Full text
1 Stimating social carrying capacity in Mediterranean mountains protected areas. Methodological orientation i María Luisa Gómez Moreno [email protected] Department of Geography. University of Málaga. Spain Ana M. Luque-Gil [email protected] Department of Geography. University of Málaga. Spain María Angeles Peláez-Fernández [email protected] Department of Social Psycology. University of Málaga. Spain Abstract The concept of social carrying capacity, though opens to debate and critique, is a valuable tool that enhances the management of recreational use in protected natural areas. In this study, conducted in Sierra de las Nieves natural park (Spain), we first categorised the hikers making use of the park and then, from the profiles obtained, analysed their perception of crowding on the trails. This assessment was subsequently used to assess levels of user satisfaction and thus to determine the psychosocial carrying capacity of the park. The results obtained can be extrapolated to most of the Spanish natural parks in Mediterranean mountain areas, due to their comparable levels of visitor numbers and to the prevalence of recreational hiking use. The results suggest that management efforts should be directed toward relocating trails outside the core areas, such that user preferences may be satisfied while less impact is made on the areas of highest environmental value. Key words: Hiking; visitors classification; natural areas planning and management; social carrying capacity. 1.Introducción Natural parks (a status created by Act No. 4/1989 and equivalent to the IUCN Protected Area Category V - Landscapes/Seascapes (Dudley, 2008)) are widespread in Iberian Mediterranean Mountains as a consequence of its better Biodiversity conservation compared to another agrarian environments. Accordingly, recreational practices in natural spaces are still at an embryonic stage of development, although visitor numbers are growing. This changing pattern reflects a situation similar to that already experienced in the sociological context of Anglo-Saxon countries, where the
2 protection of natural spaces and the practice of recreational activities in such spaces date back to the 1950s and 60s. Accordingly, literature review reveal that empiric information about number and motivation of users is uneven and scarce opposite to the deepers and more assorted studies in Anglo-Saxon area. Working on this assumption, the aims of this study are: -Know users motivation -Apply motivation to the analysis of the crowding perceived by users as a basis for determining social charge -Generate an instrument for park planning and management, verifying the degree of consistence between management goals for the natural park and visitor’s motivations. The natural park of Sierra de las Nieves (Andalusia, Spain, see Fig. 1) has been chosen as a significant study site. Applied methods have been: -Territorial analisys of park planning and public outodoor recreation services. -Planning and carrying out a survey focused on the users of included in public trail net, the only outdoor activity included in natural park planning. -Analyse survey results according to literature review about motivation, crowding and social carrying capacity Ought to the space limitation, methods and results have been merged. 2. Methods and results 2.1. Motivation and crowding as components of social carrying capacity To achieve these goals, literature review work revealed the relationship of three concepts: motivation, crowding and social carrying capacity. Early studies focused on estimating the social carrying capacity of recreational and protected natural areas (Wagar, 1964). Subsequently, differences in users’motivation were introduced as a factor underlying their perceptions of crowding (Driver, Brown and Perry, 1978; McCool and Petersen, 1982). Knowledge of users’ motivations is fundamental to our study goals, as this factor is the basis for understanding the demand for recreational facilities and, at the same time, a valuable tool for developing effective management measures (Arnegger, Woltering & Job, 2010; Saepórsdóttir, 2010; Farias, 2011) and for estimating social carrying capacity from perceptions of crowding. In this way, crowding perceptions, being subjective judgments by individuals, depend on widely varying social and/or
3 psychological factors, including the type of user, the activity performed and the environment in which it takes place (Graefe & Vaske, 1987). Literature review also show that survey is usually the way to fit both motivation and crowding perception. For developing these ideas, we start with territorial analisys (1 st ) as a determining factor of survey planning (2 nd ) and finish with survey results analysis (3 rd ). 2.2. Territorial analisys of user-outdoor recreation environment Study Area and Sampling The natural park of Sierra de las Nieves (Andalusia, Spain, see Fig. 1) was selected as the study site for various reasons. First, it is a significant example of the function of Mediterranean mountain areas in the context of the European Union, as many natural parks are located in such areas; second, it reflects, in terms of visitor numbers and the hiking-oriented focus of the park’s infrastructure and regulations, the user conditions prevailing in Spanish natural parks; third, its planning is based in the existence of Abies pinsapo bois, a high value tree from the biodiversity viewpoint. Figure 1. Study area: Natural Park Sierra de las Nieves Regarding to the number of users of park trails, 23.000 per year, we know it throughout the dataloggers (automatic data recorders) installed (see figure 2). In contextualizing this number, we can find significant information about the representativeness of the
