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Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
Version 2.0 Project Plan Template – July 2018
Offset Project Plan
Verdant Energy Ltd - DAPP Power Electric Generation Facility
Project Developer:
Fortistar Biomass
Prepared by:
Cap-Op Energy
Date:
October 4, 2018
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
Page 2 of 36
Version 2.0 Project Plan Form – July 2018
Table of Contents
1.0 Contact Information .............................................................................................. 3 2.0 Project Scope and Site Description .......................................................................... 3
2.1 Project Description ................................................................................................ 6 2.2 Protocol ............................................................................................................... 6 2.3 Risks ................................................................................................................... 7
3.0 Project Quantification ............................................................................................ 8 3.1 Inventory or Sources and Sinks .............................................................................. 8 3.2 Baseline and Project Condition ................................................................................ 9 3.3 Quantification Plan .............................................................................................. 10 3.4 Monitoring Plan ................................................................................................... 15 3.5 Data Management System.................................................................................... 27
4.0 Project Developer Signature ................................................................................. 31 5.0 References ......................................................................................................... 32 Appendix A: Supporting Information ..................................................................................... 33
List of Tables
Table 1: Project Contact Information ...................................................................................... 3 Table 2: Project Information .................................................................................................. 3 Figure 1: Dapp Generating Facility Plant Layout ....................................................................... 5 Table 3: List of Sources and Sinks Included in the Project Quantification ..................................... 8 Table 5: Meter Maintenance & Calibration.............................................................................. 28 Figure 2: Diesel Fuel Consumption Data Management ............................................................. 33 Figure 3: Gasoline Consumption Data Management ................................................................ 34 Figure 4: Electricity Production and Consumption Data Management......................................... 34 Figure 5: Natural Gas Consumption Data Management ............................................................ 35 Figure 6: Propane Consumption Data Management ................................................................. 35 Figure 7: Biomass Diversion Data Management ...................................................................... 36
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
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Version 2.0 Project Plan Form – July 2018
1.0 Contact Information
Table 1: Project Contact Information
Project Developer Contact Information Additional Contact Information
Dapp Power L.P. Dapp Power L.P.
Grant Noll, Vice President - Operations Dominick Zimmerman, Plant Manager/Chief
Engineer
201 – 525 11th Avenue SW Box 6, Site 4, RR1
Calgary, AB, T2R 0C9 Westlock, AB, T7P 2N9
(403) – 261 - 9754 (780) 954 - 2089
www.fortistar.com www.fortistar.com
[email protected] [email protected]
Authorized Project Contact (if applicable)
Cap-Op Energy
Cooper Robinson, Managing Director
610 – 600 6 Ave SW
Calgary, AB, T2P 0S5
(403) 457 - 1029
www.capopenergy.com
2.0 Project Scope and Site Description
Table 2: Project Information
Project title Verdant Energy Ltd – Dapp Power Electric Generation Facility
Project purpose and
objectives
Dapp Power LP and its wholly owned subsidiary Biofuels Inc. (the Project)
is an electrical energy from biomass project located northwest of
Westlock, Alberta and wood recycling depot located at a landfill on the
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
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Version 2.0 Project Plan Form – July 2018
west side of Edmonton. The purpose of the project is to generate carbon
offsets from:
• Indirect GHG emission reductions by using biomass to offset non-
renewable electricity production; and
• Creating direct GHG emission reductions by avoiding methane
emissions from the decomposition of biomass in landfills.
Emission reductions from this project are generated under the
Quantification Protocol for Energy Generation from the Combustion of
Biomass Waste, Version 2.2, June 2018 and therefore meet the
requirements of the Alberta Offset System.
Activity start date September 2005
Offset crediting
period
January 1, 2006 to December 31, 2013; with a five-year extension from
January 1, 2014 to December 31, 2018
Estimated emission
reductions/
sequestration
100,000 to 150,000 tonnes CO2e/year.
Over the thirteen years of the project thus far, approximately 2.5 M
tonnes of CO2e have been be reduced.
Unique site identifier Dapp Generation Facility is located north of the town of Westlock, AB. The
legal description of the site is SW1/4 Section 1, Township 63, Range 2,
W5. The corresponding latitude and longitude is:
54.415042, -114.176788
The wood recycling depot is located on the Northland Sand and Gravel
Landfill in Edmonton at 231st St and Highway 16A in Parkland County.
The corresponding latitude and longitude is:
53.546444, -113.718401
Is the project located
in Alberta?
Yes
Project boundary The project boundary includes energy generation at the Dapp generating
facility and the waste biomass processing facility owned by Bio-Fuels Inc.
The specific physical boundaries are the facility boundaries located at the
areas identified above. A map of the Dapp generating facility plant layout
is included in Figure 1.
Waste wood biomass is received at Biofuels’ site and processed before
being shipped to the Dapp Generating Facility. Biofuels Inc. also sources
processed wood waste from other landfills or waste transfer stations,
which is transported directly to Dapp Power. This reduces handling and
transportation costs for the waste owner.
Ownership The Project is registered and operated under the name of Dapp Power
Limited Partnership (LP). It is owned and operated by Verdant Energy
Ltd, an Alberta based enterprise under the FORTISTAR Biomass Group of
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
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Version 2.0 Project Plan Form – July 2018
White Plans, New York. Only Dapp and it’s holding companies have
entitlement to the benefits associated with the emission offsets, and the
right to sell the credits.
Figure 1: Dapp Generating Facility Plant Layout
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
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Version 2.0 Project Plan Form – July 2018
2.1 Project Description
The project generates carbon-offset credits in two ways:
1. Using biomass to offset non-renewable electricity production (indirect GHG reductions);
and,
2. Diverting biomass waste away from landfills (direct GHG emission reductions).
If Verdant Energy did not initiate this electrical generation project, the waste biomass would
have been sent to landfill and decomposed anaerobically to form methane emissions. Other
biomass would be sent to beehive or olivine burners where combustion emissions were emitted
with no heat or electricity recovered, stockpiled, or disposed of by other unknown or
undocumented means. For the purposes of the flexibility mechanism applied, only feedstock with
documented disposal for landfill will generated avoided landfill emission credits. There was no
baseline activity at the Dapp Generating Facility prior to the project start date.
