6511- CPA DD Specific_26Jun2012
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Transcript of 6511- CPA DD Specific_26Jun2012
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 1
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
CLEAN DEVELOPMENT MECHANISMSMALL-SCALE PROGRAM ACTIVITY DESIGN DOCUMENT FORM (CDM-SSC-CPA-DD)
Version 01
CONTENTS
A. General description of CDM programme activity (CPA)
B. Eligibility of CPA and Estimation of Emission Reductions
C. Environmental Analysis
D. Stakeholder comments
Annexes
Annex 1: Contact information on entity/individual responsible for the CPA
Annex 2: Information regarding public funding
Annex 3: Baseline information
Annex 4: Monitoring plan
NOTE:
(i) This form is for submission of CPAs that apply a small scale approved methodology using the
provision of the proposed small scale CDM PoA.
(ii) The coordinating/managing entity shall prepare a CDM Small Scale Programme Activity Design
Document (CDM-SSC-CPA-DD)1,2
that is specified to the proposed PoA by using the provisions stated
in the SSC PoA DD. At the time of requesting registration the SSC PoA DD must be accompanied by aCDM-SSC CPA-DD form that has been specified for the proposed SSC PoA, as well as by one
completed CDM-SSC CPA-DD (using a real case). After the first CPA, every CPA that is added over
time to the SSC PoA must submit a completed CDM-SSC CPA-DD.
1The latest version of the template form CDM-CPA-DD is available on the UNFCCC CDM web site in the
reference/document section.
2At the time of requesting validation/registration, the coordinating managing entity is required to submit a
completed CDM-POA-DD, the PoA specific CDM-CPA-DD, as well as one of such CDM-CPA-DD completed
(using a real case).
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 2
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
SECTION A. General description of small scale CDM programme activity (CPA)
A.1. Title of the small-scale CPA:
>>
Socfindo EFB plus POME Co-composting Project (CPA No. 001)
Version: 03
31/05/2012
A.2. Description of the small-scale CPA:
>>
Socfindo EFB plus POME Co-composting Project at Bangun Bandar, hereafter referred as the Project
Activity, is a small-scale CDM programme activity (CPA) involving the installation and operation of asophisticated Aerated Bunker Co-composting (ABC) plant at PT.Socfin Indonesias (Socfindo) Bangun
Bandar Crude Palm Oil Mill (Mill Facility). The project activity will be constructed at the Mill Facility
which has capacity to process Fresh Fruit Bunches (FFB) of 23 tons/hour. The Project Activity is located
at Bangun Bandar, North Sumatra Province, Indonesia.
In the process of producing CPO, the Mill Facility has four types of waste: Empty Fruit Bunches (EFB),
fibers, palm kernel shells (PKS), and liquid waste known as palm oil mill effluent (POME). While fiber
and a proportion of PKS is used as fuel for the mill boilers to generate heat and electricity for the whole
plant, the EFBs are discharged as waste and left to decay in unmanaged dumpsites. POME is treated in a
series of open air anaerobic and aerobic ponds before being discharged into a local waterway.
The Project Activity utilizes both EFB and POME for the co-composting process, and the output of the
co-composting process is organic compost which will be recycled by Socfindo and reapplied to its
neighbouring plantations. Therefore the Project Activity will reduce the methane emissions from
anaerobic digestion of POME treatment by avoiding the current open air anaerobic wastewater treatment
system. Moreover it will also avoid methane emissions from the EFB solid waste that is currently
disposed of and left to decay in unmanaged solid waste disposal sites situated in the oil palm plantation
area.
The Aerated Bunker Co-composting (ABC) process is an enclosed co-composting system with a
computer controlled environment which continually monitors O2 and temperature to ensure the optimum
ambient environment for natural aerobic decomposition of the waste streams.
Contribution to Sustainable Development
In response to the urgent and pressing global call for sustainably produced palm oil, the Roundtable on
Sustainable Palm Oil (RSPO) was formed in 2004 with the objective ofpromoting the growth and use of
sustainable oil palm products through credible global standards and engagement of stakeholders. The
RSPO is a not-for-profit association that unites stakeholders from seven sectors of the palm oil industry -
oil palm producers, palm oil processors or traders, consumer goods manufacturers, retailers, banks and
investors, environmental or nature conservation NGOs and social or developmental NGOs - to develop
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 3
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
and implement global standards for sustainable palm oil3
. Socfindo has been an early joining member ofthe Roundtable on Sustainable Palm Oil (RSPO) since the 7
thDecember 2004 and has consistently been
moving towards obtaining RSPO certification in its Mills.
The Project Activity will have a positive contribution to the Sustainable Development of Indonesia as
defined by the Designated National Authority. The contribution of the Project Activity to sustainable
development is significant assessed by using the sustainable development criteria of Indonesia4.
Indonesias sustainable development criteria and indicators for assessing a proposed CDM project are
categorised into four groups: environmental, economic, social and technological sustainability. Details of
the positive contribution to sustainable development are:
Environmental sustainability: (The scope of evaluation is the area having direct ecological impacts
from the project).
The Project Activity facilitates the use of Mill waste (EFB and POME) to create high-value organiccompost that can be reapplied to the Palm Plantation. This reduces local waste production and
conserves natural resources by turning unwanted waste into a valuable resource (organic compost).
The Project Activity which involves the implementation and operation of Co-composting activity ofPalm Mill waste has a number of positive local environmental effects including:
Reducing or avoiding completely the negative environmental effects associated with baselinetreatment of POME in open air lagoons including:
Avoiding methane emissions thus reducing GHG emissions;
Avoiding negative odour associated with POME lagoons;
Reducing or avoiding altogether the discharge of treated POME into natural waterways,therefore improving water quality of local streams for biota and community use.
Avoiding negative environmental effects in relation to the dumping or disposal of EFB in the
baseline situation by fully utilizing the Mills waste EFB for the production of organic
fertilizer;
Improving soil health by application of high nutrient organic compost onto plantations increasing organic matter in soil, improving moisture retention, providing a source of
microorganisms and nutrients and a potential replacement to inorganic fertilizers.
Improving local health by eliminating all of the existing anaerobic POME ponds and some or
3For more detail on RSPO and its mission please seehttp://www.rspo.org/?q=page/16.
4Website of the Indonesian DNA (the Indonesian National Commission for Clean Development Mechanism) setting
out Indonesias Sustainable Development Criteria and Indicatorshttp://dna-cdm.menlh.go.id/en/susdev/(accessed 18
December, 2010).
http://www.rspo.org/?q=page/16http://www.rspo.org/?q=page/16http://www.rspo.org/?q=page/16http://dna-cdm.menlh.go.id/en/susdev/http://dna-cdm.menlh.go.id/en/susdev/http://dna-cdm.menlh.go.id/en/susdev/http://dna-cdm.menlh.go.id/en/susdev/http://www.rspo.org/?q=page/16 -
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 4
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
all of the aerobic POME ponds which are a source of odour;
No additional resources (e.g. water) will be used for the composting process, as the humidityrequired will be provided by the POME.
Economic sustainability
The Project Activity will make a small contribution to employment by providing opportunity of new
jobs for local community starting from construction to commissioning and later on in operation and
maintenance of the plant;
The Project Activity will turn waste products (EFB and POME) into organic compost which:
Potentially partly replaces the existing use of purchased chemical or organic fertilizer for aplantation.
