Titulo:

An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
.

Sumario:

Colombia is a major flower exporter of a wide variety of species, among which the chrysanthemum plays a major role due to its exporting volume and profitability on the international market. This study examines the major environmental impacts of the chrysanthemum supply chain through a life cycle assessment (LCA). One kg of stems export quality was used as the functional unit (FU). The study examines cut-flowers systems from raw material extraction to final product commercialization for two markets (London and Miami) and analyzes two agroecosystems: one certified system and one uncertified system. The transport phase to London resulted in more significant environmental impacts than the transport phase to Miami, and climate change (GWP100) ca... Ver más

Guardado en:

1794-1237

2463-0950

16

2019-01-20

27

42

Revista EIA - 2019

info:eu-repo/semantics/openAccess

http://purl.org/coar/access_right/c_abf2

id metarevistapublica_eia_revistaeia_10_article_747
record_format ojs
spelling An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
An environmental evaluation of the cut-flower supply chain (Dendranthema grandiflora) through a life cycle assessment
Colombia is a major flower exporter of a wide variety of species, among which the chrysanthemum plays a major role due to its exporting volume and profitability on the international market. This study examines the major environmental impacts of the chrysanthemum supply chain through a life cycle assessment (LCA). One kg of stems export quality was used as the functional unit (FU). The study examines cut-flowers systems from raw material extraction to final product commercialization for two markets (London and Miami) and analyzes two agroecosystems: one certified system and one uncertified system. The transport phase to London resulted in more significant environmental impacts than the transport phase to Miami, and climate change (GWP100) category was significant in both cities, generating values of 9.10E+00 and 2.51E+00 kg CO2-eq*FU for London and Miami, respectively. Furthermore, when exclusively considering pre-export phases, the uncertified system was found to have a greater impact than the certified system with respect to fertilizer use (certified 1,448E-02 kg*FU, uncertified 2.23E-01 kg*FU) and pesticide use (certified 1.24 E-04 kg*FU, uncertified 2.24E-03 kg*FU). With respect to the crop management, eutrophication (EP) and acidification (AP) processes imposed the greatest level of environmental impact. Strategies that would significantly reduce the environmental impact of this supply chain are considered, including the use of shipping and a 50% reduction in fertilizer use.
Colombia is a major flower exporter of a wide variety of species, among which the chrysanthemum plays a major role due to its exporting volume and profitability on the international market. This study examines the major environmental impacts of the chrysanthemum supply chain through a life cycle assessment (LCA). One kg of stems export quality was used as the functional unit (FU). The study examines cut-flowers systems from raw material extraction to final product commercialization for two markets (London and Miami) and analyzes two agroecosystems: one certified system and one uncertified system. The transport phase to London resulted in more significant environmental impacts than the transport phase to Miami, and climate change (GWP100) category was significant in both cities, generating values of 9.10E+00 and 2.51E+00 kg CO2-eq*FU for London and Miami, respectively. Furthermore, when exclusively considering pre-export phases, the uncertified system was found to have a greater impact than the certified system with respect to fertilizer use (certified 1,448E-02 kg*FU, uncertified 2.23E-01 kg*FU) and pesticide use (certified 1.24 E-04 kg*FU, uncertified 2.24E-03 kg*FU). With respect to the crop management, eutrophication (EP) and acidification (AP) processes imposed the greatest level of environmental impact. Strategies that would significantly reduce the environmental impact of this supply chain are considered, including the use of shipping and a 50% reduction in fertilizer use.
