Palm uses in northwestern South America: a quantitative review.
IntroductionThe great and quantitatively dominant ethnobotanical importance of palms (Arecaceae) in comparison to other botanical families in tropical American forests is well documented (Prance et al., 1987; Pinedo-Vasquez et al., 1990; Phillips & Gentry, 1993; Galeano, 2000; Macia et al., 2001; Lawrence et al., 2005). Palms have great cultural and economic importance among rural indigenous and peasant populations in tropical America (Schultes, 1974; Bodley & Benson, 1979; Balick, 1984; Balslev & Barfod, 1987; Balde, 1988; DeWalt et al., 1999; Galeano, 2000; Macia, 2004; Paniagua-Zambrana et al., 2007; Brokamp et al., 2011), and numerous studies have described their essential role in covering basic needs for human subsistence, such as for food and house construction (L6pez-Parodi, 1988; Morcote-Rios et al., 1998; Coomes & Burt, 2001; Campos & Ehringhaus, 2003; Macia, 2004; PaniaguaZambrana et al., 2007). Their great importance is closely related to their ecological, morphological, physiological and bromatological characteristics, Palms are conspicuous and abundant in many different tropical forest types (Henderson et al., 1995; Macia & Svelming, 2005; Balslev et al., 2011) and they are distributed in all forest strata and soil types (Kahn & de Granville, 1992; Kahn & Henderson, 1999; Vormisto, 2002b; Balslev et al., 2010a; 2011). Palms have distinctive morphological and physiological characteristics: they have straight and generally un-branched stems, large pinnate leaves, a vascular system with living cells throughout the plant's lifespan, they produce many adventitious roots, and are highly durable (Balick, 1984; Tomlinson, 2006). Their fruits and seeds contain starch, essential amino acids, and oils that are rich in polyunsaturated fatty acids (Balick, 1984; Balre, 1988; Moraes et al., 1996; Olvera-Fonseca, 2004).
Their extensive use and relatively well known taxonomy have facilitated their utilisation as model organisms for analysing the influence of ecological and socioeconomic variables on interrelations between humans and plants in tropical American ecosystems (Uhl & Dransfield, 1987; Henderson, 1995; Henderson et al., 1995; Borchsenius et al., 1998; Moraes, 2004; Govaerts & Dransfield, 2005; Dransfield et al., 2008; Galeano & Bernal, 2010). Several studies have shown that humans tend to use to a higher degree those species that are widespread and conspicuous (Ruokolainen & Vormisto, 2000; Byg et al., 2006). However the most used species are not always the same as those with greatest ecological importance (Boom, 1986). Moreover, higher species diversity in one region does not necessarily imply a greater use by the local population (Byg et al., 2007). The most abundant species in an ecosystem are often used, although with different intensities, and some of the more important species are managed to obtain a better use of their products (Paniagua-Zambrana, 2005; Byg et al., 2006; Bernal et al., 2011). Palms are used more by human groups which have more limitations in their access to markets (Byg & Balslev, 2004; Macia, 2004; Byg & Balslev, 2006; Byg et al., 2007; Paniagua-Zambrana et al., 2007). Recent studies have shown that indigenous people usually posses greater ethnobotanical knowledge than other human groups (Campos & Ehringhaus, 2003; Byg & Balslev, 2004; De la Torre et al., 2008).
Despite the large number of publications on traditional use of palms in tropical America, at a local or regional scale, comparative studies presenting a general vision of the use of palms at a larger geographical scale, and comparing use patterns in different biogeographic regions, habitats, countries or human groups, have not been done so far. Here, we present an exhaustive revision of the use of palms in north-western South America, where an effort has been done to compile existing bibliographical references at the local scale and of limited diffusion. The specific aims of this compilation are: (a) to quantitatively evaluate the use of palms in north-western South America, comparing different ecoregions (the Amazon, Andes and Chocd) and countries (Colombia, Ecuador, Peru and Bolivia); (b) to compare palm use patterns in different ethnobotanical use-categories and subcategories; (c) to analyze differences in the use of palms among different human groups (indigenous, mestizos, afroamericans and colonos) and compare the knowledge between different indigenous groups; and (d) to identify the most important palm species for the local populations living in the tropical forests of the study region.
Methods
Study Area
We compiled ethnobotanical information for palms occurring in the Amazon and Andes of Colombia, Ecuador, Peru and Bolivia, and the Choc6 of Colombia and Ecuador (Fig. 1). The Amazon ecoregion was defined as the lowlands to the east of the Andes up to 1,000 m elevation (Rennet et al., 1990; Jorgensen & Ledn-Yfinez, 1999). Data for species existing in all broad forest types were included: both welldrained terra firme forests and floodplain forests, and poorly-drained swamp forests. The Andes ecoregion was defined as the montane forests on both slopes of the Andes above 1,000 m, including the forests of the inter-Andean valleys of Bolivia with lower precipitation (Beck et al., 1993). The Choc6 ecoregion was defined as the area of humid forests along the Pacific coast of Colombia and northern Ecuador.
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Bibliographical Search and Data Organization
A thorough bibliographic revision was performed to search for international and national publications for each of the four countries, including ethnographical publications with data on the uses of palms, when species identification was clear. Three categories of publications were selected. The first included publications based on original data gathered from fieldwork, including scientific papers, books, monographs, book chapters, and graduate, masters and doctoral theses. The second category included review publications for which we checked that data had not been previously published, in order to avoid duplication of information. The third type included publications based on herbarium material which included ethnobotanical information that was not included in any publications (Borchsenius et al., 1998; Moraes, 2004; Moreno Suarez & Moreno Suarez, 2006).
A database was constructed in Microsoft Access. For each publication, the following information was included (when available): scientific name of the species as it was published, country, ecoregion, human group, assignation to categories and subcategories of use, plant part used, and vernacular names. To unify the nomenclature of the scientific names, the world checklist of palms was followed (Govaerts & Dransfield, 2005; Govaerts et al., 2006). The only exception was Cero[C],lon peruvianum, which was recently described (Galeano et al., 2008), and therefore was not included in the checklist. The three broad habitat types in the Amazon ecoregion were lumped because most bibliographical references did not specify which of the three regions they referred to. Four human groups were recognized: (a) Indigenous, original population of a particular geographic region; (b) Mestizo, population of mixed origin, born from a father and mother of different race, generally white-indigenous; (c) Afroamerican, population of black race descendant of African slaves brought to America; in the study area they only live in the Choc6 of Colombia and Ecuador; and (d) Colono, native to an ecoregion different to the one where they presently live due to recent migrations (e.g. Andean people living in the Amazon). Those use-reports where no indication of human group was mentioned were classified as "Not identified." The Ecuadorean Quichua and Shuar indigenous groups living in the transition between the Amazon and the Andes ecoregions were considered Amazonian groups because the majority of existing literature referring to them is from that ecoregion. Mixed populations of two or more indigenous groups were considered as a single group for analysis, but were not computed as a different ethnic group.
All uses recorded from the literature were classified in 10 ethnobotanical categories that were further divided into subcategories (Table 1). When the ethnobotanical information was not classifiable within the previous subcategories, it was assigned to the subcategory "Other". In the Medicinal and Veterinary category we also used the term "Not Specified" when a medicinal use description contained insufficient information to assign the use to one of the described subcategories. The vernacular names of all palm species cited in the bibliography were compiled, independent of the existence of ethnobotanical information.
Data Analysis
All data analysis were performed at the species level and thus the ethnobotanical information obtained for infraspecific taxa (i.e., subspecies or varieties) were lumped into the corresponding species. Ethnobotanical data recorded only at the genus level (460 use-reports) were excluded from the analysis, and seven references recorded palm uses only at this level (Acosta-Solis, 1948; Forero, 1980; Toumon et al., 1986; Salick, 1989; Fujisaka & White, 1998; Vasquez, 2000; Bussmann & Sharon, 2006).
To analyse the uses of palms in different ecoregions, countries and human groups, the term "palm use" for a given species was defined as the use associated to a use category and use subcategory for a specific plant part. To analyse the abundance of palm uses, the term "use-report" was defined as the palm use described previously in one bibliographical reference.
To quantify the relative importance of the different use categories, the percentage of useful species for each category with respect to the total number of species used per ecoregion or country was used. In the case of the use subcategories, the percentage of useful species in each subcategory with respect to the total species used in the associated category was used.
To have an estimation of the ethnobotanical knowledge that exists in both different countries and ecoregions with respect to the total number of palm species, the percentage of useful species was calculated following the catalogue of Pintaud et al. (2008). To have an estimation of the number of indigenous groups with ethnobotanical information with respect to the existing total number of indigenous groups in the study area, the percentage of indigenous groups was calculated following Lewis (2009). In these latter calculations, the linguistic variants for the denomination of the same indigenous group were not considered.
