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Day 1 - Session 4 - IPIECA

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Bioenergy and Food<br />

Security Projects<br />

Implementing biofuels sustainability schemes –<br />

Coverage of socio-economic sustainability issues<br />

and limitations<br />

Andrea Rossi<br />

<strong>IPIECA</strong>-CONCAWE Workshop, Brussels, 18-19 September 2012


Main socio-economic dimensions<br />

that may be affected by bioenergy development<br />

• Access to land<br />

• Employment, wages and labour conditions<br />

• Income generation and inclusion of smallholders<br />

• Local food security<br />

• Community development<br />

• Energy security and local access to energy<br />

• Gender equity<br />

‹#›<br />

2


Factors determining socio-economic impacts<br />

of bioenergy production<br />

• The local socio-economic context<br />

• the regional, national and local policy environment<br />

• the types of bioenergy, feedstocks and processing<br />

technologies<br />

• the way production (especially feedstock production) is<br />

managed<br />

• the scale and ownership of production<br />

• the types of business models found along the bioenergy<br />

supply chain<br />

3<br />

‹#›


Bioenergy policies and socio-economic sustainability<br />

‹#›<br />

4


Voluntary standards and socio-economic sustainability<br />

‹#›<br />

5


Coverage of socio-economic sustainability: overview<br />

‹#›<br />

6


Socio-economic sustainability:<br />

coverage and limitations<br />

• Relatively broad set of socio-economic sustainability<br />

issues covered by voluntary standards (beyond<br />

requirements of regulatory frameworks)<br />

• But, in most cases, lack of specific compliance indicators,<br />

benchmarks and thresholds, especially with regard to food<br />

security<br />

‹#›<br />

7


BEFS Operator Level Food Security<br />

Assessment Tool<br />

Key environmental and socioeconomic issues to consider in<br />

assessing operator level impacts on food security:<br />

1. Change in the supply of food (crops and livestock) to<br />

the domestic market<br />

2. Resource availability and efficiency of use (land,<br />

water and fertilizers)<br />

3. Physical displacement, change in access to<br />

resources, compensation and income generation<br />

‹#›<br />

8


BEFS Operator Level Food Security<br />

Assessment Tool<br />

For each indicator, specific benchmarks and thresholds<br />

are included to allow for a desk level assessment of a<br />

planned or existing project’s impact on food security:<br />

• Potential Benefit for Food Security<br />

• No Significant Influence on Food Security<br />

• Potential Risk to Food Security<br />

www.fao.org/bioenergy/foodsecurity/befsci/operator-tool<br />

‹#›<br />

9


THANK YOU!<br />

http://www.fao.org/bioenergy/foodsecurity/befs<br />

PLEASE DO NOT HESITATE TO CONTACT US:<br />

E-mail: BEFS-Project@fao.org<br />

Phone: +39 06 57055376<br />

Fax: +39 06 570 53369<br />

‹#›<br />

10


Sustainability standards and biofuels<br />

Contributions to understanding impacts<br />

18 Sept 2012<br />

Sustainable Biofuels Regulation Workshop<br />

Kristin Komives, ISEAL M&E Senior Manager<br />

Photo © Rainforest Alliance


Outline<br />

1. Setting the stage<br />

› The ISEAL Alliance<br />

› ISEAL and impacts<br />

measurement<br />

› Standards and biofuels<br />

2. Measuring impacts of biofuels<br />

› Which impacts?<br />

› What can standards<br />

systems contribute?<br />

Photo © Aid for Trade Foundation


Setting the stage<br />

Photo © Rainforest Alliance


What is the ISEAL<br />

Alliance?<br />

› Founded 2002<br />

› Membership organisation<br />

• Of standards and<br />

international<br />

accreditation bodies<br />

› ISEAL defines credibility for<br />

social and environmental<br />

standard systems.<br />

Photo © Simon Rawles | Fairtrade International


The ISEAL Alliance: A Growing Movement…<br />

Full Members<br />

Associate Members


ISEAL members and<br />

biofuels<br />

› Supply chain standards<br />

• E.g. RSB (Roundtable for<br />

Sustainable Biofuels)<br />

› Feedstock standards -<br />

production for the food or<br />

fuel market<br />

• Agricultural standards,<br />

e.g. Bonsucro, Rainforest<br />

Alliance<br />

UTZ Certified


Codes & Credibility<br />

Principles<br />

Codes define good practice<br />

and are conditions of<br />

membership.<br />

› Standard-Setting Code (since<br />

2004)<br />

› Impacts Code (since 2010)<br />

› Assurance Code (In 2012)<br />

Key “Credibility Principles”<br />

inform the Codes<br />

› Public consultation on-going<br />

Photo © Rainforest Alliance


Impacts are at the<br />

heart of ISEAL’s work<br />