Moreno, Carmen Alicia Parrado
Hernández, Ricardo Esteba Ricardo
Arredondo, Héctor Iván Velásquez
Castro, Sergio Hernando Lopera
--, Christian Hasenstab
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental analysis
energy use
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental impact
energy flows
16
31
Artículo de revista
Journal article
2019-01-20 00:00:00
2019-01-20 00:00:00
2019-01-20
application/pdf
Fondo Editorial EIA - Universidad EIA
Revista EIA
1794-1237
2463-0950
https://revistas.eia.edu.co/index.php/reveia/article/view/747
10.24050/reia.v16i31.747
https://doi.org/10.24050/reia.v16i31.747
spa
https://creativecommons.org/licenses/by-nc-sa/4.0/
Revista EIA - 2019
27
42
Audsley, E. 1997. Harmonisation of environmental life cycle assessment. European Commision DG VI Agriculture. Final report concerted action AIRCT94-2028.
Baranowska, I., Barchańska, H. and Pyrsz, A. 2005.Distribution of pesticides and heavy metals in trophic chain. Chemosphere 60 (11), 1590–1599. doi:10.1016/j.chemosphere.2005.02.053
Blengini, G.A. and Busto, M., 2009. The life cycle of rice: LCA of alternative agri-food chain management systems in Vercelli (Italy). Journal of Environmental Management 90 (3), 512-1522. doi:10.1016/j.jenvman.2008.10.006
Bojacá, C. and Schrevens, E. 2010. Parameter uncertainty in LCA: stochastic sampling under correlation. The International Journal of Life Cycle Assessment 15, 3, 238-246. doi:10.1007/s11367-010-0150-0
Bojacá, C.R., Wyckhuys, K.A.G. and Schrevens, E. 2014. Life cycle assessment of Colombian greenhouse tomato production based on farmer-level survey data. Journal of Cleaner Production 69, 26-33. doi: 10.1016/j.jclepro.2014.01.078
Brentrup F., Kusters, J., Lammel, J. and Kuchlmann, H. (2000). Methods to estimate On-field Nitrogen emissions from crop production as an input to LCA studies in the agricultural sector. The International Journal of Life Cycle Assessment 5 (6), 349-357. doi: 10.1007/BF02978670
Guinée, J.B., Gorree, M., Heijungs, R., Huppes, G., Kleijn, R., De Koning, A., Wegener Sleeswijk, A., Suh, S., Udo de Haes, H.A., De Bruijn, J.A., Van Duin, R. and Huijbregts, M.A.J. 2002. Handbook on Life Cycle Assessment. Operational Guide to the ISO Standards. Kluwer, The Netherlands. doi: 10.1007/BF02978784
Hauschild, M., 2000. Estimating pesticide emissions for LCA of agricultural products. In: Weidama, B., Meeusen, M.J.G. (Eds.), Agricultural Data for Life Cycle Assessments, 2. LEI, The Hague, pp. 64–79
Heathwaite, L. (2000). Flows of phosphourous in the environment: identifying pathways of loss from agricultural land. In M. M. J. G. (Ed.), Agricultural data for Life Cycle Assessment, Volume 2. (pp. 25-38). The Hague: Agricultural Economics Research Institute (LEI).
Hospido, A., Davis, J., Berlin, J. and Sonesson, U. 2010.A review of methodological issues affecting LCA of novel food products. The International Journal of Life cycle assessment 15, 44–52. doi: 10.1007/s11367-009-0130-4
ISO 14040, 2006. Environmental managementelife cycle assessment e principles and framework.
Iriarte, A., Rieradevall, J. and Gabarrell, X. 2010. Life cycle assessment of sunflower and rapeseed as energy crops Ander Chilean conditions. Journal of Cleaner Production 18, 336-345. doi: 10.1016/j.jclepro.2009.11.004
Landis, A., Miller, S. and Theis, T. 2007. Life cycle of the corn–soybean agroecosystem for biobased production. Environmental Science and Technology, 41 (4), 1457–1464. doi: 10.1021/es0606125
Medina, A. Cooman, A., Parrado, C.A. and Schrevens, E. 2006. Evaluation of energy use and some environmental impacts for greenhouse tomato production in the high altitude tropics. Acta Hort, 718, 415-422.
Mourad, A., Coltro, L., Oliveira, PAPLV, Kletecke, R.M, Baddini, J. 2007. A Simple Methodology for Elaborating the Life Cycle Inventory of Agricultural Products. The International Journal of Life Cycle Assessment 12, 6, 408-413. doi: 10.1065/lca2006.09.272.