Biomass arrives at Dapp in one of two ways:
• Direct transportation to Dapp Generating Facility; or,
• Transportation to Bio-Fuels Inc. wood recycling depot, where it is processed and then
transported approximately 135 km to the Generating Facility
Biomass that is directly transported is weighed at the Ancoma truck scale and then received at
its wood receiving system. Wood waste is processed to proper size through a ‘hog’ located at the
plant site. A front loader moves the biomass either into open-air storage or to a fuel reclaim
system that carries it by conveyor to the power plant. Once in the plant, biomass is fed into a
steam power boiler that generated steam to turn a steam turbine coupled to an electric
generator. Steam exhaust is cooled and returned to the boiler in a closed loop system.
Biomass received by Bio-Fuels Inc includes construction and demolition waste, shipping pallets
and crates, other industrial/commercial wood waste and tree trimmings. Biomass is processed
through a 500 hp diesel powered wood shredder, with the ability to separate nails and metals.
Mobile equipment is used to load tractor-trailer units with the processed waste, which is shipped
to the Dapp Generating Station using Dapp owned and 3rd-Party owned trucks.
All collected waste biomass is combusted to generate zero-emission electricity for the Alberta
grid, offsetting high-emission-intensity electricity currently supplied to the grid. The project
produces 16.5 MW of electricity using a bubbling fluidized bed gasifier/boiler and steam turbine.
The expected remaining life of the Generating Facility is 10-15 years, with regular maintenance
and equipment upgrades.
2.2 Protocol
This project uses the Protocol for Energy Generation from the Combustion of Biomass Waste,
Version 2.2, June 2018. This project is directly relevant to the protocol because emissions offsets
are produced from the combustion of waste biomass (waste wood products), and from the
avoided methane emissions from diverting woody biomass destined for landfills. In the absence
of this project, woody biomass would end up in landfills and zero-emission electricity would not
be generated from biomass combustion.
This project meets the general eligibility criteria for offset projects within the Alberta Offset
System as outlined in Section 1.2 of the Carbon Competitiveness Incentive Regulation, as well
as the specific requirements for the Protocol, namely:
• The first batch of feedstock was received in 2005, which is after the specified date of January
1, 2002;
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October 2018
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Version 2.0 Project Plan Form – July 2018
• Dapp Power and its wholly owned subsidiary Biofuels Inc. are Alberta based;
• The project offset credits were generated from activities that go beyond business and usual
practices, and the changes in practices were not required by law or regulation;
• Any carbon offset credits generated in this project will be serialized for use in the Alberta
Offset System only and will not be used or counted in any other jurisdiction;
• Reductions achieved by the project are based on actual measurement and monitoring as per
the requirements of the protocol; and
• The project meets the offset system eligibility criteria specified in the CCIR, standards and
guidance documents for the Alberta Offset System, and will be verified according to the CCIR.
The flexibility mechanism applied to this project includes diversion of biomass waste from
landfills. The Dapp generating facility has been diverting waste wood from landfills and generating
credits for methane avoidance for the last 13 years, at which point the original records were
provided to the Climate Change Office. (Section 5.1.2). Flexibility quantification methods were
also applied, including site-specific emission factors and default factors in other locations.
Environment Canada or equivalent emission factors were used for fossil fuel emissions and
biomass fuel combustion. Boiler fuel consumption is calculated based on steam production, fuel
density, moisture content and fuel inventory surveys.
The Protocol has been fully approved and registered under the Alberta Offset System. There are
no deviations that apply to this project.
2.3 Risks
The project faces several risks as part of its operations and business environment, including:
• Fuel Supply Shortfall - Wood biomass supply may be interrupted due to market changes
that impact the economic circumstances of suppliers. In order to help mitigate this risk, the
Project obtains wood biomass from numerous suppliers. Currently, annual biomass supply
exceeds project needs.
• Plant Availability – Physical or technical issues may arise at the plant. This may curtail or
cease production and therefore, would have a direct impact on CO2e offsets created. To
mitigate this risk, the plant has 24-hours/day staff presence as well as industry standard
operating and maintenance practices. The plant is also insured for significant property and
equipment loss.
• Infrastructure Failure – Road or electrical grid access could be lost due to events beyond the
Project’s control. This would be an event of force majeure and could curtail or cease
production; directly impacting the volume of offsets created. As stated above, to mitigate this
risk, the plant has 24-hours/day staff presence as well as industry standard operating and
maintenance practices. The plant is also insured for significant property and equipment loss.
Approximately one to two months of fuel supply are stock piled at the facility to mitigate
against this risk. Fuel piles are consumed first-in-first-out (FIFO).
• Commercial or Market Condtions - Plant operations may be curtailed or ceased due to negative
changes in power markets or other commercial circumstances affecting economic viability.
• Legislative or Regulatory Changes - Changes to regulations, protocols or legislation affecting
recognition of environmental attributes of the project may jeopardize the viability of the
project revenue.
The plant operates under approval by the Alberta Energy Utilities Board and Alberta Environment
Sustainable Resource Development. Therefore the plant must meet certain requirements in order
to continue to be in regulatory compliance.
Verdant Energy Ltd - DAPP Power Electric Generation Facility
October 2018
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Version 2.0 Project Plan Form – July 2018
3.0 Project Quantification
3.1 Inventory or Sources and Sinks
The total list of selected sources and sinks included in this project are included below. Many other
sources and sinks were excluded from the quantification as per guidance from the quantification
protocol.