To identify the most important useful species in each ecoregion, the Relative Importance (RI) index was calculated: RI-NUC+NT, where NUC=number of use categories in which a given species is used, divided by the total number of use categories of the most versatile species; NT=number of total use subcategories in which the cited species is found, divided by the total number of use subcategories that the most versatile species obtained (Bennett & Prance, 2000; Albuquerque et al., 2006). The maximum RI value that a species could obtain was 2. This index values the importance of the different species as a function of their versatility, without considering data relative to the number of bibliographic citations (Cartaxo et al., 2010).
Results
Palm Use by Ecoregions and Countries
A total of 194 useful palm species (representing 63% of the potentially existing species in north-western South America), 2,395 different uses, and 6,141 use-reports were found in the revision of 255 bibliographical references, including 95 palm use monographs (Table 2; Appendix). The average (+ SD) number of different uses per species was 12.3 ([+ or -] 18.7) although great variability was observed between different species. Ethnobotanical information was recorded for 54 indigenous groups, which represents 49% of the total indigenous groups living in the study area (Lewis, 2009; Fig. 1).
The Amazon was the ecoregion with the highest values in all the variables compared: 134 useful species (90% of those potentially present), 82% of total different uses, 84% of total use-reports, an average ([+ or -] SD) of 14.7 ([+ or -] 20.0) uses per species, and 81% of total bibliographic references found (Table 2). Ethnobotanical information was found for 48% of all indigenous groups living in the area.
Comparing the Amazon ecoregion in each of the four countries (Colombia, Ecuador, Peru and Bolivia) independently also gave the highest values in all the variables analysed (Table 2). The highest number of useful species, different uses and bibliographical references was found in the Peruvian Amazon, but the number of uses per species was the lowest there. In the Ecuadorean Amazon we found both the highest percentage of useful species and the highest percentage of indigenous groups studied, while the lowest percentages for these variables were found in the Amazon of Colombia and Peru.
In the Andes and Choc6 ecoregions similar results were found for many of the studied variables, including number of palm uses, percentage of useful species, and number of bibliographic references (Table 2). However, even if the Andes ecoregion was slightly more diverse in useful palm species than the Choc6 ecoregion (68 vs. 52), the average of different uses per species was highest in Choc6 (6.7 vs. 5.1), where we found a higher number of use-reports (569 vs. 439). In general, the Andes was the second ecoregion in relative importance for Ecuador, Peru and Bolivia, whereas in Colombia the Choc6 was more important than the Andes. The Andean region of Bolivia was the best studied of the four countries since in the Andes of Colombia, Ecuador and Peru no information was recorded for any indigenous group.
Colombia was the country with the highest number of useful palm species (105) and the highest number of indigenous groups for which ethnobotanical information about palms has been published (23), although the proportion of indigenous groups studied with respect to the total groups for the country was moderate (49%), and inferior only to Peru (Table 2). However, in Colombia the percentage of useful species in relation to palm species richness was the lowest of the four countries (48%), as was the average number of uses per species (7.8 [+ or -]10.1). Colombia was the country with the second lowest number of bibliographical references referring to palm uses, but the number of different palm uses and use-reports was comparatively high, only surpassed by Ecuador.
In Ecuador, the number of useful species found was slightly lower than for Colombia (103 vs. 105). Nonetheless, it was the country with the highest values for many of the variables compared: the highest number of different uses (936), use-reports (2010), percentages of useful species in relation to the palm species richness of the country (79%), percentage of indigenous groups studied (83%) and number of bibliographical references (81), including 31 palm monographs (Table 2).
Peru had intermediate values for most analyzed variables (Table 2). It was the country with the second highest proportion of useful species relative to the total palm species number in the country (76%), and also with respect to the number of bibliographical references with information on palm uses (74). And while it was the country with the second highest number of indigenous groups with published ethnobotanical information about palms (18), the percentage of indigenous groups studied (38%) was the lowest of the four countries.
Bolivia had the lowest values in most of the analyzed variables except for the average number of uses per species, which was the highest of the four countries (10.6+ 14.7) (Table 2). The percentage of useful species in relation to the total palm species richness in the country (74%) and the percentage of indigenous groups with published ethnobotanical palm information (61%) were the second most important. Concerning the published bibliographical references, a great number of palm use monographs were registered compared to other countries.
Palms in Different Use Categories and Plant Parts Used
In general, the use categories and subcategories with most useful species were the same as those with most use-reports. The main exceptions to this were (a) the Agroforestry subcategory in the Environmental Uses category, where the number of use-reports was frequently higher than the number of species found (e.g. overall 48% of the species and 53% of the use-reports; in Colombia 48% vs. 94%), as well as (b) in the Firewood subcategory in the Fuel category (e.g. in Colombia, especially in the Choc6 ecoregion, 88% of the species and 94% of the use-reports). Therefore, to facilitate the interpretation of data in Table 3, only percentages of useful species for different use categories and subcategories are shown.
The main uses of palms in north-western South America were in the categories Human Food (70%), Utensils and Tools (66%), Construction (63%) and Cultural Uses (56%) (Table 3). The categories Animal Food (37%), Medicinal and Veterinary (35%), Environmental Uses (35%) and Fuel (22%) had the lowest numbers of useful species. In the initially proposed Toxic category, there were no use-reports. All parts of the palms had some ethnobotanical use, although the most used parts among all use categories (except in Construction) were fruits, stem and leaves (Table 4). For 9% of the use-reports, the plant part used was not indicated.
At the ecoregion level, the percentages of palm uses were higher in the lowlands (the Amazon and Chocr) than in the Andes for the majority of the use categories (Table 3). In the Amazon, the relative importance of the different use categories was similar to the general pattern previously described, with the only exception of Medicinal and Veterinary, palms, which were more important than Animal Food (46% vs. 43%). The Choco ecoregion had the same pattern of palm use as the Amazon, except in the Environmental Uses category, which was more prevalent (35% vs. 29%). In the Andes, the general pattern of palm use described above was also found, but with some notable exceptions: the Construction category had greater relative importance in the Andes compared to the lowlands, the Environmental Uses category, such as in Chocr, had more relevance than in the Amazon, and the Utensils and Tools category was less important in the Andes than in it was in the lowlands.
At the country level, the categories Human Food, Construction, Utensils" and Tools and Cultural Uses were, in this order of importance, the ones that presented the highest percentages of useful species, except in Colombia, where Utensils' and Tools" was the most important category (62%) and Human Food occupied the fourth position (52%) (Table 3). In Colombia and Peru, the greater relative importance of the Medicinal and Veterinary category was notable compared to Ecuador and Bolivia, although the latter country had the highest percentage of use-reports for this category. The categories of Animal Food and Environmental Uses had varying importance in the different countries, without a recognizable pattern. Finally, the categories of Fuel and Other Uses were the least important in all countries.
Human Food. Palm uses in the different subcategories of Human Food were similar for all ecoregions and countries (Table 3; Appendix). Over 90% of the species were used as food or snack and more than 25% were used to prepare fermented or unfermented drinks, such as leche or chicha especially in the Amazon. Preparation of oils for human consumption was very important throughout the study region, though most prominent in the Choc6 (34%) and Bolivia (33%). The use of palms for food additives was more prominent in the Amazon (11%) compared to other ecoregions, and at the country level in Bolivia and Colombia (14% and 11%, respectively). The palm parts most often used in this category were fruits (61%), palm heart (20%) and seeds (12%) (Table 4).
Utensils and Tools. In all ecoregions and countries, most species (77%) were used to make several objects for domestic use, such as hammocks, fans, carrying bags, baskets or mats (Table 3; Appendix). The second most important activity was the construction of tools for hunting and fishing (56%), including bows, arrows, harpoons and different types of traps, although this category had lower importance in the Andes (27%). The manufacturing of tools for cultivation in their fields (chacras or chagras) and homegardens was more important in the lowlands than in the Andes, especially in Ecuador (20%). The use of palm leaves for wrapping food or other objects was mostly recorded in the Amazon of Ecuador and Peru. Rope manufacture was less important, but uniform, for all ecoregions and countries, except in the Colombian Andes and Choc6. The subcategory Other uses had high values because many use-reports simply described the use as 'handicrafts' or 'ivory' (for instance, the use of Phytelephas seeds which were also used as handicrafts), and therefore could not be precisely assigned to a particular subcategory. The most important palm parts used for utensils and tools were the stem (30%), leaves (20%) and immature spear leaves (11%) (Table 4).
