1. Title of project: Scolel Té: Carbon Sequestration and Sustainable Forest Management in
Chiapas
2. Host country: Mexico
3. Brief project description:
Scolel Té is a forestry and land-use project located in northeast Chiapas, Mexico. This project will
assist farmers primarily in nine Mayan indigenous communities located in highland and lowland ecoregions
with developing small agroforestry and forestry enterprises. The greenhouse gas (GHG) benefits of the
project accrue from forest growth (i.e., carbon sequestration) that would not have occurred in the absence
of project activities. In addition to reducing forest degradation and conversion to agriculture and
improving the sustainability of local farming systems, this project is expected to contribute to the social
and economic welfare of these communities as well as the preservation of the region's rich
biodiversity.
4. Participants:
Name of Organization or Individual
Country
El Colegio de la Frontera Sur (ECOSUR)
Mexico
Unión de Crédito Agropecuario e Industrial de los Estados de Chiapas y Oaxaca, Pajal
Ya Kac'Tic S.A. de C.V. (Unión de Crédito Pajal)
Mexico
American Forests
U.S.A.
Econergy International Corporation (EIC)
U.S.A.
Commission for Environmental Cooperation (CEC)
Multilateral
University of Edinburgh
Scotland
International Energy Agency (IEA)
England
UK Darwin Initiative
UK Overseas Development Administration Forestry Research Program
Fédération Internationale de l'Automobile (FIA)/Fédération
Internationale Pour l'Isolement du Carbone (FIPIC)
Belgium/France
Item
Organization
Name of organization (original language)
or
Name of individual if unaffiliated with any organization
The Tzeltal (lowland) and Tojolobal (highland) regions of northeast Chiapas, a southern state
bordering Guatemala, and additional areas yet to be identified
Key Dates and Current Stage of Project
Project starting date (month/year)
June 1997
Project ending date (month/year)
May 2027
Project lifetime (years)
30
Current stage of project
In progress
General Project Description and Technical Data
Scolel Té (which means "growing trees" in Tzeltal and Tojolobal) is a forestry and
land-use project that will assist farmers primarily in nine Mayan indigenous communities with
developing small agroforestry and forestry enterprises. The objective of the project is to promote
carbon sequestration and sustainable farming practices by providing local farmers with technical
assistance and financial incentives to shift from agriculture to agroforestry, convert pastures to
plantations, restore degraded forest, and better manage natural forest. The carbon benefits
generated by these enterprises are expected to range from a minimum of 55,000 metric tonnes (t) of
CO2 (15,000 t C) up to 1.21 million t CO2 (330,000 t C), depending on
funding. In addition, this project is expected to contribute to the social and economic welfare of
these communities as well as the preservation of the region's rich biodiversity.
Approximately 75% of the project's inputs will be directed to five Tzeltal (lowland Mayan)
villages located at about 800 meters (m) above sea level and located in the municipality of
Chilón, and four Tojolobal (highland Mayan) villages located at about 1,500 m above sea
level and split between the municipalities of Comitán and Las Margaritas. The remaining 25%
of the project's inputs will be directed to other groups that have yet to be identified. The
area of the nine participating villages totals 13,289 hectares (ha), of which 41% is forest, 26% is
used for maize, 14% is fallow, 7% is pasture, 4% is used for coffee, and 9% is used for other
purposes. Of the 13,289 ha, approximately 2,000 ha will be involved in the Scolel Té
project, with 400 ha located in the Tzeltal region and 1,600 ha located in the Tojolobal region.
Within each region, the project area will be split evenly between agroforestry and other
forest/land management projects. An additional 400 ha will be added to the project area as other
participants are identified.
The project's pilot phase will last three years, during which time local farmers will develop
and register their own land management plans and begin to receive technical and financial
assistance. The land that is registered during the three-year pilot phase will accrue carbon
benefits for the ensuing 27 years. The sale of "proto-carbon credits" in anticipation of
these carbon benefits will be used to finance implementation of the project, which will eventually
become self-sustaining.
6. Cost
(a) Explanation of methodology for calculating cost data
Methodology for Calculating Cost Data
As part of the research and development activities for this project, the project team developed a
cost model to derive carbon sequestration costs as a function of land use and biomass growth rates.