Table 3: List of Sources and Sinks Included in the Project Quantification
Included
Source or Sink
Justification for
Selection
Tracking
Description
Quantification
Description
B1 & P1:
Collection,
Transfer, and
Transport of
Biomass
Collection and transport
may change in project
condition depending on
type of biomass residues,
and pre-processing
required
Feedstock collection
and transport
documented and any
additional fuels in
project condition
tracked and
measured
Fuel usage directly
metered or measured
and emission factors
applied
B3 & P3:
Processing of
Biomass
Processing variable by
biomass waste type and
conditions, all electricity
or fuel use should be
tracked and applied
Any energy or fuel
used for feedstock
processing
documented, tracked
and measured
Fuel usage and/or
electricity directly
metered or measured
and emission factors
applied
B4 & P4: Fuel
Extraction &
Processing
Baseline emissions are
expected to be higher
than project emissions
Volumes and types of
fuels used tracked
Emission factors for
fuel extraction &
processing applied
B6: Offsite
Electricity
Generation
Displaced
Off-site emissions
displaced through export
of electricity (there was
no heat exported)
Using facility
production data
Directly metered
electricity generation
from facility
operations
B12 & P12:
Facility
Operations
Emissions from electricity
use or other fuels for
facility operations &
equipment
All processes
documented and any
additional fuel or
electricity usage
tracked
Fuel usage and/or
electricity directly
metered or measured
and emission factors
applied
B13: On-site
Electricity
Generation
Displaced in
Project
Emissions that occurred
to generate electricity in
the baseline conditions
which have been
displaced by project
activity (no heat)
Using facility
production data
(projection based)
Directly metered
electricity generation
from facility
operations
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October 2018
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Version 2.0 Project Plan Form – July 2018
Included
Source or Sink
Justification for
Selection
Tracking
Description
Quantification
Description
P15: Combustion
of Biomass or
Fossil Fuels
Emissions (CH4 and N2O)
resulting from the
combustion of biomass
must be quantified,
biogenic CO2 emissions
are excluded
Using facility
production data on
biogenic biomass
processed and
consumed
Biomass measured
based on change in
fuel inventory (by
survey) and scale
records of fuel
receipts. Fossil fuel
consumption is
directly measured by
meter.
B15: Disposal of
Biomass
Disposal of biomass
varies according to type
and source – this was
quantified because the
flexibility mechanism was
applied
Using biogenic
biomass
transportation &
feedstock records
Biomass measured
based on change in
fuel inventory (by
survey) and scale
records of fuel
receipts.
3.2 Baseline and Project Condition
The baseline condition is characterized by the following:
• The production of energy from fossil fuels for electricity; and,
• The disposal of biomass by a means described by a flexibility mechanism in Section 1.3 of
the protocol.
Baseline electricity emissions are quantified using published grid emission factors, while baseline
upstream diversion emissions are quantified based on historical data of biomass waste disposal.
The waste streams include the following suppliers:
Landfill Wood –construction, demolition and commercial/industrial wood waste diverted
from the following landfills or related transfer stations:
o Northland Sand and Gravel Landfill (Biofuels Inc operating site);
o Edmonton Waste Management Centre/Ryley Landfill.
None of the landfills sites listed above currently have landfill gas capture systems in place for
incoming waste streams or active cells. The Edmonton Waste Management Center diverts wood
waste for compost as a first priority and any material sent to Dapp is excess material or unsuitable
for their compost needs.
Forest Products Mill Residuals (previously incinerated)
o Slave Lake Pulp (SLP) – forest trimmings and mill by-product not diverted from
landfill;
o Alberta Plywood Ltd (APL) – forest trimmings and mill by-product not landfill
diverted.
o Blue Ridge Lumber
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o Other surrounding mills on a periodic basis including Vanderwell Contractors, Millar
Western Forest Products, Tolko Industries
The project condition is characterized by the following:
• Transportation and Processing of waste biomass directly received by Dapp Generating Facility;
• Transportation and Processing waste biomass received by Bio Fuels Inc. (diverted from
landfills);
• Transportation of diverted waste biomass from Bio Fuels Inc. to Dapp Generating Facility;
• Electricity generation at Dapp facility from combustion of waste biomass
The project is estimated to result in 150,000 – 225,000 tCO2e that would be avoided from the
atmosphere yearly. These emission reductions are attributed to both the processing of biomass
to generate electricity and methane avoidance from landfill diversion of the eligible wood waste
materials.
The baseline and project conditions are functionally equivalent because electricity produced in
the project condition displaces electricity generated in the baseline scenario, and wood waste
combusted in the project scenario replaces alternative disposal methods employed in the
baseline scenario.
3.3 Quantification Plan
The quantification of the reductions, removals and reversals of relevant SS’s for each of the
greenhouse gases will be completed using the methodologies outlined in Section 4.1.2 and 4.1.3
of the Protocol. The methodologies serve to complete the following equations for calculating
emission reductions:
Eligible Emission Reductions = Emissions Non-Levied Baseline – Emissions Non-Levied Project
Emissions Non-Levied Baseline = (B4) Emissions Fuel Extraction and Processing + (B6) Emissions Off-Site
Electricity + (B13) Emissions On-site Electricity + (B15) Emissions Disposal of
Biomass + (B12) Emissions Facility Operation + (B3) Emissions Processing of
Biomass
Emissions Non-Levied Project = (P4) Emissions Fuel Extraction and Processing + (P15) Emissions Combustion
of Biomass + (P12) Emissions Facility Operations + (P3) Emissions Processing
of Biomass
Levied Emission Reductions = Emissions Levied Baseline – Emissions Levied Project
Emissions Levied Baseline = (B1) Emissions Collection, Transfer, Transport + (B3) Emissions Processing of
Biomass + (B12) Emissions Facility Operations + (B16) Emissions Off-Site Heat
+ (B18) Emissions On-Site Heat
Emissions Levied Project = (P1) Emissions Collection, Transfer, Transport + (P3) Emissions Biomass
Processing + (P12) Emissions Facility Operations + (P15) Emissions Combustion
of Biomass & Fossil Fuels
Where:
Emissions Baseline = Sum of included emissions under the baseline condition