4 study área. This type of natural space, with relatively low visitor numbers, is the most common and accounts for the largest total surface area, both in Spain as a whole and in the region of Andalusia in particular, in the category of natural park Cabalar, 2013; Muñoz, 2008). In this respect, Spain’s parks are well behind those in the USA and other European countries (Fernández & Santos, 2010) and the scarce and not much reliable sources show a low number of visits. (EUROPARC, 2013 2012). Thus, 92% of these parks receive fewer than 50,000 visitors a year, and 64% receive 10,000-50,000 visitors (Sierra de las Nieves is in this visitor range). On this point, and nevertheless it’s a secondary factor in this study, it must be outlined the lack of automatic data recorder. Often, the information belong only to visitors centres, without knowing if their activity affect more vulnerable natural elements and avoiding the measurement of carrying capacity. Figure 2. Dataloggers and survey points situation in public trail network. Natural park Sierra de las Nieves Focusing on hiking, it is significant that the only park activities assigned a specific location are those of leisure (recreation areas) and hiking (see Fig. 2). Hiking is the most popular recreational activity, both in protected natural areas and among all outdoor recreational activities in Spain; according to a report published by the Spanish
5 Centre for Sociological Research (CIS, 2010), 8.6% of people aged over 14 years practise mountaineering, hiking and/or backpacking. Likewise, several studies (Cabalar, 2013; Farias, 2011; Muñoz, 2008) show that virtually all Spanish protected areas have public trails with or without signposting. The definition and management of this natural park (with a total surface area of 20,163 ha) is the responsibility of the Andalusian Regional Government, in application of Act No. 4/1989 of 27 March on the Conservation of Natural Areas and Wildlife (Junta de Andalucía, 1989). This status is equivalent to the IUCN Protected Area Category V - Landscapes/Seascapes (Dudley, 2008). The fundamental justification for establishing this natural park is the delicate situation of two species, the Spanish fir (Abies pinsapo bois) and, to a lesser extent, the gall oak (Quercus faginea ssp. Faginea). The Spanish fir dates from the Tertiary period and is only found in a few areas of the Serranía de Ronda and in the Yebala range in northern Morocco. Thus, in terms of biodiversity, this area is of great importance. Nevertheless, processes of deforestation, incessant since the fifteenth century, had led to a clear risk of this species’ extinction, a risk known to the National Forestry Department for several decades. In 1995, the area (extended) was declared a Biosphere Reserve, but in Spain there are no specific management and zoning regulations for this territorial category, and so it is subject to the regulations applicable to natural parks. Among other objectives, the park managers seek to consolidate and amalgamate the currently discontinuous presence of Spanish firs, previously found only in shaded valleys where the altitude and orientation provided the humidity and cool temperatures needed for their survival. Applying protectionist zoning criteria, these formations comprise the central area afforded the very highest levels of protection (see Figure 2), as stipulated in the Natural Resources Management Plan (Junta de Andalucía, 2003), although the same degree of protection was also granted to other isolated areas. In addition, a peripheral area of protection was established around the Spanish fir woods. In this way, we understand that the trail network is localiced in the areas with most biodiversity values ought to planning linking with the earlier UICN proposals (environmental education). However, the area presents other physical factors that are of greater significance for the nearby population, in the provinces of Málaga, Cádiz and Sevilla, namely its altitude and the presence of snow. Torrecilla mountain, at 1,919 m above sea level, is the
6 highest peak in the province of Málaga. Snow is a rare sight in coastal Western Andalusia and so its presence on the slopes of Sierra de las Nieves (“Snowy Mountains”) makes it a prime destination for winter recreation, despite the absence of any kind of infrastructure for snow sports, which would be unviable due to its short duration. The connection between the park and its snow cover arises from its location, concerning both the atmospheric conditions that produce snowfalls and its altitude, determined by the geology of the mountains. The third physical factor is a further identifier of the park in terms of recreational activities, but for a much more restricted population – speleologists. The limestone formations contain a series of chasms of international importance, especially the GESM sinkhole, which at 1,100 m, is the deepest in Andalusia and one of the deepest in Europe. Of these four factors – the Spanish fir, Torrecilla mountain, access to snow and speleology – the first three constitute the main attractions for visitors, and as a result of their dependence on altitude, they share the same space, namely the area afforded the highest levels of protection. 