This model incorporates multiple factors for each land-use type, including (1) site quality and
expected wood production, (2) capital and recurrent costs of implementation (e.g., establishment,
maintenance, silvicultural treatments, and harvesting), (3) opportunity costs of land and labor
diverted to forestry/agroforestry, and (4) potential income from forestry/agroforestry products.
Discount rates are applied to the costs. The project's target mean cost is US$10/t C.
The exact project costs will be dependent upon the nature of the land-use projects, which have yet
to be developed. In the proposal, the project developer provided estimated costs for agroforestry
and plantation projects ranging from US$2.32/t C-ha (live fence) to US$3.98/t C-ha (enriched
fallow) for the Tzeltal region, and US$2.50/t C-ha (live fence) to US$11.15/t C-ha (plantation) for
the Tojolobal region. These cost estimates are based upon an intermediate level of production
intensity and a discount rate of 5%. By raising the discount rate to 10%, these cost estimates
shift to US$1.84/t C-ha to US$2.71/t C-ha for the Tzeltal region, and US$1.47/t C-ha to US$8.89/t
C-ha for the Tojolobal region, respectively.
(b) Cost data-Project development
Itemized Project Development Costs
(c) Cost data-Project implementation
This information is not yet available.
7. Monitoring and verification of AIJ project activities and results
Item
Party(ies) that will be monitoring project activities
(1) Participating farmers, (2) a technical team composed of trained professionals and local
promoters, and (3) a research team composed of researchers from ECOSUR and the University of
Edinburgh
Party(ies) that will be externally verifying project results
This information is not yet available.
Date when the monitoring plan became (or will become) operational (month/year)
This information is not yet available.
Types of data that will be collected
Biomass density, biomass growth rate, tree species and age class, soil carbon content,
documentation of land ownership and approval of forest plans, participation of women and impact of
projects on women, comparative economic productivity, biological diversity, impact on water quality
and watershed integrity, and availability and affordability of technical training
Description of Monitoring and Verification Activities and Schedule for Implementation
Three groups will conduct monitoring and verification activities: farmers, the technical team, and
the research team. The participating farmers will be responsible for reporting the performance of
their individual projects; these reports will serve as the basis for the payment of annuities to
the farmers. The technical team, composed of trained professionals and local promoters, will be
responsible for (1) evaluating the proposed projects, (2) training farmers to implement the
projects and record the performance of their projects, (3) estimating the carbon fluxes for each
project, and (4) assessing overall project impacts. The research team, composed of researchers from
ECOSUR and the University of Edinburgh, will (1) develop carbon flux models for each category of
project system within each ecological region, and (2) train the technical team to assess project
viability, carbon fluxes, and project impacts.
Monitoring will be conducted in four stages. The first stage consists of evaluating the progress
achieved by project promotion and training activities. The second stage consists of evaluating the
documented working plans submitted by farmers in order to develop estimates of carbon fluxes
resulting from the projects. The third stage, which follows project implementation, consists of
data collection by the farmers and internal verification of this data collection through the random
sampling of project participants by the technical team. The fourth stage involves similar data
collection activities that continue as projects are maintained, expanded, and/or upgraded.
In addition to data relating to the measurement of carbon fluxes, indicators of project
sustainability will be monitored. These indicators will be used to assess project impacts in areas
such as the participation of women, comparative economic productivity, biodiversity, water quality
and watershed integrity, and the long-term availability and affordability of technical training.
These criteria were reviewed and developed by several international organizations, including UNCED
and the Forest Stewardship Council.
B. Governmental approval
Item
Please check one of the following.
This report is a first
report.
or
This report is an intermediate report.
or
This report is a final report.
Please check one of the following:
This report is a joint
report. Letter(s) of approval of this report from the designated national authority of the other
Party(ies) involved in the activity is(are) attached in Section J, Annex.
or
This report is a separate report.
Additional comments (if any):
C. Compatibility with, and supportiveness of, national economic development and socioeconomic and
environmental priorities and strategies
Compatibility with Economic Development and Socioeconomic and Environmental Priorities
The Scolel Té project seeks to promote forestry and agroforestry projects that are designed
and implemented by indigenous communities to meet their economic development needs and increase the
sustainability of their land-use management practices. These projects will be implemented on both
privately-owned and communal land.
