Concept of the integrative aspects of the forest ecosystem services with case study on recreation services assessment in Slovakia
© Kovalcik; licensee Springer 2014
Received: 4 November 2013
Accepted: 18 May 2014
Published: 26 July 2014
This paper presents basic information on the research, classification, and application of the functions of tree species and their communities (mainly forest) in Slovakia. The main aim is a scientific assessment of acquired knowledge regarding the functional effects of forests under real ecological, forest management and socio-economic conditions from various regions in Slovakia; the most up-to-date findings concerning the ecology and economics of natural resources will be applied here. The second part of the paper presents methodological possibilities for valuation of outdoor recreation in forests. Different methods and methodological approaches suitable to a valuation of recreation based on various principles and criteria (preference and non-preference methods, cost-based methods, revenue-based methods, and direct and indirect methods) are analyzed. A practical application of one indirect preference method (travel cost method) is made to evaluate outdoor recreation in forests in Slovakia.
Results and conclusions
A new classification system and a methodology of integrative utilization of forest functions for the forest ecosystem services are constructed. Outdoor recreation in forests, besides recreational forests and areas, assumes the character of a public good: its use by individuals has some influence on utilization by other individuals, and single users cannot be excluded from its utilization. Therefore, some stimulation for its production is missing. In principle, there are no markets for these kinds of public goods and services. The total value of outdoor recreation in forests in Slovakia amounted to €163.4 million; if opportunity time costs were included, this amounted to as much as €825.7 million.
Forests and other communities of tree species represent an irreplaceable function in the landscape from the viewpoint of the ecological stability of the landscape, its rational utilization, and sustainable development. Forests represent a basic landscape, forming an ecological and stabilizing element within the landscape. They are the most important source of renewable resources and, thanks to their functions, they also play an important role in the formation and protection of individual components of the natural environment, as well as changes to the environment caused by anthropogenic activities and anthropic activities (artificial environment created by people).
Interrelations of human society and tree species and utilization of their functions have changed in time and space. People’s use of the functions of tree species and respective communities in the landscape is subject to the size of the specific human population, the natural conditions, the style of living, and, finally, the social, economic, and cultural development of a society.
In accordance with EU forestry strategy (Directorate-General for Agriculture and Rural Development ), one of the basic goals of forest policy in Slovakia (Moravčík et al. ) is enhancement of multifunctional (functionally integrated) management of forests and protection of their potential functions. We must handle functional potentiality of forests as natural wealth, and preserve and improve it through proper management. Among the most serious problems limiting effective application of the system of multifunctional forest management is a discordance between the social order of forest functions and their economic funding.
Forest management as a production sector survives through the sale of its own products. From this viewpoint, production of the forest functions brings profit, and all other forest functions are merely an encumbrance for forest managers; this means they are not equal to production function. The core of the integration of forest functions is namely mutual comparison and evaluation of various forest functions, their position within the system of forest management, assessment of benefits resulting from various methods, and the interlinking of forest function use into optimal proportions. Forest managers must know which forest benefits society requires, to be able to set the goals of management.
Outdoor recreation in forests, in addition to recreational forests and areas, assumes the character of a public good; its use by individuals has some influence on the utilization of other individuals, and single users cannot be excluded from its utilization (Mavsar ). Therefore, some stimulation for its production is missing. In particular, there are no markets for these kinds of public goods and services. To achieve valuation of these forest functions, one must search for appropriate methods and methodical approaches, for example, indirect methods; that is, preference methods.
Evaluation of outdoor recreation in Slovakia as environmental services by using the ‘travel cost’ preference method is the main aim of this paper.
The starting point in Slovakia for a definition and classification of forest function was the ecosystem viewpoint, based on which functions follow from relationships between elements of an ecosystem, surrounding systems and their erroneous feedback (Zachar ; Vyskot ). Drawing on many ecosystem definitions of forest functions, the following definition was determined: the functions of forests and forest ecosystems are capabilities, effects, and influences appearing in basic components of ecosystems and interaction systems, including human ones. From a socio-economic viewpoint, there is a very large number of definitions of forest functions. We will follow these proposed by Czech colleagues Matejíček () ‘Forest functions express the natural and biological characteristics of a forest that form the background and means of satisfying human needs’, and Šišák et al. () ‘Forest functions express social order, which forestry fulfils in given places, at various times, and under various social conditions’.