Improves palm health and contributes to improved yield through improved soil health, thussupporting a strong and sustainable Indonesian Palm Oil Industry.
Social sustainability
The Project Activity will act as a clean technology demonstration project and will encourage otherPalm Mill operators as well as other agri-processing industries to come up with similar projects.
Provision of staff training to improve their technical skills in relation to monitoring and datamanagement for CDM .
The Project Activity facilitates the voluntary adoption and uptake of Palm Mill Waste treatmentprocesses which are more environmentally friendly and sustainable than that legally required.
Technology sustainability
Supports the uptake and adoption of industry best practice techniques and technology for palm wasteprocessing via co-composting technology from abroad thereby facilitating early adoption of such
practices to displace current practice and become the baseline industry practice in Indonesia.
The Project Activity will provide an opportunity for local people to acquire know-how forconstruction, optimal maintenance and operation of state-of-the-art co-composting plant, equipment
and systems.
The Project Activity will contribute to provide an opportunity for technology transfer.
A.3. Entity/individual responsible for the small-scale CPA:
>>
PT.Socfin Indonesia is the responsible entity for the small-scale CPA.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 5
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
A.4. Technical description of the small-scale CPA:
A.4.1. Identification of the small-scale CPA:
>>
The technology used in the project activity is an advanced; automated and enclosed co-composting
technology, called the Aerated Bunker Co-composting System or ABC System. In essence, ABC aerobic
composting system provides the optimum external ambient conditions required by natural micro-
organisms to aerobically decompose the mill waste streams efficiently in a short period to produce fertile
organic compost.
How will the system ensure the aerobic conditions in the compost?
The ABC system is specifically designed as an aerobic composting system. Firstly the compost is placed
in bunkers, within concrete walls, a concrete aerated floor and under a roof which are designed to enable
the ambient environment to be controlled and to allow passive ventilation for the compost by air (see
photo of bunker below). To further facilitate the addition of the large volumes of POME, the compost is
moved every 3 to 4 days through a series of bunkers. The entire process will take approximately 25 days.
16
Empty Composting Bunker
The compost environment is computer controlled with real time monitoring of oxygen and temperature of
the compost mass through a probe which is strategically placed into the heart of the compost mass. The
computer system will automatically start the fans if the oxygen levels within the compost mass is near
10% (or at any other level if demanded) thus ensuring that the compost is not in anaerobic conditions.
Oxygen is injected into the compost from the fans through a specifically designed concrete floor which
allows air to be injected up into the compost mass (see figure below). In addition, the ABC system also
incorporates a methane meter to monitor presence of methane within the process.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 6
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Temperature, oxygen and methane levels are recorded at short intervals throughout the process by the
computer, not only for controlling the process but also for recording the compost batches history
throughout the process. Furthermore, all the compost settings and parameters used in this composting
system can be tailored to suit specific and individual requirements.
How does the system ensure that there is no run off or leakage?
Any liquid that percolates through the aerated floor will go through the compost drains and is piped into
a sump where it is re-circulated back to the compost with any excess being stored in an enclosed buffer
tank. The bunkers are covered so ambient rainwater is eliminated from the bulk of the composting area.
All the run-off water from the compost is kept within the system and constantly recycled.
The Aerated Bunker Composting System (ABC) Process:
The Aerobic Bunker composting system (ABC) is made of concrete walls on an aerated floor, under a
roof. The process is controlled by a computer that helps to maintain the mass of the compost in idealconditions for the aerobic micro- flora to function optimally in converting the blended waste streams to
an organic fertilizer. The ABC System at the Mill operates as follows:
a. Pressed EFB which is collected in Hoppers at the mill, will be delivered to the composting area viatruck. Although the composting facility is immediately adjacent to the mill, lorries will still be used to
move the EFB storage hoppers. The trucks will directly tip the EFB into the first bunker. The Project
is estimated to have a total of up to 8 bunkers.
b. POME from the Mill Facility will be stored in an enclosed tank which will circulate the POME.
Todays production will be continuously used so methane will not be produced during this time. The
COMPOST
Aerated floor keeps compost in aerobic
condition and drains excess POME back to
sump
Roof to exclude rain
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 7
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
POME will also be aerated and agitated to prevent solids from settling, and further restrict the growthof methane producing organisms.
c. The POME will be pumped from this holding tank and over the composting period, will be blendedwith the EFB and any other waste stream that the mill may be producing. The POME is piped from
the holding tank and sprayed in through a sprinkler system in the roof of each bunkers. POME will
also be added to the EFB initially through the specially designed bunker filler machine as it enters the
bunker and again to the surface of the compost when desired through the sprinkler system.
d. To facilitate the addition of the large volumes of POME from the mill, the compost is movedperiodically through the set of bunkers. After 3 to 4 days the compost will be moved and restacked in
the next bunker. Additional POME can again be added to the surface through the sprinkler system as
required during the period in the Bunker. At each move the compost is taken out of the bunker with a
front loading tractor, and transferred to the next bunker where the Bunker Mixer Filling Machine
mixes the EFB with more POME and re stacks the compost to a height of approximately 6m. The
Bunker Mixer Filling machine helps to re-blend the compost and at the same time add an even amount
of fresh POME to the compost. It breaks up any lumps that may be formed allowing air to easily
penetrate the whole mass during the next period.
e. This process is then repeated every 3 to 4 days until the end of the composting period. This processcan accommodate all the EFB and POME generated by the mill as waste and it will take
approximately 25 days. The exact application rate of POME will be determined through both
calculation and analysis. Any free liquid which is not fully absorbed by the compost can be drained
through the specially designed floor system and run back to the recycling sump for re use.
f. Throughout the process, the compost material is continually monitored by a probe inserted within thecompost which is connected to the control computer. Records are kept automatically and real time
performance of temperature and levels of oxygen and methane within the compost mass can be
monitored 24 hours a day. These probes are connected to the computer which controls the activity of
the fans. These fans control the air flow to maintain the compost in an aerobic state ideal for the
micro-flora to be fully active and prevent methane being generated. When required, the fans will be
activated to inject and force air through the specially designed bunker floor into the compost to ensure
optimum aerobic conditions are maintained. The methane monitoring unit has the capability to
override the other controls if the levels of methane rise, thus ensures that no methane is produced
during the process. From these records and by using the computer controls, it is possible to fine tune
future batches of compost and make adjustments to the composting programme to suit any seasonalvariations or changes in materials.
g. This whole process takes around 25 days to complete, after which time the output compost can betaken to the plantation via truck and spread by tractor as an organic fertilizer.
A.4.1.1. Host Party:
>>
Republic of Indonesia
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 8
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
A.4.1.2. Geographic reference or other means of identification allowing theunique identification of the small-scale CPA (maximum one page):
>>
The project activity is located at Socfin Indonesias Bangun Bandar crude palm oil mill, Martebing
village, Dolok Masihul district, Serdang Bedagai regency, and North Sumatra province, Indonesia. The
project location is about 3 hours from Medan city and has geographical location of985758.70-
99436.33 E and 31624.46 - 32032.54 N.
The map of the project location is shown in following figure5:
5Source fromhttp://maps.google.co.id/
http://maps.google.co.id/http://maps.google.co.id/http://maps.google.co.id/http://maps.google.co.id/ -
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 9
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
A.4.2. Duration of the small-scale CPA:
A.4.2.1. Starting date of the small-scale CPA:
>>
04/07/2011
A.4.2.2. Expected operational lifetime of the small-scale CPA:
>>
20 years
A.4.3. Choice of the crediting period and related information:
Renewable crediting period
A.4.3.1. Starting date of the crediting period:
>>
01/01/2013 or registration date, whichever is later
A.4.3.2. Length of the crediting period, first crediting period if the choice is
renewable CP:
>>
This CPA is the first CPA under the PoA named Co-composting Programme of Activities in Indonesia;
therefore the length of crediting period (renewable/3x7 years/21 years) is below the length of the PoA
(28 years).