Michael, D. 2011. Life Cycle Assessment of Waxflowers (Chamelaucium spp.). Australian Life Cycle Assessment Society (ALCAS) Conference. 9 p.
Murty, K.G. 2000. Greenhouse Gas Pollution in the Stratosphere Due to Increasing Airplane Traffic, Effects on Environment. Department of Industrial and Operations Engineering, University of Michigan, 5 p.
Ntiamoah, A. and Afrane, G.2008. Environmental impacts of cocoa production and processing in Ghana: life cycle assessment approach. Journal of Cleaner Production 16, 1735-1740. Doi: 10.1016/j.jclepro.2007.11.004.
Panichelli, L. 2006. Análisis de ciclo de Vida (ACV) de la producción de biodiesel (B100) en argentina. Universidad de Buenos Aires. Buenos Aires, 90 p.
Parrado, C.A and Leiva, F. 2011. Huella de Carbono (HC) en cadenas de suministro de flores de corte colombianas, rosas y claveles, para mercados internacionales. Revista Asocolflores 77, 26-33.
Parrado, C.A. and Bojacá C.R. 2009. Environmental impact of greenhouse tomato production strategies using life cycle assessment approach. Acta Hort. 821,125-132.
Pervanchon, F., Bockstallerb, C. and Girardin, P. 2002. Assessment of energy use in arable farming systems by means of an agro-ecological indicator: the energy indicator. Agricultural Systems 72, 149-172. doi:10.1016/S0308-521X(01)00073-7
Queiroz, A.G.,França, L. and Ponte, M.X. 2012.The life cycle assessment of biodiesel from palm oil “dendeˆ” in the Amazon. Biomass and Bioenergy 36, 50-59. doi:10.1016/j.biombioe.2011.10.007
Roy, P., Nei, D., Orikasa, T., Xu, Q. and Okadome, H. 2009. A review of life cycle assessment (LCA) on some food products. Journal of Food Engineering 90, 1-10. doi:10.1016/j.jfoodeng.2008.06.016.
Sahle, A. and Potting, J. 2013. Environmental life cycle assessment of Ethiopian rose cultivation. Science of The Total Environment 443,163-172. doi:10.1016/j.scitotenv.2012.10.048
Shau, E.M. and Fet, A.M. 2008. LCA studies of food products as background for environmental product declarations. The International Journal of Life Cycle Assessment 13, 255-264. doi: 10.1065/lca2007.12.372
Udo de Haes, H.A., Jolliet O., Finnveden G., Hauschild M., Krewitt W. and Müller-Wenk R. 1999. Best available practice regarding impact categories and category indicators in life cycle impact assessment, Background Document for the Second Working Group on Life Cycle Impact Assessment of SETACEurope (WIA-2). The International Journal of Life Cycle Assessment 4 (3), 167- 174. doi: 10.1007/BF02979453
Vringer, K. and Blok, K. 2000.The energy requirement of cut flowers and consumer options to reduce it. Resources, Conservation and Recycling 28, 3-28. doi:10.1016/S0921-3449(99)00024-5
Walter, C. and Hartmut, H. 2009. A new method for assessing the sustainability of land-use systems (I): Identifying the relevant issues. Ecological Economics 68, 1275-1287. doi:10.1016/j.ecolecon.2008.11.016
Weidema B. and Meeusen M. (Eds.). 2000. Agricultural data for life cycle assessment, vol. II. The Hague: Agricultural Economics Research Institute. 169 p.
Williams, A. 2007. Comparative Study of Cut Roses for the British Market Produced in Kenya and the Netherlands. Report for World Flowers, 7 p.
Yañez, E., Silva, E., Da Costa, R. and Andrade, E. 2007.The energy balance in the Palm Oil-Derived Methyl Ester (PME) life cycle for the cases in Brazil and Colombia. Renewable Energy 34, 2905-291. doi: doi:10.1016/j.renene.2009.05.007.
https://revistas.eia.edu.co/index.php/reveia/article/download/747/1217
info:eu-repo/semantics/article
http://purl.org/coar/resource_type/c_6501
http://purl.org/coar/resource_type/c_2df8fbb1
http://purl.org/redcol/resource_type/ART
info:eu-repo/semantics/publishedVersion
http://purl.org/coar/version/c_970fb48d4fbd8a85
info:eu-repo/semantics/openAccess
http://purl.org/coar/access_right/c_abf2
Text
Publication
institution UNIVERSIDAD EIA
thumbnail https://nuevo.metarevistas.org/UNIVERSIDADEIA/logo.png
country_str Colombia
collection Revista EIA
title An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
spellingShingle An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
Moreno, Carmen Alicia Parrado
Hernández, Ricardo Esteba Ricardo
