The Economic Valuation of Ecosystem Services of Biodiversity Components in Protected Areas: A Review for a Framework of Analysis for the Gargano National Park
Abstract
:1. Introduction
ES, Biodiversity Definition and Their Relationship
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- Provisioning services: which represent the contribution of the ecosystem to goods extracted or collected from the ecosystem (e.g., genetic resources, food, fresh water, etc.);
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- Regulating services: which represent ES ability to regulate biological processes, influencing climatic and hydrological cycles and maintaining the environmental conditions benefited by the society and individuals (e.g., air quality regulation, erosion regulation, climate regulation, etc.);
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- Cultural services: which include non-tangible services. They refer to the experiences that human beings could benefit from ecosystems (e.g., cultural, spiritual, recreation, etc.).
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- Supporting services: which are the services necessary for the production of other ES (nutrient cycling and primary production).
2. ES Mapping Techniques
- (1)
- WebGIS. With a WebGIS, traditional DesktopGIS applications can be implemented on a web server (also called map server) allowing the interaction between the cartography and the associated data. The data processing offered by web interfaces are nowadays still limited compared to DesktopGIS software, but it is still possible to carry out targeted queries and analyses. The strength of WebGIS is the availability of information regardless of the platform, installation and location. In addition, WebGIS can be consulted through Client-type applications, which can be generic (web browser) or specific (GIS software). Several types of WebGIS applications are available according to the degree of complexity [43], provided by the following services: viewing, associated info (attributes), processing queries/tools, data and mapping download and upload and instructions. The following WebGIS sites are used for biodiversity and ESs mapping: SoilConsWeb (Multifunctional Soil Conservation and Land Management through the Development of a Web-Based Spatial Decision Supporting System) [44], Rewetland (widespread introduction of constructed wetlands for a wastewater treatment of Agro Pontino ) [45], FaceCoast (FACE i.e. the challenge of climate change in the med COASTal zones) [46], HABEaS (Hotspot Areas for Biodiversity and Ecosystem Services) [47] and Lakes ES (Lakes Ecosystem Service) [48].
- (2)
- The assessment of supply and demand of ES in protected areas, applied to potable water and protection from hydrological instability and aesthetic value [42]; crops for farmers, natural fodder for breeders, wood and fibres for processing and fuel use; and mushroom and truffle harvesting [52]. This method allows users to take into account the peculiarity of the territorial context under study.
- (3)
- GIS techniques. It provides attractive valuations through photointerpretation in terms of used surface through digital imaging and vegetation/habitat coverage change. On the other hand, the qualitative aspect is generally retrieved by means of phytosociological surveys (e.g., tree coverage, shrub and herbaceous layer, number of species surveyed and their relative coverage) and forestry data (e.g., presence of dead wood, pathogens) which provide further information on biodiversity, the conservation of the tree components and the sources of disturbance such as overgrazing, tourism, etc. The above queries and surveys should be repeated over time as suggested by the habitat monitoring manual for each habitat. Subsequently, for each recorded data (from forestry, vegetation, fauna and soil surveys) a value (to be defined) is generally attached. This value can be referred to, for example, the plant biodiversity index (ipb) (for phytosociological data), forest biodiversity index (ifod) (for forest data), fauna biodiversity index (ifab) and soil biodiversity index (isb) (on sampling and subsequent laboratory analysis). Other indicators may also apply such as an index of climatic biodiversity (icb) (temperature, precipitation, wind) and an index of insect biodiversity (iib) (detection of insects and small organisms at litter level). Finally, a specific algorithm is specified to provide a full value of biodiversity, useful for evaluating ES. The above multidisciplinary approach generally involves nine professional figures (a botanist, forest expert, fauna expert, soil scientist, climatologist, entomologist, economist, mathematician and GIS expert) leading to reliable data used as an estimated value for ES.
3. Total Economic Value and the Valuation Methods
3.1. Total Economic Value (TEV)
3.2. Valuation Methods
4. Literature Review
4.1. Methods and Data
4.2. Results
4.2.1. Provisioning
4.2.2. Regulating
4.2.3. Cultural
4.2.4. Supporting
4.2.5. Biodiversity
5. Mapping of Ecosystem Service and Biodiversity of the Gargano National Park
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- Supporting services. Soil-forming and nutrient cycling provide the foundation for all life on Earth. Plants form the critical basis of food chains in nearly all ecosystems. In general, native plants support other native species more effectively than non-native plants.