2.3. The survey: its planning and primary results As it has been enounced, we followed the proposals of Graefe y Vaske (1987) for survey planning and we started from a set of premises stemmed from the territorial analysis of the study area and from the visitors affluence chronology provided by dataloggers. The first of these was the seasonality of park use. This question was addressed in order to clarify the relationship between visitor numbers, natural cycles and the work year; for this purpose, the survey period was divided according to these criteria over a full year. The availability of dataloggers facilitated the counting of the annual distribution of visits; the fact that one year’s accumulated data had previously been obtained was used as a criterion for the timing of the survey. The following selection criteria were applied with regard to natural cycles: high summer temperatures, seasonal changes in vegetation in accordance with the annual hydrological cycle, the existence of sunny days with mild temperatures during the winter months, and the presence of snow. According to the Natural Resources Management Plan (Junta de Andalucía, 2003), the latter factor is associated with episodes of overcrowding. Data collection was interrupted during the hottest months (June to September), as the dataloggers reflect a
7 sharp fall in the numbers of trail users in these months. As regards the advisability of conducting visitor surveys on days of rain or mist, we decided to determine visitor numbers during these periods, before excluding them from the study period. In practice, these weather conditions were found to be dissuasive, and so when the forecasts supplied by the National Meteorological Agency suggested the likelihood of unfavourable weather, surveys were not conducted. On the contrary, the days when the presence of snow coincided with good weather conditions were specifically included in the survey programme (28% of the surveys). These weather conditions were identified directly by the interviewer as one of the items checked on the questionnaire. Regarding the working day/holiday status of the date, the survey days were classed as weekends (7 days, 58.6% of the surveys), long weekends (7 days, 17.4% of the surveys), Christmas period (10% of the surveys) and working days (2 days, 1.2% of the surveys). The Easter holidays were excluded due to the abnormally rainy weather experienced in the year in question. The second issue considered was to include in the survey only those persons identified as users of public trails. To ensure this outcome, the survey was planned such that the survey sites were exclusively those where there was access by motor vehicle to the start point of a trail (see Fig. 1). Of these sites, we then selected the three which preliminary field work had shown to be most frequented by vehicles (see Fig. 2). The criteria for selecting respondents was that they should be aged over 16 years and have hiked the trail in question, in full or in part. The visitors who agreed to participate in the study were given a brief description of the study goals. Data were collected from midday until sunset (the exact time depending on the month), and so the answers provided referred to activities that had already been carried out. The questionnaires were completed by the interviewers. A total of 345 valid questionnaires were obtained. The questionnaire contained three sections relating to the following study goals (Ocaña et al., 2013): visitor characteristics (origin, age, sex, profession), motivation and perception of crowding (this latter aspect was fundamental to estimating the social carrying capacity) and satisfaction with the trail experience, as described in the literature review. The characteristics of the respondents were similar to those reported by Wöran & Arnberger (2012) in a study carried out in the Austrian Alps. The age range was 16-75 years, with an average of 37.7 years (vs. 41.4 years in the above-cited
8 study), with a relatively low participation by women (28% vs. 47%). 50% of the visitors were university educated and 81% were in employment (vs. 74.2%), but the numbers of pensioners (2.3% vs. 11.9%) and students (2.6% vs. 10.0%) were very low. These differences reflect the social environment of the recreational activities in Mediterranean societies, and the fact that such active, outdoor activities have only recently been widely adopted, hence the scant presence of retired persons. On the other hand, the low number of women doesn’t match with the Spanish eco tourist profile (Muñoz, 2008: 294). As regards the visitors’ origins, the data obtained for users’ profiles in Sierra de las Nieves corresponds to the prevailing pattern in natural parks in Andalusia (Hidalgo, 2009), with most visitors arriving from nearby urban areas. Figure 1 shows the location of this natural park with respect to the potential demand for its recreational activities. The metropolitan areas of Sevilla, Algeciras and Málaga-Costa del Sol, all at a distance of about two hours by car, depending on the access point (see Fig. 1) provide a potential user population of around one million in the first and third cases, and of 300,000 in the second. Analysis of the survey results shows that the relationship between road access, the respondents’ place of origin and their distribution among the three selected survey points corresponds to a proximity model. These three areas account for 