consumption-waste treatment-recycling chain have an essential influence on Nitrogen (N) metabolic features, especially for densely-populated urban agglomeration. A few studies carried out research on detailed analysis and comparison of N flow patterns along the entire food chain among cities, to recognize these influences and accordingly explore effective measures for improving N use efficiencies. In this study, we developed an integrated N flow analysis model to quantify N flows in the food system illustrated by production, processing, consumption, and waste management sectors. Influence of anthropogenic activities on N flow patterns is recognized through comparison among cities and predictions of future scenarios. Using the Pearl River Delta (PRD) region as a case study, we find that (1) in 2016, the annual N import into the production sector in the food system in the PRD region was about 714.5 Gg, among which only 241.6 Gg entered food products. The removal rate of N pollution in all waste stream was about 62.3%, and only 9% of N became resources through reclamation. (2) Among the nine cities in the PRD region, the average amounts of N pollution emission to the air, water, and soil all range from 0.57–5.38 kg cap 1 yr 1, showing significant discrepancy among cities. Cities with relatively lower economic development undertake substantial N pollution embedded in their exported agricultural products. (3) Recycling of agricultural waste is the prior N management measure for Zhaoqing, Jiangmen, and Huizhou, while highly urbanized cities should mainly concentrate on recycling of food waste and sewage sludge. We further put forward suggestions such as cross-city resource recycling to realize better N resource recycling and pollution reduction on the whole urban agglomeration scale. This study provides an in-depth example of depicting N flow patterns and identifying proper N management measures for urban agglomerations.
Persistent Identifierhttp://hdl.handle.net/10722/358036
ISSN
2023 Impact Factor: 8.2
2023 SCImago Journal Rankings: 1.998
ISI Accession Number ID

 

DC FieldValueLanguage
dc.contributor.authorChen, Chen-
dc.contributor.authorWen, Zongguo-
dc.contributor.authorWang, Yihan-
dc.date.accessioned2025-07-23T03:00:44Z-
dc.date.available2025-07-23T03:00:44Z-
dc.date.issued2020-
dc.identifier.citationScience of the Total Environment, 2020, v. 703, article no. 135506-
dc.identifier.issn0048-9697-
dc.identifier.urihttp://hdl.handle.net/10722/358036-
dc.description.abstractHuman activities along the entire food supply-consumption-waste treatment-recycling chain have an essential influence on Nitrogen (N) metabolic features, especially for densely-populated urban agglomeration. A few studies carried out research on detailed analysis and comparison of N flow patterns along the entire food chain among cities, to recognize these influences and accordingly explore effective measures for improving N use efficiencies. In this study, we developed an integrated N flow analysis model to quantify N flows in the food system illustrated by production, processing, consumption, and waste management sectors. Influence of anthropogenic activities on N flow patterns is recognized through comparison among cities and predictions of future scenarios. Using the Pearl River Delta (PRD) region as a case study, we find that (1) in 2016, the annual N import into the production sector in the food system in the PRD region was about 714.5 Gg, among which only 241.6 Gg entered food products. The removal rate of N pollution in all waste stream was about 62.3%, and only 9% of N became resources through reclamation. (2) Among the nine cities in the PRD region, the average amounts of N pollution emission to the air, water, and soil all range from 0.57–5.38 kg cap<sup>−</sup> <sup>1</sup> yr<sup>−</sup> <sup>1</sup>, showing significant discrepancy among cities. Cities with relatively lower economic development undertake substantial N pollution embedded in their exported agricultural products. (3) Recycling of agricultural waste is the prior N management measure for Zhaoqing, Jiangmen, and Huizhou, while highly urbanized cities should mainly concentrate on recycling of food waste and sewage sludge. We further put forward suggestions such as cross-city resource recycling to realize better N resource recycling and pollution reduction on the whole urban agglomeration scale. This study provides an in-depth example of depicting N flow patterns and identifying proper N management measures for urban agglomerations.-
dc.languageeng-
dc.relation.ispartofScience of the Total Environment-
dc.subjectFood system-
dc.subjectNitrogen-
dc.subjectResource recovery-
dc.subjectScenario analysis-
dc.subjectSubstance flow analysis-
dc.subjectUrban agglomeration-
dc.titleNitrogen flow patterns in the food system among cities within urban agglomeration: A case study of the Pearl River Delta region-
dc.typeArticle-
dc.description.naturelink_to_subscribed_fulltext-
dc.identifier.doi10.1016/j.scitotenv.2019.135506-
dc.identifier.pmid31759702-
dc.identifier.scopuseid_2-s2.0-85075853119-
dc.identifier.volume703-
dc.identifier.spagearticle no. 135506-
dc.identifier.epagearticle no. 135506-
dc.identifier.eissn1879-1026-
dc.identifier.isiWOS:000505924300120-

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