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- Provisioning services. Supply services include food, fresh water, fuel, fibre and medicines collected from natural and managed ecosystems. Many native plants are harvested for food, animal feed and fibre. These are often referred to as wild harvested plants (WHP). In the GNP, many species of wild mushrooms, sweet chestnut (Castanea sativa Mill.), common hazel (Corylus avellana L.), wild strawberry (Fragaria vesca L. subsp. vesca), wild apple (Malus sylvestris (L.) Mill.), blackthorn (Prunus spinosa L. subsp. spinosa), bramble (Rubus canescens DC.), wild blackberry (Rubus ulmifolius Schott) and many edible herbaceous species that could be traded are simply harvested. Some people use native plants as medicines, such as rustyback (Asplenium ceterach L.), deadly nightshade (Atropa bella-donna L.), starflower (Borago officinalis L.), Saint John’s wort (Hypericum perforatum L.), bay laurel (Laurus nobilis L.), common mallow (Malva sylvestris L.), Lemon balm (Melissa officinalis L.), mint (Mentha sp. pl.), dog rose (Rosa canina L.), dog figworts (Scrophularia canina L.) and Marian thistle (Silybum marianum (L.) Gaertn), while they have lost the use as dye plants, such as dyer’s croton (Chrozophora tinctoria (L.) A. Juss.), dyer’s alkanet (Alkanna tinctoria Tausch subsp. tinctoria), woad (Isatis tinctoria L. subsp. tinctoria) and golden marguerite (Cota tinctoria (L.) J. Gay). In addition, native trees and shrubs are mainly used for firewood and the production of wood for building purposes. Other potential wild-grown trees should also be evaluated [122], including prioritised ones [123].
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- Regulating services. Native plants contribute to regulate ecosystem functions such as climate, flood, diseases, pests, the purification of water and pollination. For example: (1) The habitat functions are correlated with the diversity of ecosystem environments and processes that contribute to produce this diversity (e.g., the shelter and nursery functions of ecosystems support specific and genetic diversity, forming the basis for most of all other ecosystem functions); (2) several native plant communities along roadsides slow down water and can prevent flooding much more effectively than mowed lawns. Additionally, during photosynthesis, plants absorb carbon dioxide from the atmosphere, release oxygen for breathing and store carbon in their roots and stems, helping to regulate greenhouse gases.
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- Cultural services. Native plants are valuable to human cultures for recreational and spiritual uses. Historically, shrub species such as olive (Olea europaea L.), blackthorn (Prunus spinosa L. subsp. spinosa) and rush broom (Spartium junceum L.) are used to make wicker baskets, or fruits of blackthorn or common centaury (Centaurium erythraea Rafn) for liqueur; blackberries (Rubus sp. pl.) and figs (Ficus carica L.) for jams; and wild oregano (Origanum vulgare L. subsp. viridulum (Martrin-Donos) Nyman) and Lesser calamint (Clinopodium nepeta (L.) Kuntze) for spices. As for recreational use, many people nowadays enjoy a wooded park-like setting for camping, picnics and other family gatherings [124]. Some make a special pilgrimage to their favorite woodland each spring to view the wildflowers [125], or they grow particular native plants in their garden to support butterfly larvae or bees [126].
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Author | Geographical Information | Provisioning | Regulating | Cultural | Supporting | Biodiversity |
---|---|---|---|---|---|---|
Považan et al., 2015 [87] | Muránska Planina National Park (Slvakia) | x | x | x | ||
Gandarillas et al., 2016 [88] | Sajama National Park (Bolivia) | x | x | x | ||
Ninan et al., 2016 [89] | Nagarhole National Park (India) | x | x | x | x | x |
Torres-Miralles et al., 2017 [90] | Cazorla, Segura y Las Villa National Park (Spain) | x | x | x | x | |
Schirpke et al., 2017 [91] | Alto Garda Bresciano Park and Val Grigna Park (Italy) | x | x | x | ||
Ferreira et al., 2017 [92] | Biophysical Interest Zone of Avencas, ZIBA (Portugal) | x | ||||
Marta-Pedroso et al., 2018 [93] | Natural Park of Serra de São Mamede (Portugal) | x | x | x | ||
Valasiuk et al., 2018 [94] | Fulufjället National Park Area (Sweden-Norway) | x | ||||
Molina et al., 2019 [95] | Cazorla, Segura y Las Villa National Park and Doñana National Park (Spain) | x | ||||
Chi-Ok Oh et al., 2019 [96] | Jiri Mountains National Park (Korea) | x | ||||
Ramel C et al., 2020 [97] | Western Swiss Alps (Switzerland) | x | x | x |
Author | Type of ES | Sub-Category | Estimation Driver | Valuation Method |
---|---|---|---|---|
Považan et al., 2015 [87] | Provisioning | Food | Honey | Market price |
Seed | Market price | |||
Crop | Market price | |||
Livestock | Market price | |||
Fibre | Timber | Market price | ||
Fresh water | Water supply | Market price | ||
Gandarillas et al., 2016 [88] | Provisioning | Food | Livestock | Market price |
Fresh water | Water supply | Replacement cost | ||
Ninan et al., 2016 [89] | Provisioning | Food | Livestock | Benefit transfer |
Food | Market price | |||
Torres-Miralles et al., 2017 [90] | Provisioning | Food | Olive groves | Contingent valuation |