A human society may use a complex combination of these functions for economic or social purposes. Then forestry, water management, game management, agriculture, the energy industry, the food industry, the building industry, the chemical industry, the cosmetics industries, the pharmaceutical industry, and so on, belong to anthropic fields, using forest functions in an economic area. Similarly, forest functions may also be used in social areas, that is, for recreation, therapy, hygiene, nature protection, formation and protection of the environment, science and research, education and training, aesthetics and arts, culture and history, and others. In this sense also, the Millennium Ecosystem Assessment () has defined ecosystem service as benefits to humanity from ecosystems. One of the most visible forest functions broadly used by the public is recreation services.
To evaluate outdoor recreation, an indirect preference method was used; the travel cost method. A questionnaire survey was used as the data source for the travel cost method. The target group was a sample of inhabitants above age 14 from the Slovak republic. In the survey, 2,515 respondents were interviewed, out of which 1,732 answered and 783 (31.13) gave no answer. The object of the survey was to ascertain data on the number of forest visits for the previous 12 months for the purpose of outdoor recreation, the length of each forest visit, the distance traveled to a recreational site, and socio-economic data, such as age, income of respondents, and village size, if possible. Other data were to be ascertained as well, such as number of inhabitants in the region to be evaluated, travel costs and the opportunity costs of time spent by visiting a forest and traveling.
Age distribution of respondents
14 to 30
31 to 50
Distribution of respondents by sex
Slovakian population (≥14 years)
In other words, the price is an imperfect measure of the good’s cost incurred by the purchaser. Under these conditions, the utility maximizing consumer’s behavior should be reformulated, to take into account such costs: given two goods or services (x1, x2), their prices (p1, p2), their access costs (c1, c2) and the consumer’s income (R). The utility function can be divided into two parts: one part expresses market goods and services (x1) and the other part shows public goods (x2). Now, assume that negligible access costs to the market goods are zero, (c1 = 0), but the consumer pays market price (p1). The access costs are higher for public goods, (c2 > 0), but the market price equals zero, (p2 = 0), whereby the consumer does not pay for these goods and services. A typical example for this kind of public goods is outdoor recreation in forests; this is free, but its access costs are expressed by travel costs. Under these conditions, the utility maximizing behavior of the consumer depends on:
The consumer’s preferences (u(x1, x2)),
The consumer’s budget (R),
The prices of the private goods and services (p1),
The access cost to the recreational site (c2).
The travel cost method is based on the hypotheses that changes in access costs to the recreational site (c2) have the same effect as price variations, and that as the number of visits to a site decreases, the cost per visit increases.
Results and discussion
Results of the travel cost analysis were ascertained by the modified zonal travel cost method on the sample of respondents (n = 1,732). An evaluation of results was carried out in two steps: first of all, distances between single recreational sites and the starting point of travel were calculated; the sites were divided into zones, and average visit rates were calculated for these zones. The value of outdoor recreation is calculated in two alternatives: without time costs and with time costs spent on outdoor recreation. Opportunity time costs were calculated on the basis of respondent income and only for employees, entrepreneurs, and part-time employees. Opportunity time costs equaled zero for other groups of respondents, because they had no market income for their work.
Reaction function of zonal travel costs method
Zone 20 km
Zone 40 km
Without time costs
visit rate = e5.1224 − 0,0132×TrC
visit rate = e5.6356 – 0.0105×TrC
With time costs
visit rate = e5.1224 – 0.0029×TC
visit rate = e5.6356 – 0.0023×TC
number of zones
The reaction function was evaluated using the ordinary least squares method, and the coefficient of determination describes the function’s power. As the single parameters were statistically significant in both cases, it is better to use the zone with a width of 40 km. The calculated determination function can be used to calculate the demand function for outdoor recreation as it is dependent on simulated entrance fees. It is assumed that the forest visitors will react in the same way after implementation of simulated entrance fees as to an increase in transport and travel costs.