According to a technical paper prepared by the project team and included in the proposal,
"Based on the 1992 land reform, Mexico has sought to implement a progressive forest policy,
particularly in tropical areas which contain the most important forest extensions of the country.
This policy has been underlined by a number of activities: the development of a National Tropical
Forestry Action Plan (SARH, 1994), - the establishment of the headquarters of the Forest
Stewardship Council in Oaxaca, southern Mexico, - the elimination of subsidies and credit for
extensive cattle ranching in the tropical states, - [and] the government support to various
community controlled forest management projects....The 1992 change in the Mexican Land-Tenure Law
(Articulo 27) gives legal title to the rural communities for the land they manage as an ejido
[productive grouping of people with land given in common ownership after the 1917 revolution] or
community. This allows rural farmers legal status to establish joint ventures with investors, so
that capital can be invested in alternative land-use systems."
D. Environmental, social/cultural, and economic impacts of the AIJ project
Non-Greenhouse-Gas Environmental Impacts of the Project
This project is expected to contribute substantially to the preservation of biodiversity, both
within and outside the project area. Within the project area, the genetic diversity of valuable
tree species will be preserved through reforestation and agroforestry activities, including planned
seed collection. In addition, the reforestation of degraded land and pasture will reduce forest
fragmentation, offer expanded forest habitat for fauna within the project area, reduce soil
erosion, and improve watershed integrity. By providing a sustainable source of timber and fuelwood,
the project is expected to reduce harvesting of wood from the cloud forest in the Tzeltal area,
which supports rare endemic species. The project's economic development opportunities may also
slow the migration of local residents to the "agriculture-forest frontier" of the
Lacandon rainforest, thereby helping to conserve its biodiversity and other resources.
The project developer identified the increased use of agrochemicals by farmers as one possible
result of the higher incomes generated by the project. It is also possible that farmers may be able
to purchase agrochemicals that are of higher quality and less toxic, and upgrade their spraying
equipment. The project team plans to work with the agricultural advisory team of the Unión
de Crédito Pajal to monitor and address this issue.
Social/Cultural Impacts of the Project
The project developer has incorporated specific measures into the project to improve the welfare of
women in the participating communities. These measures are based on the needs and wishes expressed
by local women during the feasibility study, and include women's participation in the
production of fruit trees and ornamentals and the tending and management of tree nurseries. The
project team will also pursue efforts to place a significant portion of incentive payments in the
hands of women, when appropriate.
Economic Impacts of the Project
Initial funding for the projects will be provided through the sale of "proto-carbon
credits." The projects are expected to become self-sustaining after approximately 18 years,
and the sale of timber products should provide sufficient income for the farmers to enter into a
new cycle of tree growth and harvesting after the end of the project. The project developer expects
that additional local economic development will result from the stimulation of forest-based
enterprises, including carpentry shops, ecotourism, and the sale of non-timber forest products.
E. Greenhouse gas impacts of the AIJ project
1. Scenario description
Item
Site Designation
Site number (order of presentation in this report)
1 of 9
Site name/designation
Yaluma (Tojolobal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Yaluma village comprises 3,085 ha in the Tojolobal (highland) region. The primary land uses in
this village are forest (19%), fallow (13%), pasture (8%), maize (49%), and other (11%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
2 of 9
Site name/designation
Lomantan (Tojolobal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Lomantan village comprises 2,900 ha in the Tojolobal (highland) region. The primary land uses
in this village are forest (52%), fallow (26%), maize (14%), and other (9%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
3 of 9
Site name/designation
Palma Real (Tojolobal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Palma Real village comprises 819 ha in the Tojolobal (highland) region. The primary land uses
in this village are forest (12%), pasture (49%), maize (37%), and other (2%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
4 of 9
Site name/designation
Jusnajab (Tojolobal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Jusnajab village comprises 3,800 ha in the Tojolobal (highland) region. The primary land uses
in this village are forest (68%), fallow (5%), pasture (3%), maize (16%), and other (9%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
5 of 9
Site name/designation
Alan Cantajal (Tzeltal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Alan Cantajal village comprises 180 ha in the Tzeltal (lowland) region. The primary land uses
in this village are forest (11%), fallow (13%), pasture (1%), maize (19%), coffee (38%), and other
(18%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
6 of 9
Site name/designation
Chapullil (Tzeltal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Chapullil village comprises 300 ha in the Tzeltal (lowland) region. The primary land uses in
this village are forest (12%), fallow (22%), pasture (22%), maize (11%), coffee (30%), and other
(3%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
7 of 9
Site name/designation
Segunda Coloteel (Tzeltal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Segunda Coloteel village comprises 245 ha in the Tzeltal (lowland) region. The primary land
uses in this village are fallow (27%), pasture (5%), maize (24%), coffee (41%), and other
(3%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
8 of 9
Site name/designation
Jolcacuala (Tzeltal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Jolcacuala village comprises 1,220 ha in the Tzeltal (lowland) region. The primary land uses in
this village are forest (41%), fallow (11%), pasture (1%), maize (33%), coffee (6%), and other
(8%).