Credible standards deliver<br />

expected impacts effectively<br />

and efficiently<br />

› To do this, each part of the<br />

system must operate well<br />

• The standard<br />

• The assurance process<br />

• Capacity building and other<br />

supporting strategies<br />

• Monitoring, evaluation, and<br />

internal learning<br />

Photo © Charlie Rainforest Watson| Rainforest Alliance Alliance


Impact and ISEAL’s Credibility Principles<br />

Draft for public consultation Sept 2012


Stakeholders demand better information<br />

on results and impacts<br />

Most organisations today<br />

MYTH ANECDOTE OBSERVATION COMPARISON REPLICATED RRC<br />

Systematic<br />

Indicators<br />

+ Research<br />

Strategy<br />

Adapted from Rainforest Alliance


The Impacts Code as a response….<br />

Code compliance is a membership requirement<br />

› Full compliance by Dec 2013<br />

› Or 2 years after becoming an Associate Member<br />

What does the Code require?<br />

› Clear articulation of sustainability goals<br />

› Theory of change<br />

› On-going monitoring (output and outcome indicators)<br />

› Periodic outcome and impact evaluations (could be external)<br />

› Public sharing of information and results<br />

› Internal learning and improvement


Impacts of biofuels<br />

Photo © Rainforest Alliance


Issues of primary concern in studies<br />

Category of impact<br />

Planet<br />

People<br />

Profit<br />

Specific concerns<br />

Greenhouse gas emissions<br />

Land conversion<br />

Competition for water<br />

Biodiversity<br />

Deforestation<br />

Food prices and food insecurity<br />

Employment in rural areas<br />

Access to land for the poor<br />

Rural employment / ag and rural development<br />

National energy security<br />

Economic growth in developing countries<br />

Adapted from Michalopoulos et al 2011


Challenges for<br />

biofuels impact<br />

evaluation<br />

› Impacts at different scales<br />

• Adding up = gaps and<br />

double-counting<br />

› Differences across<br />

contexts (“hotspots”)<br />

› A “complex” system<br />

› “Avoiding harm” or<br />

“better than…” research<br />

› Traceability of feedstock<br />

Simon Rawles Fairtrade Foundation


What can standard systems<br />

contribute?<br />

Photo © Rainforest Alliance


Scope of concerns<br />

vs. standards<br />

› Concerns about biofuels<br />

are systemic, regional,<br />

national, or international<br />

›Scope of standard systems<br />

is generally the certified<br />

entity and the activities and<br />

resources it controls<br />

› Some standards try to go<br />

beyond boundary<br />

›Certified biofuels are small<br />

part of market<br />

Simon Rawles Fairtrade Foundation


Standard systems’ assurance and M&E<br />

systems match their scope<br />

› Compliance with standard<br />

• Practice –based: are practices implemented?<br />

• Performance–based or metric: outcomes achieved?<br />

› Monitoring and evaluation<br />

• Goal = are they achieving their intended outputs, outcomes,<br />

and impact?, are strategies and standard effective?<br />

» Monitoring – focus on certified entity and direct, shortterm<br />

results<br />

» Outcome and impact evaluation – may be broader and<br />

could potentially pick up landscape level issues


Contribution of<br />

standards?<br />

› Site level information<br />

› Average outcomes for<br />

certified crops or<br />

operations in particular<br />

regions<br />

› Participate in systemlevel<br />

or regional-level<br />

discussions and<br />

evaluations


Maximizing the<br />

contribution<br />

› Relevant site-level indicators<br />

› Methods for aggregating<br />

site level data<br />

› Regional studies to which<br />

they can contribute<br />

›Financial support for data<br />

collection and processing<br />

› Small organisations, with limited<br />

means for M&E<br />

› Info gathering is costly and should<br />

not fall on farmers<br />

Simon Rawles Fairtrade Intl


Thank you!<br />

For questions or further information, contact:<br />

Kristin Komives (kristin@isealalliance.org)<br />

Norma Tregurtha (norma@isealalliance.org)<br />

Photo © Rainforest Alliance


WINROCK INTERNATIONAL<br />

Building capacity for monitoring compliance<br />

with standards<br />

<strong>IPIECA</strong> Seminar<br />

Biofuels sustainability standards and regulations<br />

Brussels<br />

www.winrock.org<br />

Jessica Chalmers<br />

September 18 th , 2012


Winrock Objectives<br />

• Non-profit organisation that aims to:<br />

– Empower the disadvantaged and accelerate economic development<br />

opportunities through effective management of natural resources<br />

– Build local and regional capacity to apply and improve available technology<br />