A.4.4. Estimated amount of emission reductions over the chosen crediting period:
>>
Compost product generated by the project activity is expected to be 28,098 ton/year. This will be
achieved through the utilization of 18,732 ton EFB and 47,612 m3
POME per year. Therefore the Project
Activity would have emission reductions of approximately 10,130 ton CO2 per year by avoiding the
emissions of methane to the atmosphere from organic matter that would have otherwise been left to
decay anaerobically in a solid waste (EFB) disposal site including the wastewater (POME) treatment.
The total GHG emission reductions over the first crediting period are estimated of 70,910 tons CO2.
Annual emission reduction is listed in table below:
YearEstimation of annual emissions reductions in
tons of CO2
2013 10,130
2014 10,130
2015 10,130
2016 10,130
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 10
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
2017 10,130
2018 10,130
2019 10,130
Total reductions over the crediting
period (tons CO2)
70,910
Annual average of the estimated
reductions over the crediting period
(tons CO2)
10,130
A.4.5. Public funding of the CPA:
>>
No public funding is involved in the project activity.
A.4.6. Information to confirm that the proposed small-scale CPA is not a de-bundled
component
>>
As per EB 54 annex 13, following information demonstrate that the proposed project activity is not a
debundled component of a large scale activity as there are no Activities:
1. that have the same activity implementer as the proposed small scale CPA or has a coordinating ormanaging entity, which also manages a large scale PoA of the same technology/measure, and;
2. which are within 1 km of the boundary of the proposed small-scale CPA, at the closest point.
Moreover, as per PoA section A.4.4.1, PT.Socfin Indonesia has certified in writing that the proposed
CPA is not a debundled part of a bigger project.
A.4.7. Confirmation that small-scale CPA is neither registered as an individual CDM
project activity or is part of another Registered PoA:
>>
The proposed Project Activity is not registered as an individual CDM project and is not part of another
registered PoA. In addition as per the PoA-DD section A.4.4.1, PT.Socfin Indonesia have certified in
writing that the Project Activity is not and will not be registered as an individual CDM project, nor be
included within another PoA.
SECTION B. Eligibility of small-scale CPA and Estimation of emissions reductions
B.1. Title and reference of the Registered PoA to which small-scale CPA is added:
>>
Co-composting and Composting Program of Activities for Palm Oil Mills in Indonesia
B.2. Justification of the why the small-scale CPA is eligible to be included in the Registered
PoA :
>>
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 11
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
NoCriteria of technology/measure under approved
methodology AMS-III.F version 10Project Description
1. This methodology comprises measures to avoid the
emissions of methane to the atmosphere from
biomass or other organic matter that would have
otherwise been left to decay anaerobically in a solid
waste disposal site (SWDS), or in an animal waste
management system (AWMS), or in a wastewater
treatment system (WWTS). In the project activity,
controlled aerobic treatment by composting of
biomass is introduced.
Project Activity will utilize solid waste
(EFB) and wastewater (POME) for co-
composting process.
2. The project activity does not recover or combust
landfill gas from the disposal site (unlike AMS-
III.G Landfill methane recovery), and does not
undertake controlled combustion of the waste that
is not treated biologically in a first step (unlike
AMS-III.E Avoidance of methane production from
decay of biomass through controlled combustion,
gasification or mechanical/thermal treatment).
Project activities that recover biogas from
wastewater treatment shall use methodology AMS-
III.H Methane recovery in wastewater treatment.
Project activities involving co-digestion of organicmatters shall apply methodology AMS-III.AO
Methane recovery through controlled anaerobic
digestion.
Project Activity, which is the co-composting
process, belongs neither to one of the
following types:
a. Recover or combust landfill gas from thedisposal site;
b. Undertake controlled combustion of thewaste that is not treated biologically in
first step;
c. Recover biogas from wastewatertreatment, and without co-digestion of
organic matters.
3. Measures are limited to those that result in
emission reductions of less than or equal to 60 kt
CO2 equivalent annually.
Project activity will reduce approximately
emissions of 10,130 tons CO2 per year. This
is well below the maximum of 60,000 tCO2
per annum.
4. This methodology is applicable to the composting
of the organic fraction of municipal solid waste and
biomass waste from agricultural or agro-industrial
activities including manure.
The Project Activity is co-composting
process.
5. This methodology includes construction and
expansion of treatment facilities as well as
activities that increase capacity utilization at an
existing facility. For project activities that increase
capacity utilization at existing facilities, project
participant(s) shall demonstrate that special efforts
are made to increase the capacity utilization, that
the existing facility meets all applicable laws and
regulations and that the existing facility is not
included in a separate CDM project activity. The
Project Activity is newly built co-
composting plant.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 12
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
special efforts should be identified and described.6. This methodology is also applicable for co-
composting wastewater and solid biomass waste,
where wastewater would otherwise have been
treated in an anaerobic wastewater treatment
system without biogas recovery. The wastewater in
the project scenario is used as a source of moisture
and/or nutrients to the biological treatment process
e.g. composting of empty fruit bunches (EFB), a
residue from palm oil production, with the addition
of palm oil mill effluent (POME) which is the
wastewater co-produced from palm oil production.
The Project Activity is co-composting which
would utilize solid waste (EFB) and
wastewater (POME) for co-composting
process.
7. In case of co-composting, if it can not be
demonstrated that the organic matter would
otherwise been left to decay anaerobically, baseline
emissions related to such organic matter shall be
accounted for as zero, whereas project emissions
shall be calculated according to the procedures
presented in this methodology for all co-composted
substrates.
In the baseline condition, the shredded solid
waste (EFB) is directly dumped in the
plantation. This demonstrates that the
organic matter would otherwise been left to
decay anaerobically.
9. The location and characteristics of the disposal site
of the biomass, animal manure and co-composting
wastewater in the baseline condition shall be
known, in such a way as to allow the estimation ofits methane emissions, using the provisions of
AMS-III.G, AMS-III.E (concerning stockpile),
AMS-III.D Methane recovery in animal manure
management systems or AMS-III.H respectively.
The EFBs dump site and open lagoons of
wastewater treatment in the baseline
condition is clearly located and
characterized.
10. The project participants shall clearly define the
geographical boundary of the region referred in
paragraph 9 (b), and document it in the CDM-PDD.
In defining the geographical boundary of the
region, project participants should take into account
the source of the waste i.e. if waste is transported
up to 50 km, the region may cover a radius of 50km around the project activity. In addition, it
should also consider the distance to which the final
product after composting will be transported. In
either case, the region should cover a reasonable
radius around the project activity that can be
justified with reference to the project circumstances
but in no case it shall be more than 200 km. Once
defined, the region should not be changed during
the crediting period(s).
The maximum distance for transporting the
waste utilized by the Project Activity is 50
km; therefore the geographical boundary of
the Project Activity is within radius of 50
km around the Project Activity location.