Construction. In this category, most species (>76%) were used for thatching houses and for temporal sheds in all ecoregions and countries (Table 3; Appendix). In second place was the use of palms in the construction of different house parts, such as beams, walls, floors or materials for the roof. The use of palms for construction of canoes was particularly relevant in the Choc6 (14%) and the Amazon (7%), and for construction of bridges in the Amazon (9%). In the subcategory Other Uses, many use-reports only mentioned 'construction', which is a general term, for which reason the use could not be assigned with precision to a particular subcategory. The most used palm parts were the leaves (53%) and the stem (36%) (Table 4).
Cultural Uses. The most important cultural use in all ecoregions and countries was for ritual purposes, including festivals and feasts, particularly in the Andes (62%), and among the countries in Ecuador (56%) and Bolivia (52%) (Table 3; Appendix). In the Amazon (57%) and particularly in Colombia (60%), the recreational use of palms for the manufacture of musical instruments and toys, and for the preparation of ashes from several palm parts to be used in the traditional consumption of tobacco (Nicotiana spp.) and coca leaves (Erythroxylum coca) were of great importance. The use of palms for personal adornment, such as necklaces, bracelets, armbands, pectorals or earrings, had great importance in the Amazon (51%), and at the country level in Ecuador (50%). In the manufacture of cloth and accessories, like hats or buttons, and in the preparation of cosmetics, the highest importance was recorded in the Amazon, and at the country level in Bolivia (37% and 48% for the first subcategory and 33% and 48% for the second, respectively). The use of palms to produce natural dyes was minor, but it was registered in all ecoregions and countries, and was of particular importance in the Choc6 (17%). The most used palm parts were the entire leaves (18%), seeds (17%), and the fruits (14%) (Table 4).
Animal Food. The highest percentage of species used for Animal Food were used as wildlife attractant for hunting (72%), particularly in the Amazon (79%), and among the countries in Ecuador (91%) and Colombia (76%) (Table 3; Appendix). However, in the Andes and Choc6 the use of palms as fodder had greater importance (57% and 50% respectively), and particularly in Bolivia (50%). The use of palms as fish bait had high values in the Amazon (30%) and in Peru (52%). The fruits were clearly the palm part most used (77%), followed by the seeds (5%) and leaves (4%) (Table 4).
Medicinal and Veterinary. Medicinal uses were found in all the proposed subcategories and were especially important in the Amazon, where the highest percentages were recorded for most subcategories (Table 3; Appendix). The highest percentage of medicinal species (56%) was registered for the treatment of ailments of the digestive system (e.g. stomach pains and diarrhoea), particularly in the Andes and the Amazon (55% and 54%, respectively) and, among the countries, for Peru (64%). The treatment of respiratory ailments, in particular colds and catarrh, were very important in the Amazon (39%) and Bolivia (48%). The use of palms to treat general common ailments of nonspecific character, such as headaches, general discomfort and body pains, was the subcategory with the third highest percentage of useful species (34%) in particular in the Amazon, and among the countries in Peru and Bolivia. Similarly, the treatment of infectious and parasitic diseases was most prominent in the Amazon (33%) and in Peru (42%). The percentages of palms used for skin and subcutaneous ailments were higher in the Amazon and Andes than in the Choc6, and among countries its use was highest in Bolivia (38%). The treatment of ailments and injuries of the muscular-skeletal system such as traumatisms, bone fractures, dislocations or sprains were more relevant in the Amazon (23%) and in Bolivia (33%). Palms were also used as antidotes against snakebites, scorpion stings and ant bites and stings, especially in the Amazon (21%), and in Colombia and Bolivia (24% in both cases). The percentage of palm species used for treating diseases of the reproductive system and for sexual health was higher in Choc6 (25%) than in the other ecoregions, and among countries in Peru and Bolivia. Palms were also used to treat less well defined diseases, such as aire, evil eye, and arrebato, especially in the Choc6 (25%) the Andes (18%), and in Bolivia (19%). For the treatment of blood and cardiovascular system ailments, the highest percentage of species was reported for the Choc6 (17%) and in Bolivia (14%). The percentage of species used in both diseases and ailments of the urinary system, like cystitis, and the treatment of problems relating to pregnancy, birth and puerperium was highest in the Andes in both cases (27% and 18%, respectively). For the treatment of dental problems, diseases of the endocrine system, metabolic and nutritional problems, and for veterinary use, medicinal palm species were only reported in the Amazon, and the greatest percentage was registered in Bolivia (10% in all cases, except in the subcategory Veterinary Uses which was 5%). For treating diseases and ailments of the nervous system, mental health and sensory system, the highest percentage of useful species was found in the Andes (9% in both cases) and in Ecuador (9% and 6%, respectively). The subcategory Other Uses included species with medicinal uses which could not be assigned to a described subcategory, for example for the treatment of cancer, hernia, or when the nature of an illness was not specified. The most used plant parts in popular medicine were the roots (31%), fruits (24%) and seeds (12%) (Table 4).
Environmental Uses. The main use in the category Environmental Uses" was as ornamental plants for all ecoregions and countries except Peru, with special importance in the Andes (68%) and among the countries in Ecuador (67%) (Table 3; Appendix). The use of palms in agroforestry systems with different degrees of management ranked second, particularly in the Amazon (58%) and in Peru (71%), where it was the most important use. The use of palms as natural barriers and to delimit properties was used in all ecoregions and especially in Bolivia and Peru. The
use of palms to improve soils was only registered in the Amazon of Peru and Bolivia. In this category the whole plant (65%) and the stem (21%) were mostly used (Table 4).
Fuel. The majority of the species were used for firewood in all countries and ecoregions, especially in the Amazon (85%) and among the countries in Bolivia and Colombia (89% and 88%, respectively) (Table 3; Appendix). The palms had notable importance as fire starters and as torches, candles, and lamps, particularly in the Chocr. Within the subcategory Other Uses, the use of palm leaves for burning and water-proofing canoes was important in the Amazon, particularly in Peru. The predominant parts used were the stem (52%), leaves (22%) and the fruits (8%) (Table 4).
Other Uses. The highest percentage of useful palms in all ecoregions and countries was related to the use of the larvae of the Rhyncophorus palmarum (Coleoptera) for human food (66% of total species), medicinal use, and as fish bait (Table 3; Appendix). These larvae develop mainly in rotting palm stems. The remaining uses are miscellaneous. The plant parts mostly used were the stem (65%), seeds (8%) and fruits (6%) (Table 4).
Palm Uses by Different Human Groups
Indigenous groups clearly used palms more prominently than other human groups. They presented the highest palm use values: number of useful species (129), different uses (1,555), use-reports (3,713), and higher average number of uses per species (12.1 [+ or ] 16.7), although they were also the best studied human group (166 bibliographical references) (Table 5). The Amazon was the ecoregion with the highest values in all countries and for all human groups, except for the mestizos in Ecuador. In the Chocr, the indigenous groups recorded higher values for all variables compared to the Andes of Colombia and Ecuador, although in Ecuador the differences between these ecoregions were small.
The mestizos were the second human group in terms of palm use values (Table 5). The Amazon was the ecoregion with the highest values, with the exception of Ecuador, where the Andes had a greater importance. Peru was the country with the highest number of bibliographical references. No use-report was found for mestizos in the Choc6 ecoregion or Colombia.
A greater number of useful pahns were registered for the afroamericans, when compared to colonos (Table 5). Colombia reported higher values than Ecuador for all the variables analyzed, and these values were similar to those registered for the Colombian indigenous groups of the same ecoregion, despite having a lower number of references.
The colonos presented the lowest values of all groups compared in all countries, except for the average number of uses per species, which was slightly higher than for afroamericans (Table 5). Most information was registered in the Amazon, and among the countries in Colombia and Ecuador.
Finally, it is worth mentioning that for all ecoregions and countries very high values were registered for unidentified human groups, since the bibliographical information was not precise. Curiously, they registered the highest number of useful species (170) (Table 5).
Palm Uses by Indigenous Groups
Ethnobotanical information concerning palms was found for 54 indigenous groups: 47 in the Amazon ecoregion, two in the Andes, and five in the Choc6 (Fig. 1; Table 2). There was great variation in the ethnobotanical knowledge of palms for the different indigenous groups, and the greatest knowledge was observed in Ecuador for all three ecoregions (Table 6). In general, the most studied indigenous groups were also those with the greatest observed ethnobotanical knowledge. For example, for some indigenous groups (e.g. Quichua, Huaorani or Shuar in Ecuador) many useful palm species, different uses and use-reports were found, but this may be because they were particularly well studied ([greater than or equal to]13 bibliographical references per group). However, other indigenous groups (e.g. Muinane of Colombia or Cocama of Peru) also had many useful palm species, different uses and use-reports, but these were described in just two bibliographical references.
A total of 1,933 vernacular palm names were registered (including orthographic variants), corresponding to 178 palm species. Of these names, 33% were in Spanish (158 species) and 67% in different indigenous languages (130 species).
