Ecosystem services and the need for
multiple classification system –
Justifications
Presented by- Hina Chaudhary
Department of Botany, Delhi University
INTRODUCTION
• Ecosystem services are the benefits people obtain from ecosystems. This
terminology is derived from two representative definitions:
• “Ecosystem goods (such as food) and services (such as waste assimilation)
represent the benefits human populations derive, directly or indirectly, from
ecosystem functions ”(Costanza et al., 1997).
• “Ecosystem services are the conditions and processes through which
natural ecosystems, and the species that make them up, sustain and fulfill
human life. They maintain biodiversity and the production of ecosystem
goods” (Daily, 1997).
Classification of ecosystem services
• Ecosystem services have been classified in various ways, including:
Functional groupings’
such as regulation,
carrier, habitat,
production, and
information services
(de Groot et al. 2002)
Organisational groupings’,
such as services associated with
certain species that regulate
external inputs into a system, and
those related to the organisation of
biological entities
(Norberg 1999)
Descriptive groupings’,
such as renewable
resource goods, non-
renewable resource
goods, physical structure
services, biotic services,
biogeochemical services,
information services, and
social and cultural
services
(Moberg and Folke 1999)
http://jncc.defra.gov.uk/default.aspx?page=6382
The most widely adopted classification is the ‘functional
grouping’ where ecosystem services are divided into four
categories. Some overlap occurs between categories but the four
main groupings include:
Assessment, Millennium Ecosystem. "Ecosystem and human well-being: biodiversity synthesis." World Resources Institute, Washington, DC (2005).
• Several ES classification systems have been proposed (Costanza et al.,
1997; Daily, 1997, 1999; De Groot et al., 2002; MEA, 2003; de Groot
2006; Boyd and Banzhaf, 2007; Fisher and Turner, 2008; TEEB, 2010).
• Various Classifications have been proposed for Scientific analysis,
Economic valuation and Policy making.
• Costanza (2008) states that there are many useful ways to classify
ecosystem goods and services, and that the goal should not be to have a
single, consistent system, but rather a pluralism of typologies that can
be useful for different purposes.
• A drawback is that the use of multiple classification systems makes
comparisons and integration of assessments with other data difficult
(Haines-Young and Potschin, 2011).
Among the more commonly used classification systems,
 Costanza et al. (1997) categorized Ecosystem Services into 17
major groups
1Gas regulation 2 Climate regulation 3 Disturbance regulation
4 Water regulation 5 Water supply. 6 Erosion control and
sediment retention. 7 Soil formation 8 Nutrient cycling
9 Waste treatment 10 Pollination 11 Biological control.
12 Refugia 13 Food production 14 Raw materials .
15 Genetic resources. 16 Recreation. 17 Cultural
Assessment, Millennium Ecosystem. "Ecosystem and human well-being: biodiversity synthesis." World
Resources Institute, Washington, DC (2005).
MEA (2005) Millennium Ecosystem Assessment, categorized a similar set of ES
as “provisioning”, “regulating”, “supporting” and “cultural
HABITAT OR SUPPORTING SERVICES’
cover habitats for species and maintenance of genetic diversity.
TEEB, 2010. The Economics of Ecosystems and Biodiversity: Mainstreaming the Economics of Nature: A synthesis of the
approach, conclusions and recommendations of TEEB. p. 36.
The Economics of Ecosystems and Biodiversity (TEEB) initiative (2010)
adopted a classification based on MEA, but considered “supporting services” to be ecological processes
rather than Ecosystem Services, and emphasized the importance of “habitat services” by assigning it a
separate category. Initially, the TEEB classification contained 22 ES (TEEB, 2010) but was reduced to 17
ES (TEEB, 2010).
The hierarchical structure of CICES, illustrated with reference to a provisioning service (cultivated
plants- cereals) (Source: CICES,2011)
A new classification system, the Common International Classification of Ecosystem
Services (CICES), is being developed by the European Environment Agency (www.cices.eu).
The aim of CICES is to propose a universal classification of ES that is both consistent with accepted
categorizations and allows easy translation of statistical information between different
applications (Haines-Young and Potschin, 2011).
Case Study
•This paper identifies and qualitatively assesses methods for Mapping ES in terrestrial
landscapes, based on a systematic review of the scientific literature.
•Mapping ecosystem services is essential to understand how ecosystems contribute to
human wellbeing and to support policies which have an impact on natural resources.
•Landscape - An area viewed at a scale determined by ecological, cultural-historical,
social and/or economic considerations.
•Landscape services - The contributions of landscapes and landscape elements to
human well-being
Geographical distribution of reviewed studies (n = 170). The number of studies performed in
each country ranges from 1 (light grey) to 26 (black). White = zero.
