Colombia Amazónica 5(2):163-193 Weber JC, Sotelo Montes C, Vidaurre H, Dawson IK, Simons AJ (2001) Participatory domestication of agroforestry trees: an example from the

Peruvian Amazon. Dev Pract 11(4):425–433CrossRef Weitzman ML (1998) The Noah’s Ark Problem. Econometrica Givinostat 66:1279–1298CrossRef Winogrond W (2004) Colombia alternative development project. Survey of Department of Cauca. Chemonics International Inc., Washington Ydrogo HF (1994) Efecto de la inoculación de lombrices de tierra Pontoscolex corethrurus (Glossoscolecidae) en las micorrizas Vesículo arbusculares y en la etapa de crecimiento de arazá (Eugenia stipitata), achiote (Bixa orellana) y pijuayo (Bactris gasipaes) en suelos ultisoles de Yurimaguas. Master thesis, Universidad Nacional de San Martín Yuyama LKO, Cozzolino SMF (1996) Effect of supplementation with peach palm as source of vitamin A: study with rats. Rev Saude Publica 30(1):61–66PubMedCrossRef Yuyama LKO, Favaro RMD, Yuyama K, Vannucchi H (1991) Bioavailability of vitamin-A from peach palm (Bactris gasipaes HBK) and from mango (Mangifera indica l) in rats. Nutr

Res 11(10):1167–1175CrossRef Yuyama LKO, Aguiar JPL, Yuyama K, Clement CR, Macedo SHM, Favaro DIT, PFT�� Alfonso C, Vasconcellos MBA, Pimentel SA, Badolato ESG, Vannucchi H (2003) Chemical composition of the fruit mesocarp of three peach palm (Bactris gasipaes) populations grown in Central Amazonia Brazil. Int J Food Sci Nutr 54(1):49–56PubMed Zambrana NYP, Byg A, Svenning J-C, Moraes

M, Grandez C, Balslev H (2007) Diversity of palm uses in the western Amazon. Biodivers Conserv 16:2771–2787CrossRef Zapata A (1972) Pejibaye palm from the pacific coast of colombia (a detailed chemical analysis). Econ Bot 26(2):156–159CrossRef Ziegler RG (1989) A review of epidemiologic evidence that carotenoids reduce the risk of cancer. J Nutr 119(1):116–122PubMed Zumbado ME, Murillo MG (1984) Composition and nutritive-value of pejibaye (Bactris gasipaes) in animal feeds. Rev Biol Trop 32(1):51–56PubMed”
“Introduction In recent decades, transportation agencies have become increasingly aware of the effects of roads, railroads and Suplatast tosilate other linear infrastructure on wildlife (Forman and Alexander 1998; Trombulak and Frissell 2000; Coffin 2007). Roads and traffic may increase mortality of wildlife due to wildlife-vehicle collisions, act as barriers to animal movement and migration, and affect both the amount and quality of wildlife habitat (Spellerberg 2002; Forman et al. 2003). Consequently, roads and road Transmembrane Transporters inhibitor networks potentially jeopardize the long-term persistence of wildlife populations, communities and ecosystems (van der Grift et al. 2003; Jaeger and Fahrig 2004; Fahrig and Rytwinski 2009; van der Ree et al. 2009; Benítez-López et al. 2010; Borda-de-Agua et al.