This paper estimates the foodmiles (embedded distances) and transport-related carbon emissions of 27 Food Quality Scheme (FQS) products – Protected Designation of Origin (PDO), Protected Geographical Indications (PGI) and organic – and their reference products. It goes further than the existing literature by adopting a value chain perspective, instead of the traditional consumer perspective, and focusing on FQS products. The same methodology is applied across all the case studies. The article specifically investigates the determinants of differences between FQS and their references. FQS products travel significantly shorter distances (−30%) and generate significantly lower transport-related emissions (−23%) than conventional food products. The differences are even greater for vegetal and organic products. The relationship between distance and transport-related emissions is not exactly proportional and highlights the importance of transport modes and logistics, in particular for exports and imports. Finally, we stress the importance of the spatial distribution of the different stages in the value chains (e.g. production, processing). PDO technical specifications delimit a geographical area for production and processing, thereby limiting distances and transport-related emissions compared to conventional food products, but also compared to other types of FQS.
Funding source: European Commission
Award Identifier / Grant number: 678024
This project has received funding from the European Union’s Horizon 2020 research and innovation programme under grant agreement No 678024. Partners listed as co-authors in this article were responsible for collecting data related to two case studies on average, i.e. two FQS products along with two reference products over the value chain. The authors would like to thank all the people and institutions who collected or provided raw data for this publication. Statistical analysis were conducted using the R software.
A detailed description of the variables used is presented below. These variables are to be completed for each transport mode used in a given section of the value chain. Indeed, different transport modes have different emission rates associated. Please refer to Bellassen et al. (2019) for more details.
Distance: either directly given in kilometers by case study conductors (usually from expert interviews) or computed by the corresponding author using online tools based on an origin point and a destination point. The shortest distance proposed is systematically selected when using online tools to estimate distances (https://www.maps.google.com for road transport, https://sea-distances.org/ for sea distances, and https://www.worldatlas.com/travelaids/flight_distance.htm for flight distances).
Transport mode: the Excel data file provides the following options from a drop-down list: Road – Light Goods vehicle – Petrol; Road – Light Goods vehicle – Diesel; Road – Heavy Goods vehicle; Rail; Air; Ship – Small tanker; Ship – Large tanker; Ship – Very large tanker; Ship – Small BC; Ship – Large BC; Ship – Very large BC; Ship – Small CV; Ship – Large CV. Detailed description helps choosing the appropriate mode. Light goods vehicles are vehicles carrying loads less than 3.5 tons (3.9 US tons), while heavy goods vehicles are vehicles carrying loads greater than 3.5 tons (3.9 US tons). A tanker is a ship designed to transport or store liquids or gases in bulk. Small tankers carry about 1000 tons, while large tankers carry 20,000 tons and very large tankers carry 100,000 tons. BC states for Bulk Carrier, a ship especially designed to transport unpackaged bulk cargo, such as grains, coal, ore, and cement. Small bulk carriers carry up to 2000 tons, while large bulk carriers carry 15,000 tons and very large bulk carriers carry 70,000 tons. CV states for Container Vessel, a cargo ship that carries its load in truck-size intermodal containers, in a technique called containerization. Small container vessels carry 2500 tons, while large container vessels carry about 20,000 tons. When no further information is available about sea transport, the ship category “large CV” is selected. Indeed, today about 90% of non-bulk cargo worldwide is transported by container ships. Different sizes of transport modes correspond to different carbon emission rates.
Logistics: the Excel data file provides the following options from a drop-down list: single journey; returning empty. The logistics variable indicates when a transport mode runs back empty or not. Only road transport modes may run back empty, air and sea transport are assumed to travel single journeys and to run back or further to another destination full of another commodity. When no information is available on logistics for road transport, we assume trucks run back empty.
Share of the product concerned: the share of the product traveling with a given transport mode and between two steps of the value chain. This variable is used to weight the distance when several modes are used for a given segment of the value chain, or when the value chain divides into several segments at a given level (e.g., exports and domestic market at retail level).
Product concentration: the final product ratio variable applies to value chains with at least one processing or packing stage. It gives an idea of the product concentration and of the degree of embeddedness of distance and emissions into the final product. For instance, a product ratio of 0.1 indicates that 10 units of raw product are required to produce 1 unit of final product. In this case, when raw products travel x kilometers upstream, there will be 10 times x kilometers embedded in the final product. When there are more than one processing stage, the product concentration for the (raw) product concerned at a given level is indicated with respect to the final product.