Most studies were carried out in Europe (87), followed by North America (31), Asia (15),
Africa and Australia (12 each), and South America (11)
O. Englund et al., 2017
O. Englund et al., 2017
Number of times different ES have been mapped at a landscape scale, divided into different
method types used.
Regulating and maintenance services were most commonly mapped (165),followed
by cultural (85), and provisioning services (73).
O. Englund et al., 2017
CONCLUSION
•The reviewed papers used different classification systems, but conversion of the
reviewed ES into the CICES classification system was in most cases fairly
straight-forward.
•Most of the ES that could not be fitted into CICES were either bundles of ES
mapped together or examples of ecosystem processes rather than ES.
•Further development of CICES should consider whether to only include final ES
and thus exclude ecosystem processes and functions.
O. Englund et al., 2017
Final ES
Intermediate ES,
or an ecosystem
function.by weathering,
decomposition
what benefits to humans
the soils facilitate!
Soil formation
and composition
Cultivation of crops,
or—indirectly, since
soils facilitate
vegetation growth
mediation of water
flows, and climate
control
References
• Ecosystem services: Multiple classification systems are needed, Biological
conservation 141 Robert Costanza (2008) 350 –352
• Costanza, Robert, et al. "The value of the world's ecosystem services and natural
capital." nature 387.6630 (1997): 253.
• Assessment, Millennium Ecosystem. "Ecosystem and human well-being:
biodiversity synthesis." World Resources Institute, Washington, DC (2005).
• TEEB, 2010. The Economics of Ecosystems and Biodiversity: Mainstreaming the
Economics of Nature: A synthesis of the approach, conclusions and
recommendations of TEEB. p. 36.
• Haines-Young, R., Potschin, M., 2013. Common International Classification of
Ecosystem Services (CICES): Consultation on Version 4, August-December 2012.
EEA Framework Contract No EEA/IEA/09/003. Pieejams: http://cices.eu/
• Costanza, Robert, et al. "Twenty years of ecosystem services: how far have we
come and how far do we still need to go?." Ecosystem Services 28 (2017): 1-16.
• Englund, Oskar, Göran Berndes, and Christel Cederberg. "How to analyse
ecosystem services in landscapes—A systematic review." Ecological Indicators 73
(2017): 492-504.
Thank you.

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Ecosysytem services&classification

  • 1. Ecosystem services and the need for multiple classification system – Justifications Presented by- Hina Chaudhary Department of Botany, Delhi University
  • 2. INTRODUCTION • Ecosystem services are the benefits people obtain from ecosystems. This terminology is derived from two representative definitions: • “Ecosystem goods (such as food) and services (such as waste assimilation) represent the benefits human populations derive, directly or indirectly, from ecosystem functions ”(Costanza et al., 1997). • “Ecosystem services are the conditions and processes through which natural ecosystems, and the species that make them up, sustain and fulfill human life. They maintain biodiversity and the production of ecosystem goods” (Daily, 1997).
  • 3. Classification of ecosystem services • Ecosystem services have been classified in various ways, including: Functional groupings’ such as regulation, carrier, habitat, production, and information services (de Groot et al. 2002) Organisational groupings’, such as services associated with certain species that regulate external inputs into a system, and those related to the organisation of biological entities (Norberg 1999) Descriptive groupings’, such as renewable resource goods, non- renewable resource goods, physical structure services, biotic services, biogeochemical services, information services, and social and cultural services (Moberg and Folke 1999) http://jncc.defra.gov.uk/default.aspx?page=6382
  • 4. The most widely adopted classification is the ‘functional grouping’ where ecosystem services are divided into four categories. Some overlap occurs between categories but the four main groupings include: Assessment, Millennium Ecosystem. "Ecosystem and human well-being: biodiversity synthesis." World Resources Institute, Washington, DC (2005).
  • 5. • Several ES classification systems have been proposed (Costanza et al., 1997; Daily, 1997, 1999; De Groot et al., 2002; MEA, 2003; de Groot 2006; Boyd and Banzhaf, 2007; Fisher and Turner, 2008; TEEB, 2010). • Various Classifications have been proposed for Scientific analysis, Economic valuation and Policy making. • Costanza (2008) states that there are many useful ways to classify ecosystem goods and services, and that the goal should not be to have a single, consistent system, but rather a pluralism of typologies that can be useful for different purposes. • A drawback is that the use of multiple classification systems makes comparisons and integration of assessments with other data difficult (Haines-Young and Potschin, 2011).