Additional information is not yet available.
Predicted Project Scenario
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Actual Project
Primary activity(ies)
This information is not yet available.
Description:
This information is not yet available.
Item
Site Designation
Site number (order of presentation in this report)
9 of 9
Site name/designation
Muquenal (Tzeltal)
Project sector
Land-use change and forestry
Reference Scenario
Primary activity(ies)
This information is not yet available.
Has the reference scenario changed since the last report? (If yes, explain any changes below.)
Yes
No
This is the first project
report.
Description:
The Muquenal village comprises 740 ha in the Tzeltal (highland) region. The primary land uses in
this village are forest (14%), fallow (27%), pasture (7%), maize (14%), coffee (27%), and other
(12%).
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
The simulation model CO2FIX was used to calculate net carbon emissions/sequestration. Total carbon
sequestration was calculated for a 150-year period, equivalent to five rotations (30 years per
rotation) of Tojolobal land and six rotations (25 years per rotation) of Tzeltal land, to avoid
overestimation of carbon stocks in short-rotation forest systems. Annual averages for carbon
sequestration were derived from carbon sequestration totals for the first rotation. Tree growth was
assumed to be linear.
In the Tojolobal region, live fence was assumed to consist of Pinus oocarpa , P. michoacana , or
Cupressus sp. planted at a distance of 3 m. Production levels for poor, medium-fertile, and fertile
sites were assumed to be 3.2, 4.0, and 4.8 m3/ha-yr. For these production levels,
average annual carbon sequestration was calculated to be 0.96, 1.25, and 1.54 t C/ha for a period
of 30 years.
In the Tzeltal region, live fence was assumed to consist of Cedrela odorata planted at a distance
of 3 m. Production levels for poor, medium-fertile, and fertile sites were assumed to be 4.8, 6.0,
and 7.2 m3/ha-yr. For these production levels, average annual carbon sequestration was
calculated to be 1.66, 2.19, and 2.72 t C/ha for a period of 25 years.
Description of Calculation Methodology for the Actual Project
Coffee/shade tree projects-Site numbers to be determined
Project sector
Land-use change and forestry
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
The simulation model CO2FIX was used to calculate net carbon emissions/sequestration. Total carbon
sequestration was calculated for a 150-year period, equivalent to six rotations (25 years per
rotation) of Tzeltal land, to avoid overestimation of carbon stocks in short-rotation forest
systems. Annual averages for carbon sequestration were derived from carbon sequestration totals for
the first rotation. Tree growth was assumed to be linear.
In the Tzeltal region, Cedrela odorata or Cordia alliodora were assumed to be planted as shade
trees in coffee plantations at a distance of 10 x 10 m. Production levels for poor, medium-fertile,
and fertile sites were assumed to be 6.0, 7.5, and 9.0 m3/ha-yr. For these production
levels, average annual carbon sequestration was calculated to be 2.11, 2.76, and 3.41 t C/ha for a
period of 25 years.
Description of Calculation Methodology for the Actual Project
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
The simulation model CO2FIX was used to calculate net carbon emissions/sequestration. Total carbon
sequestration was calculated for a 150-year period, equivalent to five rotations (30 years per
rotation) of Tojolobal land and six rotations (25 years per rotation) of Tzeltal land, to avoid
overestimation of carbon stocks in short-rotation forest systems. Annual averages for carbon
sequestration were derived from carbon sequestration totals for the first rotation. Tree growth was
assumed to be linear.