Co-product value: the value of co-products compared to the value of final products. This variable allows to weight the foodmiles and transport-related carbon emissions by removing the foodmiles and emissions attributable to co-products.
Energy: default hypothesis are made in Cool Farm Tool (e.g., heavy goods vehicles are necessarily powered by diesel) and the energy variable only makes a difference for road light goods vehicles. When no further information is available on the energy used by light goods vehicles, the national energy mix is considered.
Table 5 presents the most important data sources on which each case studied and reference product rely, as well as a detailed description of the reference products used along the value chain.
|Case studied||Type of FQS||Country||Reference product||Most important data sources|
|Buon Ma Thuot coffee||PGI||Vietnam||Interviews, accountancy data|
|Dalmatian prosciutto||PGI||Croatia||Conventional prosciutto made from pigs raised in Croatia||Interviews|
|Olive oil||PDO||Croatia||Conventional olives and conventional olive oil produced in Croatia||FQS: Interviews|
REF: Interviews, FAOSTAT (2015), Croatian Bureau of Statistics (2015)
|Saint-Michel bay bouchot mussels||PDO||France||FQS: Interviews|
REF: Interviews, FranceAgriMer (2016)
|Organic flour||Organic||France||FQS: Interviews, ANMF (2016)|
REF: ANMF (2016), Passion Céréales (2017), France Export Céréales (2017)
|Comte cheese||PDO||France||FQS: Interviews, CIGC (2018)|
REF: CNIEL (2016), Maison du Lait (2016)
|Camargue rice||Organic||France||FQS: Interviews|
REF: Interviews, Eurostat (2015)
|Gyulai sausage||PGI||Hungary||Conventional (generic) sausage from Gyulai region, in Hungary||FQS: Interviews, company data|
REF: interviews, industry data, World Bank (2017)
|Kalocsai paprika powder||PDO||Hungary||Interviews, World Bank (2017)|
|Parmigiano Reggiano cheese||PDO||Italy||Biraghi cheese (similar non-PDO cheese)||Interviews, ISTAT (2016)|
|Kastoria apples||PGI||Greece||Conventional apples produced by the cooperative Kissavos, in Agia, Greece||Interviews|
|Zagora apples||PDO||Greece||Conventional apples produced by the cooperative Kissavos, in Agia, Greece||Interviews|
|Phu Quoc fish sauce||PDO||Vietnam||Conventional fish sauce from Phu Quoc island in Vietnam||Interviews|
|Organic pasta||Organic||Poland||Conventional cereals produced by the 14 model conventional farms||Interviews|
|Kaszubska Strawberry||PGI||Poland||Conventional strawberries from Poland||Interviews|
|Organic pork||Organic||Germany||Conventional pork from Germany||ISN (2016)|
|Organic raspberries||Organic||Serbia||Conventional raspberries from Serbia||Interviews, National Institute of Statistics of Serbia (2016)|
|Sjenica cheese||PDO||Serbia||Conventional cow cheese produced in Serbia||Interviews, National Institute of Statistics of Serbia (2016)|
|Organic tomato from Emilia Romagna||Organic||Italy||Interviews, ISTAT (2017), ANICAV (2017)|
|Organic yoghurt||Organic||Germany||Interviews, AMI (2018), Müller-Lindenlauf et al. (2014), Destatis (2017)|
|Opperdoezer Ronde potatoes||PDO||The Netherlands||Conventional fresh consumption potato from The Netherlands||Interviews, Central Bureau of Statistics (2016)|
|Lofoten stockfish||PGI||Norway||Interviews, Seafood Council (2016)|
|Organic salmon||Organic||Norway||FQS: Interviews|
REF: Interviews, Seafood Council (2016)
|Sobrasada of Mallorca||PGI||Spain||Interviews, DGAR|
|Ternasco de Aragon||PGI||Spain||Conventional lamb from Aragon region, in Spain||FQS: Interviews, MAGRAMA (2016)|
REF: Interviews, DataComex (2016)
|Thung Kula Rong-Hai (TKR) Hom Mali rice||PGI||Thailand||FQS: Interviews|
REF: Interviews, Potchanasin et al. (2017), MOC (2017)
|Doi Chaang Coffee||PGI||Thailand||Interviews|
NB: REF = reference product.