– Mobilize investment<br />

– Use robust science and economics to inform its work<br />

Why bioenergy & biofuel?<br />

• Development benefits of bioenergy<br />

– New sources of revenue and jobs for rural areas<br />

– Strengthened rural infrastructure (roads, communications, technical<br />

services, production inputs, governance)<br />

– Increase quantity and reliability of local energy supply<br />

www.winrock.org


Presentation Overview<br />

• Common items for compliance<br />

• Relevant tools and techniques<br />

– focus on exploring remote sensing<br />

• Assessing compliance vs monitoring<br />

outcomes<br />

www.winrock.org


Common items for compliance<br />

within standards (environmental)<br />

Land cover /land use<br />

Need to identify at 1ha scale. Satellite data with a 30m or higher (max 60m) is considered sufficient to serve<br />

as reliable evidence of the land cover but may not be conclusive (EU guidance for RED)<br />

Carbon stocks<br />

Biological diversity<br />

Water quality<br />

Water availability<br />

Soil health<br />

Avoid high carbon stocks<br />

Proxies using land cover and assigning carbon stock numbers<br />

Some no-go area approach; protected areas,<br />

‘highly biodiverse’ grasslands*<br />

(At least) No detriment to water quality<br />

Often requires water management plan<br />

(At least) No detriment to water availability<br />

Often requires water management plan<br />

(At least) no detriment to soil health<br />

References to sustainable residue removal rates<br />

www.winrock.org


Land cover identification from<br />

freely available satellite imagery<br />

Screenshots from the CANASAT Project, Brazil, illustrating<br />

changes in cane distribution from crop year 2005/6 to 2008/9.<br />

www.dsr.inpe.br/laf/series<br />

Source: CANASAT Project (2009).<br />

www.winrock.org


US Cropland Data Layer<br />

www.nassgeodata.gmu.edu/CropScape<br />

www.winrock.org


Global tools for monitoring<br />

carbon stocks and change<br />

BioCarbon Tracker uses satellite data to<br />

• map the ecosystems where biocarbon is stored<br />

• identify vegetation at risk from land use change and<br />

• monitor where high biocarbon stock land such as forest is converted to<br />

agriculture (soil carbon not yet included).<br />

Source: http://biocarbontracker.com/<br />

www.winrock.org


Tools to address carbon stock<br />

requirements: regional scale<br />

• Under discussion – create go and no-go area mapping to demonstrate compliance with<br />

RED carbon criteria.<br />

– Options: hard distinctions vs indicative risks<br />

Impact<br />

“High threat”<br />

High Negative Impact<br />

Moderate Negative Impact<br />

Range of change in<br />

GHG emissions<br />

TBD<br />

TBD<br />

Notes<br />

Ranges are likely to demonstrate that even accounting for errors<br />

the impact is negative.<br />

The outcome on paper is negative, but the ranges are based on<br />

numbers that suggest they can be mitigated with best agricultural<br />

management practices.<br />

Moderate Positive Impact<br />

“Low threat”<br />

High Positive Impact<br />

• Issues<br />

TBD<br />

TBD<br />

– No clear support for approach<br />

– Potentially substantial uncertainty<br />

The outcome on paper is positive, but the ranges are too<br />

uncertain to determine the impact without more precise data.<br />

Ranges are likely to demonstrate that even accounting for errors<br />

the impact is positive.<br />

• Coarse scale estimates of carbon stocks can help develop threat assessments at<br />

national scales (using MODIS data).<br />

• Forest carbon estimates improving but others e.g., pasture land not well assessed<br />

– Still based on good identification of land cover so appropriate geographic scale and<br />

www.winrock.org availability of satellite data (e.g., for 2008 reference date) are issues


