CLEAN DEVELOPMENT MECHANISM
AR-ACM0003
A/R Large-scale Consolidated Methodology Afforestation and reforestation of lands except wetlands
Version 02.0
Sectoral scope(s): 14
TABLE OF CONTENTS Page
1.INTRODUCTION (3)
2.SCOPE, APPLICABILITY, AND ENTRY INTO FORCE (3)
2.1.Scope (3)
2.2.Applicability (3)
2.3.Entry into force (3)
3.NORMATIVE REFERENCES (4)
4.DEFINITIONS (4)
5.BASELINE AND MONITORING METHODOLOGY (5)
5.1.Selection of carbon pools and greenhou gas accounted (5)
5.2.Identification of the baline scenario and demonstration of additionality (5)
5.3.Stratification (5)
5.4.Baline net GHG removals by sinks (6)
5.5.Actual net GHG removals by sinks (7)
5.6.Leakage (8)
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5.7.Net anthropogenic GHG removals by sinks (8)
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5.8.Calculation of tCERs and lCERs (8)
6.MONITORING PROCEDURE (9)
6.1.Monitoring plan (9)
6.2.Monitoring of project implementation (9)
6.3.Precision requirements (10)
6.4.Data requirements under the methodology (10)
APPENDIX 1. CROPLAND IN WHICH SOIL DISTURBANCE IS RESTRICTED (11)
APPENDIX 2. GRASSLAND IN WHICH SOIL DISTURBANCE IS RESTRICTED (14)
1. Introduction
1. This methodology allows afforestation and reforestation of any land that does not fall into
the category of wetland. Where the land in its baline land-u has soil organic carbon (SOC) conte
nt that is expected to be higher than that under the land-u of “forestry”, the methodology restricts the extent of soil disturbance in the project to be no more than
10 per cent. The higher SOC content in the baline may result either becau of the
nature of the soils (e.g. the soils are organic soils) or becau of anthropogenic activities
(e.g. soils are not tilled and external organic matter is added as inputs). Apart from this
restriction on the extent of soil disturbance in certain types of soils and land-u practices, the methodology has a broad scope of application1. Project activities applying this methodology may choo to exclude or include accounting of any of the three carbon pools of dead wood, litter, and soil organic carbon.
2. Scope, applicability, and entry into force
2.1. Scope
2. This methodology excludes from its scope the land that falls into the category of wetland.
处女女和摩羯男2.2. Applicability
3. This methodology is applicable under the following conditions:
(a) The land subject to the project activity does not fall in wetland category;
(b) Soil disturbance attributable to the project activity does not cover more than 10
per cent of area2in each of the following types of land, when the lands are
included within the project boundary:
(i) Land containing organic soils;
(ii) Land which, in the baline, is subjected to land-u and management practices and receives inputs listed in appendices 1 and 2 to this
methodology.
4. A project activity applying this methodology shall also comply with the applicability
conditions of the tools contained within the methodology and applied by the project activity.
2.3. Entry into force
5. The date of entry into force of the revision is the date of the publication of the EB 75
meeting report on 4 October 2013.
1For example, the land to be afforested or reforested does not have to be degraded land.
矩形的判定定理
2For example, digging pits of size 0.50 m × 0.50 m (length × width) at a spacing of 3 m × 3 m is equal to a coverage of 2.78 per cent; continuous ploughing of land is equal to a coverage of 100 per cent.
3. Normative references
6. The following documents are indispensable for application of this methodology:3
(a) Clean development mechanism project standard;
(b) A/R methodological tools:
(i) “Combined tool to identify the baline scenario and demonstrate
additionality in A/R CDM project activities”;
(ii) “Estimation of carbon stocks and change in carbon stocks of trees and shrubs in A/R CDM project activities”;
(iii) “Estimation of carbon stocks and change in carbon stocks in dead wood and litter in A/R CDM project activities”;
(iv) “Tool for estimation of change in soil organic carbon stocks due to the implementation of A/R CDM project activities”;
(v) “Estimation of non-CO2greenhou gas (GHG) emissions resulting from burning of biomass attributable to an A/R CDM project activity”;
(vi) “Estimation of the increa in GHG emissions attributable to displacement of pre-project agricultural activities in A/R CDM project activity”.
4. Definitions
7. The definitions contained in the following documents shall apply:4
(a) “Glossary of CDM terms”;
(b) “Modalities and procedures for afforestation and reforestation project activities
under the clean development mechanism (A/R CDM modalities and procedures)
as contained in the annex to decision 5/CMP.1”;
(c) “IPCC Good Practice Guidance for Land U, Land-U Change and Forestry,
2003”.
8. For the purpo of this methodology, the following definition shall apply:
(a) Soil disturbance - refers to any activity that results in a decrea in soil organic
carbon (SOC), for example ploughing, ripping, scarification, digging of pits and
trenches, stump removal, etc.
3The documents are available online at: <cdm.unfccc.int/Reference/index.html>.
4The documents are available online at the following URLs:
(a) <cdm.unfccc.int/Reference/index.html>;
(b) <cdm.unfccc.int/Reference/COPMOP/index.html>;
(c) <www.ipcc jp/public/gpglulucf/gpglulucf.html>.
5. Baline and monitoring methodology
5.1. Selection of carbon pools and greenhou gas accounted
9. The carbon pools lected for accounting of carbon stock changes are shown in table 1.
Table 1. Carbon pools lected for accounting of carbon stock changes
春晚观后感10. The emission sources and associated GHGs lected for accounting are shown in table
2.
Table 2. Emission sources and GHGs lected for accounting
5.2. Identification of the baline scenario and demonstration of additionality 11. Project participants (PPs) shall identify the baline demonstrate that the project activity
is additional by lecting one of the following options:凤凰古城旅游
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(a) Applying the “Combined tool to identify the baline scenario and demonstrate
三妖additionality in A/R CDM project activities”;
(b) Applying an approved standardized baline appropriate to their project.
5.3. Stratification
12. If biomass distribution over the project area is not homogeneous, stratification should be
carried out to improve the precision of biomass estimation. Different stratifications may
