SLIDE 1 Aligning Biodiversity Measures for Business Sub-group 3A Corporate data inputs
Webinar 20 September 2019
SLIDE 2 ❑ Reminder of the objectives and context of the Aligning Biodiversity Measures for Business initiative ❑ Reminder of the objectives of the sub-group and of the webinar ❑ Presentation of the database on state, pressure, activity and response data sets ❑ Review of the SG3A position paper to finalize it for the Brazil workshop
▪ Output #1 - Data mapping – data used by each tool ▪ Output #2 - Agreement on common nomenclatures to request data from companies ▪ Output #3 – Link between between inventories of species and habitat and aggregated metrics approaches ▪ Output #4 – Other common ground principle
Agenda
SLIDE 3
Reminder of the objectives and context of the Aligning Biodiversity Measures for Business initiative
SLIDE 4
Reminder of the objectives of the sub-group and of the webinar
SLIDE 5
❑ Go to www.menti.com and use the code 76 29 81 ❑ What is this session about?
Mentimeter
SLIDE 6
1. Map the data sets required by each methodology as assessment inputs and briefly describe them (public or private, modelled or real data, geographic coverage, etc.). The focus is on data used to assess the extent of the impacts, and not to attribute them among stakeholders. 2. Identify common input data sets and agree on a limited set of input indicators and formats (including granularity) which companies could collect to feed most measurement approaches. 3. Determine links between site and corporate / portfolio level approaches and how data sets differ / are complementary or can reinforce each other.
Objectives of the sub-group
SLIDE 7
1. Complete data mapping for each initiative to determine which data sets are used and what further data may be available now and in the future based on a call for information from the European B@B platform for information. 2. Common nomenclature for data used within measurement approaches, relating this to the ‘tiers’ of accuracy within the IPCC and the the Natural Capital Protocol, and agreement on common data requests to companies. 3. Exploration of linkages of approaches that rely on data estimates and proxies with approaches that rely on measured data through common ground nomenclature of data pressures, for example. 4. Discussion and agreement to support other common ground principles identified previously.
Expected outputs of the sub-group
SLIDE 8 Linkage of the sub-group with sub-group 3B on metrics and characterisation factors
Input data
Sub-group 3A
Impacts on biodiversity (endpoint)
Tools or approach
Secondary inventory data CF & midpoints CF
Endpoints CF
Sub-group 3B (characterisation factors) ① Company’s data ② Fall back data sets Sub-group 3B (rationale of the different metrics)
Modeling of biodiversity impacts based on pressures and economic activity
Input data Impacts on biodiversity
① Company’s data ② Fall back data sets
Direct evaluation of biodiversity impacts based on data on biodiversity state
Sub-group 3A Sub-group 3B (rationale of the different metrics)
SLIDE 9
1. Review the SG3A draft position paper and provide feedback to validate it as input of the sub-group to the Brazil workshop.
Objectives of the webinar
SLIDE 10
❑ Go to www.menti.com and use the code 76 29 81 ❑ Questions? ➔ add them to the parking lot
Mentimeter
SLIDE 11
Review of the SG3A position paper to finalize it for the Brazil workshop
SLIDE 12
❑ 20190917_ABMB_SG3A-datasets_position- paper_v2.docx ❑ Sent by Julie Dimitrijevic on 17th September
SG3A position paper
SLIDE 13
❑ QUESTION #1: Should “attribution” data inputs be covered by the sub-group and how comprehensively? ❑ Go to www.menti.com and use the code 76 29 81
Remaining open questions
SLIDE 14
REVIEW - Output #1 - Data mapping – data used by each tool
SLIDE 15
❑ QUESTION #2A: In Table 1, should pressure categories be classified by sub-pressure instead? For instance, hydrological disturbance, etc. ❑ QUESTION #2B: Should data categories be mutually exclusive? Especially for data on biodiversity state. ❑ Go to www.menti.com and use the code 76 29 81
Remaining open questions
SLIDE 16 Data mapping – Figure 2
PAGE 16
Inventory data Pressures State Resources & emissions Economic quantification
activities
① Economic quantification of human activities ② Pressures, resources and emissions ③ State
SG3B SG3A
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SLIDE 17 Data mapping – Figure 3
PAGE 17 Area of irrigated cropland
Input indicator names
Water consummed Methane emissions
① ② ③ Values
10 100 1 567
Units
ha m3 kg
Categories
Land use Water resources Greenhouse gas emissions
Coming from company data (user-collected data) or from data sets
- riginating from external databases (e.g. Production/Crops data set
- riginating from FAOSTAT database)
These 6 input indicators are all input data. The input indicators within a category are expressed based on a
- nomenclature. For instance input
indicator ① and ② are expressed with the GLOBIO’s land use nomenclature and ③ and ④ are expressed with ReCiPe’s land use nomenclature
Area of intensive cropland 5 ha Area of monoculture crops/weeds 10 ha Area of intensive crops/weeds 5 ha
⑤ ⑥ ④
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SLIDE 18 Data mapping – Figure 4
PAGE 18
Database (e.g. FAOSTAT)
