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The True Cost of American Food, San Francisco, USA, 16 April 2016
SUSTAINABILITY METHODS AND METRICS
NADIA EL-HAGE SCIALABBA
Senior Natural Resources Officer, FAO Climate and Environment Division
COMMENTS ON THE EBBRAT MODEL
(Ecosystem-based business risk analysis tool)
Taking ecosystem services as the focus for determining reliance on all natural resources (including atmosphere, land, water and
biodiversity) is brilliant for environmental assessment – but social wellbeing aspects may be understated
EBBRAT assesses qualitatively and quantitatively but also monetize risks and opportunities: this allows identifying individual hotspots,
trade-offs and synergies and different performances could be aggregated into a single index – but it is unclear how the results would be
displayed to ease decision-making
Performance evaluation of enterprises is subjective, as short-term perceived impacts are chosen over longer-term and objective
assessments – the problem is not the self-reporting process but the absence of a template (or check list) to follow, with clear criteria for
variations
Qualitative assessments address conflicts between sustainability pillars while trade-offs are mainly observed within single dimension,
namely environmental
COMMENTS ON THE EBBRAT MODEL (2)
(Ecosystem-based business risk analysis tool)
The overall approach to monetizing ecosystem service categories is sound:
Provisioning services: direct market value
Regulating services: replacement costs (and production function?)
Supporting services: avoided costs
Cultural services: benefit transfer (but employment to be further stressed)
However:
Are there templates for farm questionnaires with default indicators?
Use of “available” biophysical data may be insufficient
Indicators could be improved by including more comparable variables, such as: crop erosion potential (for soil replacement
costs); water scarcity (for consumptive use); renewable energy ratio (for energy budget)
Monetary units could be debatable (e.g. Carbon price)
VALUATION APPROACHES
Direct market value Replacement costs Hedonic pricing (WTP) & Production function & Damage cost avoided & Travel Costs (recreational areas)
Monetary valuation based on market data is defensible, but monetization remains an inaccurate proxy for societal values:
Carbon price may be lower than true economic value: market price of carbon depends on trade carbon emissions, which depend on volatile markets (from $45/t a few years ago to $5/t today); Carbon taxes and fines, defined by governments, reflect political reality (EU/ETS Euro 100/t) but not damage costs; Social Cost of Carbon has a wide range of variation ($ 8-112/t) depending on coverage and key parameters choice (i.e. discount rate, time-horizon, risk aversion and climate sensitivity)
Soil erosion rate values have a large cost spectrum (varying by a factor of 2 to 50) for both on-site damage (e.g. yield losses, drop in land value) and off-site (e.g. flooding, sedimentation, health)
Biodiversity (of species and ecosystems) is most difficult to monetize as: biodiversity is not always marketed nor has observable prices, while presenting double counting challenges with Carbon, land and water valuations
MONETIZATION CHALLENGES
MONETIZATION CHALLENGES (2)Water use cost do not reflect contribution to water scarcity ($ 2.02 to 18.8/m3): most direct use (irrigation) water costs are already reflected in
producer prices; no agreement on accounting for extraction or consumption volumes; infrastructure and provisioning costs often not included in
consumptive use. Water quality is relatively easy to value through clean-up expenditures for pesticides removal (30% in USA) and nitrates from
drinking water, as well as mitigation of eutrophication (N and P)
Other challenges of market valuation:
market prices may be distorted by policy failures (e.g. water price)
replacement costs may under-estimate the bundle of all ecosystem services
damage costs avoided can be complex, as values involve annual average damages associated with different return periods (e.g. 5, 30, 50, 100
years)
benefit transfer to ecosystem services is difficult to apply (recreation indirect use)
the quality of an asset refers to a given point in time: pristine biomes?
