A día 6 de agosto de 2019, el índice h del grupo de investigación PELCAN, según Scopus, es de 31. El índice h es un sistema propuesto por Jorge Hirsch, de la Universidad de California, para la medición de la calidad profesional de los científicos, en función de la cantidad de citas que han recibido sus artículos científicos. Un científico o investigador tiene índice h si ha publicado h trabajos con al menos h citas cada uno. Para este caso en concreto, hemos asumido el índice h acumulado de todos los investigadores del grupo.
| 1 | 200 | Exploring e-waste management systems in the United States |
| 2 | 184 | Environmental, social, and economic implications of global reuse and recycling of personal computers |
| 3 | 104 | Joint life cycle assessment and data envelopment analysis of grape production for vinification in the Rías Baixas appellation (NW Spain) |
| 4 | 87 | A comprehensive review of carbon footprint analysis as an extended environmental indicator in the wine sector |
| 5 | 86 | Eco-efficiency analysis of Spanish WWTPs using the LCA+DEA method |
| 6 | 86 | Combined application of life cycle assessment and data envelopment analysis as a methodological approach for the assessment of fisheries |
| 7 | 74 | Evolution of product lifespan and implications for environmental assessment and management: A case study of personal computers in higher education |
| 8 | 70 | Further potentials in the joint implementation of life cycle assessment and data envelopment analysis |
| 9 | 68 | Eco-efficiency assessment of the Peruvian anchoveta steel and wooden fleets using the LCA+DEA framework |
| 10 | 64 | Environmental analysis of Ribeiro wine from a timeline perspective: Harvest year matters when reporting environmental impacts |
| 11 | 60 | Comparative life cycle assessment in the wine sector: Biodynamic vs. conventional viticulture activities in NW Spain |
| 12 | 59 | Product or waste? Importation and end-of-life processing of computers in Peru |
| 13 | 59 | Life cycle assessment of horse mackerel fisheries in Galicia (NW Spain): Comparative analysis of two major fishing methods |
| 14 | 56 | Applying consequential LCA to support energy policy: Land use change effects of bioenergy production |
| 15 | 51 | On the feasibility of using emergy analysis as a source of benchmarking criteria through data envelopment analysis: A case study for wind energy |
| 16 | 51 | Best practices in life cycle assessment implementation in fisheries. Improving and broadening environmental assessment for seafood production systems |
| 17 | 44 | Energy potential from rice husk through direct combustion and fast pyrolysis: A review |
| 18 | 44 | Tapping carbon footprint variations in the European wine sector |
| 19 | 43 | Application of three independent consequential LCA approaches to the agricultural sector in Luxembourg |
| 20 | 42 | Environmental assessment of the Atlantic mackerel (Scomber scombrus) season in the Basque Country. Increasing the timeline delimitation in fishery LCA studies |
| 21 | 41 | Materials flow analysis of e-waste: Domestic flows and exports of used computers from the United States |
| 22 | 40 | Life cycle assessment of milk produced in two smallholder dairy systems in the highlands and the coast of Peru |
| 23 | 38 | Review of life-cycle approaches coupled with data envelopment analysis: Launching the CFP + DEA method for energy policy making |
| 24 | 38 | Estimation of the carbon footprint of the Galician fishing activity (NW Spain) |
| 25 | 37 | Identifying the importance of the «skipper effect» within sources of measured inefficiency in fisheries through data envelopment analysis (DEA) |
| 26 | 37 | Environmental impacts over the life cycle of residential buildings using different exterior wall systems |
| 27 | 34 | Computation of operational and environmental benchmarks within selected galician fishing fleets |
| 28 | 33 | Benchmarking wastewater treatment plants under an eco-efficiency perspective |
| 29 | 33 | Inclusion of discard assessment indicators in fisheries life cycle assessment studies. Expanding the use of fishery-specific impact categories |
| 30 | 32 | Environmental assessment of digestate treatment technologies using LCA methodology |
| 31 | 32 | Life Cycle Assessment of fresh hake fillets captured by the Galician fleet in the Northern Stock |