Data set #1 (e.g. Production/Crops) Input indicator #1.1 (e.g. Area harvested) Data set #2 (e.g. Forestry Production and Trade) Input indicator #1.2 (e.g. Yield) Input indicator #1.3 (e.g Production Quantity) Input indicator #2.1 (e.g. Production Quantity) Input indicator #2.2 (e.g. Import Quantity) Etc. www.menti.com Code 76 29 81
SLIDE 19 PAGE 19
Data mapping
❑ A database has been built by UNEP-WCMC and participants to the Gaining Consensus workshop in May 2019 in Cambridge, UK ❑ It has been refined to map the data sets used by approaches followed by the ABMB initiative and can be found here: https://www.dropbox.com/sh/ym0agydww9haz40/AABhLuktuX Ny3Ue8qfWv696Ca?dl=0 ❑ The following slides list categories of data contained in this
- database. The objective is NOT to have an exhaustive list
- f categories but rather to categorize properly data already in
the database.
SLIDE 20 PAGE 20
Data mapping
❑ Each initiative can use the database to map the data inputs it uses as externally collected input data or as inputs to build characterisation factors. ❑ This mapping is led coherently with the EU B@B update on biodiversity accounting tools for business led by Johan Lammerant: no need to do the work twice! ❑ The ID (#14 etc.) cited refer to the database here: https://www.dropbox.com/sh/ym0agydww9haz40/AABhLuktuX Ny3Ue8qfWv696Ca?dl=0
SLIDE 21 PAGE 21
Data mapping – Key messages
❑ Missing data for several approaches: Kering EP&L, Agrobiodiversity Index, STAR, Biodiversity Footprint calculator, BFFI. ❑ Overlap on some input data: ▪ FAO data on area harvested, yield, production of crops ▪ EXIOBASE data on emissions and resource consumption ▪ IBAT data on presence of threatened species, protected area proximity, etc.
SLIDE 22 PAGE 22
Data mapping – Biodiversity state – Table 3
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors GBS Integration of abundance data (ecological surveys) under consideration. IBAT data for extinction risk screening. NA BIM NA Range rarity layer. NA BIE Company data on one or more species identified as a priority biodiversity feature or area of priority habitat (as a proxy). Not known NA PBF Sectoral and local ecological studies used to adjust characterisation factors. NA IBAT data. BFFI NA NA NA
SLIDE 23 PAGE 23
Data mapping – Biodiversity state – Table 3
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors STAR Not known Not known Not known ABD Index Not known Not known Not known BF NA NA NA LIFE Index Status of conservation of natural vegetation; Length and width of biodiversity corridors; Stage of vegetal dynamics. Protected area categories; #45 – Ecoregions; Biological Importance of the Area (national classifications); threat status of species;
SLIDE 24 PAGE 24
Data mapping – Pressures, resources and emissions – Table 4
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors GBS Company data on land use change (LUC, including wetlands), GHG emissions, water consumption, N & P concentration (and in the future pollutant emissions). GLOBIO scenarios as proxy
FAO data on yields; Aqueduct data on water consumption by watershed; USGS data on mines around the world; EXIOBASE data on material consumption. BIM Company data on land use changes. NA #151 – FAO (crop) yield. BIE Company data for emissions to water and air, water abstraction, habitat destruction/degradation, disturbance and invasive species, assessed qualitatively based on timing
- f pressure, proportion of
population affected and severity of pressure. National or global averages of the same data if primary data unavailable NA PBF Company data on Energy use, Water use, Land
transformation, Emissions to water, Emissions to soil, Same data but from Life Cycle Inventories. NA
SLIDE 25 PAGE 25
Data mapping – Pressures, resources and emissions – Table 4
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors GBS Company data on land use change (LUC, including wetlands), GHG emissions, water consumption, N & P concentration (and in the future pollutant emissions). GLOBIO scenarios as proxy
FAO data on yields; Aqueduct data on water consumption by watershed; USGS data on mines around the world; EXIOBASE data on material consumption. BIM Company data on land use changes. NA #151 – FAO (crop) yield. BIE Company data for emissions to water and air, water abstraction, habitat destruction/degradation, disturbance and invasive species, assessed qualitatively based on timing
- f pressure, proportion of
population affected and severity of pressure. National or global averages of the same data if primary data unavailable NA
SLIDE 26 PAGE 26
Data mapping – Pressures, resources and emissions – Table 4
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors PBF Company data on Energy use, Water use, Land
transformation, Emissions to water, Emissions to soil, Emissions to air Same data but from Life Cycle Inventories. NA BFFI NA
- EXIOBASE data on resource
(land occupation) and material consumption Species Threat Abatement and Recovery (IUCN) Global pressure maps on climate change & severe weather, transportation & service corridor based on global data sets and combined to the threat assessment from the IUCN Red List. Combined to qualitative assessments of how threats would evolve due to actions implemented by the business assessed.