Outstanding Useful Palm Species by Ecoregions
In general, the species with the highest relative importance values also had the highest number of palm uses, use-reports and bibliographical references (Table 7). Five species were found as the most important in all three ecoregions: Bactris gasipaes, Iriartea deltoidea, Oenocarpus bataua, O. mapora and Socratea exorrhiza. In the Amazon ecoregion, the most important genera were Astrocaryum, Attalea, Oenocarpus and Phytelephas, each with more than one species with the highest relative importance whereas in the Choc6 three of them, Attalea, Oenocarpus and Phywlephas, were among the most important. In contrast, in the Andes the genera Ceroxylon, Oenocarpus and Parajubaea were the most important. In the Amazon and Choc6 ecoregions, the most versatile species were used in all countries, but in the Andes the most important species did not have such a broad geographical range of use, with the exception of Bactris gasipaes, which was registered in all four countries.
Discussion
Areeaceae is probably the most important plant family in the Neotropics, in terms of use diversity and abundance. Palms are widely used for a great number of purposes throughout all ecoregions and by all human groups in north-western South America. The use of palms has been documented in several monographs with local or national scope (e.g. Balslev & Barfod, 1987; Bemal, 1992; Borchsenius et al., 1998) and in numerous cthnobotanical studies with diverse indigenous groups (e.g. Boom, 1986; Kronik, 2001; Macia, 2004), mestizos (e.g. Mejia, 1988; Stagegaard et al., 2002; Balslev et al., 2008), afroamericans (e.g. Galeano, 2000), and colonos (e.g. Flores Paitfin, 1998). The present quantitative revision underlines the great importance of comparative ethnobotanical studies at a regional geographic scale, and call attention to many different uses and species consistently shared between different human groups across the western Amazon, the Choc6 and the Andes ecoregions.
The use of palms is not random since their main uses are the same in different ecoregions and countries: palms are mostly used for human food, for manufacture of objects and utensils of domestic use, and for the construction of houses. This underlines their fundamental role in satisfying basic subsistence needs of rural indigenous and peasant population of north-western South America, in the same way that previous studies have demonstrated the importance of palms on local scales (Galeano, 2000; Narvaez et al., 2000; Gertsch et al., 2002; Campos 8,: Ehringhaus, 2003; Macia, 2004; Paniagua-Zambrana et al., 2007). Palms also have great importance in different cultural practices, which also confirms at regional scales the results of previous papers showing the cultural importance of palms for some ethnic groups in South America (Schultes, 1974; Bodley & Benson, 1979; Gertsch et al., 2002).
The enormous importance of palms in the Amazon can be explained by two complementary factors. On the one hand, their high species diversity allows access to a wide array of potential resources (Begossi, 1996; De la Torre et al., 2009; Brokamp et al., 2011), and on the other hand, the great diversity of indigenous groups favours a highly distinctive ethnobotanical knowledge (Campos & Ehringhaus, 2003). Although the Amazon was clearly the best studied ecoregion, ethnobotanical studies (that include palms) have so far only been conducted among less than 50% of the remaining indigenous groups. Likewise, in the Andes and the Choc6, ethnobotanical knowledge of palms is even more restricted, and for more than 50% of the species in both ecoregions, no uses have been documented.
We found that Ecuador is the best studied of the four countries in all ecoregions. There, and to a lesser degree in Bolivia, the percentage of useful palm species and the percentage of indigenous groups with documented palm uses were higher, which indicates that the use of palms is comparatively better documented than in Peru and Colombia. The high average number of uses per species recorded in Bolivia could be explained by the higher number of palm monographs from that country. Following this thinking, Peru and Colombia would be less known in palm ethnobotany than the two other countries. In Peru, the high number of indigenous groups for which we do not have ethnobotanical information underlines that the available data on palm uses remains incomplete. In Colombia a very low percentage of useful species was recorded, even though it is the country with the highest species richness. All this points to the need for more studies to complement the ethnobotanical knowledge on palms in all three ecoregions, but particularly in the Choc6 where a great richness of potentially useful species has been reported (Galeano & Bernal, 2010).
Previous studies suggested that indigenous people possess a greater knowledge about the uses of palms than mestizos or colonos possess in north-western South America (Campos & Ehringhaus, 2003; Byg & Balslev, 2004; Byg et al., 2007) and our paper reinforces this conclusion. This is the result of a complex set of interactions between diverse factors, including: (a) historical ones, since a long occupation of a territory facilitates the development of extensive ethnobotanical knowledge, (b) cultural ones, based on hundreds of years of orally transmitted traditional ecological knowledge, and (c) economic ones, in particular by the reduced degree of access to markets which mean they use palms for subsistence and are not able to purchase palm products substitutes (Alcorn, 1981; Balre, 1994; Byg & Balslev, 2004; Byg et al., 2007; Paniagua-Zambrana et al., 2007). Moreover, indigenous knowledge is highly differentiated, even between ethnic groups that occupy nearby geographical areas and share similar resources such as palms (Campos & Ehringhaus, 2003), or medicinal plants (Shepard, 2004; Collins et al., 2006). In general, the best studied indigenous groups had a richer and more diversified ethnobotanical knowledge. But, not only the number of publications existing for each group is important, so is the existence of monographs on palms that contribute to a greater degree to the number of useful species and different uses. This again underlines the need for more ethnobotanical studies focusing on palms, as information is nonexistent for over 50% of the indigenous groups in north-western South America.
The traditional knowledge of mestizos should not be undervalued, since it is equally diverse and even complementary to that of indigenous groups in several use categories (see also De la Torre et al., 2008). Frequently, mestizos have a long settlement history, which allow them to develop a profound ecological knowledge in their environment, which may be similar to those of various indigenous groups. In our study, the number of palm uses for mestizo people could probably be higher, because many publications do not mention explicitly the human group studied, and it is likely that many of these publications refer to mestizos.
The Colombian afroamericans, who have been better studied than the Ecuadorean afroamericans, had a similar level of knowledge of palms as did indigenous groups in the Choc6 ecoregion. This can be explained by the group's long history of residence and their prolonged contact with indigenous people in this region (Mendoza et al., 1995).
Some palm species have an enormous importance due to their large number of different uses. This uneven distribution in their uses has also been registered in previous studies (Campos & Ehringhaus, 2003; Macia, 2004; Byg et al., 2006; Paniagua-Zambrana et al., 2007; Balslev et al., 2010b). Such species are often trees that are relatively abundant in the different habitats, due to their wide ecological amplitude (Ruokolainen & Vormisto, 2000; Byg et al., 2006; Balslev et al., 2011). The preference for certain uses can be interpreted as the result of a number of factors, including easy accessibility to the species, larger quantities of resources available, and the potentially greater sustainability of their use under minimum management (Byg et al., 2006; Bernal et al., 2011). These multi-use species play a fundamental role in the local subsistence strategies and represent key cultural species (Garibaldi & Turner, 2004; Balslev et al., 2010b).
The unequal number of bibliographic references and monographs that refer to the different variables analyzed (ecoregions, countries, human groups, indigenous groups, and palm species), certainly limits the strength of the conclusions that can be drawn. Nevertheless, the variables with higher use-reports showed a more intense and diversified use of palms.
As a result of the experience gained in this palm use revision, we suggest a more precise ethnobotanical data collection that would include: (a) making an effort to identify plants to the species level; (b) writing vernacular names carefully and indicating the language in each case; (c) gathering information from different uses as completely as possible in order to subsequently classify uses within at least two levels of utility (category and subcategory); (d) noting the plant part used for each different use; (e) specifying the human group and/or ethnic group from which the information was gathered; (f) obtaining detailed geographical information of the study area, including forest types or habitats; and lastly, (g) in the case of medicinal species, writing precisely the medicinal indication, mode of preparation and ways of administration for each case.
Acknowledgements We kindly thank Joaquina Alban, Rodrigo Bernal, Roxanna Castaneda, Lucia de la Torre, Gloria Galeano, Eva Ledezma, and Laura Mesa for their assistance in searching for bibliographical references, Bob Allkin, Bill Baker and Anders Barfod for their help in the construction of our database, and Patricia Balvanera, Rodrigo Berual, Jamie Nicole Cotta, and Lucia de la Torte for their helpful comments on an earlier draft of the manuscript. This study was funded by European Union, 7'h Framework Programme (contract no. 212631) for which we are grateful. Henrik Balslev also acknowledges support from the Danish Council for Independent Research--Natural Sciences (grant no. 10-83348).