94% of the respondents, with a clear predominance of those from Málaga (75%). This population, therefore, is mainly a nearby one, which is in accordance with the characteristics observed in other protected natural areas, both in Spain as a whole (Ruiz & Galdós, 2007) and in Andalusia (Hidalgo, 2009). This finding is also in line with Wöran & Arnberger (2012) regarding the prevalence of users from the same country, although the latter study did not report the proximity of visitors’ area of origin or the duration of their visit. In both studies, visitors predominantly arrived in their own vehicles (98.5% vs. 97%), which suggests proximity. Results for the duration of the visit, however, were unequal; in our study, 90% of the respondents were on a day trip (vs. 46.1% for Wöran & Arnberger). Our assessment of these data is that, in contrast to the universal nature of its biodiversity values, the spatial context of this natural park as a tourist destination is very limited. As regards the visitors’ origins, figure 1 shows that metropolitan áreas of Sevilla, Gibraltar-Algeciras and Málaga-Costa del Sol, all at a distance of about two hours by car, provide a potential user population of around one million in the first case and third
9 cases, and of 300,00 in the second. These three areas account for 94% of the respondents, with a clear predominance of those from Málaga (75%). This population, therefore, is mainly a nearby one, that chose protected areas more as outdoor recreation areas that by their biodiversity values. This profiles matches with the studies of Ruiz y Galdós, 2007 in Basque Country and Hidalgo (2009) in Andalusia, but not with Cabalar findings in some natural parks in Galicia (Cabalar 2013). 2.4. Results: motivation and crowding perception In relation to questionnaire content, literature review showed that most of surveys employ Likert scales and then analyzed the results obtained using cluster or factorial methods that combine motivation items with sociological ones. Besides that, Spanish research has accepted some of these results and researchers have adapted them in a wide range of profiles (Muñoz, 2008). Nevertheless, given the lack of basic information about study area visitors, we decided to start from the definition of motivation proposed by Manfredo, Driver & Tarrant (1996), as “the individual’s intrinsic or extrinsic incentive to engage with an activity”, and to including in the questionnaire the Recreation Experience Preference (REP) items (Driver, 1977 apud Gallowey, 2012). Regarding to activity selected (Graefe y Vaske, 1987), the survey focused on the public trail users, as public trail network is the only outdoor recreation equipment offered. In this way, first at all we need to know what weight hiking had as motivation among public trail users. Specifically, Item 3 of the survey “When you go out into the country, is hiking your main reason for doing so?” with a closed yes/no line of response, provided a first line of segmentation. The answer divided the study group into hikers (those who answered yes, 87,8%) and visitors (those who answered no, 12,25) (table 4). After that we applied Recreation Experience Preference (REP) items (Driver, 1977 apud Gallowey, 2012), having into account the goals study (to get basic information) and the embryonic stage of development of hiking in Spain. But, in order to avoid that if the questionnaire design were based solely on the principles applied in previous studies biased results might be obtained, we decided to combine closed and open answers (question 2 and counter question 36, see table 1). The closed ones referred to the REP items listed in Table 1, selected from the REP items, such as “to enjoy nature”, “for physical fitness”, “to learn” and “to be in company” (in the latter
16 Based on these results, we have developed the remaining study goals in the Discussion and Conclusions paragraph. Graphic 2. Relationship between motivation and crowding perception 5. Discussion and Conclusions 1.-Estimation of social carrying capacity and possibility of extrapolate study results to another natural parks in Spanish mediterranean mountain. Two study areas facts, 1.- focusing methods in hiking and 2.-low total number of users, let extrapolate the results to this rank of Spanish natural park. 1.1. Following an epistemological order, the first result is about users motivation. According to Spanish literature (Hidalgo, 2009; Ruiz and Galdós, 2007) prevail nearby users that identify themselves as hikers, they don’t overnight in the park and whose motivation combine enjoy nature with physical fitness and to a lesser extent, learn the surroundings. On the opposite, with a much lower number, users that identify themselves as visitors; the only outstanding difference regarding on motivation is that learn get more presence among visitors. In this way, results verify LEADER European Observatory (2001) approach: trail users don’t identify hiking as a sport. About this subject, our proposal is: a) To consider hiking as a multipurpose outdoor recreation activity and consider that multipurpose motivation doesn’t blur users motivation but, on the contrary, it must be understood as an improvement of the outdoor experience. We derive of this the following management proposal: to include both cultural and natural elements in trails route b) The propriety of keeping the difference hiker/visitor in the statement of users profiles, despite the low number of the last ones.