ACEA. 2018. Car Fleet by Fuel Type, Data 2013–2016. European Automobile Manufacturers Association of Passenger. Also available at https://www.acea.be/statistics/tag/category/passenger-car-fleet-by-fuel-type.Search in Google Scholar
Agence BIO. 2019. Organic Farming and Market in the European Union, 2019 Ed. International Publications by Agence Bio. https://www.agencebio.org/wp-content/uploads/2020/04/Organic_farming_market_EU_2019.pdf.Search in Google Scholar
AMI. 2018. Markt Bilanz – Milch 2018. Rheinbreitbach: AMI GmbH 04/2018.Search in Google Scholar
ANMF. 2016. Association Nationale de la Meunerie Française. Fiche statistiques - 2015. Juin 2016.Search in Google Scholar
Arfini, F., and V. Bellassen, eds. (2019). Sustainability of European Food Quality Schemes: Multi-performance, structure, and governance of PDO, PGI and Organic Agri-Food Systems, 567. Switzerland: Springer Nature Switzerland AG.10.1007/978-3-030-27508-2Search in Google Scholar
Barbier, C., C. Couturier, P. Pourouchottamin, J.-M. Cayla, M. Silvestre, and I. Pharabod. 2019. L’empreinte énergétique et carbone de l’alimentation en France. de la production à la consommation, Club Ingénierie Prospective Energie et Environnement, 24. Paris: IDDRI.Search in Google Scholar
Bellassen, et al.. (2020 or 2021). “The Carbon and Land Footprint of Certified Food Products.” Journal of Agriculture and Food Industrial Organization 19: 113–26.10.1515/jafio-2019-0037Search in Google Scholar
Bellassen, V., F. Antonioli, A. Bodini, M. Donati, M. Drut, M. Duboys de Labarre, M. Hilal, S. Monier-Dilhan, P. Muller, T. Poméon, and M. Veneziani. 2019. “Common Methods and Sustainability Indicators.” In Sustainability of European Food Quality Schemes: Multi-Performance, Structure, and Governance of PDO, PGI and Organic Agri-Food Systems, edited by F. Arfini and V. Bellassen, 567. Switzerland: Springer Nature Switzerland AG.10.1007/978-3-030-27508-2_2Search in Google Scholar
CNIEL. 2016. Centre National Interprofessionnel de l’Economie Laitière. Also available at http://www.filiere-laitiere.fr/fr/les-organisations/cniel.Search in Google Scholar
Coley, D., M. Howard, and M. Winter. 2009. “Local Food, Food Miles and Carbon Emissions: A Comparison of Farm Shop and Mass Distribution Approaches.” Food Policy 34: 150–5, https://doi.org/10.1016/j.foodpol.2008.11.001.Search in Google Scholar
Destatis. 2017. Statistisches Bundesamt. Bundesanstalt für Landwirtschaft und Ernährung (BLE). Also available at https://www.destatis.de/DE/Themen/Branchen-Unternehmen/Landwirtschaft-Forstwirtschaft-Fischerei/Tiere-Tierische-Erzeugung/_inhalt.html.Search in Google Scholar
Door database. 2020. Also available athttps://ec.europa.eu/agriculture/quality/door/list.html.Search in Google Scholar
Eurostat. 2018. Statistics Explained. Road freight transport by journey characteristics. Also available at https://ec.europa.eu/eurostat/statistics-explained/index.php/Road_freight_transport_by_journey_characteristics (accessed on July 4 2019).Search in Google Scholar
Eurostat. 2019. Statistics Explained. Glossary: Tonne-kilometre (tkm). https://ec.europa.eu/eurostat/statistics-explained/index.php/Glossary:Tonne-kilometre_(tkm) (accessed June 7, 2019).Search in Google Scholar
FAO. 2013. SAFA Indicators. Rome, Italy: Food and Agriculture Organization of the United Nations (FAO).Search in Google Scholar
FranceAgriMer. 2016. Visio - données en ligne. Also available at https://www.franceagrimer.fr/Eclairer/Outils/VISIO-Donnees-en-ligne.Search in Google Scholar
France Export Céréales. 2017. Rapport d’activité 2016–2017.Search in Google Scholar
Halweil, B., and H. Grown. (2002). The Case for Local Food in a Global Market, edited by T. Prugh. Wolrdwatch paper 163, November.Search in Google Scholar
Hillier, J., C. Walter, D. Malin, T. Garcia-Suarez, L. Mila-i-Canals, and P. Smith. 2011. “A Farm-Focused Calculator for Emissions from Crop and Livestock Production.” Environmental Modelling & Software 26: 1070–8, https://doi.org/10.1016/j.envsoft.2011.03.014.Search in Google Scholar