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DOI 10.1007/s12229-011-9086-8
Manuel J. Macia (1,5) * Pedro J. Armesilla (1) * Rodrigo Camara-Leret (1) * Narel Paniagua-Zambrana (2) * Soraya Villalba (3) * Henrik Balslev (4) * Manuel Pardo-de-Santayana (1)
(1) Departamento de Biologia, Area de Botanica, Universidad Autonoma de Madrid, Calle Darwin 2, ES28049 Madrid, Spain
(2) Herbario Nacional de Bolivia, Universidad Mayor de San Andres, Campus Universitario, Cota Cota calle 27, Casilla 10077--Correo Central, La Paz, Bolivia
(3) Royal Botanic Gardens, Kew, Richmond, Surrey TW9 3AE, United Kingdom
(4) Department of Biological Sciences. Ecoinformatics & Biodiversity Research Group, Aarhus University, Build. 1540, Ny Munkegade 114, DK-8000 Aarhus C, Denmark
(5) Author for Correspondence; e-mail: manuel.macia@uam.es
Table 1 Description of use categories and subcategories in the present review Use category Use subcategory Description Animal Food Fish Bait Bait for fishing Fodder Food for domestic animals Wildlife Attractant Palms that provide food for mammals and whose location constitutes preferential areas for hunting Construction Bridges Materials to bridge watercourses Houses Houses and other constructions such as temporary camps, animal yards Thatch House thatching and other constructions Transportation Canoes, rafts, oars and other materials for sealing Other Uses not classifiable within the previous subcategories, for example stems used as posts for telephone lines and gutters to transport water Cultural Uses Clothes and Accessories Articles of clothing and accessories such as hats Cosmetic Beauty products, including perfumes, oils, shampoo, and other hair care products Dyes Dyeing of diverse materials (vegetables) and as body paint Personal Adornment Necklaces, bracelets, earrings, armbands, pectorals, anklets Recreational Musical instruments, toys, ashes as additives to the consumption of tobacco and coca leaves Ritual Uses related to myth-religious aspects, including festivals and feasts, construction of coffins, to drive away feared animals, sorcery Other Uses not classifiable under the previous subcategories Environmental Agroforestry Palms that are part of Uses agroforestry systems with Fences different management degrees Delimitation of properties, barriers Ornamental Palms cultivated for ornamental purposes Soil Improvers Fertilizers, edaphic protectors and agents against soil erosion Fuel Firewood Wood to make fire Fire Starter Combustion starters Lighting Lamps, torches and candles Other Uses not classifiable within the previous subcategories, for example for waterproofing canoes Human Food Beverages Elaboration of unfermented or fermented drinks Food Edible, generally with little preparation Food Additives Ingredients used in the preparation and processing of foods Oils Edible fats Medicinal and Blood and Anemia, cardiovascular Veterinary Cardio-vascular System problems and ailments, cardiac diseases, varicose veins, hypertension, hypotension, haemorrhoids Cultural Diseases and Ailments or disorders of Disorders magic-religious origin recognized by a specific culture, like mal aire Use category Use subcategory Description (`bad air'), arrebato (`outburst'), Dental Health susto, huarana Caries, tooth pains, fillings, dental hygiene Digestive System Carminative, colics, flatulence, emetic, indigestion, purgative, gastric or intestinal ulcers, diarrhea, laxatives, liver and vesicular disorders, hepatitis Endocrine System Diabetes General Ailments with General ailments like body Unspecific Symptoms pains, general discomfort, weakness, headache, fever Infections and Malaria, leishmaniasis, Infestations measles, antihelminthic, louse, fleas, chiggers, scabies Metabolic System and Obesity, weight loss Nutrition Muscular-Skeletal Rheumatism, twists, System fractures, sciatic, lumbalgia Nervous System and Migraine, mental Mental Health disorders, epilepsy, paralysis, nervous disorders Poisoning Snakebites, scorpion stings, rays, spiders, insects Pregnancy, Birth and Gestation, haemorrhage, Puerperium childbirth, postnatal, lactation, abortive, postpartum Reproductive System Menstruation, fertility, and Reproductive venereal diseases, Health prostrate, impotence, menopause, aphrodisiacs, contraceptives Respiratory System Flu, cold, loss of voice, bronchitis, pneumonia, expectorant, cough Sensory System Eye infections, cataracts, loss of sight or smell, deafness, ear infection Skin and Subcutaneous Acne, boils, eczemas, Tissue bums, extraction of spines stuck on the skin Urinary System Diuretic, kidney stones, urinary incontinence, urinary infections, cystitis Veterinary Treatment of diseases or ailments for domestic animals Not Specified Medicinal use or with pharmacological properties, but with insufficient information to assign to one of the described subcategories Other Uses not classifiable within the previous subcategories, for example tumours, cancer, anaesthetic Toxic Fishing Fish poison Hunting Poison for hunting Utensils and Domestic Utensils Baskets, fans, hammocks, Tools bags, domestic furniture, air freshener Hunting and Fishing Bows, arrows, blowpipes, Tools harpoons, fishing nets, hunting traps Labour Tools Agricultural or domestic tools like spinners, machetes and lubricants of these materials Rope Manufacturing of ropes and moorings Wrappers Wrappers for materials and foods Other Uses not classifiable within the previous subcategories, for example insect repellents Other Uses Miscellaneous Uses not classifiable within the previous categories. Indirect use of palms: insect larvae feeding on rotting stems used as food, medicine or bait Table 2 Palm uses in the Amazon and Andes ecoregions of Colombia, Ecuador, Peru and Bolivia, and in the Choco ecoregion of Colombia and Ecuador Country/Ecoregion Useful Palm uses Palm use-reports species All countries 194 2,395 6,141 Amazon 134 1,972 5,144 Andes 68 344 439 Choco 52 347 569 Colombia 105 814 1,429 Amazon 70 615 1,049 Andes 18 35 39 Choco 38 225 341 Ecuador 103 936 2,010 Amazon 62 676 1,494 Andes 52 240 295 Choco 30 167 228 Peru 96 785 1,390 Amazon 93 772 1,369 Andes 4 19 21 Bolivia 62 655 1,348 Amazon 54 603 1,267 Andes 13 77 84 Country/Ecoregion