Tools to address carbon stocks:<br />

site scale<br />

Source: Pearson et al, 2005 www.winrock.org/.../TAP_presentation-M3DADIvsCONV_2006.pdf<br />

www.winrock.org


Biodiversity tools<br />

• Integrated Biodiversity<br />

Assessment Tool (IBAT)<br />

• High Conservation Value<br />

areas<br />

– Referenced by a number of<br />

standards<br />

– A framework for regional<br />

and site scales<br />

– Includes social values<br />

– Requires trained /<br />

experienced people to<br />

undertake<br />

Remote sensing: Identifying habitats and suitability has been done through the<br />

use of RS but measuring function within an ecosystem is challenging.<br />

www.winrock.org


Other uses of RS<br />

Water consumption<br />

Harvest practice<br />

Annual total ET in Imperial Valley (California, US) in the<br />

period Oct 1997 – Sep 1998. The image dimension is<br />

approx 75 km x 75 km, pixel size is 30 m (source:<br />

Thoreson et al., 2009 cited in eLEAF/Winrock paper).<br />

Differences between burned (dark) and unburned fields<br />

in Brazil. Presented by Dr. Bernardo Rudorff at Winrock<br />

workshop on RS for monitoring biofuels, Jan 2012.<br />

www.winrock.org<br />

Residues: there is not a good operational sensor that can estimate dry<br />

cellulosic matter well.


Optical satellite data: infrastructure<br />

the elephant in the room<br />

• Lack of trained data analysts<br />

• Lack of clear demand/promotion<br />

for this approach from potential<br />

users<br />

• Lack of infrastructure for some<br />

developed and developing nations<br />

for downloading RS data<br />

• Landsat 5 failure this year with a<br />

serious potential loss of data<br />

• Some regions have problems<br />

getting cloud-free imagery and<br />

need supplementary RS data<br />

(may incur costs)<br />

Landsat active ground station. Green circles download Landsat 7 data, red<br />

circles Landsat 5, red and green Landsat 5&7, and yellow circles are<br />

potential future stations<br />

(http://landsat.usgs.gov/about_ground_stations.php).<br />

• Small field sizes (


Infrastructure<br />

Resources<br />

Tools and<br />

techniques<br />

Significant bottleneck<br />

No bottleneck<br />

Presence of ground stations to receive satelllite data<br />

Internet speeds to download data<br />

Storage capacity for data - hardware<br />

Potential data gap from failure of<br />

Landsat 5<br />

Availability of technical analysts to<br />

interpret existing data<br />

No freely available global radar to<br />

avoid cloud cover issues<br />

Lack of thermal band on<br />

Landsat continuation mission<br />

Availability of products<br />

to facilitate use of data<br />

Some optical data not<br />

freely available<br />

Freely available optical data (e.g.,<br />

MODIS, Landsat)<br />

Understanding of needs and capabilities<br />

between users and providers of data<br />

Existence of techniques<br />

for monitoring<br />

www.winrock.org<br />

Awareness of the capacity of existing<br />

data to meet monitoring needs


Assessing compliance vs monitoring<br />

outcomes: the case of water<br />

• Some requirements of standards include: water management plans, water<br />

footprints, reduction of water use by X%<br />

• But what about the appropriate context? – river basin availability<br />

Water Stress Indicator – major river basins<br />

Source: Smahktin et al, 2005<br />

www.winrock.org


Monitoring outcomes is the essential feedback<br />

loop for delivering sustainable biofuels<br />

e) Evaluate<br />

performance<br />

and outcomes<br />

a)<br />

Establish<br />

baseline<br />

and<br />

identify<br />

threats<br />

d) Monitor & verify<br />

performance and<br />

outcomes<br />

c) Develop &<br />

implement<br />

strategy, policy,<br />

practices to<br />

mitigate threat<br />

and optimize<br />

benefits<br />

b) Identify<br />

performance<br />

requirements to<br />

mitigate threats<br />

www.winrock.org


Links across geographic scales<br />

are critical<br />

www.winrock.org


Conclusions: building capacity<br />

for monitoring<br />

• Objectives of standard and therefore the requirements for building capacity may differ<br />

between standards, actors and within different national settings<br />

• Generally, tools and techniques to assess compliance are available – different scales<br />

• Remote sensing is underutilised, not a panacea but could make substantial contributions<br />

and could reduce admin burden<br />

– Freely available imagery (Landsat and MODIS) could be used to a much greater<br />

extent than currently but..<br />

• Will they be acceptable for compliance? At what scales?<br />

– Dialogue between potential users and RS scientists needed<br />

• Investment in infrastructure needed (failure of Landsat 5, future of Landsat?)<br />

• Need to train analysts in utilising the information<br />

• Need ground-truth data for validation of RS data<br />

• Enabling access to imagery is key<br />

• Creating new and user-friendly products likely to be needed<br />

• We need to focus on monitoring outcomes not just one-off assessments for compliance.<br />

– Assessment and monitoring across temporal and geographic scales is needed –<br />

context and baseline data<br />

– Communication network needed to co-ordinate data across geographic scales (top<br />

www.winrock.org<br />

down and bottom up) Are we really delivering biofuels sustainably?


