{"id":1709,"date":"2025-01-07T14:55:05","date_gmt":"2025-01-07T14:55:05","guid":{"rendered":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/?post_type=kpi&#038;p=1709"},"modified":"2025-01-08T16:53:23","modified_gmt":"2025-01-08T16:53:23","slug":"ecosystem-condition-change-by-ecosystem-type","status":"publish","type":"kpi","link":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/","title":{"rendered":"[Secondary] Ecosystem condition change, by ecosystem type"},"template":"","impact_area":[3],"sdg":[18,21,29,19,13],"class_list":["post-1709","kpi","type-kpi","status-publish","hentry","impact_area-biodiversity","sdg-18","sdg-21","sdg-29","sdg-19","sdg-13"],"acf":{"id":"BIO 02","units":"Change in condition, from baseline","rationale":"<p>Measuring changes in ecosystem condition at a site over time is one way to track changes in biodiversity. This is reflected in key guidance on metrics from the <a href=\"https:\/\/tnfd.global\/\">Taskforce on Nature-related Financial Disclosures<\/a> (TNFD), the <a href=\"https:\/\/capitalscoalition.org\/project\/align\/\">Aligning Accounting Approaches for Nature<\/a> project and the System of Environmental-Economic Accounting (SEEA).<\/p>\n<p>Best practice guidance in biodiversity metrics acknowledges ecosystems and species metrics as key components for measuring the state of nature Ecosystem metrics can be divided into extent and condition metrics. While positive impact measures based upon ecosystem extent are simpler to assess (and are more heavily reflected in the Positive Impact Indicators Directory), it is important to complement them with condition metrics where possible. Measuring extent alone fails to account for changes in the quality of ecosystems.<\/p>\n<p>This indicator is aligned with the Nature Positive Initiative\u2019s proposed SON Metric Framework (SON A2 and S6 \u2013 Ecosystem condition change by ecosystem type).<\/p>\n<p>While this indicator needs to be considered and measurement processes constructed at a site level, it can also be summed across the portfolio by using condition-adjusted area (see below for details).<\/p>\n","methodology":"<p>Measurement approaches for ecosystem condition vary in their underlying methods (<a href=\"https:\/\/capitalscoalition.org\/wp-content\/uploads\/2023\/10\/Align_eco_condition_primer.pdf\">Align, 2023<\/a>), but here we will focus on methods that will enable the tracking of change in condition over the course of an investment. It is possible to estimate ecosystem condition indirectly, using global datasets that map pressures on ecosystems. However, these are generally not granular enough, nor updated quickly enough, to reflect changes in ecosystem condition within a project site of the course of an investment (for example, over a period of 3 \u2013 10 years). Therefore, on the ground data collection, specific to the ecosystem type, is necessary to gather meaningful impact data for this indicator.<\/p>\n<p>Metrics to assess ecosystem condition reflect three different elements of condition: composition, structure and function. The variables measured to assess these will vary site by site, depending on the type of ecosystem assessed. Measuring ecosystem condition therefore entails identifying relevant characteristics to assess, then developing indicators and metrics for those characteristics, and combining them to assess overall condition.<\/p>\n<p><a href=\"https:\/\/capitalscoalition.org\/wp-content\/uploads\/2023\/10\/Align_eco_condition_primer.pdf\">Align (2023)<\/a>, following the SEEA methodology, gives the following definitions for composition, structure and function indicators. These are also reflected in <a href=\"https:\/\/tnfd.global\/wp-content\/uploads\/2023\/08\/Guidance_on_the_identification_and_assessment_of_nature-related_Issues_The_TNFD_LEAP_approach_V1.1_October2023.pdf\">TNFD guidance (2023, pg 133)<\/a>:<\/p>\n<ul>\n<li><em>Composition: Indicators that measure what species are present in the species assemblage as a whole and their relative abundances (rather than the number of individuals within a single species) within an ecosystem. <\/em><\/li>\n<li><em>Structure: Indicators that reflect aggregate biophysical properties of ecosystems, irrespective of specific species composition, such as vegetation heights or seabed habitat complexity. At a landscape scale, structure also includes levels of fragmentation and connectivity (i.e., how linked one patch of habitat is to another). <\/em><\/li>\n<li><em>Function: Indicators that measure a process that the ecosystem completes or reflects the ability to undertake these processes, e.g., net primary production, water filtration.<\/em><\/li>\n<\/ul>\n<p><u>To measure against this indicator:<\/u><\/p>\n<ol>\n<li>First, identify which ecosystem types are represented within your financed area. Ecosystem types are delineated within Levels 5 and 6 of the <a href=\"https:\/\/global-ecosystems.org\/page\/typology\">IUCN Global Ecosystem Typology<\/a>, and are often mapped within national-level databases.<\/li>\n<li>Then calculate the condition of each ecosystem type. Where possible, this should be done following established rating methods for that ecosystem (see references for sources). Where this is not possible, use the following steps, for each ecosystem type, which is in line with draft A2 and S6 \u2013 Ecosystem condition change by ecosystem type.