11. In case produced compost is handled aerobically The compost product will be directly applied
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 13
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
and submitted to soil application, the properconditions and procedures (not resulting in methane
emissions) must be ensured.
to plantation; this ensures no methaneemissions occur.
12. In case produced compost is treated
thermally/mechanically, the provisions in AMS-
III.E related to thermal/mechanical treatment shall
be applied.
The produced compost will not be treated
thermally/mechanically.
13. In case produced compost is stored under anaerobic
conditions and/or delivered to a landfill, emissions
from the residual organic content shall to be taken
into account and calculated as per the latest version
of the Tool to determine methane emissionsavoided from disposal of waste at a solid waste
disposal site.
The produced compost will not be stored
under anaerobic condition and/or delivered
to landfill. The produced compost would be
directly applied to plantation by a spreader
machine.
Following table demonstrates the project activity satisfies all eligibility criteria listed in the PoA:
No Eligibility criteria as per PoA DD Section A.4.2.2 Project Description1.
Boundary:
(i)Physical Boundary: The entire boundary of theCPA project activity must be physically located
within the territory of the Republic of Indonesia as
set out in section A.4.1.2 of this PoA-DD.(ii)Time Induced Boundary: No CPA shall commence
before the Start Date of the PoA, as set out in section
B.1. of this PoA-DD. In addition, no CPA shall
commence later than 28 years after the start date of
the PoA-DD as set out in section B.1. of this PoA-
DD.
The CPA No.001 is located in the
territory of the Republic of Indonesia
and has commencement date of 04 July
2011, which was after start date of the
PoA, therefore the CPA No.001 iseligible to be included in the PoA.
2.
Double counting: To avoid double counting of emission
reductions each CPA must: Provide specific geographic
GPS coordinates for the Project Activity to enableunique identification of the Project activity.
The CPA No.001 has geographic GPS
coordinate of 985758.70-
99436.33 E and 31624.46 -32032.54 N, therefore the CPA
No.001 is eligible to be included in the
PoA.
3.Cooperation Agreement: Each CPA owner must enter
into a cooperation agreement with the Coordinating
entity which includes at a minimum the matters set out
in section A.4.4.1(iv), ie that:
i. The CPA Owner is aware and voluntarily agrees
The cooperation agreement has been
made between CPA owner and
coordinating entity and the agreement
considers following items:
i. The CPA Owner is aware and
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 14
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
that the CPA will be subscribed to the present PoAunder the conditions as required by the approved
PoA and the contractual arrangement between the
CPA Owner and the Coordinating Entity.ii. Certifies the CPA has not been and will not be
registered as a single CDM project activity nor as a
CPA under another PoA, nor any voluntary scheme
and warrants on an ongoing basis that they will not
seek to have the project activity which forms the
basis of the proposed CPA registered as a CDM
project or registered under any other scheme that
earns carbon credits for the emission reductions
achieved while the project is included in a CPA or
proposed CPA under the present PoA.iii. The CPA Owner will certify in writing that the
proposed CPA is not a debundled part of a bigger
project.
iv. CPA Owner cedes all rights to independently claimand own emission reductions under the Clean
Development Mechanism of the UNFCCC or any
voluntary scheme other than through the managing
entity of the present PoA as agreed.
voluntarily agrees that the CPAwill be subscribed to the present
PoA under the conditions as
required by the approved PoA
and the contractual arrangement
between the CPA Owner and the
Coordinating Entity.ii. Certifies the CPA has not been
and will not be registered as a
single CDM project activity nor
as a CPA under another PoA, nor
any voluntary scheme and
warrants on an ongoing basis that
they will not seek to have the
project activity which forms the
basis of the proposed CPA
registered as a CDM project or
registered under any other
scheme that earns carbon credits
for the emission reductions
achieved while the project is
included in a CPA or proposed
CPA under the present PoA.
iii. The CPA Owner certifies that theproposed CPA is not a debundled
part of a bigger project.
iv. CPA Owner cedes all rights to
independently claim and own
emission reductions under the
Clean Development Mechanism
of the UNFCCC or any voluntary
scheme other than through the
managing entity of the present
PoA as agreed.
Therefore the CPA No.001 is eligible to
be included in the PoA.
4.
No Pre-existing Co-composting or Composting at
Site: Each CPA shall be implemented at a Palm Oil Mill
site where no composting or co-composting activity was
taking place before the Project Activity.
The CPA No.001 implements a co-
composting activity where there was no
existing co-composting at site the site
prior to the Project Activity, therefore
the CPA No.001 is eligible to be
included in the PoA.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 15
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
5.Technology and compliance with Methodology: Each
CPA must be a newly developed, co- composting or
composting facility using composting technology that
(i)Uses Palm Oil Mill Organic waste as inputs andvia an aerobic composting process within the
parameters set out in section A.4.2.1 of the PoA-
DD produces organic compost for reapplication
to land as organic fertilizer
(ii)Meets the requirements of approvedmethodology AMS-III.F version 10, including
applicability criteria, its relevant assessment tools
and guidelines,
(iii)In addition in order ensure the environmental
integrity of each co-composting facility that is
brought under this PoA and to ensure that the co-
composting facility does not become a source of
environmental pollution itself, each facility must:
i. Locate the main composting facility upon
an impermeable composting pad / floor of
concrete or some other impermeable
material (This ensures leaching from the
compost does not take place directly into
the soil below and improves thecomposting process);
ii. Incorporates a system / process toadequately deal with any run-off or
leachate from the compost itself and / or
ensure any liquid discharge would be
diluted or treated to environmentally
acceptable levels before entering the
surrounding environment.
The CPA is a newly developed co-
composting facility that:
(i) Uses Palm Oil Mill Organicwaste as inputs and via an
aerobic composting process
within the parameters set out in
section A.4.2.1 of the PoA-DD
produces organic compost for
reapplication to land as organic
fertilizer
(ii) Meets the requirements ofapproved methodology AMS-
III.F version 10, including
applicability criteria, its relevant
assessment tools and guidelines,
(iii) In addition:
i. The composting facility islocated on a floor of
concrete (This ensures
leaching from the compost
does not take place
directly into the soil below
and improves thecomposting process);
ii. Incorporates a system /process to adequately deal
with any run-off or
leachate from the compost
itself and / or ensure any
liquid discharge would be
diluted or treated to
environmentally
acceptable levels before
entering the surroundingenvironment.
Therefore the CPA No.001 is eligible to
be included in the PoA.
6.
Start date: Each CPA Owner must be able to provide
documentary evidence to verify the start date of the
CPA.
The first contract document with
manufacturer has been provided as
evidence to verify the start date of the
CPA No.001.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 16
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
7.Additionality: Each CPA must be able to demonstrate
that the Project Activity which forms the CPA would
not have occurred anyway due to an investment barrier
by following and applying all steps of the additionally
assessment as set out in sections E.5.1 and E.5.2 of this
PoA-DD.
The CPA No.001 has undertaken an
additionality test in accordance with
section E.5.1 and E.5.2 of the PoA-DD.
The results of the additionality test
demonstrate that the Project Activity
which forms the CPA would not have
occurred anyway due to an investment
barrier therefore the CPA No.001 is
eligible to be included in the PoA.
8.
PoA Specific Requirements:
(i) Environmental Impact Analysis (EIA):
Each CPA which involves the implementation
of a Compost Facility with a compost output
capacity
i. Greater than or equal to 100tons per day shall provide a
copy of their EIA which has
been submitted to, and
approved by the Indonesian
Ministry of the Environment.ii. less than 100 tons per day,
shall provide a copy of the
Environmental Management
and Monitoring Plan
(EMMP) that was submitted
and approved by the
responsible Indonesian
authorities.