sity Index (Biodiversity International) Not known Not known
SLIDE 27 PAGE 27
Data mapping – Pressures, resources and emissions – Table 4
Measurement approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) Used as direct inputs Used to build characterisation factors Biodiversity Footprint Calculator (Plansup) Company data on LUC, GHG emissions NA NA LIFE Impact Index (LIFE Institute) Company data on land use change (including wetlands, restored area, “area of
- ccupation severity index”),
GHG emissions, water usage, waste generation, energy
- consumption. Pesticide use
(used only for the management recommendations, not in the Index). Company data on the energy source used and waste generated are also collected. NA? Country total consumptions (from governmental agencies) for: water usage, waste generation, energy consumption, original natural areas by ecoregion; water balance by hydrographic region.
SLIDE 28 PAGE 28
Data mapping – Economic quantification of human activities – Table 5 Approach User-collected input data (company’s data) Externally collected input data (e.g. global data sets) GBS Consumption
commodities, services
refined products inventories (only GBS?) Public financial reports, private database on turnover (e.g. ISS-
BIM NA NA BIE NA NA PBF NA NA BFFI NA Public financial reports, private database on turnover STAR Not known Not known AI NA NA BF NA NA LIFE Index NA NA Bioscope NA NA
SLIDE 29
❑ What is your general feedback on output #1 – Data mapping?
Data mapping
SLIDE 30
REVIEW - Output #2 - Agreement on common nomenclatures to request data from companies
SLIDE 31
❑ Accuracy refers to how close an assessed value is to the actual (true) value. ❑ Precision refers to how close the assessed values are to each other. A precise assessment will for instance be able to claim that the assessed value is “15.126” and not just “15”.
Accuracy and precision
SLIDE 32 Impact factor and data quality tiers to quickly assess data accuracy - Table 6
Real or modelled Data quality tier Description Example for characterisation factors Modelled 1 Simple linear approach. Tier 1 characterisation factors are international defaults. Average agricultural yield of wheat across the world. 2 Region (country)-specific linear factors or more refined empirical estimation methodologies. Average agricultural yield of wheat in Brazil. 3 Characterisation factors derived from the use of relationships (equations) linking the impact source (for instance a land use change) to biodiversity impacts, with inputs requiring a translation into the appropriate typology. Characterisation factors for data in formats requiring transformation to be fed to dynamic bio-geophysical simulation models using multi-year time series and context-specific parameterization (such as GLOBIO). 4 Characterisation factors derived from the use of direct relationships (equations) to biodiversity Characterisation factors for data which can be directly fed to dynamic bio-geophysical simulation models using multi-year time series and context-specific parameterization. Real 5 Direct measurements.
Feedback from BIE’s data quality tiers? www.menti.com Code 76 29 81
SLIDE 33 PAGE 33
Which data quality for which use?
