The Department will provide for the award of CO2 offset allowances to sponsors of CO2 emissions offset projects that have reduced or avoided atmospheric loading of CO2, CO2 equivalent or sequestered carbon as demonstrated in accordance with the applicable provisions. The requirements seek to ensure that CO2 offset allowances awarded represent CO2 equivalent emission reductions or carbon sequestration that are real, additional, verifiable, enforceable, and permanent within the framework of a standards-based approach. Subject to the relevant compliance deduction limitations of subsection 6.5.1.3, CO2 offset allowances may be used by any CO2 budget source for compliance purposes.
"The undersigned project sponsor recognizes and accepts that the application for, and the receipt of, CO2 offset allowances under the CO2 Budget Trading Program is predicated on the project sponsor following all the requirements of Section 10.0. The undersigned project sponsor holds the legal rights to the offset project, or has been granted the right to act on behalf of a party that holds the legal rights to the offset project. I understand that eligibility for the award of CO2 offset allowances under Section 10.0 is contingent on meeting the requirements of Section 10.0. I authorize the Department or its agent to audit this offset project for purposes of verifying that the offset project, including the monitoring and verification plan, has been implemented as described in this application. I understand that this right to audit shall include the right to enter the physical location of the offset project. I submit to the legal jurisdiction of the State of Delaware."
Emissions (tons CO2 e) = (V x M x (1-OX) x GWP)/2000
Where:
V = Volume of CH4 collected (ft3)
M = Mass of CH4 per cubic foot (0.04246 lbs/ft3 default value at 1 atmosphere and 20° C)
OX = Oxidation factor (0.10), representing estimated portion of collected CH4 that would have eventually oxidized to CO2 if not collected
GWP = CO2 e global warming potential of CH4 (28)
Emissions Reductions (tons CO2 e) = (V x M x (1 - OX) x Cef x GWP)/2000
Where:
V = Volume of CH4 collected (ft 3)
M = Mass of CH4 per cubic foot (0.04246 lbs/ft3 default value at 1 atmosphere and 20° C)
OX = Oxidation factor (0.10), representing estimated portion of collected CH4 that would have eventually oxidized to CO2 if not collected
Cef = Combustion efficiency of methane control technology (0.98)
GWP = CO2 e global warming potential of CH4 (28)
MP (%) = MGAD / MGSTATE
Where:
MGAD = Average annual manure generation for the number of dairy cows and swine serving all anaerobic digester projects in the applicable state at the time of submission of a consistency application pursuant to subsection 10.4.
MGSTATE = average annual manure production of all dairy cows and swine in the state at the time of submission of a consistency application pursuant to subsection 10.4.
Eb = (Vm x M)/2000 x GWP
Where:
Eb = Potential CO2 e emissions due to calculated CH4 production under site-specific anaerobic storage and weather conditions (tons);
Vm = Volume of CH4 produced each month from decomposition of volatile solids in a baseline uncontrolled anaerobic storage scenario under site-specific storage and weather conditions for the facility at which the manure or organic food waste is generated (ft3)
M = Mass of CH4 per cubic foot (0.04246 lb/ft³ default value at one atmosphere and 20°C)
GWP = Global warming potential of CH4 (28)
VSdec = VSavail x f
Where:
VS = volatile solids as determined from the equation:
VS = Mm x TS% x VS%
where:
Mm = mass of manure or organic food waste produced per month (kg)
TS% = concentration (percent) of total solids in manure or organic food waste as determined through I-3750, "Solids, residue on evaporation at 105 degrees C, total, gravimetric," Methods for the Determination of Inorganic Substances in Water and Fluvial Sediments, Techniques of Water-Resources Investigations of the United States Geological Survey, Book 5, Chapter A1. Edited by Marvin J. Fishman and Linda C. Friedman.
VS% = concentration (percent) of volatile solids in total solids as determined through EPA 160.4 testing method (U.S.EPA Method Number 160.4, Methods for the Chemical Analysis of Water and Wastes (MCAWW) (EPA/600/4-79/020))
VSavail = volatile solids available for decomposition in manure or organic food waste storage each month as determined from the equation:
VSavail = VSp + 1/2 VSin - VSout
Where:
VSp = volatile solids present in manure or organic food waste storage at beginning of month (left over from previous month) (kg)
VSin = volatile solids added to manure or organic food waste storage during the course of the month (kg). The factor of 1/2 is multiplied by this number to represent the average mass of volatile solids available for decomposition for the entire duration of the month.