Thank you!<br />

• Winrock web: www.winrock.org<br />

• Jessica Chalmers (London-based)<br />

JChalmers@winrock.field.org<br />

+44 (0) 7985 499 061<br />

www.winrock.org


Satellite data (optical)<br />

Scale (Resolution)<br />

Large (>60m)<br />

1000m<br />

Sensor<br />

SPOT<br />

Vegetation*<br />

Swath<br />

Width<br />

Frequency<br />

of Passes<br />

Spectral<br />

Resolution<br />

2,250km 10 days 4 bands<br />

250-500m MODIS* 2,330km 8-16 day 7 bands<br />

Comment<br />

Useful mapping scale: global. General scale for identifying land cover: 100-1000ha. This<br />

imagery has been used to map large area croplands and cropland types. It can be used to<br />

identify broad forest categories such as broadleaf and conifer, but likely high error with<br />

other woody land cover like shrub lands. Able to map large grassland areas but has<br />

very limited ability to determine grassland conditions.<br />

Medium (10-60m)<br />

56m IRS AWiFS 796km 8-16 days 8 bands<br />

30m<br />

Landsat* 185km 16 days 8 bands<br />

DMC<br />

600km 4 days 3 bands<br />

Useful mapping scale: national. General scale for identifying land cover: 1-5ha. This imagery<br />

has routinely been used to map crop types across regional areas and more recently has<br />

reached national scales for countries as large as the US. Has been used to identify different<br />

forest types but is relatively limited. Has been used to determine grassland conditions in<br />

numerous studies with varying degrees of accuracy.<br />

15-60m ASTER 60km 16 days 15 bands<br />

Small (>10m)<br />

2.5-5m SPOT-5 60km 5 days** 5 bands<br />

1-4m Ikonos 11.3km 5 days** 4 bands<br />

0.5-2m WorldView-2 16.4km 3 days** 8 bands<br />

Useful mapping scale: sub-national. General scale for identifying land cover: 2-50m. This<br />

imagery can be used to map cropland types. More often high resolution is used for identifying<br />

crop conditions for purposes such as determining irrigation or fertilization deficits. Can be<br />

used to map different forest types grassland conditions and other detailed land cover<br />

dynamics.<br />

www.winrock.org


Table 3: Opportunities, limitations and challenges for RS and agricultural productivity<br />

Opportunities<br />

Quantifying annual yields on<br />

an area basis – simulation<br />

modeling<br />

Limitations and challenges<br />

Requires high resolution imagery and availability of ground truth data<br />

While substantial data is available through existing satellites there is a lack of trained analysts<br />

Multiple data sources are combined in simulation modeling and require co-operation between numerous<br />

disciplines (agronomist, meteorologist, RS experts etc)<br />

Optimizing yield through<br />

monitoring yield development<br />

throughout the growth cycle<br />

Currently only products offered are by private companies, which increases the price<br />

Requires field validation to support results<br />

Has to be dealt with seasonally and not on average<br />

Need at least weekly imagery<br />

Need to know data on cultivation cycle,harvest timings therefore collaborations between RS scientists,<br />

agronomists, meteorologists are needed<br />

www.winrock.org


Generating better and timely data:<br />

the potential role of remote sensing<br />

Carbon stocks<br />

Biodiversity<br />

Water<br />

consumption<br />

Water quality<br />

Productivity<br />

Analysis and<br />

interpretation /<br />

modeling<br />

Land cover<br />

Crop type<br />

Rainfall Evapotranspiration<br />

Leaching of<br />

rainfed<br />

cropping<br />

systems<br />

N in leaves<br />

Crop yield<br />

Biomass<br />

production<br />

Example<br />

parameters<br />

gathered by a<br />

sensor<br />

Surface temperature<br />

Soil moisture<br />

Vegetation<br />

indices<br />

Monitoring compliance is one use but RS can be used in an active management approach to<br />

optimise productivity with given resource base, providing farmers with real-time information<br />