(ii) Compliance with Relevant National
Standards: Each CPA Project Activity must
comply with the relevant Indonesian Nationalor Regional Environmental Standard (i.e.
licenses and or permits that might be required
other than EIA and EMMP).
(iii) Stakeholder Consultation: Each CPA mustbe able to demonstrate with appropriate
documentary evidence that Stakeholder
Consultation has been undertaken in
accordance with the requirements of CDM
rules and procedures.
(i). The CPA No.001 has capacityless than 100 tons per day and
therefore EMMP that was
submitted and approved by the
responsible Indonesian
authorities has been provided.
(ii). The CPA No.001 has EMMPthat complies with relevant
national standard.
(iii). The CPA No.001 has conducteda stakeholder consultation
which was in accordance with
the requirement of CDM rulesand procedures.
Therefore the CPA No.001 is eligible to
be included in the PoA.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 17
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
9.Debundling: To ensure A CPA is not a debundled
component of a large scale activity, the Project Activity
under each CPA must not:
(i) have the same activity implementer as theproposed small scale CPA or a coordinating
or managing entity, which also manages a
large scale PoA of the same
technology/measure which is within 1 km
of the boundary of the proposed small-scale
CPA, at the closest point.
The CPA No.001 is not a debundled
component of a large scale activity and
has no the same activity implementer as
the proposed small scale CPA or a
coordinating or managing entity, which
also manages a large scale PoA of the
same technology/measure which is
within 1 km of the boundary of the
proposed small-scale CPA, at the
closest point, therefore the CPA No.001
is eligible to be included in the PoA.
10.SSC Threshold Criteria: Each CPA shall not reduce
more than 60 kt CO2e annually.Project activity will reduce
approximately emissions of 10,130 tons
CO2 per year. This is well below the
maximum of 60,000 tCO2 per annum,
Therefore the CPA No.001 is eligible to
be included in the PoA.
11.
Use of Development or Assistance Funds: Each CPA
must certify in writing whether any Development Aid orAssistance funds have been used for funding the
construction and operation of the Project Activity which
forms the PoA. If any Development Aid or Assistance
funds have been used, then before inclusion in the PoA,
the CPA owner must provide evidence to confirm that
such funds do not result in a diversion of any official
development assistance funds.
A Formal letter from the Responsible
Entity for the CPA001 has beenprovided certifying that no
Development Aid or Assistance funds
have been used for funding the
construction and operation of the
Project Activity which forms the CPA-
00 and therefore the CPA No.001 is
eligible to be included in the PoA.
B.3. Assessment and demonstration of additionality of the small-scale CPA , as per eligibilitycriteria listed in the Registered PoA:
>>
With awareness of the importance of CDM incentive to the project activity, Socfin Indonesias
management decided to proceed with the project after having input from CDM consultant concerning the
quantity of the emission reduction from the project.
Below table shows the CDM consideration steps for the project activity.
Date Event Source of document
9 April 2010 CDM Consulting Agreement between Agreement document
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 18
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Date Event Source of documentCDM consultant and PT.Socfin Indonesia
27 April 2010 Feasibility Study Report (FSR) FSR document
28 April 2010 Board Meeting of PT.Socfin Indonesia
(taken as decision date)
Signed Board Minute
27 September 2010 Stakeholder Consultation Meeting (SCM) SCM document
10 August 2010 Filling and sending Prior Consideration
Form for Co-Composting Project at
Bangun Bandar, Aek Loba, Tanah
Gambus and Lae Butar.
Form officially received and loaded ontoCDM Website 20 September 2010.
Filled Prior
Consideration of the
CDM form and formal
receipt from UNFCCC
11 October 2010 Prior consideration of the CDM form and
notification of DNA were sent to the
Indonesian DNA. Formal receipt of letter
from Indonesian DNA issued on 12
October 2010
Letter of intent to
commence CDM from
Socfindo and formal
receipt from
Indonesian DNA.
03 December 2010 Request of quotation to TUV Sud Email document
26 January 2010 Request of quotation to ERM Email document
14 February 2010 Request of quotation to TUV Nord Email document
08 June 2010 Contract for Validation Services signed
with DNV
Agreement document
01 July 2011 Start date of GSP period http://cdm.unfccc.int/P
rogrammeOfActivities
/Validation/DB/2MJW
8CICWDNRL1F72D
M11M3M8A6Q8M/vi
ew.html
04 July 2011 Start date of project activity Contract document
In accordance with key criteria and data for assessing additionality of a SSC-CPA listed in the PoA
section E.5.2, following information are the main economic parameters or indicators to be applied in the
projects financial analysis.
Project Data Data and Unit Source
Technical lifetime 20 years Technical provider information which is included in the
feasibility study report on page 8.
Investment Decision Date 28 April 2010 Board minutes of meeting
Date project starts operating 8 March 2012 Letter from Technology Provider
Annual compost production
t/year
30,000 tons/year Information from technology provider.
Estimated Fertilizer savings (If 2,256.36 million Feasibility study. As specific information was available
http://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.htmlhttp://cdm.unfccc.int/ProgrammeOfActivities/Validation/DB/2MJW8CICWDNRL1F72DM11M3M8A6Q8M/view.html -
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 19
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
compost reapplied to plantationbelong to the same company as
the mill and not purchased)
IDR from externally published sources in relation to thepercentage of fertilizer savings that would be able to be
achieved using that compost technology in that region,
Option A: specific fertilizer savings template was
used to calculate the estimated fertiliser savings.Currency 1 USD = 9,013 IDR
1 Euro = 12,049 IDR
Bank Indonesia currency rate calculator (middle rate dated
27 April 2010)
Capital and Equipment costs
(Note this will be broke down
appropriately into
subcomponents)
14,281 million IDR Feasibility study, quotation from technology supplier
CER revenue 3,510.25 million
IDR
Feasibility study (average per year)
Operation & Maintenance
cost: Comprises the following
major sub-components set out
below
1,864.68 million
IDR
Feasibility study report, board estimation, and technology
provider information
Fuel and Electricity Costs
(includes any fuel and power
costs directly related to the
Project Activity)
410.26 million IDR Government price index.
Labour Costs(includes
additional labour costs
directly as a result of theProject Activity)
420.80 million IDR Internal company estimation based on current labour rates.
Maintenance costs
(includes any electrical,
mechanic, civil maintenance
and or equipment
maintenance costs directly
related to the Project
Activity)
1,033.62 million IDR Technology provider information.
Land Rental Costs
(includes any rental costs for
land directly used for Project
Activity)
IDR n/a
Feedstock Costs
(Includes any costs for any
raw material feedstock inputs
into the Compost Facility)
IDR n/a
Ongoing licensing / royalty
costs(includes any ongoing
royalty or licensing costs
required to be paid by the
CPA owner directly in
relation to the Project
Activity)
IDR n/a
Insurance. % of CAPEX or IDR n/a
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 20
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Project IRR (without CER
revenue)
-5.14 % Feasibility study report, financial analysis
Project IRR (including CER
revenue)
21.96 % Feasibility study report, financial analysis
Benchmark determination
As per PoA section E.5.2, the benchmark adopted for financial indicators is 12.5%.