Business applications (BAs) Desired and appropriate data quality tier 1.Assessment of current biodiversity performance Depends on the final goal 2.Assessment of future biodiversity performance 5 impossible so 4 at best
- 3. Tracking progress to targets
Depends on the final goal and the target
Depends on the final goal
- 5. Biodiversity Return on
Investment / Testing effectiveness
Depends on the final goal
- 6. Assessment / rating of
biodiversity performance by third parties, using external data Appropriate: 1 and 2
- 7. Certification by third parties
Depends on the level of uncertainty allowed
- 8. Screening and assessment of
biodiversity risks and opportunities Appropriate: 1
SLIDE 34 The sub-group agrees/does not agree on: ❑ The use of 5 data quality tiers for characterisation factors ❑ The need to quantify as much as possible uncertainties about the value of each measure. ▪ Uncertainties can be further broken down into different levels: inventory data, data in model, model assumptions.
PAGE 34
Common ground reached in the sub-group www.menti.com Code 76 29 81
SLIDE 35
❑ QUESTION #3: Do we agree to expand the definition of data quality tier to input data associated to characterisation factors? The IPCC uses it for characterisation factors. ❑ Go to www.menti.com and use the code 76 29 81
Remaining open questions
SLIDE 36 PAGE 36
Agreement on common nomenclatures to request data from companies
SLIDE 37 PAGE 37
Top priority for convergence: land uses
❑ The tool developers within the sub-group agree/do not agree to use the following nomenclature to request data to companies. They retain the possibility to further break-down the indicators as long as it is clear for companies this is the minimum data required. ❑ Yearly land occupation
▪ Forest
- Forest – Natural
- Forest – Used
▪ Grassland
- Natural grassland
- Pasture - moderately to intensively used
- Pasture - man-made
▪ Cropland
- Extensive cropland
- Intensive cropland
- Monoculture cropland
▪ Natural bare and ice ▪ Urban area
❑ Yearly wetland conversions
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SLIDE 38 PAGE 38
Other potential area of convergence
❑ Yearly greenhouse gas (GHG) emissions ▪ Yearly emissions to air, water and land ▪ By GHG and expressed in kg ▪ IPCC nomenclature
Greenhouse gas
Carbon dioxide (CO2) Fossil and biogenic methane (CH4) Nitrous oxide (N2O) Sulphur hexafluoride (SF6) Hydrofluorocarbons (HFCs) Perfluorocarbons (PFCs)
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SLIDE 39 PAGE 39
Other potential area of convergence
❑ Yearly water withdrawals and consumptions ▪ Expressed in m3 ▪ Water withdrawal: “[water pumped out] of e.g. a groundwater body or diverted from a river.” Also called “water abstraction” or “water use”.” ▪ Water consumption: “share of the water originally abstracted [incorporated] into the product or lost to the ecosystem it was taken from (e.g. water evapotranspirated throughout a production process)”. In other words, the “water consumption” is the abstraction minus the return
- flows. It is also called “consumptive use”.
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SLIDE 40 ❑ What is your general feedback on output #2 – Agreement
- n common nomenclatures to request data from
companies
Agreement on common nomenclatures to request data from companies
SLIDE 41
REVIEW - Output #3 – Link between between inventories of species and habitat and aggregated metrics approaches
SLIDE 42 PAGE 42
Link between between inventories of species and habitat and aggregated metrics approaches
❑ Approaches using aggregated metrics could push companies to acquire user-collected (direct measurements on their sites) and externally collected (e.g. by using IBAT) data on taxa and habitats ▪ Could satisfy screening and “environmental safeguards” phases of their assessment process and feed approaches focused on taxa and habitats with data. ❑ Approaches focusing on taxa and habitats could push companies to acquire input data useful for approaches using pressure and economic activities (e.g. land use in ha, water consumption, etc.). ▪ In particular, Yearly land occupation in the nomenclature described in #2 should be collected.
LUC (common classification) Endangered species
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❑ What is your general feedback on output #3 – Link between between inventories of species and habitat and aggregated metrics approaches The sub-group agrees/does not agree on: ❑ Cross-collecting data on taxa and habitat, and yearly land occupation.
Agreement on common nomenclatures to request data from companies www.menti.com Code 76 29 81
SLIDE 44
REVIEW - Output #4 – Other common ground principles
SLIDE 45 PAGE 45
Generic common ground
❑ Responsive to change. The measure should be susceptible to changes in the management activity. ❑ Rigor. The information, data and methods used should be technically robust or clearly stated as to the levels of accuracy it confers ❑ Compatibility. High compatibility between impact assessment measurement approaches should be maintained such that similar data sets are used
SLIDE 46
Additional material
SLIDE 47 PAGE 47
Definitions
❑ #6 - Input indicator: Specific data required to conduct (biodiversity impact) assessments, for instance an input indicator for habitat change could be “Area of natural forest” and it would be associated with a unit (e.g. hectare) or “Yearly corporate turnover by industry” (EUR). ❑ #7 – Nomenclature: A system of names or terms, or the rules for forming these terms in a particular field of arts or sciences. In other words, a typology. For instance the 22 land cover classes of GLC2000 forms a nomenclature of land covers.