<\/li>\n<li>Select a mix of composition, structure and function variables relevant for the ecosystem type, including both abiotic and biotic variables. Selecting relevant variables per ecosystem type and measuring them is likely to require local ecological expertise, and on-the-ground assessment.<\/li>\n<li>Set a reference condition for each ecosystem type to be able to assess the degree of ecosystem modification. Some examples of reference conditions given by Align (2023), are:<\/li>\n<\/ol>\n<ol>\n<li style=\"list-style-type: none;\">\n<ul>\n<li>\u00a0\u201cUndisturbed or minimally disturbed condition of an intact ecosystem: The condition of an ecosystem with maximum ecosystem integrity with no or minimal disturbance\u201d.<\/li>\n<li>\u201cHistorical condition: The condition of an ecosystem at some point or period in its history that is considered to represent a stable natural state (e.g., pre-industrial or pre-intensive agriculture)\u201d.<\/li>\n<li>\u201cLeast-disturbed condition: The currently best available condition of an ecosystem\u201d.<\/li>\n<li>\u201cContemporary condition: The condition of an ecosystem at a certain point or period in its recent history for which comparable data are available\u201d.<\/li>\n<\/ul>\n<\/li>\n<li>Calculate the ecosystem condition by assessing each of the selected variables, and categorising the state of the variable as compared to the reference condition. See <a href=\"https:\/\/seea.un.org\/sites\/seea.un.org\/files\/documents\/EA\/seea_ea_white_cover_final.pdf\">UN SEEA<\/a> guidance for more information. Groupings are often used to reflect the combined variables here \u2013 for example, \u2018low\u2019, \u2018medium\u2019, \u2018high\u2019, \u2018pristine\u2019.<\/li>\n<\/ol>\n<p>At the start of a project, the ecosystem condition <strong>baseline<\/strong> should be calculated. Then, when condition is measured throughout and at the end of the project, the change in the condition compared to this baseline should be reflected.<\/p>\n<p><u>To calculate condition-adjusted area:<\/u><\/p>\n<p>Condition-adjusted area is a way of taking the extent of an ecosystem impacted by business activities and weighting it by its condition. For example, if your investment affects an area of 100 hectares of an ecosystem, and the baseline condition is 50%, the condition-adjusted area would be 100 x 0.5 = 50 hectares equivalents. If, after several years of interventions to restore the area, the ecosystem condition was calculated to be 70%, then the condition-adjusted area would be 70 hectares equivalents.<\/p>\n<p>Using condition-adjusted area can be a helpful way of showing overall improvements (or negative impacts) across a range of sites.<\/p>\n","communication":"<p>This indicator is appropriate for providing an indication of what impact the project intervention is having upon the state of biodiversity within the project site. However, it may take several years for a trend to become apparent, as species respond to the changes in their environment.<\/p>\n<p>Following the draft <a href=\"https:\/\/www.naturepositive.org\/app\/uploads\/2024\/10\/Consultation-Brief-_State-of-Nature-Metrics_8Oct2024.pdf\">NPI SON Framework indicators<\/a> A2 and S6 (Ecosystem condition change by ecosystem type), users should report absolute and percentage of extent of each ecosystem type in each condition class and change since baseline. For example: \u2018<em>Ecosystem A: Extent = 100ha, of which 10% in Excellent, 40% in Very Good, 0% in Good, 30% in Poor and 20% in Very Poor condition\u2019.<\/em> Reporting condition adjusted area of each ecosystem type in a location (weighted ha) could also be considered.<\/p>\n<p>While this indicator needs to be considered and measurement processes constructed at a site level, it can also be summed across the portfolio by using condition-adjusted area. Condition-adjusted area but should be displayed alongside the unweighted-area for reference. Change in time can then be seen in improvements (or otherwise) of the condition-adjusted areas across the portfolio.<\/p>\n","considerations":[{"text":"Useful for funds who aim to increase or restore biodiversity through project interventions."},{"text":"Requires on the ground monitoring; it cannot be monitored remotely. "},{"text":"Relatively costly to measure effectively."},{"text":"Given the time required for ecosystem condition to increase, this indicator should only be used in long term investments (>5 years)."},{"text":"Local experts and stakeholders should be consulted in the process of variable selection for each ecosystem type, and involved in the process assessing ecosystem condition."}],"resources":[{"link_text":"United Nations et al. (2021). System of Environmental-Economic Accounting\u2014 Ecosystem Accounting (SEEA EA). White cover publication, pre-edited text subject to official editing. ","link_url":"https:\/\/seea.un.org\/ecosystem-accounting"},{"link_text":"UNEP-WCMC, Capitals Coalition, Arcadis, ICF, WCMC Europe (2023) Measuring Ecosystem Condition \u2013 A primer for business, Aligning accounting approaches for nature.","link_url":"https:\/\/capitalscoalition.org\/wp-content\/uploads\/2023\/10\/Align_eco_condition_primer.pdf"},{"link_text":"Nature Positive Initiative \u2013 State of Nature Metrics. Draft for consultation (October 2024). ","link_url":"https:\/\/www.naturepositive.org\/app\/uploads\/2024\/10\/Consultation-Brief-_State-of-Nature-Metrics_8Oct2024.pdf"},{"link_text":"Guidance on the identification and