Schirpke et al., 2017 [91] | Provisioning | Food | Crop | Market price |
Mushrooms | Market price | |||
Fibre | Timber | Market price | ||
Fresh water | Water supply | Market price | ||
Marta-Pedroso et al., 2018 [93] | Provisioning | Food | Crop | Market price |
Livestock | Market price | |||
Fibre | Timber | Market price | ||
Ramel C et al., 2020 [97] | Provisioning | Food | Milk | Market price |
Meal | Market price | |||
Cheese | Market price | |||
Fibre | Timber | Market price |
Author | Type of ES | Sub-Category | Estimation Driver | Valuation Method |
---|---|---|---|---|
Považan et al., 2015 [87] | Regulating | Climate regulation | Carbon sequestration | Benefit transfer |
Erosion regulation | Flood control and erosion control | Benefit transfer | ||
Water purification | Water retention | Benefit transfer | ||
Ninan et al., 2016 [89] | Regulating | Water purification | Water retention | Alternate cost |
Climate regulation | Carbon sequestration | Market price and damage cost | ||
Erosion regulation | Soil erosion control | Hedonic pricing and opportunity cost | ||
Air quality regulation | Air purification | Alternate cost | ||
Pollination | Pollination | Benefit transfer | ||
Torres-Miralles et al., 2017 [90] | Regulating | Air quality regulation Water purification Erosion regulation | WTP for ecosystem conservation | Contingent valuation |
Schirpke et al., 2017 [91] | Regulating | Climate regulation | Carbon sequestration | Market price |
Water purification | Water retention | Restoration cost | ||
Erosion regulation | Soil erosion control | Replacement cost | ||
Marta-Pedroso et al., 2018 [93] | Regulating | Climate regulation | Carbon sequestration | Benefit transfer |
Erosion regulation | Soil erosion control | Benefit transfer | ||
Ramel C et al., 2020 [97] | Regulating | Climate regulation | Carbon sequestration | Market price |
Erosion regulation | Soil erosion control | Avoided damage cost |
Author | Type of ES | Sub-Category | Estimation Driver | Valuation Method |
---|---|---|---|---|
Považan et al., 2015 [87] | Cultural | Recreation and ecotourism | Hunting | Market price |
Tourism | Travel cost | |||
Gandarillas et al., 2016 [88] | Cultural | Recreation and ecotourism | Ecotourism | Market price |
Cultural heritage values | Heritage value | Contingent valuation | ||
Ninan et al., 2016 [89] | Cultural | Recreation and ecotourism | Tourism | Travel cost and Benefit transfer |
Torres-Miralles et al., 2017 [90] | Cultural | Recreation and ecotourism Cultural heritage values Aesthetic value | WTP to ecosystem conservation | Contingent valuation |
Schirpke et al., 2017 [91] | Cultural | Recreation and ecotourism | Tourism | Travel cost |
Valasiuk et al., 2018 [94] | Cultural | Recreation and ecotourism | Recreational area | Choice Experiment |
Chi-Ok Oh et al., 2019 [96] | Cultural | Spiritual and religious value | Heritage value | Contingent valuation |
Ramel C et al., 2020 [97] | Cultural | Recreation and ecotourism | Hunting | Market price |
Recreational activity | Benefit transfer |
Author | Type of ES | Sub-Category | Estimation Driver | Valuation Method |
---|---|---|---|---|
Ninan et al., 2016 [89] | Supporting | Nutrient cycling | Accumulating nutrients | Alternate cost and market price |
Author | Type of ES | Estimation Driver | Valuation Method |
---|---|---|---|
Gandarillas et al., 2016 [88] | Biodiversity | - | Benefit transfer |
Ninan et al., 2016 [89] | Biodiversity | WTP for elephant conservation | Contingent valuation |
Torres-Miralles et al., 2017 [90] | Biodiversity | WTP for ecosystem conservation | Contingent valuation |
Ferreira et al., 2017 [92] | Biodiversity | WTP for the ecosystem conservation | Contingent valuation |
Marta-Pedroso et al., 2018 [93] | Biodiversity | Payment to ecosystem conservation | Contingent valuation |
Molina et al., 2019 [95] | Biodiversity | WTP for three flagship species | Contingent valuation |
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Pisani, D.; Pazienza, P.; Perrino, E.V.; Caporale, D.; De Lucia, C. The Economic Valuation of Ecosystem Services of Biodiversity Components in Protected Areas: A Review for a Framework of Analysis for the Gargano National Park. Sustainability 2021, 13, 11726. https://doi.org/10.3390/su132111726
Pisani D, Pazienza P, Perrino EV, Caporale D, De Lucia C. The Economic Valuation of Ecosystem Services of Biodiversity Components in Protected Areas: A Review for a Framework of Analysis for the Gargano National Park. Sustainability. 2021; 13(21):11726. https://doi.org/10.3390/su132111726
Chicago/Turabian StylePisani, Domenico, Pasquale Pazienza, Enrico Vito Perrino, Diana Caporale, and Caterina De Lucia. 2021. "The Economic Valuation of Ecosystem Services of Biodiversity Components in Protected Areas: A Review for a Framework of Analysis for the Gargano National Park" Sustainability 13, no. 21: 11726. https://doi.org/10.3390/su132111726
APA StylePisani, D., Pazienza, P., Perrino, E. V., Caporale, D., & De Lucia, C. (2021). The Economic Valuation of Ecosystem Services of Biodiversity Components in Protected Areas: A Review for a Framework of Analysis for the Gargano National Park. Sustainability, 13(21), 11726. https://doi.org/10.3390/su132111726