Sensitivity analysis
As specified in the excel spreadsheet supplied to the DOE, a sensitivity analysis will be also conductedusing assumptions that are conservative from the point of view of analyzing additionality, i.e.
the bestcase conditions for the project IRR were assumed by altering the following parameters: (1)
project revenues; (2) total investment, and (3) O&M by +/- 10%.
The full result of each sensitivity analysis is listed in the following table:
Table 7: Sensitivity analysis of IRR project without revenue from CDM
FactorVariation
-10% 0% 10%
Project revenue -11.12% -5.14% -1.35%Project investment -4.31% -5.14% -5.87%
O&M Cost -1.93% -5.14% -9.75%
Below are the likelihood scenarios where the IRR would meet the benchmark by adjusting project
revenue, project investment, and O&M cost;
a. The project revenue is increased by 70%: This condition is unlikely since inorganic fertilizercost estimation is based on existing market price and the inflation rate is already taken into
consideration in the calculation of yearly fertilizer incremental cost saving. This makes the current
cost saving calculation based on the most conservative approaches possible.
b. The project investment is reduced by 80%: This condition is unlikely since project costestimation is based on quotations from the technology provider and the actual expenses will not be
much different from the quotation.
c. The O&M costs are reduced by 85%: This condition is unlikely since the O&M cost is estimatedbased on existing market fuel price, existing operational man power cost, and technology provider
cost estimation. Furthermore, the maintenance cost of wheel loader, truck, compost spreader
machine and its truck, is not included in the financial analysis calculation. This makes the current
estimated operation and maintenance cost calculated already the most conservative approach
possible.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 21
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Within a reasonable variation of the project revenue, the project investment, and operation andmaintenance cost, the calculated pre-tax project IRR result remains consistently below the benchmark.
Thus the project is financially unfeasible and therefore the project is deemed additional.
The revenue from CER makes the pre-tax project IRR become 21.96%, taking it just above the
benchmark of 12.5%. Therefore it is only the addition of the CER revenue that can lift the Project IRR
from -5.14% to 21.96% to take the Project over the Benchmark of 12.5% and make the Project
financially feasible. Therefore the Project requires CDM to be financial feasible and is clearly
additional.
B.4. Description of the sources and gases included in the project boundary and proof that the
small-scale CPA is located within the geographical boundary of the registered PoA.
>>The project boundary of the project activity is defined in below figure:
Palm Oil Mill
EFB pre-treatment
Fat pit/holding tank
Co-composting
PlantPlantation
EFB dumpsite
Existing anaerobic lagoon
EFB
POME
EFB
POME
Legend :
Project condition
Baseline condition
Project Boundary
The GHG emission sources included in or excluded from the project boundary are as follows:
Source Gas Included? Justification/Explanation
Baseline
Biomass disposed
in an unmanaged
landfill / dumpsite
CO2 No
CO2 emissions from biomass
decomposition at solid waste disposalsites are considered as GHG neutral
CH4 Yes
Methane emission from decomposition
of EFB left in the solid waste disposal
site.
N2O NoExcluded for simplification. This is
conservative.
POME Treatment
in open lagoonsCO2 No
CO2 emissions from anaerobic
digestion of POME are considered as
GHG neutral.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 22
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
CH4 YesMethane emissions from anaerobicdigestion of POME in open air
lagoons.
N2O NoExcluded for simplification. This is
conservative.
ProjectActivity
CompostingProcess
CO2 No
CO2 emissions from composting
process are considered as GHG
neutral. Expected to be minimum and
excluded for simplification
CH4 No
The project activity involves the
forced aerated system, online oxygen
monitoring system, online temperaturemonitoring system, and online
methane monitoring system. This
means overall co-composting process
will be maintained in aerobic
condition.
N2O No
Excluded for simplification. This
emission source is assumed to be very
small.
Emission fromrunoff water from
the composting
yard
CO2 No
Excluded for simplification. This
emission source is assumed to be very
small.
CH4 No
The project activity involves the
roofed bunker system. The roof will
cover the co-composting from the rain.
N2O No
Excluded for simplification. This
emission source is assumed to be very
small.
Electricity
CO2 No
The mill facility is equipped with two
biomass steam turbines power
generation. The emission occurred due
to biomass will be considered as
neutral carbon.
CH4 NoExcluded for simplification. Thisemission source is assumed to be very
small.
N2O No
Excluded for simplification. This
emission source is assumed to be very
small.
Incremental use of
fossil fuels for
transportation,
auxiliary
equipment due to
CO2 Yes
The project activity will utilize a
spreader machine to re-apply the final
compost product to the plantation. The
spreader machine will use fossil fuel
(diesel oil) in the daily operation.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
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NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 23
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
projectCH4 No
Excluded for simplification. Thisemission source is assumed to be very
small.
N2O No
Excluded for simplification. This
emission source is assumed to be very
small.
B.5. Emission reductions:
B.5.1. Data and parameters that are available at validation:
>>Data / Parameter:
Data unit: -
Description: Model correction factor to account for model uncertainties
Source of data used: -
Value applied: 0.9
Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
In accordance with the Tool to determine methane emissions avoided from
disposal of waste at a solid waste disposal site version 05.1
Any comment: Oonk et el. (1994) have validated several landfill gas models based on 17
realized landfill gas projects. The mean relative error of multi-phase models
was assessed to be 18%. Given the uncertainties associated with the model and
in order to estimate emission reductions in a conservative manner, a discount of
10% is applied to the model results.
Data / Parameter: OX
Data unit: -
Description: Oxidation factor (reflecting the amount of methane from SWDS that is
oxidized in the soil or other material covering the waste)
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories, Volume 5,
chapter 3.Value applied: 0
Justification of the
choice of data or
description of
measurement methods
and procedures actually
applied :
The shredded EFB is directly dumped in the plantation and therefore
categorized as unmanaged and uncategorized SWDS
Any comment: -
Data / Parameter: F
-
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 24
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Data unit: -Description: Fraction of methane in the SWDS gas (volume fraction)
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories
Value applied: 0.5
Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
In accordance with the Tool to determine methane emissions avoided from
disposal of waste at a solid waste disposal site version 05.1
Any comment: This factor reflects the fact that some degradable organic carbon does not
degrade, or degrades very slowly, under anaerobic conditions in the SWDS. Adefault value of 0.5 is recommended by IPCC
Data / Parameter: DOCf
Data unit: -
Description: Fraction of degradable organic carbon (DOC) that can decompose
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories
Value applied: 0.5
Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
In accordance with the Tool to determine methane emissions avoided from
disposal of waste at a solid waste disposal site version 05.1
Any comment: -
Data / Parameter: MCF
Data unit: -
Description: Methane correction factor
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories
Value applied: 0
Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
None of solid waste disposal site meets the requirement of solid waste disposal
site categorised in the Tool to determine methane emissions avoided from
disposal of waste at a solid waste disposal site version 05.1 found by DOE
during site visit, therefore the MCF is considered as 0.
Any comment: The methane correction factor (MCF) accounts for the fact that unmanaged
SWDS produce less methane from a given amount of waste than managed
SWDS, because a larger fraction of waste decomposes aerobically in the top
layers of unmanaged SWDS
Data / Parameter: DOCj
Data unit: -
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 25
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Description: Fraction of degradable organic carbon (by weight) in the waste typejSource of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories (adapted from
Volume 5, Tables 2.4 and 2.5)
Value applied: 20%
Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
As perthe Tool to determine methane emissions avoided from disposal of
waste at a solid waste disposal site version 05.1, In the case of empty fruit
bunches (EFB), as their characteristics are similar to garden waste, the
parameter value correspondent of garden shall be used.