  • 6. Among the more commonly used classification systems,  Costanza et al. (1997) categorized Ecosystem Services into 17 major groups 1Gas regulation 2 Climate regulation 3 Disturbance regulation 4 Water regulation 5 Water supply. 6 Erosion control and sediment retention. 7 Soil formation 8 Nutrient cycling 9 Waste treatment 10 Pollination 11 Biological control. 12 Refugia 13 Food production 14 Raw materials . 15 Genetic resources. 16 Recreation. 17 Cultural
  • 7. Assessment, Millennium Ecosystem. "Ecosystem and human well-being: biodiversity synthesis." World Resources Institute, Washington, DC (2005). MEA (2005) Millennium Ecosystem Assessment, categorized a similar set of ES as “provisioning”, “regulating”, “supporting” and “cultural
  • 8. HABITAT OR SUPPORTING SERVICES’ cover habitats for species and maintenance of genetic diversity. TEEB, 2010. The Economics of Ecosystems and Biodiversity: Mainstreaming the Economics of Nature: A synthesis of the approach, conclusions and recommendations of TEEB. p. 36. The Economics of Ecosystems and Biodiversity (TEEB) initiative (2010) adopted a classification based on MEA, but considered “supporting services” to be ecological processes rather than Ecosystem Services, and emphasized the importance of “habitat services” by assigning it a separate category. Initially, the TEEB classification contained 22 ES (TEEB, 2010) but was reduced to 17 ES (TEEB, 2010).
  • 9. The hierarchical structure of CICES, illustrated with reference to a provisioning service (cultivated plants- cereals) (Source: CICES,2011) A new classification system, the Common International Classification of Ecosystem Services (CICES), is being developed by the European Environment Agency (www.cices.eu). The aim of CICES is to propose a universal classification of ES that is both consistent with accepted categorizations and allows easy translation of statistical information between different applications (Haines-Young and Potschin, 2011).
  • 10. Case Study •This paper identifies and qualitatively assesses methods for Mapping ES in terrestrial landscapes, based on a systematic review of the scientific literature. •Mapping ecosystem services is essential to understand how ecosystems contribute to human wellbeing and to support policies which have an impact on natural resources. •Landscape - An area viewed at a scale determined by ecological, cultural-historical, social and/or economic considerations. •Landscape services - The contributions of landscapes and landscape elements to human well-being
  • 11. Geographical distribution of reviewed studies (n = 170). The number of studies performed in each country ranges from 1 (light grey) to 26 (black). White = zero. Most studies were carried out in Europe (87), followed by North America (31), Asia (15), Africa and Australia (12 each), and South America (11) O. Englund et al., 2017
  • 12. O. Englund et al., 2017 Number of times different ES have been mapped at a landscape scale, divided into different method types used.
  • 13. Regulating and maintenance services were most commonly mapped (165),followed by cultural (85), and provisioning services (73). O. Englund et al., 2017
  • 14. CONCLUSION •The reviewed papers used different classification systems, but conversion of the reviewed ES into the CICES classification system was in most cases fairly straight-forward. •Most of the ES that could not be fitted into CICES were either bundles of ES mapped together or examples of ecosystem processes rather than ES. •Further development of CICES should consider whether to only include final ES and thus exclude ecosystem processes and functions. O. Englund et al., 2017
  • 15. Final ES Intermediate ES, or an ecosystem function.by weathering, decomposition what benefits to humans the soils facilitate! Soil formation and composition Cultivation of crops, or—indirectly, since soils facilitate vegetation growth mediation of water flows, and climate control
  • 16. References • Ecosystem services: Multiple classification systems are needed, Biological conservation 141 Robert Costanza (2008) 350 –352 • Costanza, Robert, et al. "The value of the world's ecosystem services and natural capital." nature 387.6630 (1997): 253. • Assessment, Millennium Ecosystem. "Ecosystem and human well-being: biodiversity synthesis." World Resources Institute, Washington, DC (2005). • TEEB, 2010. The Economics of Ecosystems and Biodiversity: Mainstreaming the Economics of Nature: A synthesis of the approach, conclusions and recommendations of TEEB. p. 36. • Haines-Young, R., Potschin, M., 2013. Common International Classification of Ecosystem Services (CICES): Consultation on Version 4, August-December 2012. EEA Framework Contract No EEA/IEA/09/003. Pieejams: http://cices.eu/ • Costanza, Robert, et al. "Twenty years of ecosystem services: how far have we come and how far do we still need to go?." Ecosystem Services 28 (2017): 1-16. • Englund, Oskar, Göran Berndes, and Christel Cederberg. "How to analyse ecosystem services in landscapes—A systematic review." Ecological Indicators 73 (2017): 492-504.