Arredondo, Héctor Iván Velásquez
Castro, Sergio Hernando Lopera
--, Christian Hasenstab
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental analysis
energy use
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental impact
energy flows
title_short An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
title_full An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
title_fullStr An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
title_full_unstemmed An Environmental Evaluation of the Cut-Flower Supply Chain (Dendranthema grandiflora) Through a Life Cycle Assessment
title_sort environmental evaluation of the cut-flower supply chain (dendranthema grandiflora) through a life cycle assessment
title_eng An environmental evaluation of the cut-flower supply chain (Dendranthema grandiflora) through a life cycle assessment
description Colombia is a major flower exporter of a wide variety of species, among which the chrysanthemum plays a major role due to its exporting volume and profitability on the international market. This study examines the major environmental impacts of the chrysanthemum supply chain through a life cycle assessment (LCA). One kg of stems export quality was used as the functional unit (FU). The study examines cut-flowers systems from raw material extraction to final product commercialization for two markets (London and Miami) and analyzes two agroecosystems: one certified system and one uncertified system. The transport phase to London resulted in more significant environmental impacts than the transport phase to Miami, and climate change (GWP100) category was significant in both cities, generating values of 9.10E+00 and 2.51E+00 kg CO2-eq*FU for London and Miami, respectively. Furthermore, when exclusively considering pre-export phases, the uncertified system was found to have a greater impact than the certified system with respect to fertilizer use (certified 1,448E-02 kg*FU, uncertified 2.23E-01 kg*FU) and pesticide use (certified 1.24 E-04 kg*FU, uncertified 2.24E-03 kg*FU). With respect to the crop management, eutrophication (EP) and acidification (AP) processes imposed the greatest level of environmental impact. Strategies that would significantly reduce the environmental impact of this supply chain are considered, including the use of shipping and a 50% reduction in fertilizer use.
description_eng Colombia is a major flower exporter of a wide variety of species, among which the chrysanthemum plays a major role due to its exporting volume and profitability on the international market. This study examines the major environmental impacts of the chrysanthemum supply chain through a life cycle assessment (LCA). One kg of stems export quality was used as the functional unit (FU). The study examines cut-flowers systems from raw material extraction to final product commercialization for two markets (London and Miami) and analyzes two agroecosystems: one certified system and one uncertified system. The transport phase to London resulted in more significant environmental impacts than the transport phase to Miami, and climate change (GWP100) category was significant in both cities, generating values of 9.10E+00 and 2.51E+00 kg CO2-eq*FU for London and Miami, respectively. Furthermore, when exclusively considering pre-export phases, the uncertified system was found to have a greater impact than the certified system with respect to fertilizer use (certified 1,448E-02 kg*FU, uncertified 2.23E-01 kg*FU) and pesticide use (certified 1.24 E-04 kg*FU, uncertified 2.24E-03 kg*FU). With respect to the crop management, eutrophication (EP) and acidification (AP) processes imposed the greatest level of environmental impact. Strategies that would significantly reduce the environmental impact of this supply chain are considered, including the use of shipping and a 50% reduction in fertilizer use.
author Moreno, Carmen Alicia Parrado
Hernández, Ricardo Esteba Ricardo
Arredondo, Héctor Iván Velásquez
Castro, Sergio Hernando Lopera
--, Christian Hasenstab
author_facet Moreno, Carmen Alicia Parrado
Hernández, Ricardo Esteba Ricardo
