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The carbon footprint of breastmilk substitutes in comparison with breastfeeding

Breastfeeding is one of the foundations of child health, development and survival. Breastmilk substitutes (BMS) are associated with negative influences on breastfeeding practices and subsequent health concerns and, as with all foods, production and consumption of BMS comes with an environmental cost...

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Autores principales: Karlsson, Johan O., Garnett, Tara, Rollins, Nigel C., Röös, Elin
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Elsevier Science 2019
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6472111/
https://www.ncbi.nlm.nih.gov/pubmed/31190697
http://dx.doi.org/10.1016/j.jclepro.2019.03.043
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author Karlsson, Johan O.
Garnett, Tara
Rollins, Nigel C.
Röös, Elin
author_facet Karlsson, Johan O.
Garnett, Tara
Rollins, Nigel C.
Röös, Elin
author_sort Karlsson, Johan O.
collection PubMed
description Breastfeeding is one of the foundations of child health, development and survival. Breastmilk substitutes (BMS) are associated with negative influences on breastfeeding practices and subsequent health concerns and, as with all foods, production and consumption of BMS comes with an environmental cost. The carbon footprint (CFP) of production and consumption of BMS was estimated in this study. To illustrate regional differences among the largest producers and consumers, the CFP of BMS production in New Zealand, United States (USA), Brazil and France and the CFP of BMS consumption in United Kingdom (UK), China, Brazil and Vietnam were assessed. The CFP values were then compared with the CFP of breastfeeding arising from production of the additional food needed for breastfeeding mothers to maintain energy balance (approximately 500 kcal per day). The CFP of production was estimated to be 9.2 ± 1.4, 7.0 ± 1.0, 11 ± 2 and 8.4 ± 1.3 kg CO(2)e per kg BMS in New Zealand, USA, Brazil and France, respectively, with the largest contribution (68–82% of the total) coming from production of raw milk. The CFP of consumption, which included BMS production, emissions from transport, production and in-home sterilisation of bottles, and preparation of BMS, was estimated to be 11 ± 1, 14 ± 2, 14 ± 2 and 11 ± 1 kg CO(2)e per kg BMS in UK, China, Brazil and Vietnam, respectively. Comparison of breastfeeding with feeding BMS showed a lower CFP from breastfeeding in all countries studied. However, the results were sensitive to the method used to allocate emissions from raw milk production on different dairy processing co-products (i.e. BMS, cream, cheese and lactose). Using alternative allocation methods still resulted in lower CFP from breastfeeding, but only slightly for UK, Brazil and Vietnam. Care is also needed when interpreting findings about products that are functionally different as regards child health and development.
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spelling pubmed-64721112019-06-10 The carbon footprint of breastmilk substitutes in comparison with breastfeeding Karlsson, Johan O. Garnett, Tara Rollins, Nigel C. Röös, Elin J Clean Prod Article Breastfeeding is one of the foundations of child health, development and survival. Breastmilk substitutes (BMS) are associated with negative influences on breastfeeding practices and subsequent health concerns and, as with all foods, production and consumption of BMS comes with an environmental cost. The carbon footprint (CFP) of production and consumption of BMS was estimated in this study. To illustrate regional differences among the largest producers and consumers, the CFP of BMS production in New Zealand, United States (USA), Brazil and France and the CFP of BMS consumption in United Kingdom (UK), China, Brazil and Vietnam were assessed. The CFP values were then compared with the CFP of breastfeeding arising from production of the additional food needed for breastfeeding mothers to maintain energy balance (approximately 500 kcal per day). The CFP of production was estimated to be 9.2 ± 1.4, 7.0 ± 1.0, 11 ± 2 and 8.4 ± 1.3 kg CO(2)e per kg BMS in New Zealand, USA, Brazil and France, respectively, with the largest contribution (68–82% of the total) coming from production of raw milk. The CFP of consumption, which included BMS production, emissions from transport, production and in-home sterilisation of bottles, and preparation of BMS, was estimated to be 11 ± 1, 14 ± 2, 14 ± 2 and 11 ± 1 kg CO(2)e per kg BMS in UK, China, Brazil and Vietnam, respectively. Comparison of breastfeeding with feeding BMS showed a lower CFP from breastfeeding in all countries studied. However, the results were sensitive to the method used to allocate emissions from raw milk production on different dairy processing co-products (i.e. BMS, cream, cheese and lactose). Using alternative allocation methods still resulted in lower CFP from breastfeeding, but only slightly for UK, Brazil and Vietnam. Care is also needed when interpreting findings about products that are functionally different as regards child health and development. Elsevier Science 2019-06-10 /pmc/articles/PMC6472111/ /pubmed/31190697 http://dx.doi.org/10.1016/j.jclepro.2019.03.043 Text en © 2019 The Authors http://creativecommons.org/licenses/by/4.0/ This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0/).
spellingShingle Article
Karlsson, Johan O.
Garnett, Tara
Rollins, Nigel C.
Röös, Elin
The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title_full The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title_fullStr The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title_full_unstemmed The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title_short The carbon footprint of breastmilk substitutes in comparison with breastfeeding
title_sort carbon footprint of breastmilk substitutes in comparison with breastfeeding
topic Article
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6472111/
https://www.ncbi.nlm.nih.gov/pubmed/31190697
http://dx.doi.org/10.1016/j.jclepro.2019.03.043
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