www.winrock.org


Winrock International<br />

Enterprise & Agriculture<br />

- Supports growth of small &<br />

medium-sized enterprises<br />

- Enhance productivity & connect<br />

farmers to markets<br />

- Develops public & private<br />

partnerships<br />

Environment: Forestry, Energy<br />

& Ecosystem Services<br />

- GIS techniques & imagery for<br />

natural resource management<br />

- Carbon stock surveys &<br />

measurement<br />

- Watershed management<br />

Empowe<br />

-rment &<br />

civic<br />

engagement<br />

US Programs:<br />

Specific focus<br />

on domestic<br />

development<br />

challenges<br />

facing rural<br />

communities<br />

The Henry A.<br />

Wallace<br />

Center for<br />

Agricultural<br />

and<br />

Environmental<br />

Policy<br />

Agriculture<br />

Unit<br />

Forestry &<br />

Natural<br />

Resources<br />

Management<br />

Ecosystem<br />

Services<br />

Clean Energy<br />

- Promotion of<br />

commercially<br />

viable RE<br />

systems<br />

Civil Society<br />

strengthening<br />

Women’s<br />

empowerment<br />

Youth<br />

leadership &<br />

education<br />

www.winrock.org


MEASURABLE IMPACTS OF<br />

VOLUNTARY STANDARDS:<br />

THE ENVIRONMENT<br />

A PRESENTATION AT THE<br />

IPECA BIOFUEL WORKSHOP 18-19 SEPT<br />

©2009 Rainforest Alliance


©2009 Rainforest Alliance 54


©2009 Rainforest Alliance 55


IN KEY CONSUMER MARKETS<br />

42%<br />

Australia<br />

35%<br />

Canada<br />

42%<br />

U.S.<br />

39%<br />

Germany<br />

44%<br />

Sweden<br />

44%<br />

Denmark<br />

54%<br />

U.K.<br />

44%<br />

Finland<br />

Prompted Awareness of Rainforest Alliance Certified


THROUGH GREAT COLLABORATIONS…


RAINFOREST ALLIANCE ORGANIZATION<br />

RA President<br />

Programs<br />

Communications,<br />

Finance, Development,<br />

Legal, HR<br />

RA-Cert<br />

Tourism<br />

Evaluation &<br />

Research<br />

Climate<br />

Agriculture<br />

Forestry<br />

Forestry cert<br />

Sustainable Value<br />

Chains<br />

SmartSource<br />

Ag cert<br />

Sustainable<br />

Landscapes<br />

TREES<br />

Carbon<br />

verification<br />

SAN<br />

SECRETARIAT<br />

58


THE VALUE CHAIN APPROACH OF OUR MISSION<br />

Capacity Building:<br />

Producer support<br />

and Training<br />

Certification:<br />

Sustainable Forestry<br />

Sustainable Agriculture<br />

Carbon validation / verification<br />

Market<br />

development and<br />

corporate<br />

engagement<br />

Systems development, operations, and governance<br />

Training and support for producers<br />

Auditing / certification /<br />

verification Chain of custody -<br />

traceability<br />

Corporate<br />

engagement<br />

Marketing support<br />

and brand awareness<br />

producers / processors buyers / exporters / importers distributors / brands / retailers / industry groups consumers<br />

LAND USE PRACTICES BUSINESS PRACTICES CONSUMER BEHAVIOR


USING CERTIFICATION TO TRANSFORM<br />

MARKETS AT SCALE<br />

RAINFOREST ALLIANCE CERTIFIED TM


SUSTAINABLE AGRICULTURE PROGRAM<br />

• First global Sustainable Agriculture Standard founded in 1993 with a<br />

network of NGOS in the developing world: the Sustainable Agriculture<br />

Network (SAN);<br />

• Over 575,000 certified farms. 1.8 m ha of certified agricultural land;<br />

• 31crops grown in 38 countries sold by 3000+ companies worldwide.<br />

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SUSTAINABLE FORESTRY<br />

• Pioneers of sustainable forestry certification; helped establish the Forest<br />

Stewardship Council (FSC) in 1993<br />

• Collaboration with companies and forest enterprises to harvest forest products<br />

using the most holistically sustainable methods possible.; focus on creating<br />

market access.<br />

• Leader in FSC certification: 72 million hectares across 72 countries.<br />

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CLIMATE PROGRAM<br />

• Carbon Verification & Validation: confirms carbon projects are conservationoriented<br />

and meet established international standards for carbon sequestration.<br />

• Sustainable Agriculture Climate Module:<br />

- Climate mitigation: add-on to existing standard with robust climate criteria.<br />

- Climate change adaptation: preparation for impacts on crops.<br />

• Carbon Credits: our climate services enable company and community-run projects<br />

to benefit financially from carbon credit payments.


