Day 1 - Session 4 - IPIECA
Day 1 - Session 4 - IPIECA
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
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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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