ISN. 2016. Interessengemeinschaft der Schweinehalter Deutschlands. Schweinefleisch-Export 2015. Also available at https://www.schweine.net/news/schweinefleisch-export-2015-drittlaender.html.Search in Google Scholar
Lopez, L. A., M. A. Cadarso, N. Gomez, and M. A. Tobarra. 2015. “Food Miles, Carbon Footprint and Global Value Chains for Spanish Agriculture: Assessing the Impact of a Carbon Border Tax.” Journal of Cleaner Production 103: 423–36, https://doi.org/10.1016/j.jclepro.2015.01.039.Search in Google Scholar
MAGRAMA. 2016. Cifras Y Datos. Also available at https://www.mapa.gob.es/es/alimentacion/temas/calidad-agroalimentaria/calidad-diferenciada/dop/htm/cifrasydatos.aspx.Search in Google Scholar
Maison du lait. 2016. La collecte : le maillon fort. La filière laitière française.Search in Google Scholar
MEDDE. 2012. Information CO2 des prestations de transport, guide méthodologique. Ministère de l’Ecologie, du Développement durable et de l’Energie. October.Search in Google Scholar
Müller-Lindenlauf, M., C. Cornelius, S. Gärtner, G. Reinhardt, N. Rettenmaier, and T. Schmidt. 2014. Umweltbilanz von Milch und Milcherzeugnissen. Status quo und Ableitung von Optimierungspotenzialen. ifeu - Institut für Energie- und Umweltforschung Heidelberg GmbH. October 2014.Search in Google Scholar
Mundler, P., and L. Rumpus. 2012. “La route des paniers : réflexions sur l’efficacité énergétique d’une forme de distribution alimentaire en circuits courts.” Cahiers de Géographie du Québec 56 (157): 225–41, https://doi.org/10.7202/1012220ar.Search in Google Scholar
Passion Céréales. 2017. Des chiffres et des céréales, Edition 2017 – l’essentiel de la filière.Search in Google Scholar
Pimentel, D., S. Williamson, E. A. Courtney, O. Gonzalespagan, C. Kontak, and S. E. Mulkey. 2008. “Reducing Energy Inputs in the US Food System.” Human Ecology 36 (4): 459–71, https://doi.org/10.1007/s10745-008-9184-3.Search in Google Scholar
Pirog, R. S., T. Van Pelt, K. Enshayan, and E. Cook. 2001 Food, Fuel, and Freeways: An Iowa Perspective on How Far Food Travels, Fuel Usage, and Greenhouse Gas Emissions, Leopold Center Pubs and Papers 3. Also available at https://lib.dr.iastate.edu/leopold_pubspapers/3/.Search in Google Scholar
Pirog, R. S., and A. Benjamin. 2005 Calculating Food Miles for a Multiple Ingredient Food Product, Leopold Center Pubs and Papers 147. Also available at http://lib.dr.iastate.edu/leopold_pubspapers/147.Search in Google Scholar
Potchanasin, C., S. Wattanutchariya, S. Hemtanont, and C. Siripunya. 2017. Post Survey Study: Monitoring and Evaluation (M&E) Thailand. Report Submitted to Better Rice Initiative Asia (BRIA). Thailand: Department of Agricultural and Resource Economics, Kasetsart University. October 2017.Search in Google Scholar
Röös, E., C. Sundberg, and P. A. Hansson. 2014. “Carbon Footprint of Food Products.” In Assessment of Carbon Footprint in Different Industrial Sectors, edited by S. S. Muthu. Singapore.10.1007/978-981-4560-41-2_4Search in Google Scholar
Saunders, C., and P. Hayes. 2007. Air Freight Transport of Fresh Fruit and Vegetables. Agribusiness and Economist Research Unit. Christchurch, New Zealand: Lincoln University.Search in Google Scholar
Schlich, E., and U. Fleissner. 2005. “The Ecology of Scale. Assessment of Regional Energy Turnover and Comparison with Global Food.” International Journal of Life Cycle Assessment 10 (3): 219–23, https://doi.org/10.1065/lca2004.09.180.9.Search in Google Scholar
Seafood Council. 2016. Also available at https://seafood.azureedge.net/48d8ba/globalassets/markedsinnsikt/apne-rapporter/manedsstatistikk/manedsstatistikk-desember-2017.pdf.Search in Google Scholar
Weber, C. L., and H. S. Matthews. 2008. “Food-Miles and the Relative Climate Impacts of Food Choices in the United States.” Environmental Science & Technology 42: 3508–13, https://doi.org/10.1021/es702969f.Search in Google Scholar
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