Emissions Collection, Transfer, Transport = Emissions under SS B1 Collection, Transfer and Transport of
Biomass
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Version 2.0 Project Plan Form – July 2018
Emissions Biomass Processing = Emissions under SS B3 Processing of Biomass
Emissions Fuel Extraction / Processing = Emissions under SS B4 Fuel Extraction / Processing
Emissions Electricity = Emissions under SS B6 Offsite Electricity Generation
Displaced in Project and SS B13 Onsite Electricity Generation –
(there is no applicable heat generation that is relevant to this
project)
Emissions Facility Operations = Emissions under SS B12 Facility Operations
Emissions Biomass Disposal = Emissions under SS B15 Disposal of Biomass
Emissions Project = Sum of included emissions under the project condition
Emissions Collection, Transfer, Transport = Emissions under SS P1 Collection, Transfer and Transport of
Biomass
Emissions Biomass Processing = Emissions under SS P3 Processing of Biomass
Emissions Fuel Extraction / Processing = Emissions under SS P4 Fuel Extraction / Processing
Emissions Facility Operations = Emissions under SS P12 Facility Operations
Emissions Combustion of Biomass = Emissions under SS P15 Combustion of Biomass and Fossil
Fuels
As per the protocol, emissions from levied fuels are quantified and reported where there is a
difference in the project and baseline emissions. The following list includes the parameters that will
be measured and those that will be estimated:
Source or
Sink
Procedure Description Justification
B1 & P1 Measured Volume of fuel used for
biomass collection & transport
Direct measurement of combusted
fuel – highest frequency possible
B1 & P1 Estimated Emission factors for fuel
combustion
Reference values adjusted as
needed by ECCC
B3 & P3 Measured Volume of fuel used for
biomass processing
Direct measurement of combusted
fuel – highest frequency possible
B3 & P3 Measured Volume of electricity consumed
for biomass processing
Direct measurement of electricity –
or vendor invoice
B3 & P3 Estimated Emission factors for fuel
combustion & electricity
Reference values adjusted as
needed by ECCC or ACCO
B4 & P4 Measured Volume of fuel for extraction
and processing emissions
Direct measurement of combusted
fuel – highest frequency possible
B4 & P4 Estimated Emission factors for fuel
extraction and processing
Reference values adjusted as
needed by ECCC or ACCO
B12 & P12 Measured Volume of fuel used for facility
operations
Direct measurement of combusted
fuel – highest frequency possible
B12 & P12 Measured Volume of electricity consumed
for facility operations
Direct measurement of electricity –
or vendor invoice
B12 & P12 Estimated Emission factors for fuel
combustion & electricity
Reference values adjusted as
needed by ECCC or ACCO
B13 N/A Emissions from electricity
generation displaced on-site
Not applicable since there is no on-
site electricity generation displaced
B6 Measured Electricity generated by the
project
Continuous direct metering
represents industry practice and
the highest level of detail
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October 2018
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Version 2.0 Project Plan Form – July 2018
B6 N/A Electricity consumed by the
project
There is no additional electricity
consumed by the project, electricity
is net generation sold to grid
B6 N/A Historic levels of on-site
generation
There is no historic displacement of
electricity in the project, electricity
is net generation sold to grid
B6 Estimated Emission factor for grid
electricity
Reference values adjusted as
needed by ACCO
P15 Measured Mass of biomass fuel
combusted
Direct measurement of biomass
received by the facility according to
industry practice
P15 Estimated CH4 and N2O emission factors
for waste wood combustion
Reference values adjusted as
needed
P15 N/A Volume of supplementary fossil
fuel combusted
No supplementary fossil fuel was
combusted in the project
B15 (flex-
1)
Measured Biomass waste diverted from
landfill or stockpile
Measurement is more accurate than
estimation – scale used for each
truckload diverted from landfill
B15 (flex-
1)
Calculated Amount of methane emitted
from stockpile or landfill
Using methodology and factors
published by ACCO
B15 (flex-
2)
Measured Biomass waste diverted from
open air combustion
Measurement is more accurate than
estimation – scale
B15 (flex-
2)
Estimated CH4 and N2O emission factors
for open air combustion
Using AP-42 emission factors
(section 13.1)
B20 & P20 Measured Mass of Biomass Fuel
Combusted
Measurement is more accurate than
estimation – scale used for each
truckload diverted from landfill
B20 & P20 Estimated CO2 emission factors for waste
wood combustion
Reference values are adjusted as
needed (NIR)
The records and project information used to support the specified gas emission reduction or
sequestration quantification is included in the Monitoring Plan below. Baseline documentation
includes:
• Electronic recording of values of logged primary parameters for each measurement
interval,
• Written logs of operations and maintenance of the project system including notion of all
shutdowns, start-ups and process adjustment,
• Proof of ownership or right to transact emission offsets generated,
• Records to show any fossil fuel or electricity use in the baseline,
• Retention of all copies of logs and all logged data for a period of seven years, and
• Retention of all records available for review by verification body.
Project documentation includes:
• Direct evidence of electricity production from biomass,
• Information for other fuels used including type, quantity and activity for fuel use,
• Records of biomass retention and storage on-site, and
• Historic production of biomass for three years immediately prior to project implementation.
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Version 2.0 Project Plan Form – July 2018
The records to support the flexibility mechanisms, whereby the baseline is organic woody biomass
going to landfill or open-air combusted include:
• Records for a period of at least three years prior to implementation of the project activity
that show that the waste stream was being disposed at a waste management facility with
an EPEA registration or approval,
• Records showing how the waste was treated/disposed at the waste management facility,
• Records showing a historical practice for disposing of biomass and the estimated volumes
of biomass combusted in open-air, and
• Proof that harvest levels or forest utilization standards are not generating more biomass
feedstock than occurred in the baseline condition as a result of diverting biomass from
open-air combustion.
Below is an example of the quantification approach used in this project. The tables below specify
the types of input-data and emissions factors used.