Average [+ or -] SD Percentage of useful of palm uses per species/Potential species total species All countries 12.3 [+ or -] 18.7 63.2 Amazon 14.7 [+ or -] 20.0 89.9 Andes 5.1 [+ or -] 6.0 52.7 Choco 6.7 [+ or -] 7.3 49.0 Colombia 7.8 [+ or -] 10.1 47.5 Amazon 8.8 [+ or -] 10.6 67.6 Andes 1.9 [+ or -] 1.2 19.8 Choco 5.9 [+ or -] 5.7 43.2 Ecuador 9.1 [+ or -] 11.9 79.4 Amazon 10.9 [+ or -] 12.3 91.2 Andes 4.6 [+ or -] 5.3 82.5 Choco 5.6 [+ or -] 5.2 44.6 Peru 8.2 [+ or -] 10.1 75.6 Amazon 8.3 [+ or -] 10.1 87.7 Andes 4.8 [+ or -] 3.4 9.1 Bolivia 10.6 [+ or -] 14.7 73.8 Amazon 11.2 [+ or -] 14.6 85.7 Andes 5.9 [+ or -] 6.7 43.3 Country/Ecoregion Indigenous groups with Bibliographical ethnobotanical information references (Percentage of indigenous (Palm monographs) groups with info/Total indigenous groups) All countries 54 (49.1) 255 (95) Amazon 47 (47.5) 202 (69) Andes 2 (28.6) 40 (27) Choco 5 (83.3) 38 (20) Colombia 22 (48.9) 63 (20) Amazon 19 (48.7) 41 (12) Andes -- 6 (5) Choco 3 (75.0) 25 (11) Ecuador 10 (83.3) 81 (31) Amazon 7 (87.5) 59 (17) Andes -- 20 (12) Choco 3 (75.0) 13 (10) Peru 18 (38.3) 74 (28) Amazon 18 (38.3) 70 (26) Andes -- 4 (2) Bolivia 11 (61.1) 47 (22) Amazon 10 (58.8) 41 (17) Andes 2 (100) 11 (9) Total number of species in each ecoregion and country was obtained from Pintaud et al. (2008), and total number of indigenous groups from Lewis (2009) Table 3 Percentages of useful palm species by different use categories and subcategories in tropical forests of north-western South America, broken down by ecoregion and country. Total percentages of each category (in bold) were calculated relative to the total usefid species registered for each ecoregion and country. The percentages for the different subcategories were calculated relative to the total useful species registered in each of the categories by ecoregion and country Use category/Subcategory Total Ecoregion Amazon Andes Choco Human Food 69.6 76.9 57.4 61.5 Food 95.6 95.1 97.4 93.8 Beverages 41.5 44.7 25.6 34.4 Oils 20.0 20.4 10.3 34.4 Food Additives 8.9 10.7 5.1 6.3 Utensils and Tools 65.5 73.9 32.4 57.7 Domestic 77.2 81.8 86.4 53.3 Hunting and Fishing 55.9 63.6 27.3 46.7 Labour Tools 17.3 17.2 4.5 20.0 Wrappers 13.4 16.2 4.5 -- Rope 11.8 9.1 9.1 13.3 Other 34.6 26.3 18.2 66.7 Construction 63.4 70.1 48.5 55.8 Thatch 83.7 86.2 87.9 82.8 Houses 63.4 60.6 57.6 58.6 Transportation 8.9 7.4 3.0 13.8 Bridges 8.1 8.5 3.0 3.4 Other 21.1 25.5 3.0 17.2 Cultural Uses 55.7 59.0 42.6 34.6 Ritual 49.1 40.5 62.1 61.1 Recreational 45.4 57.0 13.8 33.3 Personal Adornment 39.8 50.6 6.9 16.7 Cloth and Accessories 34.3 36.7 24.1 27.8 Cosmetic 25.0 32.9 13.8 11.1 Dyes 9.3 8.9 3.3 16.7 Other 9.3 12.7 -- -- Animal Food 36.6 42.5 20.6 19.2 Wildlife Attractant 71.8 78.9 42.9 50.0 Fodder 38.0 31.6 57.1 50.0 Fish Bait 26.8 29.8 -- 20.0 Medicinal and Veterinary 35.1 45.5 16.2 23.1 Digestive System 55.9 54.1 54.5 33.3 Respiratory System 38.2 39.3 18.2 16.7 General Ailments with 33.8 37.7 -- 8.3 Unspecified Symptoms Infections and Infestations 30.9 32.8 18.2 -- Skin and Subcutaneous Tissue 26.5 27.9 27.3 8.3 Muscular-Skeletal System 22.1 23.0 9.1 8.3 Poisoning 19.1 21.3 9.1 -- Reproductive System and 16.2 14.8 18.2 25.0 Reproductive Health Cultural Diseases and Disorders 14.7 13.1 18.2 25.0 Blood and Cardio-Vascular 11.8 9.8 -- 16.7 System Urinary System 8.8 8.2 27.3 8.3 Pregnancy, Birth and 8.8 9.8 18.2 -- Puerperium Dental Health 7.4 8.2 -- -- Endocrine System 7.4 8.2 -- -- Nervous System and Mental 7.4 6.6 9.1 -- Health Metabolic System and 4.4 4.9 -- -- Nutrition Sensory System 4.4 1.6 9.1 8.3 Veterinary 2.9 3.3 -- -- Not Specified 35.3 36.1 36.4 25.0 Other 5.9 6.6 -- -- Environmental Uses 34.5 29.4 36.8 34.6 Ornamental 62.7 57.5 68.0 55.6 Agroforestry 47.8 57.5 40.0 33.3 Fences 34.3 37.5 36.0 22.2 Soil Improvement 4.5 7.5 -- -- Fuel 22.2 24.6 17.6 9.6 Firewood 72.1 84.8 58.3 40.0 Fire Starter 23.3 21.2 16.7 20.0 Lighting 18.6 9.1 25.0 40.0 Other 9.3 12.1 -- -- Other uses 22.7 29.1 8.8 17.3 Use category/Subcategory Country Colombia Ecuador Peru Human Food 52.4 64.1 75.0 Food 96.4 95.5 94.4 Beverages 32.7 37.9 34.7 Oils 27.3 13.6 12.5 Food Additives 10.9 4.5 4.2 Utensils and Tools 61.9 58.3 56.3 Domestic 64.6 75.0 81.5 Hunting and Fishing 63.1 65.0 48.1 Labour Tools 9.2 20.0 13.0 Wrappers 7.7 15.0 13.0 Rope 13.8 10.0 9.3 Other 43.1 30.0 16.7 Construction 56.2 63.1 67.7 Thatch 76.3 86.2 83.1 Houses 44.1 47.7 66.2 Transportation 5.1 7.7 6.2 Bridges 1.7 4.6 6.2 Other 32.2 4.6 9.2 Cultural Uses 55.2 48.5 37.5 Ritual 44.8 56.0 16.7 Recreational 60.3 20.0 25.0 Personal Adornment 32.8 50.0 25.0 Cloth and Accessories 22.4 24.0 36.1 Cosmetic 10.3 26.0 33.3 Dyes 3.4 10.0 8.3 Other 5.2 8.0 13.9 Animal Food 20.0 44.7 23.9 Wildlife Attractant 76.2 91.3 30.4 Fodder 19.0 21.7 26.1 Fish Bait 28.6 10.9 52.2 Medicinal and Veterinary 27.6 31.1 34.4 Digestive System 31.0 37.5 63.6 Respiratory System 20.7 31.3 18.2 General Ailments with 6.9 18.8 42.4 Unspecified Symptoms Infections and Infestations 20.7 15.6 42.4 Skin and Subcutaneous Tissue 6.9 21.9 12.1 Muscular-Skeletal System 10.3 12.5 15.2 Poisoning 24.1 3.1 9.1 Reproductive System and 6.9 9.4 21.2 Reproductive Health Cultural Diseases and Disorders 10.3 12.5 3.0 Blood and Cardio-Vascular 6.9 3.1 9.1 System Urinary System 13.8 6.3 6.1 Pregnancy, Birth and 3.4 12.5 12.1 Puerperium Dental Health 6.9 6.3 3.0 Endocrine System -- -- 9.1 Nervous System and Mental -- 9.4 6.1 Health Metabolic System and 3.4 -- -- Nutrition Sensory System -- 6.3 -- Veterinary -- -- 3.0 Not Specified 27.6 43.8 24.2 Other -- 6.3 6.1 Environmental Uses 25.7 32.0 25.0 Ornamental 48.1 66.7 37.5 Agroforestry 48.1 39.4 70.8 Fences 18.5 27.3 41.7 Soil Improvement -- -- 8.3 Fuel 16.2 27.2 7.3 Firewood 88.2 75.0 42.9 Fire Starter 11.8 21.4 28.6 Lighting -- 21.4 -- Other -- 10.7 28.6 Other uses 21.9 14.6 28.1 Use category/Subcategory Country Bolivia Human Food 67.7 Food 90.5 Beverages 40.5 Oils 33.3 Food Additives 14.3 Utensils and Tools 53.2 Domestic 90.9 Hunting and Fishing 39.4 Labour Tools 9.1 Wrappers 9.1 Rope 12.1 Other 24.2 Construction 56.5 Thatch 80.0 Houses 62.9 Transportation 2.9 Bridges 5.7 Other 20.0 Cultural Uses 50.0 Ritual 51.6 Recreational 