SLIDE 48 ❑ #8 - User-collected data: Inputs based directly on measurements conducted by the company assessed . These measurements can relate to biodiversity state but also to pressures or inventory data. User-collected data on inventories can thus be associated to modelling of biodiversity state. ❑ #9 - Externally collected data: Data derived from external (sometimes global) data sets and not from direct measurements by the company assessed. Externally collected data can nonetheless include biodiversity state data, e.g. based on species distribution maps from the IUCN (or from the Integrated Biodiversity Assessment Tool or IBAT).
PAGE 48
Definitions
SLIDE 49 ❑ #12 - Indicator: “A quantitative or qualitative factor or variable that provides a simple and reliable means to measure achievement, to reflect changes connected to an intervention, or to help assess the performance of a development actor”. ❑ Key Performance Indicators (KPI): indicators against which to measure corporate performance. Such a KPI could for instance be the total biodiversity impact of a business, and it could for example be associated to a reduction target by 2030.
PAGE 49
Definitions
SLIDE 50 ❑ Impact indicators: sometimes known as ‘performance’ or ‘outcome’ indicators. These provide information on actual impacts of actions taken to address biodiversity or drivers of
- change. They help to answer the question, ‘how are our
activities affecting biodiversity?’ ❑ Implementation indicators: sometimes known as ‘process’
- r ‘output’ indicators, these are used to monitor the completion
- f actions that enable conservation to be achieved: e.g.
whether a Biodiversity Action Plan has been developed and implemented or not (but not to track the actual impacts on biodiversity of the Biodiversity Action Plan). They help to answer the question, ‘did we do what we said we would, when we said we would?’.
PAGE 50
Definitions
SLIDE 51 ❑ #13 - Measure: an assessment of the amount, extent or condition, usually expressed in physical terms. Can be either qualitative or quantitative. ❑ #14 - Metric: “A system or standard of measurement”. A combination of measures or modelled elements. The Mean Species Abundance (MSA) and the Potentially Disappeared Fraction (PDF) are for instance metrics expressed as a percentage. ❑ #15 - Unit: a standard measure that is used to express
- amounts. For instance MSA.m2 or PDF.yr.m2 are units.
PAGE 51
Definitions
SLIDE 52 PAGE 52
Data categories - State
Type Theme Category
State Ecosystem Ecoregion Functional richness Marine Soil Ecosystem service Provision - fish Gene Genetic diversity Habitat Wetland map Other habitats Species Risk of extinction Species distribution Species richness Taxa Plant Other Biomass Ecological integrity Priority areas
SLIDE 53 PAGE 53
Data categories - Pressure
Type Theme Category Pressure Land / sea use change (including in aquatic ecosystems, e.g. hydrological disturbance) Forest cover Infrastructure and roads Land cover Land cover change Land use (cover + intensity) Land tenure and value Water resources Direct exploitation Invasive alien species Pollution Air pollution Nitrogen and phosphorous Pesticides Climate change Greenhouse gas emission Other Indirect driver Natural disaster Soil erosion Synthetic indicator of pressures Multi-pressure Extractive Tourism
SLIDE 54 PAGE 54
Data categories - Response
Type Theme Category Response Response Indigenous land Protected area Restoration
SLIDE 55 PAGE 55
Data categories - Economic quantification of human activities
Type Theme Category Economic quantification
Activity Company turnover Company purchase
SLIDE 56 PAGE 56
Output #2 - Other potential area of convergence with no progress
❑ Ecological survey data ▪ No proposal made? ❑ Nitrogen and phosphorous concentrations in water ❑ Pesticides
SLIDE 57 Contacts Aligning Biodiversity Measures for Business Annelisa Grigg, UN Environment World Conservation Monitoring Centre Tel: +44 (0)1223 277314 Email: annelisa.grigg@unep- wcmc.org Sub-group 3A chair Joshua Berger, CDC Biodiversité Tel: +33 (0)1 80 40 15 41 Email: joshua.berger@cdc- biodiversite.fr