BUIDING CAPACITY AT PRODUCER LEVEL<br />

ONLINE TRAINING PLATFORM<br />

WWW.SUSTAINABLEAGRICULTURETRAINING.ORG<br />

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Environmental<br />

Social<br />

Economic<br />

COMPREHENSIVE CERTIFICATION CRITERIA<br />

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The Sustainable Agriculture Network Standard<br />

10 PRINCIPLES<br />

Must score minimum of 50% in<br />

each principle<br />

99 CRITERIA<br />

Must score a minimum of 80%<br />

overall<br />

15 CRITICAL CRITERIA<br />

Must score 100% in all 15<br />

1. Social and Environmental<br />

Management System<br />

2. Ecosystem Conservation<br />

3. Wildlife Protection<br />

4. Water Conservation<br />

5. Fair Treatment and Good Working<br />

Conditions for Workers<br />

6. Occupational Health and Safety<br />

7. Community Relations<br />

8. Integrated Crop Management<br />

9. Soil Management and Conservation<br />

10. Integrated Waste Management


COLLABORATING -----<br />

• Collaboration :with RTS and other standard systems<br />

• Supporting standard development.<br />

• Leading harmonization.<br />

• Raising the bar and seeking solutions.<br />

• Field-proofing policy.


....AND DIFFERENTIATING<br />

• COMPREHENSIVE: Environmental, economic, and social components<br />

• CREDIBLE: 25 years developing and delivering sustainability certification<br />

• Focus on BIODIVERSITY and NO DEFORESTATION<br />

– No high value ecosystem destruction since 2005<br />

– 2.4. Management plan for extraction; threatened species cannot be harvested<br />

– 2.5. Separation between production areas and natural ecosystems<br />

– 2.8. Integration of trees in the productive landscape<br />

– 9.3. Vegetation required to reduce soil erosion<br />

– 9.4/5. No burning or land clearing for agriculture<br />

• RIGOROUS: Detailed standards with thorough audits<br />

• Applies to LARGE PLANTATIONS AND SMALLHOLDERS<br />

• LOCAL INTERPRETATION guidelines<br />

• Does not deal with TERMS OF TRADE


IN BIOFUEL ARENA...<br />

• How does the Rainforest Alliance fit into the sustainable palm oil<br />

landscape?<br />

• Robust environmental criteria, including species monitoring and biodiversity<br />

conservation, and mitigation of any damage resulting from deforestation since November<br />

1999.<br />

• Boots on the ground: Field based staff working in the field, including 9 organizational<br />

partners in Latin America alone. Capacity to monitor and evaluate during and after the<br />

certification process.<br />

• Traceability to origin<br />

• Power of the frog seal to engage consumers in specific markets/brands<br />

• Diversification of sources of certified sustainable palm oil will allow large companies who have made wide<br />

commitments to achieve their public targets.<br />

• How does Rainforest Alliance certification compare with that of the<br />

RSB and ISCC?<br />

• Sourcing policies and SmartSouce mapping and supply chain analysis. Develop protocols for<br />

alignment of standards;<br />

• Joint training with other cert systems, NGOs and Technical Assistant providers; s and joint<br />

auditing, combi-certs;<br />

• Supporting the roundtables and stakeholder engagement;<br />

• Brazil. Bonsucro and IMAFLORA (SAN Partner) already working together;<br />

• How does Rainforest Alliance Certified palm oil compare to RSPO<br />

Certified palm oil?<br />

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MEASURABLE IMPACTS – A SHORT LIST<br />

• Biodiversity on farms – fauna and flora<br />

• Biodiversity impacts in broader landscapes<br />

• Water conservation<br />

• Water quality<br />

• Pesticides and chemical use and abuse<br />

• Riparian protection<br />

• Soil conservation<br />

• Soil fertility<br />

• Habitat change – fragmentation and connectivity<br />

• Economic sustainability: productivity, prices and market access<br />

• Social sustainability: workers’ and children’s welfare; community and family<br />

cohesion<br />

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IS IT WORKING?<br />

UNILEVER SUSTAINABLE TEA:<br />

LEAPFROGGING TO MAINSTREAM<br />

IMD-2-0157<br />

20.09.2010<br />

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OTHER INDEPENDENT STUDIES<br />

• COSA Cocoa impact study<br />

• and would like to have any data or studies we have available to make the case<br />