Any comment: -
Data / Parameter: kj
Data unit: -
Description: Decay rate for the waste typej
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories (adapted from
Volume 5, Table 3.3)
Value applied: 0.17
Justification of the
choice of data or
description of
measurement methods
and proceduresactually applied :
As perTool to determine methane emissions avoided from disposal of waste at
a solid waste disposal site version 05.1, In the case of empty fruit bunches
(EFB), as their characteristics are similar to garden waste, the parameter values
correspondent of garden waste shall be used.
Tropical (MAT > 20oC)Wet climate (MAP > 1000 mm)
Any comment:
Data / Parameter: COD,BL,iData unit: -
Description: COD removal efficiency of the baseline treatment system i
Source of data used: Calculation, based on COD historical data of wastewater entering and leaving
the baseline wastewater treatment system.
Value applied: 99.4%
Justification of the
choice of data ordescription of
measurement methods
and procedures
actually applied :
Parameter is used to determine the COD removal of the wastewater treatment in
the baseline scenario
Any comment: The wastewater leaving the baseline of wastewater treatment system refers to
the wastewater discharged to the river
Data / Parameter: NCVdiesel oil
Data unit: TJ/Gg
Description: Net Calorific Value of Diesel Oil
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 26
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Source of data used: IPCC 2006 Guidelines for National Greenhouse Gas InventoriesValue applied: 43.3Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
Value is obtained from default value of the IPCC 2006, volume 2: Energy
(Table 1.2)
Any comment: -
Data / Parameter: EFCO2, diesel oil
Data unit: kg/TJDescription: CO2 emission factor of Diesel OilSource of data used: IPCC 2006 Guidelines for National Greenhouse Gas Inventories
Value applied: 74,800Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
Value is obtained from default value of the IPCC 2006, volume 2: Energy
(Table 1.3)
Any comment: -
Data / Parameter: Densitydiesel oil
Data unit: kg/litre
Description: Density of Diesel OilSource of data used: http://www.pertamina.com/index.php/detail/read/minyak-diesel
Value applied: 0.840Justification of the
choice of data or
description of
measurement methods
and procedures
actually applied :
Value is obtained from PERTAMINA (diesel oil main supplier).
Any comment: -
B.5.2. Ex-ante calculation of emission reductions:
>>
A. Baseline Emission
Following equation is to determine baseline emission according to AMS-III.F version 10:
4,,,4,,,4 _CHGWPMDBEBEBEBE regyymanureCHywwySWDSCH
http://www.pertamina.com/index.php/detail/read/minyak-dieselhttp://www.pertamina.com/index.php/detail/read/minyak-dieselhttp://www.pertamina.com/index.php/detail/read/minyak-diesel -
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 27
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
Where:BECH4,SWDS,y Yearly methane generation of potential solid waste composted by the project
activity during the years x from the beginning of the project activity (x=1) up to
the year y estimated as per the latest version of the Tool to determine methane
emissions avoided from disposal of waste at a solid waste disposal site (tCO 2e).
The tool may be used with the factor f=0.0 assuming that no biogas is captured
and flared. With the definition of year x as the year since the project activity
started diverting wastes from landfill disposal, x runs from the first year of
crediting period (x=1) to the year for which emissions are calculated (x=y)
MDy,reg Amount of methane that would have to be captured and combusted in the year y
to comply with the prevailing regulations (ton)
BECH4,manure,y Where applicable, baseline emissions from manure composted by the project
activities, as per the procedures of AMS-III.D
BEww,y Where applicable, baseline emissions from the wastewater co-composted,
calculated as per the procedures in AMS-III.H
GWP_CH4 GWP for CH4 (value of 21 is used)
Baseline emission due to methane generation potential of the solid waste composted:
jjkxyk
jxj
y
x
fCHySWDSCH eeDOCWMCFDOCFOXGWPfBE 112
1611 ,
1
4,,4
Where:
BECH4,SWDS,y Methane emissions avoided due to prevention of waste disposal at the solid waste
disposal site (SWDS) during the year y, from the start of project activity to the end
(tCO2e)
Model correction factor to account for model uncertainties (0.9)
f Fraction of methane captured at the SWDS and flared, combusted or used in another
manner (0 )
GWPCH4 Global Warming Potential (GWP) of methane (21)
OX Oxidation factor (reflecting the amount of methane on SWDS that is oxidised in the soil
or other material cover the waste) (0)
F Fraction of methane in the SWDS gas (volume fraction) (0.5)
DOCf Fraction of degradable organic carbon (DOC) that can decompose (0.5)
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 28
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
MCF Methane correction factor (0)
Wj,x Amount of organic waste type j prevented from disposal to the SWDS in year x
(18,732.61ton)
DOCj Fraction of degradable organic carbon (by weight) in the waste type j (0.2)
kj Decay rate for the waste type j (0.17)
j Waste type category (index)
x Year during the crediting period: x runs from the first year of the first crediting period
(x=1) to the year y for which avoided emission calculated (x=y) (1)
y Year for which methane emission are calculated (1)
Therefore:
17.01117.0
1
11
,,4 12.061.732,1805.05.012
160121019.0 eeBE ySWDSCH
BECH4,SDWS,y = 0.00 tCO2e
As per AMS-III.H version 16, baseline emission from the wastewater co-composted may comprise of
methane emissions from baseline wastewater treatment systems (BEww,treatment,y) and methane emissions onaccount of inefficiencies in the baseline wastewater treatment systems and the presence of degradable
organic carbon in the treated wastewater discharged into river/lake/sea (BEww,discharge,y).
Baseline emission due to methane emission from baseline wastewater treatment system:
i
CHBLwwoiBLtreatmentwwiBLCODyilowyiwwytreatmentww GWPUFBMCFCODQBE 4,,,,,,,,inf,,,,
Where:
Qww,i,y Volume of wastewater treated in baseline wastewater treatment system i in year y.
For ex ante estimation, forecasted wastewater generation volume or the designed
capacity of the wastewater treatment facility can be used. (47,612.39 m3)
CODinflow,i,y Chemical oxygen demand of the wastewater inflow to the baseline treatment system
i in year y (0.0585 t/m3)
COD,BL,i COD removal efficiency6
of the baseline treatment system i (99.7 %)
MCFww,treatment,BL,i Methane correction7
factor for baseline wastewater treatment systems i (0.8)
6Determined based on paragraph 26,27 or 28 of methodology AMS-III.H version 16
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 29
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
i Index for baseline wastewater treatment system
Bo,ww Methane producing capacity of the wastewater (IPCC value of 0.25 kg CH4/kg
COD)
UFBL Model correction factor to account for model uncertainties (0.89)
GWPCH4 Global Warming Potential for methane (value of 21)
Therefore:
2189.025.08.0997.00.058547,612.39,,
ytreatmentwwBE BEww,treatment,y = 10,378.58 tCO2e
Baseline emission due to methane emissions on account of inefficiencies in the baseline wastewater
treatment systems and presence of degradable organic carbon in the treated wastewater
discharged into river/lake/sea:
yedischwwyBLedischwwblwoCHywwyedischww MCFCODUFBGWPQBE ,arg,,,arg,,4,,arg,
Where:
Qww,y Volume of treated wastewater discharged in year y (47,612.39 m3)
UFBL Model correction factor to account for model uncertainties (0.89)
CODww,discharge,BL,y Chemical oxygen demand of the treated wastewater discharged into sea, river or
lake in the baseline situation in the year y (0.0002 t/m3).