Input Description Input Value (for period)
Electricity Generation 73,545,091 KWH
Electricity Purchased 659,792 KWH
Dapp Wood Consumed 128,465 Tonnes
Total Landfill Diversion 27,604 Tonnes
Dapp Natural Gas 7,764 GJ
Total Gasoline Usage 19,031 L
Total Propane 643 L
Total Site Diesel 235,274 L
Dapp Truck Diesel 145,516 L
3rd Party Transport Diesel 552,660 L
3rd Party Supplier Diesel 24,182 L
Emission Factors Used
GWP CH4 25
GWP N2O 298
Emission Factor Electricity Generation 0.59 tCO2e/MWH
Emission Factor Electricity Consumption 0.64 tCO2e/MWH
Emission Factor Diesel 2.66E-3 tCO2/L
Emission Factor Diesel 1.4E-7 tCH4/L
Emission Factor Diesel 8.2E-8 tN2O/L
Emission Factor Gasoline 2.29E-3 tCO2/L
Emission Factor Gasoline 1.4E-7 tCH4/L
Emission Factor Gasoline 2.2E-8 tN2O/L
Emission Factor Natural Gas 1.92E-3 tCO2/m3
Emission Factor Natural Gas 4.9E-7 tCH4/m3
Emission Factor Natural Gas 4.9E-8 TN2O/m3
Emission Factor Propane 1.51E-3 tCO2/L
Emission Factor Propane 2.4E-8 tCH4/L
Emission Factor Propane 1.08E-7 tN2O/L
Emission Factor Diesel Extraction 1.38E-4 tCO2/L
Emission Factor Diesel Extraction 1.09E-5 tCH4/L
Emission Factor Diesel Extraction 4E-9 tN2O/L
Emission Factor Natural Gas 1.33E-4 tCO2/m3
Emission Factor Natural Gas 2.6E-6 tCH4/m3
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Version 2.0 Project Plan Form – July 2018
Input Description Input Value (for period)
Emission Factor Natural Gas 7E-9 tN2O/m3
Emission Factor Gasoline 1.38E-4 tCO2/L
Emission Factor Gasoline 1.09E-5 tCH4/L
Emission Factor Gasoline 4E-9 tN2O/L
Emission Factor Open Air Combustion 5.53E-3 tCH4/t
Emission Factor Open Air Combustion 2.08E-4 tN2O/t
Emission Factor Biomass 0.84 tCO2/t
Emission Factor Biomass 9E-5 tCH4/t
Emission Factor Biomass 6E-5 tN2O/t
The table below presents a summary view of the emission reduction quantification that is completed
using a purpose-built Excel™ spreadsheet. The quantification distinguishes between levied and non-
levied emissions. Note that baseline counterparts to some of the project SS’s listed below are
excluded from the table for brevity since they would be null values. Specifically, B1, B3, B4, B12,
B13, B16, and B18 are not relevant to the project quantification.
Non-Levied Baseline Emissions tCO2 tCH4 tN2O tCO2e Total CO2e
B6 - Offsite Electricity Generation Displaced in Project 43,391.6 43,391.6
B15 - Disposal of Biomass (Flex 1 and 2) 1,260.4 31,509.5
B15 - Disposal of Biomass (Flex 3) 0.0 0.0 0.0
B15 - Disposal of Biomass (Flex 4) 0.0 0.0 0.0
Total Non-Levied Baseline Emissions 0.0 1,260.4 0.0 43,391.6 74,901.1
Non-Levied Project Emissions tCO2 tCH4 tN2O tCO2e Total CO2e
P3 - Processing of Biomass (Electricity) 18.6 18.6
P4 - Extraction and Processing of Fuels (nat gas, diesel, gasoline)
46.3 2.0 0.0 97.7
P15 - Combustion of Biomass and Fossil Fuels 11.6 7.7 2,586.0
P12 - Facility Operations (Electricity) 403.6 403.6
Total Non-Levied Project Emissions 46.3 13.6 7.7 422.2 3,105.9
Total Eligible Emission Reductions 0.0 1,246.8 -7.7 42,969.4 71,795.1
Levied Baseline Emissions tCO2 tCH4 tN2O tCO2e Total CO2e
Total Emissions 0 0 0 0 0
Levied Project Emissions tCO2 tCH4 tN2O tCO2e Total CO2e
P1 - Collection Transfer and Transport of Biomass (diesel) 1,859.2 0.1 0.1 1,878.7
P3 - Processing of Biomass (diesel, propane) 374.9 0.0 0.0 378.8
P12 - Facility Operation (nat gas, diesel, gasoline) 755.7 0.1 0.0 764.9
Total Levied Emission Reductions 2,989.9 0.2 0.1 0.0 3,022.4
Total Non-Eligible Emission Reductions -2,989.9 -0.2 -0.1 0.0 -3,022.4
Other Reported Emissions tCO2 tCH4 tN2O tCO2e Total CO2e
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P20 - Biogenic Caron Emissions 107,910.6 107,910.65
Total Other Reported Emissions 107,910.6 - - - 107,910.65
3.4 Monitoring Plan
The tables below present the details of monitored parameters.
Parameter Monitoring Specifications
Source/sink identifier
and name
B1/P1 – Collection, Transfer and Transport of Biomass
Data parameter Volume of Fuel Diesel
Estimation, modeling,
measurement or
calculation approaches
Measured or estimated using a direct relationship factor
(liters/tonne) as recorded by DAPP or Biofuels for
transport over similar distance to processing of waste
wood respectively.
Data unit L of diesel
Sources/Origin Biomass supplier
Sampling frequency Per load received at Dapp
Description and
justification of
monitoring method
The quantity of diesel fuel used is based on two methods
depending on the third-party activity:
• Independent operators of tractor-trailer units under
contract to Dapp Power: These parties are asked to
indicate total diesel fuel used on Dapp related work for
each month. This information is requested to be
provided with monthly commercial invoices as part of
the contract terms.
Third parties that process (grind, load and transport)
wood biomass and transport directly to the Dapp facility:
These parties deliver wood biomass by their own means
and Dapp pays for a delivered quantity at the plant
gate. Diesel fuel used is based on Dapp & Biofuel’s own
fuel used on a per tonne basis as an estimate. The third
parties use similar equipment to both process and
transport the wood biomass to Dapp and Dapp & Biofuels
combined. Therefore, Biofuels usage is believed to be a
reasonably accurate estimate of fuel usage. Adjustments
may be made if transport logistics vary significantly from
Dapp’s routes used to estimate.
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Uncertainty Moderate, fleet efficiency values are a reasonable
representation of actual fuel consumption for collection of
biomass vehicle emissions
Parameter Monitoring Specifications
Source/sink identifier
and name
B1/P1 – Collection, Transfer and Transport of Biomass
Data parameter EF Diesel CO2, EF Diesel CH4, EF Diesel N2O, GWPCH4, GWPN2O,
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCO2/L diesel, tCH4/L diesel, tN2O/L diesel, tCO2/tCH4,
tCO2/tCH4
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per offset system guidance
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B3/P3 – Processing of Biomass
Data parameter Volume of Fuel Diesel, Volume of Fuel Propane
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit L of diesel & L of Propane
Sources/Origin Biomass supplier – Biofuels Inc.