• ProForest Colombia Test results.<br />

• The Brazil coffee study<br />

• Toward Sustainability: The Roles and Limitations of Certification<br />

www.resolv.org/certificationassessment.<br />

• Through the assessment, the Steering Committee found substantial evidence<br />

of improvements in social, environmental, and economic practices resulting<br />

from certification at the site level…. However, the evidence of broader or<br />

longer-term impacts is more limited…… it is difficult to attribute outcomes<br />

directly to certification. Consequently, additional coordinated research on the<br />

impacts of certification……….is a top priority.<br />

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AND MEASURING THE IMPACTS OF OUR WORK..<br />

COSA STUDY COTE D’IVOIRE (EXAMPLE)<br />

PRODUCTION—NOT PRICE—DRIVING REVENUE<br />

Yield in<br />

Kilograms per<br />

Hectare (2011)<br />

Revenue in<br />

USD per<br />

Hectare (2011)<br />

576 334<br />

$922 $542<br />

Certified Non-certified<br />

Certified Non-certified<br />

Based on a survey of 117 RA-certified cocoa farms and 135 control farms<br />

* Difference is significant with 95% confidence<br />

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KTDA TEA IMPACT STUDY<br />

*LEI WAGENINGEN UNIVERSITY BY YUCA WAARTS , 2012<br />

• 350+ farmers from 4 Kenyan tea<br />

factories within KTDA between<br />

• July 2010 to February 2012<br />

• Impact assessment of:<br />

i. Farmer Field School (FFS)<br />

training only<br />

ii.<br />

iii.<br />

iv.<br />

Rainforest Alliance (RA)<br />

training only<br />

FFS + RA training combined<br />

No training programs<br />

(control group)<br />

• FFS + RA highest increase in knowledge of GAPs,<br />

followed by the RA only group.<br />

• RA only group had significantly higher knowledge<br />

level, especially in environmental GAPs, than other<br />

groups.<br />

• RA training showed in: better waste and water<br />

management, productivity, soil conservation, health &<br />

safety, wildlife protection, and green leaf quality.<br />

• Among the RA trained farmers:<br />

• 97% were satisfied with the training<br />

• 80% would recommend training<br />

• 84% said they benefitted from the training<br />

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RWANDA TEA<br />

• http://www.rainforest-alliance.org/multimedia/rwanda-tea-farmer<br />

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THE NEED FOR LAND HUSBANDRY<br />

‘The food industry (for various reasons) cares about<br />

what happens on farms. The fuel industry is only<br />

interested in compliance’<br />

Chris Wille,<br />

Chief of Agriculture,<br />

Rainforest Alliance<br />

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THANK YOU !<br />

Mohammad Rafiq mrafiq@ra.org<br />

Senior Vice President, Programs<br />

The Rainforest Alliance works to conserve biodiversity and ensure sustainable livelihoods<br />

by transforming land-use practices, business practices and consumer behavior.


• Supporting standard development. (we supported both the Roundtable on<br />

Sustainable Biofuels and the International Sustainability and Carbon Certification<br />

standards. As the oldest and most experienced standard and cert system, we<br />

contribute hard-earned knowledge about how to guide improvements on<br />

plantations, which produce mostly food but also biomass for biofuels)<br />

• Leading harmonization. (with support from Packard and now CLUA, we have led<br />

efforts to build unity, alignment and collaboration among the roundtables, the SAN<br />

standard and the two biofuels standards. This is beginning to pay off, as the RSB has<br />

“recognized” the SAN standard, and Bonsucro is working with IMAFLORA to find<br />

common ground)<br />

• Raising the bar and seeking solutions. (we have led or participated in coalitions<br />

working on biofuels related issues such as the definition of high conservation value<br />

ecosystems, “go” and “no-go” planting areas, equity and self-empowerment for<br />

small holders, biological corridors and buffer zones, and the troublesome Indirect<br />

Land Use Change. We and WRI have developed a Forest Cover Monitoring<br />

Methodology that uses satellite imagery and boots-on-the-ground verification. The<br />

SAN standard-setting process serves as a model for the others, and the SAN<br />

standard itself is the backbone of all the new standards.)<br />

• Field-proofing policy. (The RA and SAN feed information from the field to<br />

policymakers and support our sister NGOs in biofuels policy reform. We are not<br />

vocal in policy forums; instead we support groups like BirdLife in Europe and<br />

National Wildlife Federation and NRDC in the US, helping them see and “proof”<br />

the implications of policy changes.)<br />

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