Arredondo, Héctor Iván Velásquez
Castro, Sergio Hernando Lopera
--, Christian Hasenstab
topic Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental analysis
energy use
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental impact
energy flows
topic_facet Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental analysis
energy use
Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental impact
energy flows
topicspa_str_mv Environmental analysis
floriculture
chrysanthemum
energy
certification systems
agroecosystem
Environmental impact
energy flows
citationvolume 16
citationissue 31
publisher Fondo Editorial EIA - Universidad EIA
ispartofjournal Revista EIA
source https://revistas.eia.edu.co/index.php/reveia/article/view/747
language spa
format Article
rights https://creativecommons.org/licenses/by-nc-sa/4.0/
Revista EIA - 2019
info:eu-repo/semantics/openAccess
http://purl.org/coar/access_right/c_abf2
references Audsley, E. 1997. Harmonisation of environmental life cycle assessment. European Commision DG VI Agriculture. Final report concerted action AIRCT94-2028.
Baranowska, I., Barchańska, H. and Pyrsz, A. 2005.Distribution of pesticides and heavy metals in trophic chain. Chemosphere 60 (11), 1590–1599. doi:10.1016/j.chemosphere.2005.02.053
Blengini, G.A. and Busto, M., 2009. The life cycle of rice: LCA of alternative agri-food chain management systems in Vercelli (Italy). Journal of Environmental Management 90 (3), 512-1522. doi:10.1016/j.jenvman.2008.10.006
Bojacá, C. and Schrevens, E. 2010. Parameter uncertainty in LCA: stochastic sampling under correlation. The International Journal of Life Cycle Assessment 15, 3, 238-246. doi:10.1007/s11367-010-0150-0
Bojacá, C.R., Wyckhuys, K.A.G. and Schrevens, E. 2014. Life cycle assessment of Colombian greenhouse tomato production based on farmer-level survey data. Journal of Cleaner Production 69, 26-33. doi: 10.1016/j.jclepro.2014.01.078
Brentrup F., Kusters, J., Lammel, J. and Kuchlmann, H. (2000). Methods to estimate On-field Nitrogen emissions from crop production as an input to LCA studies in the agricultural sector. The International Journal of Life Cycle Assessment 5 (6), 349-357. doi: 10.1007/BF02978670
Guinée, J.B., Gorree, M., Heijungs, R., Huppes, G., Kleijn, R., De Koning, A., Wegener Sleeswijk, A., Suh, S., Udo de Haes, H.A., De Bruijn, J.A., Van Duin, R. and Huijbregts, M.A.J. 2002. Handbook on Life Cycle Assessment. Operational Guide to the ISO Standards. Kluwer, The Netherlands. doi: 10.1007/BF02978784
Hauschild, M., 2000. Estimating pesticide emissions for LCA of agricultural products. In: Weidama, B., Meeusen, M.J.G. (Eds.), Agricultural Data for Life Cycle Assessments, 2. LEI, The Hague, pp. 64–79
Heathwaite, L. (2000). Flows of phosphourous in the environment: identifying pathways of loss from agricultural land. In M. M. J. G. (Ed.), Agricultural data for Life Cycle Assessment, Volume 2. (pp. 25-38). The Hague: Agricultural Economics Research Institute (LEI).
Hospido, A., Davis, J., Berlin, J. and Sonesson, U. 2010.A review of methodological issues affecting LCA of novel food products. The International Journal of Life cycle assessment 15, 44–52. doi: 10.1007/s11367-009-0130-4
ISO 14040, 2006. Environmental managementelife cycle assessment e principles and framework.
Iriarte, A., Rieradevall, J. and Gabarrell, X. 2010. Life cycle assessment of sunflower and rapeseed as energy crops Ander Chilean conditions. Journal of Cleaner Production 18, 336-345. doi: 10.1016/j.jclepro.2009.11.004
Landis, A., Miller, S. and Theis, T. 2007. Life cycle of the corn–soybean agroecosystem for biobased production. Environmental Science and Technology, 41 (4), 1457–1464. doi: 10.1021/es0606125
Medina, A. Cooman, A., Parrado, C.A. and Schrevens, E. 2006. Evaluation of energy use and some environmental impacts for greenhouse tomato production in the high altitude tropics. Acta Hort, 718, 415-422.
Mourad, A., Coltro, L., Oliveira, PAPLV, Kletecke, R.M, Baddini, J. 2007. A Simple Methodology for Elaborating the Life Cycle Inventory of Agricultural Products. The International Journal of Life Cycle Assessment 12, 6, 408-413. doi: 10.1065/lca2006.09.272.