In the Tojolobal region, Taungya was assumed to be planted with Pinus oocarpa , P. michoacana , or
Cupressus sp. at a distance of 4 x 4 m. Thinnings of 25% of total stands were expected to occur in
years 8 and 16. Production levels for poor, medium-fertile, and fertile sites were assumed to be
8.0, 10.0, and 12.0 m3/ha-yr. For these production levels, average annual carbon
sequestration was calculated to be 2.61, 3.31, and 4.01 t C/ha for a period of 30 years.
In the Tzeltal region, Taungya was assumed to be planted with Cedrela odorata at a distance of 10 x
3 m. Thinnings of 25% of total stands were expected to occur in years 8 and 16. Production levels
for poor, medium-fertile, and fertile sites were assumed to be 11.9, 14.9, and 17.9
m3/ha-yr. For these production levels, average annual carbon sequestration was
calculated to be 4.71, 6.00, and 7.23 t C/ha for a period of 25 years.
Description of Calculation Methodology for the Actual Project
Enriched-fallow projects-Site numbers to be determined
Project sector
Land-use change and forestry
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
The simulation model CO2FIX was used to calculate net carbon emissions/sequestration. Total carbon
sequestration was calculated for a 150-year period, equivalent to five rotations (30 years per
rotation) of Tojolobal land and six rotations (25 years per rotation) of Tzeltal land, to avoid
overestimation of carbon stocks in short-rotation forest systems. Annual averages for carbon
sequestration were derived from carbon sequestration totals for the first rotation. Tree growth was
assumed to be linear.
In the Tojolobal region, enriched fallow was assumed to be planted with Pinus oocarpa , P.
michoacana , or Cupressus sp. at a distance of 7 x 2 m. Thinnings of 25% of total stands were
expected to occur in years 8 and 16. Production levels for poor, medium-fertile, and fertile sites
were assumed to be 8.0, 10.0, and 12.0 m3/ha-yr. For these production levels, average
annual carbon sequestration was calculated to be 2.61, 3.31, and 4.01 t C/ha for a period of 30
years.
In the Tzeltal region, enriched fallow was assumed to be planted with Cedrela odorata, Cordia
alliodora, or Calophyllum brasiliense at a distance of 10 x 2 m. Thinnings of 25% of total stands
were expected to occur in years 8 and 16. Production levels for poor, medium-fertile, and fertile
sites were assumed to be 11.9, 14.9, and 17.9 m3/ha-yr. For these production levels,
average annual carbon sequestration was calculated to be 4.71, 6.00, and 7.23 t C/ha for a period
of 25 years.
Description of Calculation Methodology for the Actual Project
Reforestation, sustainable harvesting projects-Site numbers to be determined
Project sector
Land-use change and forestry
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
The simulation model CO2FIX was used to calculate net carbon emissions/sequestration. Total carbon
sequestration was calculated for a 150-year period, equivalent to five rotations (30 years per
rotation) of Tojolobal land, to avoid overestimation of carbon stocks in short-rotation forest
systems. Annual averages for carbon sequestration were derived from carbon sequestration totals for
the first rotation. Tree growth was assumed to be linear.
In the Tojolobal region, plantations were assumed to consist of Pinus oocarpa , P. michoacana , or
Cupressus sp. planted at a distance of 2 x 3 m. Thinnings of 33% of total stands were expected to
occur in years 8 and 16. Production levels for poor, medium-fertile, and fertile sites were assumed
to be 8.0, 10.0, and 12.0 m3/ha-yr. For these production levels, average annual carbon
sequestration was calculated to be 2.58, 3.27, and 3.97 t C/ha for a period of 30 years.
Description of Calculation Methodology for the Actual Project
Forest preservation, silviculture-Site numbers to be determined
Project sector
Land-use change and forestry
Description of Calculation Methodology for the Reference Scenario
This information is not yet available.
Description of Calculation Methodology for the Project Scenario
This information is not yet available.
Description of Calculation Methodology for the Actual Project
This information is not yet available.