17 1.2. Regarding to the relationship between motivation and crowding perception in order to estimate social carrying capacity. The results show that users do not sense crowding regardless of their motivation. This is consistent with the low number of people incoming. So, these results can be extrapolated stating that crowding perception don’t damage quality outdoor experience in Spanish Mediterranean mountain natural parks. Only the short and mayfly presence of snow is a crowding-pull factor and it may be considered the main cause of fluctuating crowding (Hadwen et al, 2011). 2. To apply social carrying capacity to the improvement of management and planning of Spanish Mediterranean mountain natural parks. Generate an instrument for park planning and management, . 2.1. In relation to verifying the degree of consistence between management goals for the natural park and users’ motivations, these findings highlight the inconsistency between the park management objectives of environmental protection, the location of the recreational facilities and the users’ actual preferences; thus, although the trail network is concentrated in areas of greatest environmental value, possibly because of their relation with the goals of environmental education, and also in accordance with the first proposals by the IUCN, these environmental values are of only incidental importance to most users. So we validate the suitability of knowing users motivation as a management tool. 2.2. These results are interpreted as providing a reason for diversifying the location and characterisation of the infrastructure within the natural park, and generating a methodology for relocating trails in accordance with user preferences and environmental constraints, thus alleviating the pressure on areas that are currently overutilised (http://analisisgeografico.uma.es/sierranieves/). 2.3. However, the appearance of snow as a crowding-pull factor only could be resolved by restrictive measures given its uncertain and ephemeral behaviour and its location in high biodiversity values areas. BIBLIOGRAFÍA ANÁLISIS GEOGRÁFICO: http://analisisgeografico.uma.es/sierranieves/ ARNBERGER, J., WOLTERING, M. and JOB, H. (2010): “Toward a product-based typology for naturaleza-based tourism: a conceptual framework”. Journal of Sustainable Tourism, 18 (7): 915-928. doi: 0966-9582.
18 CABALAR, M. (2013): “Análisis de la demanda de uso público en tres parques naturales de Galicia” en Boletín de la Asociación de Geógrafos Españoles, 61: 261-284. CIS (2010). Encuesta sobre los hábitos deportivos en España 2010. Ideal democrático y bienestar personal. http://www.csd.gob.es/csd/estaticos/dep_soc/encuesta-habitosdepot2010.pdf [consulta octubre 2014] DRIVER, B. and BROWN, P. (1978): “The Opportunity Spectrum concept and behavioral information in outdoor recreation resource supply inventories: A rationale”. In G. H. Lund (tech. coords.). Integrated inventories and renewable natural resources Proceedings of the Workshop. USDA Forest Service General Technical Report RM-55 pp. 24-31. Fort Collins. Rocky Mountain Forest and Range Experiment Station. DUDLEY, N. (Editor) (2008): Guidelines for applying protected area management categories (pdf). Gland, Switzerland. http://data.iucn.org/dbtw-wpd/edocs/paps-016.pdf [consulta marzo 2014] EUROPARC-ESPAÑA: Anuario 2013 del estado de las áreas protegidas en España http://www.redeuroparc.org/anuario_europarc_espana.jsp [consulta diciembre 2015] FARIAS, E. (2011): “Managing for recreational experience opportunities: the case of hikers in protected areas in Catalonia, Spain”. Environmental Management, 47, 482496. doi: 0301-4797. FERNÁNDEZ, A. & SANTOS, E. (2010): “Turismo y Parques Naturales en Andalucía tras veinte años desde su declaración. Análisis estadístico, tipología de parques y problemática de la situación actual”. Anales de Geografía de la Universidad Complutense, 30 (1): 29-54. doi: 0211-9803. GALLOWEY, S. (2012): Recreation specialization among New Zealand river recreation users: A multiactivity study of motivation and site preference. Leisure Sciences, 34: 256–271. doi: 1521-0588. GRAEFE, A.R. y VASKE, J.J. (1987): “A framework for managing quality in the tourist experience”. Annals of Tourism Research, 14: 390-404. doi: 0160-7383. HADWEN, W., ARTHINGTON, A., BOON, P, TAYLOR, B. AND FELLOWS, CH. (2011): “Do climatic or institutional factors drive seasonal patterns of tourism visitation to Protected Areas across diverse climate zones in eastern Australia?” Tourism Geographies: an International Journal of Tourism Space, Place and Environment, 13:2: 187-208. doi: 1470-1340.