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Sampling frequency Monthly invoices
Description and
justification of
monitoring method
The quantity of diesel fuel used is based on two methods
depending on the third-party activity:
• Biomass processed through Biofuels: Monthly
invoices for fuel purchases is industry standard and
represents a reasonable level of diligence and
accuracy
Third parties that process (grind, load and transport)
wood biomass and transport directly to the Dapp facility:
These parties deliver wood biomass by their own means
and Dapp pays for a delivered quantity at the plant
gate. Diesel fuel used is based on Dapp & Biofuel’s own
fuel used on a per tonne basis as an estimate. The third
parties use similar equipment to both process and
transport the wood biomass to Dapp and Dapp & Biofuels
combined. Therefore, Biofuels usage is believed to be a
reasonably accurate estimate of fuel usage. Adjustments
may be made if transport logistics vary significantly from
Dapp’s routes used to estimate.
Uncertainty Low, fuel invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
Parameter Monitoring Specifications
Source/sink identifier
and name
B3/P3 – Processing of Biomass
Data parameter EF Diesel CO2, EF Diesel CH4, EF Diesel N2O, GWPCH4, GWPN2O, EF
(electricity)
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCO2/L diesel, tCH4/L diesel, tN2O/L diesel, tCO2/tCH4,
tCO2/tCH4 tCO2e/MWh
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
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Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B3/P3 – Processing of Biomass
Data parameter Volume of electricity (Biofuels)
Estimation, modeling,
measurement or
calculation approaches
Measured – EPCOR utility meter
Data unit MWh of Electricity
Sources/Origin Electric utility meter
Sampling frequency Monthly invoices
Description and
justification of
monitoring method
The quantity of electricity used is based on two methods
depending on the third-party activity:
• Monthly invoices for electricity purchases is
industry standard and represents a reasonable
level of diligence and accuracy. A statement is
received each month from EPCOR for any electricity
metered and recorded as purchased from the grid.
Third parties that process (grind, load and transport)
wood biomass and transport directly to the Dapp facility:
These parties deliver wood biomass by their own means
and Dapp pays for a delivered quantity at the plant
gate. Electricity is based on Dapp & Biofuel’s own fuel
used on a per tonne basis as an estimate. The third
parties use similar equipment to both process and
transport the wood biomass to Dapp and Dapp & Biofuels
combined. Therefore, Biofuels usage is believed to be a
reasonably accurate estimate of fuel usage.
Uncertainty Low, electricity invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
Parameter Monitoring Specifications
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Source/sink identifier
and name
B3/P3 – Processing of Biomass
Data parameter EF Propane CO2, EF Propane CH4, EF Propane N2O
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCO2/L, tCH4/L, tN2O/L
Sources/Origin Environment Canada Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B4/P4 – Fuel Extraction / Processing
Data parameter Volume of Fuel Diesel
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit L of diesel
Sources/Origin Biomass supplier
Sampling frequency Monthly invoices
Description and
justification of
monitoring method
Monthly invoices for fuel purchases is industry standard
and represents a reasonable level of diligence and
accuracy
Uncertainty Low, fuel invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
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Parameter Monitoring Specifications
Source/sink identifier
and name
B4/P4 – Fuel Extraction / Processing
Data parameter EF Diesel CO2, EF Diesel CH4, EF Diesel N2O
EF Natural Gas CO2, EF Natural Gas CH4, EF Natural Gas N2O
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCO2/L diesel, tCH4/L diesel, tN2O/L diesel
tCO2/m3 natural gas, tCH4/m3 natural gas, tN2O/m3
natural gas
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B4/P4 – Fuel Extraction Processing
Data parameter Volume of Fuel Natural Gas
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit m3 of natural gas
Sources/Origin Pembina Gas Co-operative utility meter - TransCanada
Tap # 4617. (SE1/4 - 32-62-1 W5)
Sampling frequency Monthly invoices
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Description and
justification of
monitoring method
Monthly invoices for fuel purchases is industry standard
and represents a reasonable level of diligence and
accuracy. An invoice is received from the supplier at the
end of each month.
Uncertainty Low, fuel invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
Parameter Monitoring Specifications
Source/sink identifier
and name
B6 Off-Site Electricity Displaced by Project
Data parameter Volume of Electricity
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit kWh
Sources/Origin Utility Meter - PM-9803B004-5 – Midas Metering
downloads data and supplies to TransAlta for invoicing
Sampling frequency Monthly invoices
Description and
justification of
monitoring method
Monthly invoices for electricity generation is industry
standard and represents a reasonable level of diligence
and accuracy
Uncertainty Low, invoices are measured for purchasing and
uncertainty is limited by the utility
Parameter Monitoring Specifications
Source/sink identifier
and name
B6 Off-Site Electricity Displaced by Project
Data parameter EFEG
Estimation, modeling,
measurement or
calculation approaches
Reference value - Provided in the Handbook of Emissions
Factors
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Data unit tCO2e/MWh
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B12/P12 – Facility Operations
Data parameter Volume of Fuel Diesel and Volume of Fuel Gasoline
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit L of diesel & L of gasoline
Sources/Origin Fuel vendor
Sampling frequency Monthly invoices
Description and
justification of
monitoring method
Monthly invoices for fuel purchases is industry standard
and represents a reasonable level of diligence and
accuracy. An invoice is received from the supplier at the
end of each month. A hard copy of this invoice is kept in
a folder from which the volume will be manually
transposed into the quantification calculator.
Uncertainty Low, fuel invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
Parameter Monitoring Specifications
Source/sink identifier
and name
B12/P12 – Facility Operations
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Data parameter EF Diesel CO2, EF Diesel CH4, EF Diesel N2O & EF Gasoline CO2, EF Gasoline
CH4, EF Gasoline N2O & EF Natural Gas CO2, EF Natural Gas CH4, EF Natural
Gas N2O
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCO2/L diesel, tCH4/L diesel, tN2O/L diesel & tCO2/L
gasoline, tCH4/L gasoline, tN2O/L gasoline & tCO2/m3
natural gas, tCH4/m3 natural gas, tN2O/m3 natural gas
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
B12/P12 – Facility Operations
Data parameter Volume of Fuel Natural Gas
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit m3 of natural gas
Sources/Origin Pembina Gas Co-operative utility meter - TransCanada
Tap # 4617. (SE1/4 - 32-62-1 W5)
Sampling frequency Monthly invoices
Description and
justification of
monitoring method
Monthly invoices for fuel purchases is industry standard
and represents a reasonable level of diligence and
accuracy. An invoice is received from the supplier at the
end of each month.