assessment of nature-related issues: The LEAP approach. Version 1.1. October 2023","link_url":"https:\/\/tnfd.global\/wp-content\/uploads\/2023\/08\/Guidance_on_the_identification_and_assessment_of_nature-related_Issues_The_TNFD_LEAP_approach_V1.1_October2023.pdf"}],"links_to_other_impact_area_kpis":"<p>Projects reporting positive impact through this KPI may also demonstrate benefits for:<\/p>\n<p>Biodiversity \u2013 BIO 01, BIO 03, BIO 04<\/p>\n<p>Climate Action \u2013 CMA 01, CMA 02 and CMA 04<\/p>\n<p>Livelihoods and Gender \u2013 LG 02<\/p>\n<p>Sustainable Production \u2013 PRO 04, PRO 06, PRO 07<\/p>\n","case_studies":"<p>TBD<\/p>\n","requirements":{"spatial_data":false,"project_specific_criteria":true,"on_the_ground_verification":true},"download":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/wp-content\/uploads\/2025\/01\/BIO-02-Ecosystem-condition-change-by-ecosystem-type.pdf"},"yoast_head":"<!-- This site is optimized with the Yoast SEO plugin v19.14 - https:\/\/yoast.com\/wordpress\/plugins\/seo\/ -->\n<title>[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub<\/title>\n<meta name=\"robots\" content=\"index, follow, max-snippet:-1, max-image-preview:large, max-video-preview:-1\" \/>\n<link rel=\"canonical\" href=\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/\" \/>\n<meta property=\"og:locale\" content=\"en_US\" \/>\n<meta property=\"og:type\" content=\"article\" \/>\n<meta property=\"og:title\" content=\"[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub\" \/>\n<meta property=\"og:url\" content=\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/\" \/>\n<meta property=\"og:site_name\" content=\"Land Use Impact Hub\" \/>\n<meta property=\"article:modified_time\" content=\"2025-01-08T16:53:23+00:00\" \/>\n<meta name=\"twitter:card\" content=\"summary_large_image\" \/>\n<script type=\"application\/ld+json\" class=\"yoast-schema-graph\">{\"@context\":\"https:\/\/schema.org\",\"@graph\":[{\"@type\":\"WebPage\",\"@id\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/\",\"url\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/\",\"name\":\"[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub\",\"isPartOf\":{\"@id\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/#website\"},\"datePublished\":\"2025-01-07T14:55:05+00:00\",\"dateModified\":\"2025-01-08T16:53:23+00:00\",\"inLanguage\":\"en-US\",\"potentialAction\":[{\"@type\":\"ReadAction\",\"target\":[\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/\"]}]},{\"@type\":\"WebSite\",\"@id\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/#website\",\"url\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/\",\"name\":\"Land Use Impact Hub\",\"description\":\"Just another WordPress site\",\"potentialAction\":[{\"@type\":\"SearchAction\",\"target\":{\"@type\":\"EntryPoint\",\"urlTemplate\":\"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/?s={search_term_string}\"},\"query-input\":\"required name=search_term_string\"}],\"inLanguage\":\"en-US\"}]}<\/script>\n<!-- \/ Yoast SEO plugin. -->","yoast_head_json":{"title":"[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub","robots":{"index":"index","follow":"follow","max-snippet":"max-snippet:-1","max-image-preview":"max-image-preview:large","max-video-preview":"max-video-preview:-1"},"canonical":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/","og_locale":"en_US","og_type":"article","og_title":"[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub","og_url":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/","og_site_name":"Land Use Impact Hub","article_modified_time":"2025-01-08T16:53:23+00:00","twitter_card":"summary_large_image","schema":{"@context":"https:\/\/schema.org","@graph":[{"@type":"WebPage","@id":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/","url":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/","name":"[Secondary] Ecosystem condition change, by ecosystem type - Land Use Impact Hub","isPartOf":{"@id":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/#website"},"datePublished":"2025-01-07T14:55:05+00:00","dateModified":"2025-01-08T16:53:23+00:00","inLanguage":"en-US","potentialAction":[{"@type":"ReadAction","target":["https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/kpi\/ecosystem-condition-change-by-ecosystem-type\/"]}]},{"@type":"WebSite","@id":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/#website","url":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/","name":"Land Use Impact Hub","description":"Just another WordPress site","potentialAction":[{"@type":"SearchAction","target":{"@type":"EntryPoint","urlTemplate":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/?s={search_term_string}"},"query-input":"required name=search_term_string"}],"inLanguage":"en-US"}]}},"_links":{"self":[{"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/kpi\/1709"}],"collection":[{"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/kpi"}],"about":[{"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/types\/kpi"}],"wp:attachment":[{"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/media?parent=1709"}],"wp:term":[{"taxonomy":"impact_area","embeddable":true,"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/impact_area?post=1709"},{"taxonomy":"sdg","embeddable":true,"href":"https:\/\/kpi-directory.shared-api-01.production.linode.unep-wcmc.org\/index.php\/wp-json\/wp\/v2\/sdg?post=1709"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}