19 HIDALGO, S. (2009): Uso público en los parques naturales de Andalucía. Granada: Ediciones Instituto de Desarrollo Regional. LEADER European Observatory (2001). Developing walking holidays in rural areas: Guide on how to design and implement a walking holiday project. http://ec.europa.eu/agriculture/rur/leader2/rural-en/biblio/walking/walking.pdf [consulta octubre 2014] MANFREDO, M., DRIVER, B. L., & TARRANT, M. (1996): “Measuring leisure motivation: A meta-analysis of the recreation experience preference scale”s. Journal of Leisure Research, 28(3), 188-213. doi: 0022-2216. MCCOOL, S.F. AND M. PETERSEN (1982): “An application of the two factor theory of satisfaction to recreational settings”. Forestry Sciences Laboratory Report. Missoula Montana. USDA Forest Service. MUÑOZ, J.C. (2008): “El turismo en los espacios naturales protegidos españoles, algo más que una moda reciente” en Boletín de la Asociación de Geógrafos Españoles, 46: 291-304. OCAÑA, C., GÓMEZ, M. L., ARREBOLA, J.A, GALACHO, F.B., LARRUBIA, R., LUQUE, A. M. y VÍAS, J. (2013): “Desarrollo metodológico sobre la evaluación de la capacidad de uso recreativo de espacios protegidos”, Nimbus, 31-32 pp. 447-460 PATTERSON, M.E. y HAMMITT, W.E. (1990). Backcountry encounters norms, actual reported encounters, and their relationship to wilderness solitude. Journal of Leisure Research, 22 (3), 259-275. doi: 0022-2216. RUIZ, E. AND GALDÓS, R. (2007): Los espacios protegidos del País Vasco, en Molinero, F. (ed.), Espacios naturales protegidos. III Coloquio Hispano-Francés de Geografía Rural / IIIe Colloque Franco-Espagnol de Géographie Rurale (pp. 7-25). Baeza (Spain). AGE-UNIA sede Antonio Machado, CNFG. SAEPÓRSDÓTTIR, A.D. (2010): “Planning naturaleza tourism in Iceland based on tourist attitudes”. Tourism Geographies: an International Journal of Tourism, Space, Place and Environment. 12 (1), 25-52. doi: 1470-1340. SHELBY, B. AND HEBERLEIN, A. (1986): Carrying capacity in recreation settings. Oregon State University Press, Corvallis, OR.
20 TARRANT, M.A., CORDELL, H.K. y KIBLER, T.L. (1997): “Measuring perceived crowding for high-density river recreation: the effects of situational conditions and personal factors”. Leisure Sciences, 19: 97– 112. doi: 1521-0588. VERA, F. (1997): Análisis territorial del turismo, Barcelona, Ed. Ariel. WAGAR (1964): “The carrying capacity of wildlands for recreation”. Forest Science Monograph, 7, 1-24. doi: 0015-749X. WÖRAN, B., & ARNBERGER, A. (2012): “Relationships between recreation specialization, restorative environments and mountain hikers’ flow experience.” Leisure Sciences, 34: 95–114. doi: 1521-0588. Legislación y normativa Decreto 344/2003, de 9 de diciembre, por el que se aprueba el PORN y PRUG del Parque Natural Sierra de las Nieves http://www.juntadeandalucia.es/medioambiente/portal_web/web/temas_ambientales/esp acios_protegidos/planificacion/PORN/PORN_PRUG_Sierra_Nieves/decreto344snieves. pdf Last accessed: November 2012 [consulta octubre 2015] Ley 4/1989 de 27 de marzo de conservación de los espacios naturales y de la flora y fauna silvestres, aplicada en Andalucía a través de la Ley 2/1989, de 18 de julio, por la que se aprueba el inventario de espacios naturales protegidos de Andalucía, y se establecen medidas adicionales para su protección Mapas PN Sierra de Las Nieves. Junta Rectora Consejería de Medio Ambiente (s/f). E.1: 80.000. Papel. i Esta comunicación forma parte de los resultados de la suma de dos proyectos: el Proyecto I+D+I, del Ministerio de Ciencia e innovación del Gobierno de España (referencia SEJ-2007-67690), con Carmen Ocaña Ocaña como investigadora responsable, y el Proyecto de Excelencia de la Consejería de Innovación, ciencia y empresa de la Junta de Andalucía (Referencia P07_HUM_03049), con Mª Luisa Gómez Moreno, como investigadora responsable.