41.9 Personal Adornment 32.3 Cloth and Accessories 48.4 Cosmetic 48.4 Dyes 6.5 Other 12.9 Animal Food 35.5 Wildlife Attractant 63.6 Fodder 50.0 Fish Bait 9.1 Medicinal and Veterinary 33.9 Digestive System 42.9 Respiratory System 47.6 General Ailments with 47.6 Unspecified Symptoms Infections and Infestations 9.5 Skin and Subcutaneous Tissue 38.1 Muscular-Skeletal System 33.3 Poisoning 23.8 Reproductive System and 19.0 Reproductive Health Cultural Diseases and Disorders 19.0 Blood and Cardio-Vascular 14.3 System Urinary System 14.3 Pregnancy, Birth and 9.5 Puerperium Dental Health 9.5 Endocrine System 9.5 Nervous System and Mental -- Health Metabolic System and 9.5 Nutrition Sensory System 4.8 Veterinary 4.8 Not Specified 33.3 Other -- Environmental Uses 37.1 Ornamental 52.2 Agroforestry 52.2 Fences 43.5 Soil Improvement 4.3 Fuel 14.5 Firewood 88.9 Fire Starter 11.1 Lighting 22.2 Other -- Other uses 14.5 Table 4 Percentages of use-reports for the different palm parts used in each category in tropical forests of north-western South America Plant part Human Food Utensils and Tools Construction Fruit 60.6 2.4 -- Stem 0.8 30.0 36.1 Entire leaf 0.1 20.2 53.4 Seed 11.6 4.4 -- Palm heart 19.5 0.5 -- Root 0.2 3.2 -- Entire plant -- -- -- Spear leaf -- 10.6 0.1 Petiole -- 5.1 0.5 Leaf rachis -- 4.8 0.2 Leaf sheath -- 3.1 -- Bract -- 1.7 -- Inflorescence 0.3 0.7 -- Flower 0.6 -- -- Spine -- 0.4 -- Infructescence <0.1 0.2 -- Not specified 6.3 12.6 9.7 Plant part Cultural Animal Food Medicinal and Veterinary Fruit 13.7 76.5 23.8 Stem 7.7 0.9 4.0 Entire leaf 17.6 4.3 4.5 Seed 17.4 5.2 11.6 Palm heart 3.1 2.2 9.4 Root 2.5 -- 31.3 Entire plant 7.4 -- 0.4 Spear leaf 8.3 -- -- Petiole 1.3 -- 0.2 Leaf rachis 1.3 -- 0.2 Leaf sheath 0.5 -- 0.2 Bract 3.5 -- -- Inflorescence 2.9 0.9 1.0 Flower 0.6 0.9 2.4 Spine 1.3 -- 1.4 Infructescence 0.3 -- 0.2 Not specified 10.5 9.1 9.4 Plant part Environmental Fuel Other Uses Total Fruit 1.1 7.8 6.0 25.1 Stem 20.7 52.3 64.7 18.1 Entire leaf 5.2 21.9 1.3 16.7 Seed 2.9 7.8 8.2 7.9 Palm heart 0.4 -- -- 7.1 Root - -- 0.4 3.9 Entire plant 65.3 -- -- 3.6 Spear leaf -- 0.8 4.7 3.1 Petiole -- 0.8 0.9 1.2 Leaf rachis -- -- -- 1.1 Leaf sheath -- 3.1 0.9 0.8 Bract -- -- -- 0.7 Inflorescence 0.4 -- -- 0.7 Flower 0.4 -- -- 0.5 Spine -- -- 0.4 0.4 Infructescence 0.4 -- -- 0.1 Not specified 3.3 5.5 12.5 9.0 Table 5 Use of palms by different human groups in tropical forests of north-western South America. For some ecoregions and countries no data was available Human group/ Ecoregion Useful Palm Palm use- Country species uses reports Indigenous Total 129 1,555 3,713 Colombia All ecoregions 74 574 926 Amazon 59 513 823 Andes 1 1 1 Choco 26 87 102 Ecuador All ecoregions 78 770 1,704 Amazon 59 656 1,448 Andes 23 95 109 Choco 24 110 149 Peru All ecoregions/ 47 278 402 Amazon Bolivia All ecoregions 33 397 716 Amazon 32 385 694 Andes 3 25 25 Mestizo Total 49 215 304 Ecuador All ecoregions 15 28 30 Amazon 5 6 5 Andes 11 24 25 Peru All ecoregions 35 163 239 Amazon 34 155 226 Andes 2 11 13 Bolivia All ecoregions 10 35 35 Amazon 9 29 29 Andes 2 6 6 Afroamerican Total 24 82 90 Colombia All ecoregions/ 23 77 84 Choco Ecuador All ecoregions/ 3 6 6 Choco Colono Total 15 56 61 Colombia All ecoregions/ 10 33 33 Amazon Ecuador All ecoregions 8 14 14 Amazon 6 9 9 Andes I I I Choco 1 4 4 Peru All ecoregions/ 4 9 9 Amazon Bolivia All ecoregions/ 2 5 5 Amazon Not identified Total 170 1,166 2,012 Colombia All ecoregions 82 293 393 Amazon 51 173 199 Andes 18 35 39 Choco 29 113 156 Ecuador All ecoregions 61 242 273 Amazon 19 36 43 Andes 38 155 160 Choco 16 63 74 Peru All ecoregions 87 531 750 Amazon 85 523 742 Andes 2 8 8 Bolivia All ecoregions 56 382 596 Amazon 48 340 543 Andes 10 47 53 Human group/ Ecoregion Uses [+ or -] SD References Country per species Indigenous Total 12.1 [+ or -] 16.7 166 Colombia All ecoregions 7.8 [+ or -] 9.8 48 Amazon 8.7 [+ or -] 10.3 37 Andes 1.0 [+ or -] 0.0 1 Choco 3.3 [+ or -] 2.9 13 Ecuador All ecoregions 9.9 [+ or -] 11.9 67 Amazon 11.1 [+ or -] 12.2 57 Andes 4.1 [+ or -] 3.0 10 Choco 4.6 [+ or -] 3.8 8 Peru All ecoregions/ 5.9 [+ or -] 5.8 29 Amazon Bolivia All ecoregions 12.0 [+ or -] 13.3 30 Amazon 12.0 [+ or -] 12.2 28 Andes 8.3 [+ or -] 11.0 3 Mestizo Total 4.4 [+ or -] 4.5 30 Ecuador All ecoregions 1.9 [+ or -] 1.8 4 Amazon 1.0 [+ or -] 0.0 2 Andes 2.2 [+ or -] 2.0 3 Peru All ecoregions 4.7 [+ or -] 4.5 22 Amazon 4.6 [+ or -] 4.1 20 Andes 5.5 [+ or -] 4.9 2 Bolivia All ecoregions 3.5 [+ or -] 2.1 4 Amazon 3.2 [+ or -] 2.1 3 Andes 3.0 [+ or -] 1.4 1 Afroamerican Total 3.4 [+ or -] 2.7 7 Colombia All ecoregions/ 3.3 [+ or -] 2.4 5 Choco Ecuador All ecoregions/ 2.0 [+ or -] 1.7 2 Choco Colono Total 3.7 [+ or -] 2.7 12 Colombia All ecoregions/ 3.3 [+ or -] 1.6 3 Amazon Ecuador All ecoregions 1.8 [+ or -] 1.0 7 Amazon 1.5 [+ or -] 0.5 5 Andes 1.0 [+ or -] 0.0 1 Choco 4.0 [+ or -] 0.0 1 Peru All ecoregions/ 2.3 [+ or -] 0.5 1 Amazon Bolivia All ecoregions/ 2.5 [+ or -] 0.7 1 Amazon Not identified Total 6.9 [+ or -] 10.1 86 Colombia All ecoregions 3.6 [+ or -] 3.9 21 Amazon 3.4 [+ or -] 3.3 11 Andes 1.9 [+ or -] 1.2 6 Choco 3.9 [+ or -] 3.1 12 Ecuador All ecoregions 4.0 [+ or -] 5.0 18 Amazon 1.9 [+ or -] 2.7 6 Andes 4.1 [+ or -] 4.6 9 Choco 3.9 [+ or -] 5.0 9 Peru All ecoregions 6.1 [+ or -] 6.9 30 Amazon 6.2 [+ or -] 7.0 28 Andes 4.0 [+ or -] 2.8 2 Bolivia All ecoregions 6.8 [+ or -] 8.0 18 Amazon 7.1 [+ or -] 8.2 15 Andes 4.7 [+ or -] 5.3 7 Table 6 Use of palms by the different indigenous groups living in the tropical forests of north-western South America Indigenous Country Useful Palm Palm use- group species uses reports Amazon Quichua (also Ecuador 44 243 387 in Andes) Huaorani Ecuador 43 337 500 Shuar(also Ecuador 40 186 305 in Andes) Mumane Colombia 36 183 183 Secoya Ecuador/Peru 29 93 105 Cofdn Ecuador 26 99 127 Cocama Peru 25 59 59 Tacana Bolivia 23 205 262 Siona Colombia/Ecuador 22 39 40 Shipibo- Peru 20 55 63 Combo Tikuna Colombia 19 77 80 Tsimane/ Bolivia 18 108 121 Mosetene Cubeo Colombia 18 45 46 Achuar Ecuador/Peru 18 41 49 Huitoto Colombia/Peru 17 62 62 Chayahuita Peru 17 26 26 Mirana Colombia 16 63 67 Matsigenka Peru 16 31 31 Nukak Colombia 15 120 168 Bora Colombia/Peru 14 58 66 