2022
DOI: 10.3897/oneeco.7.e84925
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The Integrated system for Natural Capital Accounting (INCA) in Europe: twelve lessons learned from empirical ecosystem service accounting

Abstract: The Integrated system for Natural Capital Accounting (INCA) was developed and supported by the European Commission to test and implement the System of integrated Environmental and Economic Accounting -Ecosystem Accounting (SEEA EA). Through the compilation of nine Ecosystem Services (ES) accounts, INCA can make available to any interested ecosystem accountant a number of lessons learned. Amongst the conceptual lessons learned, we can mention: (i) for accounting purposes, ES should be clustered according to the… Show more

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Cited by 6 publications
(3 citation statements)
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“…Estimation of the benefits each ecosystem service provided to the economy is complex and difficult as there is no monitoring system that can measure these services in detail [111]. The Integrated System for Natural Capital Accounting (INCA) developed a method of measuring ES potential and ES demand at the European scale [112], aggregating over an accounting area, and then estimating the actual ES use as the share of demand that can be satisfied by the potential. ES use was calculated for every ecosystem type that provided the service and was recorded in the supply table, but instead of monetary values (provided in an aggregated form for the entire EU), we used relative supply estimates (Table A3) [111].…”
Section: Fire Exposure and Vulnerabilitymentioning
confidence: 99%
“…Estimation of the benefits each ecosystem service provided to the economy is complex and difficult as there is no monitoring system that can measure these services in detail [111]. The Integrated System for Natural Capital Accounting (INCA) developed a method of measuring ES potential and ES demand at the European scale [112], aggregating over an accounting area, and then estimating the actual ES use as the share of demand that can be satisfied by the potential. ES use was calculated for every ecosystem type that provided the service and was recorded in the supply table, but instead of monetary values (provided in an aggregated form for the entire EU), we used relative supply estimates (Table A3) [111].…”
Section: Fire Exposure and Vulnerabilitymentioning
confidence: 99%
“…The ES capacity of other vegetation types possible at that location (e.g., potential natural vegetation (PNV)), or ET changes related to major changes in land use (e.g., forest clearing for agricultural areas or habitat restoration) are not considered; In MAES-HU, we did not define the first level of the cascade merely as the basic structure of the ecosystems (as in earlier works, e.g., [26,75]), but we also added a normative aspect to our selection criteria, so that the selected indicators would be able to distinguish between "good" and "bad" conditions [76]. In addition, we also aimed to catch those features of the ecosystems that describe their integrity connected to the delivery of ES in a mechanistic way (as set out in [50,76]) and that can be therefore linked to ES models [77]. This could be implemented more in the ES-specific condition indicators but were less required for general EC indicators (see also [35]).…”
Section: How Can We Define Ecosystem Service Capacity Operationally?mentioning
confidence: 99%
“…The Common International Classification of Ecosystem Services (CICES) provides a broadly accepted, unified framework that underlines the development of the global system of natural capital accounting. In Europe, the related standards are set by the INCA project (La Notte et al, 2022), while in the United States, the implementation of environmental-economic accounting is guided by a strategy document (White House, 2023).…”
Section: Introductionmentioning
confidence: 99%