3. GHG emission/sequestration data
(a) Reporting of GHG emissions/sequestration
Annual estimates are not yet available. Cumulative GHG benefits of the project are anticipated to range
from a minimum of 55,000 t CO2 up to 1.21 million t CO2, depending on funding.
(b) Additional information on GHG emissions/sequestration
Indirect or Secondary GHG Impacts (Positive and Negative)
The implementation of agroforestry and forest preservation projects may result in some leakage of
project benefits if agricultural activities are displaced to other areas. The assessment of
opportunities for leakage will be included in monitoring activities during the first year of the
project. The project team plans to offset leakage by assisting farmers with intensifying production
in areas not used for agroforestry and forestry.
It is possible that local farmers who do not officially participate in the project may be
influenced by the results achieved by project participants and decide to adopt forestry and
agroforestry measures on their own accord. This could result in a secondary GHG benefit.
By providing a sustainable source of timber and fuelwood as well as local economic development
opportunities, this project may reduce extraction of timber and fuelwood from other areas outside
the project, particularly the cloud forest in the Tzeltal area and the Lacandon rainforest
conservation area. This could result in an indirect GHG benefit.
Factors That Could Cause the Future Loss or Reversal of GHG Benefits
Natural disasters such as fire and pestilence could cause the loss of GHG benefits. In addition,
both internal and external sociopolitical factors could cause the loss of GHG benefits. Internally,
the level of farmers' participation in project activities for the duration of the project and
the quality of farmers' land management activities will affect the long-term success of the
project. Externally, political unrest in the vicinity of the project, such as the recent Zapatista
uprising, could impact the management of communal areas.
Strategy for Reducing the Risk of Future Loss or Reversal of GHG Benefits
The project team will advocate land management practices that reduce the risk of fire and
pestilence. Internal social divisions and other problems will be taken into account and managed by
the project team to the extent possible. The project team reports that the communities involved in
the project have remained intact and relatively peaceful despite the recent Zapatista uprising. In
addition, the land tenure in these communities is secure and well established, which will help to
reduce their vulnerability.
F. Funding of the AIJ project
1. Identification of funding sources
(a) Funding sources for project development
Funding Source
Country ofFundingSource
Amount($US)
Percentof Total Funding(%)
UK Overseas Development Administration Forestry Research Program
213,200
56
UK Darwin Initiative
65,600
17
Commission for Environmental Cooperation
Multilateral
20,000
5
International Energy Agency's Greenhouse Gas R&D Programme
England
82,000
22
Total
380,800
100
(b) Funding sources for project implementation
Funding Source
Country ofFunding Source
Amount($US)
Percentof TotalFunding(%)
Is This Funding Assured? (Y/N)
Fédération Internationale de l'Automobile/Fédération Internationale
Pour l'Isolement du Carbone (FIPIC)
Belgium/France
150,000
5
Y
Undetermined
3,150,000
95
N
Total
3,300,000
100
2. Assessment of additional funding needs
Current or Planned Activities to Obtain Additional Funding
The current level of funding will support sequestration of 15,000 t C out of a possible total of
330,000 t C over the lifetime of the project. American Forests and EIC will arrange for the sale of
additional "proto-carbon credits" to support project activities. The current sale price
of these credits is US$10/t C, which was used to calculate total funding needs of US$3,300,000.
G. Contribution to capacity building and technology transfer
Contribution to Capacity Building and Technology Transfer
Participating farmers will receive technical assistance in conducting agroforestry and silviculture
activities and monitoring project results.
H. Recent developments, technical difficulties, and obstacles encountered
Recent Project Developments
This information is not yet available.
Technical Difficulties and Other Obstacles Encountered
This information is not yet available.
I. Additional information
Additional Information
None.
J. Annex
1. Host country acceptance of the AIJ project
Country/Project Title
Name, Title, and Government Agencyof the DesignatedNational Authority
Date of Approval(day/month/year)
Scolel Té: Carbon Sequestration and Sustainable Forest Management in Chiapas
Dr. Carlos Gay, Coordinator of the Unit for International Cooperation and Agreement, National
Ecology Institute (INE), Secretariat of the Environment, Natural Resources, and Fisheries
(SEMARNAP)