Matse Peru 14 36 36 Chacobo Bolivia 13 36 37 Quechua/ Bolivia 12 73 73 Tacana Aguaruna Peru II 36 40 Yucarare/ Bolivia 10 69 69 Trinitario Andoque Colombia 10 28 28 Yucuna Colombia 10 20 20 Puinave Colombia 9 18 18 Yagua Peru 9 15 15 Ese Eja Bolivia/Peru 9 14 14 Tsimane Bolivia 8 39 43 Mosetene Bolivia 7 26 29 Siona-Secoya Colombia/Ecuador 6 11 11 Bora-Ocaina- Peru 5 21 21 Huitoto Siriono Bolivia 5 16 26 Orejon Peru 5 7 7 Guayabero Colombia 3 18 18 Curripaco Colombia 3 8 8 Yuracare Bolivia 3 8 9 Ocaina Peru 3 5 5 Omagua Peru 3 4 4 Yanesha Peru 2 8 8 Ashaninka Peru 2 3 3 Desano Colombia 2 2 2 Makuna Colombia 2 2 2 Piapoco Colombia 1 2 2 Trinitario Bolivia l 2 2 Tukano Colombia 1 2 2 Cashibo Peru I 1 I Coreguaje Colombia 1 1 1 Sikuani Colombia I I 1 Araona Bolivia 1 1 1 Andes Leco Bolivia 2 24 24 Quechua Bolivia l I 1 Choco Awa Colombia/Ecuador 18 74 84 Chachi Ecuador 15 70 87 Tsachila Ecuador 13 27 28 Embera Colombia 6 9 9 Waunan Colombia 1 8 8 Indigenous Uses [+ or -] SD References group per species Amazon Quichua (also 5.5 [+ or -] 6.8 23 in Andes) Huaorani 7.8 [+ or -] 6.8 13 Shuar(also 4.7 [+ or -] 4.7 15 in Andes) Mumane 5.1 [+ or -] 3.8 2 Secoya 3.2 [+ or -] 2.1 6 Cofdn 3.8 [+ or -] 2.8 5 Cocama 2.4 [+ or -] 1.4 2 Tacana 8.9 [+ or -] 8.1 5 Siona 1.8 [+ or -] 1.9 4 Shipibo- 2.8 [+ or -] 1.5 4 Combo Tikuna 4.1 [+ or -] 2.7 5 Tsimane/ 6.0 [+ or -] 2.9 3 Mosetene Cubeo 2.5 [+ or -] 2.8 4 Achuar 2.3 [+ or -] 1.4 7 Huitoto 3.6 [+ or -] 3.6 9 Chayahuita 1.5 [+ or -] 0.9 l Mirana 3.9 [+ or -] 2.9 4 Matsigenka 1.9 [+ or -] 1.0 1 Nukak 8.0 [+ or -] 5.2 3 Bora 4.1 [+ or -] 2.9 10 Matse 2.6 [+ or -] 1.5 1 Chacobo 2.8 [+ or -] 1.5 2 Quechua/ 6.1 [+ or -] 3.3 1 Tacana Aguaruna 3.3 [+ or -] 2.0 2 Yucarare/ 6.9 [+ or -] 3.4 2 Trinitario Andoque 2.8 [+ or -] 1.3 2 Yucuna 2.0 [+ or -] 1.1 4 Puinave 2.0 [+ or -] 1.4 4 Yagua 1.7 [+ or -] 0.9 3 Ese Eja 1.6 [+ or -] 0.7 2 Tsimane 4.9 [+ or -] 3.9 5 Mosetene 3.7 [+ or -] 2.3 4 Siona-Secoya 1.8 [+ or -] 0.8 2 Bora-Ocaina- 4.2 [+ or -] 2.0 1 Huitoto Siriono 3.2 [+ or -] 4.9 3 Orejon 1.4 [+ or -] 0.9 2 Guayabero 6.0 [+ or -] 1.7 1 Curripaco 2.7 [+ or -] 2.9 2 Yuracare 2.7 [+ or -] 2.1 3 Ocaina 1.7 [+ or -] 1.2 2 Omagua 1.3 [+ or -] 0.6 1 Yanesha 4.0 [+ or -] 2.8 2 Ashaninka 1.5 [+ or -] 0.7 1 Desano 1.0 [+ or -] 0.0 1 Makuna 1.0 [+ or -] 0.0 I Piapoco 2.0 [+ or -] 0.0 1 Trinitario 2.0 [+ or -] 0.0 1 Tukano 2.0 [+ or -] 0.0 1 Cashibo 1.0 [+ or -] 0.0 I Coreguaje 1.0 [+ or -] 0.0 I Sikuani 1.0 [+ or -] 0.0 1 Araona 1.0 [+ or -] 0.0 1 Andes Leco 12.0 [+ or -] 12.7 2 Quechua 1.0 [+ or -] 0.0 1 Choco Awa 4.1 [+ or -] 3.4 8 Chachi 4.9 [+ or -] 3.5 6 Tsachila 2.1 [+ or -] 1.1 3 Embera 1.5 [+ or -] 1.2 2 Waunan 8.0 [+ or -] 0.0 1 Table 7 Useful palms with high relative importance value index in different ecoregions of tropical forests of north-western South America Species per ecoregion Relative Palm Palm use- Importance uses reports Amazon Bactris gasipaes 2.0 76 414 Euterpe precatoria 2.0 89 358 Oenocaipus bataua 2.0 107 544 Attalea phalerata 1.9 78 227 Mauritia flexuosa 1.9 95 381 Attalea maripa 1.7 61 136 Iriartea deltoidea 1.7 70 283 Oenocarpus mapora 1.7 50 175 Socratea exorrhiza 1.7 63 236 Astrocaryum chambira 1.6 60 255 Astrocaryum murumuru 1.6 53 103 Attalea butyracea 1.6 37 85 Astrocaryum aculeatum 1.5 39 65 Phytelephas macrocarpa 1.5 35 118 Phytelephas tenuicaulis 1.4 30 72 Andes Bactris gasipaes 2.0 34 45 Oenocarpus bataua 1.6 22 38 Iriartea deltoidea 1.4 18 24 Attalea phalerata 1.3 21 21 Wettinia maynensis 1.3 17 26 Socratea exorrhiza 1.1 10 15 Ceroxylon echinulatum 1.0 8 14 Oenocarpus mapora 1.0 10 12 Ceroxylon ventricosum 0.9 7 7 Parajubaea sunkha 0.9 16 16 Phytelephas aequatorialis 0.9 8 8 Prestoea ensiformis 0.9 9 9 Dictyocaryum lamarckianum 0.8 9 11 Parajubaea torallyi 0.8 12 13 Choco Cocos nucifera 2.0 30 48 Bactris gasipaes 1.6 24 46 Wettinia quinaria 1.6 20 32 Astrocaryum standleyanum 1.4 27 54 Iriartea deltoidea 1.4 17 32 Euterpe oleracea 1.3 17 40 Oenocarpus bataua 1.2 18 36 Phrtelephas aequatorialis 1.2 14 20 Oenocarpus mapora 1.1 14 20 Attalea colenda 1.0 12 21 Socratea exorrhiza 1.0 14 21 Manicaria saccifera 0.9 10 20 Attalea cuatrecasana 0.8 10 13 Geonoma cuneata 0.8 8 10 Phytelephas seemannii 0.8 7 13 Synechanthus warscewiczianus 0.8 7 8 Species per ecoregion Countries References Amazon Bactris gasipaes C, E, P, B 109 Euterpe precatoria C, E, P, B 91 Oenocaipus bataua C, E, P, B 117 Attalea phalerata P, B 28 Mauritia flexuosa C, E, P, B 101 Attalea maripa C, E, P, B 31 Iriartea deltoidea C, E, P, B 79 Oenocarpus mapora C, E, P, B 51 Socratea exorrhiza C, E, P, B 69 Astrocaryum chambira C, E, P 68 Astrocaryum murumuru C, E, P, B 24 Attalea butyracea C, E, P, B 26 Astrocaryum aculeatum C, P, B 17 Phytelephas macrocarpa C, E, P, B 47 Phytelephas tenuicaulis C, E, P 18 Andes Bactris gasipaes C, E, P, B 8 Oenocarpus bataua E, S 6 Iriartea deltoidea C, E 4 Attalea phalerata B I Wettinia maynensis E 5 Socratea exorrhiza E 3 Ceroxylon echinulatum C, E, P 4 Oenocarpus mapora E 2 Ceroxylon ventricosum E 1 Parajubaea sunkha B 3 Phytelephas aequatorialis E 2 Prestoea ensiformis E 1 Dictyocaryum lamarckianum C, E, B 6 Parajubaea torallyi B 3 Choco Cocos nucifera C, E 11 Bactris gasipaes C, E 13 Wettinia quinaria C, E 13 Astrocaryum standleyanum C, E 18 Iriartea deltoidea C, E 14 Euterpe oleracea C, E 12 Oenocarpus bataua C, E 15 Phrtelephas aequatorialis E 5 Oenocarpus mapora C, E 8 Attalea colenda C, E 8 Socratea exorrhiza C, E 10 Manicaria saccifera C 9 Attalea cuatrecasana C 5 Geonoma cuneata C, E 5 Phytelephas seemannii C 7 Synechanthus warscewiczianus E 5 Country abbreviations C Colombia, E Ecuador, P Peru, B Bolivia
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Title Annotation: | Part 1 |
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Author: | Macia, Manuel J.; Armesilla, Pedro J.; Camara-Leret, Rodrigo; Paniagua-Zambrana, Narel; Villalba, So |
Publication: | The Botanical Review |
Article Type: | Report |
Geographic Code: | 4EUDE |
Date: | Dec 1, 2011 |
Words: | 18817 |
Previous Article: | Disturbance and resilience in tropical American palm populations and communities. |
Next Article: | Appendix. |
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