Uncertainty Low, fuel invoices are measured for purchasing and
uncertainty is limited by the fuel vendor
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Parameter Monitoring Specifications
Source/sink identifier
and name
B15 – Disposal of Biomass
Data parameter Wc
Estimation, modeling,
measurement or
calculation approaches
Measured
Data unit Tonnes waste
Sources/Origin Weigh scales
Sampling frequency Per load
Description and
justification of
monitoring method
Each truck delivering a load is weighed both full and
empty, thus giving an exact weight of each load of
biomass being delivered to the facility. The weight is
electronically read, and a paper ticket is automatically
printed. These hard copies are kept and then transposed
manually into the quantification calculator. Loads are
tracked by both shipper and source location.
Uncertainty Limited to uncertainty of scales
Parameter Monitoring Specifications
Source/sink identifier
and name
B15 – Disposal of Biomass
Data parameter k
Estimation, modeling,
measurement or
calculation approaches
Calculated
Data unit Unitless
Sources/Origin Emission Factor Handbook
Sampling frequency Annual
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Description and
justification of
monitoring method
Methane Generation figure using annual regional
precipitation figures from Environment Canada weather
station
Uncertainty Low, limited to uncertainty of scientific evidence for how
precipitation and evaporation rates affect methane
generation
Parameter Monitoring Specifications
Source/sink identifier
and name
B15 – Disposal of Biomass
Data parameter Lo, DOC, DOCf, MCF, F
Estimation, modeling,
measurement or
calculation approaches
Calculated
Data unit Lo – tonne methane / tonne waste
Sources/Origin Emission Factor Handbook
Sampling frequency Annual
Description and
justification of
monitoring method
Methane Generation Potential, using wood waste landfill
MCF, and wood waste for DOC and DOCf
Uncertainty Low – since protocol methodology is employed
Parameter Monitoring Specifications
Source/sink identifier
and name
B15 – Disposal of Biomass
Data parameter R & OX
Estimation, modeling,
measurement or
calculation approaches
Estimated using default values
Data unit Percent
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Sources/Origin Emission Factor Handbook
Sampling frequency Annual
Description and
justification of
monitoring method
Oxidation Factor default rates of 0.1 and Methane
Collection and Destruction default rates for temporary
covered cells
Uncertainty Low – since protocol methodology is employed
Parameter Monitoring Specifications
Source/sink identifier
and name
B15 – Disposal of Biomass
Data parameter EF Biomass CH4, EF Biomass N2O
Estimation, modeling,
measurement or
calculation approaches
Reference value
Data unit tCH4/MJ or kg, tN2O/MJ or kg
Sources/Origin AP-42
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
Parameter Monitoring Specifications
Source/sink identifier
and name
P15 – Combustion of Biomass and Fossil Fuels
Data parameter EFBiomass CH4, EFBiomass, N2O
Estimation, modeling,
measurement or
calculation approaches
Reference value
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Data unit tCO2/tonne biomass
Sources/Origin Handbook of Emission Factors
Sampling frequency Annual
Description and
justification of
monitoring method
As per protocol
Uncertainty Limited to uncertainty of emission factor supporting data
3.5 Data Management System
There are several data collection points for emissions related to diesel consumption. Each of these
points is accounted through one of several emission source/sinks and are depicted in Figure 2: Diesel
Fuel Consumption Data
Diesel fuel is consumed by the DAPP facility, on-site for fuel loading and storage management in
various loaders. Fuel is stored on-site in a tank that is owned by Dapp and Biofuels. Fuel is supplied
by a fuel wholesaler (EFA, Petro Canada, etc.). Fuel is tracked through metering by the fuel
wholesaler when deliveries are made and is invoiced directly to DAPP. Invoices are kept as records
for the project and volume data is manually transcribe into the emission reduction calculation
spreadsheets.
There are several data collection points for emissions related to electricity consumption. Each of
these points is accounted through one of several emission source/sinks and are depicted in
Figure 4: Electricity Production and Consumption Data Management.
Electricity is consumed by the DAPP facility for various electrical loads (lights, office equipment, etc.)
as well as produced through the generator on-site. Electricity production is measured through Midas
on a Schnieder Electric measurement system that is remotely accessed and provided to TransAlta on
a daily basis. TransAlta aggregates the electricity production data and provides DAPP with electricity
purchase invoices on a monthly basis. This meter is net of internal load when producing power. When
the plant is down it records net purchase. During times of no generation and disruption to grid,
internal load is met by backup diesel generation which is recorded as diesel consumption. Invoices
are kept for both the production and consumption of electricity and manually transcribed into the
emission reduction calculator.
Electricity is consumed by the Bio-Fuels Inc. facility for various electrical loads (lights, office
equipment, motors, etc.). Electricity measurement for purchased electricity is through the
utility/retailer EPCOR. The meter is utility owned and operated. Invoices are provided to Biofuels on
a monthly basis which are provided to DAPP and manually transcribed into the emission reduction
calculator.
The data collection points and emissions related to gasoline consumption can be found in Figure 3:
Gasoline Consumption Data Management. Gasoline fuel is consumed by passenger vehicles for site
operations. Fuel is purchased through gasoline retailers at consumer gas stations. Fuel is tracked
through metering by the fuel retailers upon purchase and is invoiced directly to DAPP. Invoices are
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kept as records for the project and volume data is manually transcribe into the emission reduction
calculation spreadsheets.
The data collection points and emissions related to natural gas consumption can be found in Figure 5:
Natural Gas Consumption Data Management. Natural gas fuel is consumed by the DAPP facility, on-site for
various space heating needs and boiler start-up. Fuel is purchased through Pembina Gas Co-Op on-
site. Fuel is tracked through metering by the utility gas co-op meter on-site and is invoiced directly
to DAPP. Invoices are kept as records for the project and volume data is manually transcribed into
the emission reduction calculation spreadsheets.