Most valuation techniques involve selecting a range of parameters and giving them a value through scoring and weighting, based on data and
expert judgement
NATURAL CAPITAL COALITION
Source: Natural Capital Coalition Food and Beverage Sector Guide: Materiality Matrix for the value chain of barley used to produce beer
NATURAL CAPITAL PROTOCOL The Natural Capital Coalition (~ 200 members) is currently developing a
standardized framework that outlines why, what and how businesses can identify their impacts and dependencies on natural capital
The Natural Capital Protocol has two sector guides, one of which is for food and beverages , developed by an IUCN-led consortium to which FAO participates
The Draft Food & Beverage Sector Guide was piloted and publicly commented till end of February 2016; the final text is to be launched on 13 July 2016
The Protocol (so far) consists of 10 steps including: scoping; measuring and valuing; and applying and embedding results in business’ strategies and operations
NCP helps connecting different non-financial work streams in business (e.g. energy, water, waste) in a coherent way, as well as providing guidance on qualitative, quantitative and monetary valuation of impacts and/or dependencies for particular business contexts and applications (but no rule of best practice)
Interaction with natural capital visualized through the materiality matrix of the NCP Food & Beverage Sector Guide
Source: Natural Capital Coalition Food and Beverage Sector Guide: Materiality Matrix for the value chain of barley used to produce beer
NATURAL CAPITAL PROTOCOL METRICS
OPERATIONAL NATURAL CAPITAL INTENSITY OF CROP COMMODITIES (USD OF IMPACTS PER TONNE OF PRODUCTION)
Natural Capital Impacts in Agriculture: Supporting Better Business Decision-Making (2014) evaluated the environmental cost of global agriculture to
$3 trillion/year
FAO MATERIALITY STUDY
SETTING SPATIAL BOUNDARIES
Spatial boundaries - beyond direct operational impacts - will determine the enterprise performance’ outcome
Time horizon: SAFA focuses on present performance , while seeking continuous progress. Thus, the first SAFA determines the baseline for future (annual) assessments
SUSTAINABILITY DIMENSIONS AND THEMES
A multi-purpose framework for governments, businesses and NGOs
SUSTAINABILITY PILLAR: GOVERNANCE
Enterprises collect, analyze and report to stakeholders economic, social and environmental impacts (triple bottom line reporting) and the
accounting process makes transparent both subsidies received and direct and indirect costs externalized
Enterprises do not account for impacts and performance using any FCA regime, or have significant costs on the environment and community
which are externalized from accounting systems
SUSTAINABILITY PILLAR: ENVIRONMENT
SAFA’s environmental pillar takes a semi-quantitative MCA approach and a quantitative LCA approach to benchmark
(avoided) harm or restoration of natural resources
SUSTAINABILITY PILLAR: ECONOMIC
Theme Goal: Any contamination of produce with potentially harmful substances is avoided, and nutritional quality and traceability of all
produce are clearly stated
SUSTAINABILITY PILLAR: SOCIAL
The enterprise takes measures to avoid polluting or contaminating the local community and contributes to the health of the local community
The enterprise pollutes water, air and soils with toxic materials and expands without consideration for other area residents and their needs
A UNIVERSAL FRAMEWORK
Performance
Biodiversity Goal
Ecosystems Species Genetic
Practice
Target
← Theme Goal
(e.g. ensure conservation)
← Sub-theme Objective
(e.g. diversity, functional integrity and
connectivity of ecosystems conserved)
← Performance indicators
(e.g. Land use and land cover change)
← Practice-based indicators
(e.g. ecosystem-enhancing)
← Target-based indicators
(e.g. landscape cons. plan)
SAFA METRICS HIERARCHY
Default (and customized) indicators to fulfill Sub-themes’ objectives
METRICS FOR ALL: SAFA TOOL 2.2.40
OPEN ACCESS SOFTWARE
Self-reporting or delegated assessment
A FARMING ENTERPRISE PERFORMANCE
SAFA is NOT an index but an impact assessment tool that rates, weights and aggregate indicators
A VALUE-CHAIN PERFORMANCE
SAFA Tool overlays outcomes of production, processing and marketing
BENCHMARKING SAI Platform FSA 2.0
SAI/FSA being practice-
based, it takes a more direct
and specific focus on farmers’
issues - while SAFA’s scope is
broader and more
performance-oriented
DISAGGREGATED RATING OF A THEME
Themes’ performance is
calculated by scoring,
weighting (including “no go”
values) indicators. SAFA does
not aggregate its 21 Themes -
and all sustainability themes
are given the same weight
LESSONS AND CHALLENGES AHEAD
Like most valuation techniques, SAFA scores and weights qualitative and quantitative indicators, based on (primary and secondary) data and
expert judgement
SAFA sustainability polygone displays trade-offs and opportunities along 21 Themes that cannot be further aggregated. Monetization of
impacts offers a common denominator for the aggregation of environmental, social and economic performance (thus, comparability) – IF
rigorous and agreed metrics are developed
The 1000s application’s of SAFA in different contexts world over indicate that:
Full-Cost Accounting usually performs poorly, especially at farm level
Synergies exist between the Governance pillar and all other sustainability pillars
Trade-offs between the Economic and Social pillars are substantial (e.g. Profitability vs Public Health)
Major trade-offs are often seen between the Environment and Economic pillars
The largest trade-offs occur within the Environmental Integrity pillar (e.g. GHG vs Animal Welfare), even larger than the trade-offs with other
pillars); often, performance is limited to one theme and all goals’ achievement show high variability
www.fao.org/nr/sustainability