Value of outdoor recreation in Slovakia by the travel cost method
Value of one visit
0.95 to 1.38
5.30 to 6.47
Average number of forest visits
Number per year
Value of outdoor recreation per year
28.90 to 41.84
160.87 to 196.40
Number of inhabitants in the Slovakia above 14
Total value of outdoor recreation in Slovakia
133.59 to 176.66
743.58 to 907.79
On the basis of current knowledge and the latest approaches to forest functions, and functions of forest tree species and their communities, the method of functional integration seems to be more effective and more pragmatic than the method of purposeful differentiation and prioritization of some of the functions. The application of scientific knowledge to forest functions, forest tree species and their communities and the opportunities for their use in the landscape will enable not only their real use in the environment, but also the construction of a new classification system of the functions of forests, forest tree species and their communities, considering an ecological and, subsequently, economic approach. This approach presupposes the construction of basic typology and a system for the assessment of forest function potential as well as the assessment of real fulfilment of the functions for forest growth in various site conditions, various types of landscape (various use and degree of anthropic changes), with regard to the health condition of real forest, its current tree species composition, age and spatial structure, its ecological stability, taking into consideration expected global and regional (mainly climatic) changes, with regard to social requirements and the interests of the owners of forests.
A real assessment of the benefits of nature and human activities and their influences on human population and nature should be used in socio-economic and ecological methodical procedures in the assessment of ecosystems functions, and from the viewpoint of prospects for survival of nature and human populations. It follows from the analysis and assessment of information and methodical approaches in the evaluation and valuation of the benefits of ecosystems functions and production activities that the most problematic and least exact is evaluation and valuation of benefits, which have not recently been and will not be an object of market realization.
This publication is the result of the project implementation: Extension of the centre of Excellence ‘Adaptive Forest Ecosystems’, ITMS: 26220120049, supported by the Research & Development Operational Programme funded by the ERDF.
- Caboun V: Spatial arrangement of the territory - determining of ecological - functional areas within the project ‘Revitalization of forest ecosystems on the territory of the High Tatra Mts. affected by wind calamity on 19.11.2004’, Ecological Studies VI. In Metamorphoses of the nature protection in the Tatra Mts. Slovak Ecological Society. Slovak Academy of Sciences, Bratislava; 2005:126–136.Google Scholar
- Caboun V, Tutka J, Moravcik M: Excertation of forest functions in landscape. National Forest Centre, Zvolen; 2010.Google Scholar
- The EU Forestry Strategy. 1998.Google Scholar
- Löwenstein W: Reisekostenmethode und bedingte Bewertungsmethode, Ein ökonomischer und ökonometrischer Vergleich, Schriften zur Forstökonomie. Frankfurt am Main, JD Sauerländer; 1994.Google Scholar
- Matejíček J: Determination of basic terms and relationships from out of production forest functions field. VÚLHM, Strnady, Prague; 2003.Google Scholar
- Mavsar R: Valuation studies of non-market forest goods and services in Europe. Plenary lecture I. International conference for the integral valorization of the forest, Santiago de Compostela 2008.Google Scholar
- Ecosystems and human well-being: synthesis. Island Press, Washington DC; 2005.Google Scholar
- Národný lesnícky program Slovenskej republiky (Slovakian National Forest Programme) MPSR. NLC-LVÚ Zvolen, Bratislava; 2007.Google Scholar
- Rosato P, Defrancesco E: Individual travel cost method and flow fixed costs. FEEM Working Paper Series. 2002.Google Scholar
- Šišák L, Šach F, Kupčák V: Expression of social effectiveness of existence and utilization of forest functions in financial form in Czech Republic. Czech University of Life Sciences, Prague (in Czech); 2006.Google Scholar
- Vyskot I: Potentials of forest functions in Czech Republic by management complexes and stend types. Ministry of the Environment of the Czech. Republic, Prague (in Czech); 1999.Google Scholar
- Zachar D: The brief characteristics of forest functions. In Valuation of forest functions and its compounds. VÚLH Zvolen, Bratislava; 1989:8–11. in Slovak in SlovakGoogle Scholar
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