The data collection points and emissions related to propane consumption can be found in Figure 6:
Propane Consumption Data Management. Propane fuel is consumed by the Biofuel facility for various space
heating needs and equipment. Fuel is purchased through Superior Propane and is delivered on-site
to a storage bullet. Fuel is tracked through metering by the wholesaler on-site and is invoiced directly
to DAPP. Invoices are kept as records for the project and volume data is manually transcribed into
the emission reduction calculation spreadsheets.
Biomass diverted from landfill and combusted in the project condition contributes to avoided baseline
emissions and is tracked in the baseline emission source/sink demonstrated in Figure 7: Biomass
Diversion Data Management. The figure below depicts the data management for this data stream.
Biomass consumed by the DAPP facility for electricity generation is tracked as it arrives on-site by
weigh-in and weigh-out of delivery trucks. Waste mass is then estimated using weigh scale data,
stock pile data and an energy balance in the calculation spreadsheet. Records for the project and
biomass volume data is manually transcribed into the emission reduction calculation spreadsheets.
Characteristics of the landfills from where waste was diverted is manually transcribed into the
emission reduction calculation spreadsheet based on contractual information and records provided
by waste suppliers.
Meter Maintenance and Calibration
Maintenance and calibration for the metering systems used at the DAPP Generation Facility consists
of a maintenance and calibration program designed to ensure the accuracy of the data collection
system. The details of maintenance and calibration for each meter used in the collection of data for
emission reduction calculations are provided in the table below.
Table 4: Meter Maintenance & Calibration
Project Specific Data
Meter ID Meter Make/
Model Maintenance
Schedule Calibration Schedule
Mass of Biomass Transported to
Dapp
Truck Scale Ancoma Scale Annual third party calibration
Consumption of Natural Gas
Pembina Gas Co-Op
Utility N/A – utility meter
N/A – utility meter
Net Electricity
Generation
PM-
9803B004-5
Schneider Electric
– 7550ION
In-situ test
every 3 years
To be re-verified 6 years after
the initial verification and 5 years after the second re-verification
Steam Production HP Steam Yokogowa/EJA 110A
As Required Annual
Fuel Moisture Analysis Scale
Mass Scale OHAUS Dial-o-gram 1600
As required As Required
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Diesel Consumption
EFA, Petro Canada, etc.
Delivery truck meter
N/A – wholesaler meter
N/A – wholesaler meter
Gasoline Consumption
(various retail)
(various retail) N/A – retailer meter
N/A – retailer meter
Bio-Fuels Inc. Propane
Consumption
Superior Propane
Delivery truck meter
N/A – wholesaler
meter
N/A – wholesaler meter
Bio-Fuels Inc. Diesel Consumption
EFA, Petro Canada, etc.
Delivery truck meter
N/A – wholesaler meter
N/A – wholesaler meter
Bio-Fuels Inc.
Electricity Consumption
EPCOR Utility N/A – utility
meter
N/A – utility meter
Quality Assurance and Quality Control
The quantification of the volume of diesel used is completely manual, and is based on monthly
reconciliation of diesel bills. Monitoring and QA/QC for diesel volumes will consist of manual checking
of data entered into the Emission Reduction Calculator against the original diesel bills to ensure
independent review of the data prior to verification. Estimated diesel volumes are also treated
manually.
The quantification of the mass of biomass and volume of natural gas consumed, as well as the
generated is partially manual. Monitoring and QA/QC for biomass consists of annual pile surveys
which requires an independent survey to determine pile volume. Density of fuel is determined
through sampling and a pile mass is established. This mass is compared to the mass received at the
facility and the estimated combusted fuel is subtracted. Any fuel consumption discrepancy which has
accumulated over the period in question is adjusted in the month which the survey was completed
(typically September). At the end of each year, the pile volume is typically reduced to zero which
ensures that the reconciliation process of each year is applicable to that year only and does not
represent inaccuracies of previous years estimations.
Furthermore, the on-site stockpile size is never more than 2 months of fuel. This meets the protocol
requirement for stockpiling less than 90 days (regardless of particle size). The fuel use regime for
the on-site stockpile is ‘first-in-first-out’. This is in the best interest of the plant as the oldest fuel is
inherently drier and therefore the best for combustion. This alignment in interest helps ensures that
no parts of the stockpile remain longer than the 90-day limit and are always combusted prior to
exceeding the storage time limit.
Manual checking will be conducted on an annual basis by a third-party consultant and will consist of:
• Reconciliation of values in the calculator with hard-copy records of electronic data;
• Comparison with data from other time periods to identify any major discrepancies (“reality
checking”); and
• Recalculation of selected values to ensure that the Calculator remains accurate.
Only DAPP employees related to the project have access to the records and calculation files. This
prevents security risks by ensuring only those responsible for delivering project results and only
those with proper credentials are provided access to edit, manipulate or delete information related
to the project. This prevents tampering with project data and improves the reliability of the data
management system.
Record Keeping
Data is collected and managed by several individuals within the organization. Data is collected and
managed to meet operational, financial and commercial needs, including CO2e verification
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requirements, Data management procedures exist which are reviewed annually by financial auditors
and CO2e verifier.
Record keeping practices for the project consist of:
• Electronic recording of values of logged primary parameters for each measurement interval;
• Printing of monthly back-up hard copies of all logged data;
• Written logs of operations and maintenance of the project system including notation of all
shut-downs, start-ups and process adjustments;
• Retention of copies of logs and all logged data for a period of 7 years; and
• Keeping all records available for review by a verification body.
.
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5.0 References
Government of Alberta, 2015. Carbon Offset Emission Factor Handbook, Version 1.0. Specified
Gas Emitters Regulation.
Government of Alberta, 2018. Energy Generation from the Combustion of Biomass Waste, Version
2.2. Carbon Competitiveness Incentive Regulation.
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Appendix A: Supporting Information
Figure 2: Diesel Fuel Consumption Data Management
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Figure 3: Gasoline Consumption Data Management
Figure 4: Electricity Production and
Consumption Data Management
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Figure 5: Natural Gas Consumption Data Management
Figure 6: Propane Consumption Data Management
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Figure 7: Biomass Diversion Data Management