MCFww,BL,discharge,y Methane correction factor based on discharge pathway in the baseline situation8(river) of the wastewater (0.1)
Therefore:
1.00002.089.025.02147,612.39,arg, yedischwwBE
BEww,discharge,y = 4.38 tCO2e
B. Project Emission
Project emissions that might occur due to the co-composting process is listed as following:
a. CO2 emissions due to incremental transportation distances;b. CO2 emissions from electricity and/or fossil fuel consumption by the project activity facilities;
7MCF values as per Table III.H.1 in the methodology AMS-III.F version 16
8MCF values as per Table III.H.1 in the methodology AMS-III.H version 16
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 30
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
c. Methane emissions during composting process;d. Methane emissions from runoff water;e. In case the compost is stored under anaerobic conditions and/or delivered to a landfill: the methane
emissions from the disposal/storage of compost.
Thus, total project emission from co-composting process is summarized using equation below:
reswasteyrunoffycompypowerytranspyy PEPEPEPEPEPE ,,,,,
Where:
PEy Project activity emissions in the year y (tCO2e)
PEy,transp Emissions from incremental transportation in the year y (tCO2e)
PEy,power Emissions from electricity or fossil fuel consumption in the year y (tCO2e)
PEy,comp Methane emissions during composting process in the year y (tCO2e)
PEy,runoff Methane emissions from runoff water in the year y (tCO2e)
PEy,reswaste In case the compost produced is subjected to anaerobic storage or disposed in a landfill:
methane emissions from the anaerobic decay of the residual organic content (tCO2e)
Project emission from incremental transportation:
The co-composting facility is located in the boundary of the project activity; this means no incremental
transportation distance for both POME and EFB, therefore project emissions due to transportation of
EFB and POME to the co-composting facility is considered as zero. This means Qy, CTy,DAFw,
DAFtreatment are not necessarily deemed to be monitored. However, the Qy,treatment is to be monitored by
PT.Socfin Indonesia for internal data purpose.
In the case of final compost product handling, the Project Activity involves truck and spreader tractor,
which are using diesel oil as the fuel in the operation. For that the project emission for final compost
product handling of the project activity is calculated based on Tool to calculate project or leakage CO2
emissions from fossil fuel combustion (EB 41 annex 11).
Following equation is to determine the project emission from transportation:
2,.2, // COtreatmenttreatmentytreatmentyCOwyytranspy EFDAFCTQEFDAFCTQPE
Where:
Qy Quantity of raw waste/manure treated and/or wastewater co-treated in the year y
(18,732.61ton)
CTy Average truck capacity for transportation (6 ton/truck)
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 31
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
DAFw Average incremental distance for raw solid waste/manure and/or wastewater
transportation (0 km/truck)
EFCO2 CO2 emission factor from fuel use due to transportation (kgCO2/km, IPCC default values
or local values may be used)
Qy,treatment Quantity of compost produced in year y (28,098.91 ton)
CTy,treatment Average truck capacity for compost transportation (6 ton/truck)
DAFtreatment Average distance for compost transportation (0 km/truck)
Therefore:
22, 06/91.098,2806/18,732.61 COCOtranspy EFEFPE PEy,transp = 0
Project emission due to fossil fuel combustion for final compost transportation:
The project emission due to fossil fuel (diesel oil) combustion is calculated based on estimation of fossil
fuel consumption of the spreader machine. The estimation9of diesel oil consumption is approximately
76,582.36 kg per year. The actual emission during monitoring period will be calculated based on actual
fossil fuel consumption.
The project emission from fossil fuel combustion is calculated as following10
:
dieseloilCOdieseloilydieseloilyFC EFNVCFCPE ,2,,
Where:
FCdiesel oil,y Fossil fuel (diesel oil) consumption in year y (kg) (76,582.36 )
NCVdieseloil Net calorific value of diesel oil (TJ/Gg) (43.3)
EFCO2,dieseloil CO2 emission factor of diesel oil (kg/TJ) (74,800)
Therefore:9
, 10800,743.4336.582,76
yFCPE PEFC,y = 248.04 tCO2e
Project emissions from electricity or fossil fuel consumption:
The Mill Facility is equipped with two biomass steam turbines power generation which have capacity of
500 kW and 520 kW, and therefore the emission from the electricity generation is considered as carbon
9The estimation is taken from specific fuel consumption of Mitsubishi Diesel Engine (Feasibility Study Report)
10Project emission from fossil fuel combustion is based on Tool to calculate project or leakage CO2 emissions from
fossil fuel combustion version 2. Option B is used due to uncertainty of availability data of tC/mass unit of the fuel.
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 32
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
neutral. In the normal condition, the mill facility requires approximately 500 kW for the overalloperational system. Therefore, the mill facility still has power excess of 520 kW, of which 250 kW will
be utilized by co-composting plant.
Project emissions due to methane emission during composting activity:
As per methodology AMS-III.F version 10, EFcomposting can be set to zero for the portions ofQy if the
monitored oxygen content of the composting process in all points within the windrow are above 8%. This
can be done via sampling with maximum margin of error of 10% at a 90% confidence level. For this
purpose, a portable oxygen meter can be used with lancets of at least 1 m length. In the case of forced
aerated in-vessel and forced aerated pile composting systems, continuous measurements may also be
done using online sensor(s). Since the Project Activity involves the forced aerated bunker system, which
comprise of oxygen and temperature continuous online monitoring system (prescribed in section A.4.1),
the project emission from co-composting process is considered as zero.
Project emissions from runoff water from the composting yard:
The Project Activity is using the roofed Aerated Bunker Co-composting System or ABC System. The
roof will cover the bunker from the rain; therefore the runoff water from the rain will not occur
(Qy,ww,runoff and CODy,ww,runoffare not necessarily monitored). Furthermore, the ABC system will re-apply
or re-circulate the un-utilized POME in the co-composting process through a circulator POME pump, and
therefore the emission due to runoff water is considered as zero.
Project emission due to methane emissions from anaerobic storage and/or disposal in a landfill:
The final compost product will be directly spread in the plantation and will not be stored in anaerobic
storage and/or dispose in a landfill; therefore the project emission from anaerobic storage and/or disposal
in a landfill is considered as zero.
C. Leakage Emission
Project technology implemented is brand new and not transferred from another facility, hence the leakage
emission is considered as zero.
D. Emission Reduction
The emission reduction achieved by the project activity will be measured as the difference between the
baseline emission and the sum of the project emission and leakage, described as following equation:
)( yyyy LEPEBEER
Where:
ERy Emission reduction in the year y (tCO2e)
BEy Baseline emission in the year y (tCO2e) (10,378)
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SMALL-SCALE CDM PROGRAMME ACTIVITY DESIGN DOCUMENT FORM
(CDM-SSC-CPA-DD) - Version 01
NAME /TITLE OF THE PoA: Co-composting and Composting Program of Activitie
for Palm Oil Mills in Indonesia
CDM Executive Board page 33
This template shall not be altered. It shall be completed without modifying/adding headings or logo, format or font.
PEy Project emission in the year y (tCO2e) (248)
LEy Leakage emissions in year y (tCO2e) (0)