Michael, D. 2011. Life Cycle Assessment of Waxflowers (Chamelaucium spp.). Australian Life Cycle Assessment Society (ALCAS) Conference. 9 p.
Murty, K.G. 2000. Greenhouse Gas Pollution in the Stratosphere Due to Increasing Airplane Traffic, Effects on Environment. Department of Industrial and Operations Engineering, University of Michigan, 5 p.
Ntiamoah, A. and Afrane, G.2008. Environmental impacts of cocoa production and processing in Ghana: life cycle assessment approach. Journal of Cleaner Production 16, 1735-1740. Doi: 10.1016/j.jclepro.2007.11.004.
Panichelli, L. 2006. Análisis de ciclo de Vida (ACV) de la producción de biodiesel (B100) en argentina. Universidad de Buenos Aires. Buenos Aires, 90 p.
Parrado, C.A and Leiva, F. 2011. Huella de Carbono (HC) en cadenas de suministro de flores de corte colombianas, rosas y claveles, para mercados internacionales. Revista Asocolflores 77, 26-33.
Parrado, C.A. and Bojacá C.R. 2009. Environmental impact of greenhouse tomato production strategies using life cycle assessment approach. Acta Hort. 821,125-132.
Pervanchon, F., Bockstallerb, C. and Girardin, P. 2002. Assessment of energy use in arable farming systems by means of an agro-ecological indicator: the energy indicator. Agricultural Systems 72, 149-172. doi:10.1016/S0308-521X(01)00073-7
Queiroz, A.G.,França, L. and Ponte, M.X. 2012.The life cycle assessment of biodiesel from palm oil “dendeˆ” in the Amazon. Biomass and Bioenergy 36, 50-59. doi:10.1016/j.biombioe.2011.10.007
Roy, P., Nei, D., Orikasa, T., Xu, Q. and Okadome, H. 2009. A review of life cycle assessment (LCA) on some food products. Journal of Food Engineering 90, 1-10. doi:10.1016/j.jfoodeng.2008.06.016.
Sahle, A. and Potting, J. 2013. Environmental life cycle assessment of Ethiopian rose cultivation. Science of The Total Environment 443,163-172. doi:10.1016/j.scitotenv.2012.10.048
Shau, E.M. and Fet, A.M. 2008. LCA studies of food products as background for environmental product declarations. The International Journal of Life Cycle Assessment 13, 255-264. doi: 10.1065/lca2007.12.372
Udo de Haes, H.A., Jolliet O., Finnveden G., Hauschild M., Krewitt W. and Müller-Wenk R. 1999. Best available practice regarding impact categories and category indicators in life cycle impact assessment, Background Document for the Second Working Group on Life Cycle Impact Assessment of SETACEurope (WIA-2). The International Journal of Life Cycle Assessment 4 (3), 167- 174. doi: 10.1007/BF02979453
Vringer, K. and Blok, K. 2000.The energy requirement of cut flowers and consumer options to reduce it. Resources, Conservation and Recycling 28, 3-28. doi:10.1016/S0921-3449(99)00024-5
Walter, C. and Hartmut, H. 2009. A new method for assessing the sustainability of land-use systems (I): Identifying the relevant issues. Ecological Economics 68, 1275-1287. doi:10.1016/j.ecolecon.2008.11.016
Weidema B. and Meeusen M. (Eds.). 2000. Agricultural data for life cycle assessment, vol. II. The Hague: Agricultural Economics Research Institute. 169 p.
Williams, A. 2007. Comparative Study of Cut Roses for the British Market Produced in Kenya and the Netherlands. Report for World Flowers, 7 p.
Yañez, E., Silva, E., Da Costa, R. and Andrade, E. 2007.The energy balance in the Palm Oil-Derived Methyl Ester (PME) life cycle for the cases in Brazil and Colombia. Renewable Energy 34, 2905-291. doi: doi:10.1016/j.renene.2009.05.007.
type_driver info:eu-repo/semantics/article
type_coar http://purl.org/coar/resource_type/c_6501
type_version info:eu-repo/semantics/publishedVersion
type_coarversion http://purl.org/coar/version/c_970fb48d4fbd8a85
type_content Text
publishDate 2019-01-20
date_accessioned 2019-01-20 00:00:00
date_available 2019-01-20 00:00:00
url https://revistas.eia.edu.co/index.php/reveia/article/view/747
url_doi https://doi.org/10.24050/reia.v16i31.747
issn 1794-1237
eissn 2463-0950
doi 10.24050/reia.v16i31.747
citationstartpage 27
citationendpage 42
url2_str_mv https://revistas.eia.edu.co/index.php/reveia/article/download/747/1217
_version_ 1811200502157803520