VSout = volatile solids removed from the manure or organic food waste storage for land application or export (assumed value based on standard farm practice)
f = van't Hoff-Arrhenius factor for the specific month as determined using the equation below. Using a base temperature of 30°C, the equation is as follows:
f = exp{[E(T2 - T1)]/[(GC x T1 x T2)]}
Where:
f = conversion efficiency of VS to CH4 per month
E = activation energy constant (15,175 cal/mol)
T2 = average monthly ambient temperature for facility where manure or organic food waste is generated (converted from ° Celsius to ° Kelvin) as determined from the nearest National Weather Service certified weather station (if reported temperature ° C > 5° C; if reported temperature ° C < 5° C, then F = 0.104)
T1 = 303.15 (30° C converted to °K)
GC = ideal gas constant (1.987 cal/K mol)
Vm = (VSdec x Bo) x 35.3147
Where:
Vm = volume of CH4 (ft3)
VSdec = volatile solids decomposed (kg)
Bo = manure or organic food waste type-specific maximum methane generation constant (m3 CH4 /kg VS decomposed). For dairy cow manure, Bo = 0.24 m3 CH4 /kg VS decomposed. The methane generation constant for other types of manure shall be those cited at U.S. EPA, Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2010, Annex 3.10, Table 180 (U.S. Environmental Protection Agency, February 2017), unless the project sponsor proposes an alternate methane generation constant and that alternate is approved by the Department. If the project sponsor proposes to use a methane generation constant other than the ones found in the above-cited reference, the project sponsor must provide justification and documentation to the Department.
ERt = Eb - Ep
where:
ERt = CO2 e emissions reductions due to project activities (tons);
Eb = Potential CO2 e emissions due to calculated CH4 production under site-specific anaerobic storage and weather conditions (tons);
Ep = CO2 e emissions due to project activities additional to baseline (tons), including, but not limited to, manure transportation, flaring, venting, and effluent management.
Emissions reductions may not exceed the potential emissions of the anaerobic digester, as represented by the annual volume of CH4 produced by the anaerobic digester, as monitored pursuant to subsection 10.5.5.5. If the project is a regional-type digester, CO2 emissions due to transportation of manure and organic food waste from the site where the manure and organic food waste was generated to the anaerobic digester shall be subtracted from the emissions reduction calculated pursuant to subsections 10.5.5.3.1 through 10.5.5.3.3. Transport CO2 emissions shall be determined through one of the following methods.
Table 8. Monitoring Requirements
Parameter | Measurement Unit | Frequency of Sampling | Sampling Method(s) |
Influent flow (mass) into the digester | Kilograms (kg) per month (wet mass) | Monthly total into the digester | a) Recorded mass b) Digester influent pump flow c) Livestock population and application of American Society of Agricultural and Biological Engineers (ASABE) standard (ASAE D384.2, March 2005) |
Influent total solids concentration (TS) | Percent (of sample) | Monthly, depending upon recorded variations | U.S. EPA Method Number 160.3, Methods for the Chemical Analysis of Water and Wastes (MCAWW) (EPA/600/4-79/020) |
Influent volatile solids (VS) concentration | Percent (of TS) | Monthly, depending upon recorded variations | USEPA Method Number 160.4, Methods for the Chemical Analysis of Water and Wastes (MCAWW) (EPA/600/4-79/020) |
Average monthly ambient temperature | Temperature °C | Monthly (based on farm averages) | Closest National Weather Service-certified weather station |
Volume of biogas produced by digester | Standard cubic feet (scf) | Continuous, totalized monthly | Flow meter |
Methane composition of biogas produced by digester | Percent (of sample) | Quarterly | Bag sampling and third party laboratory analysis using applicable U.S. EPA test methods |
"The undersigned project sponsor hereby confirms and attests that the offset project upon which this monitoring and verification report is based is in full compliance with all of the requirements of the CO2 Budget Trading Program. The project sponsor holds the legal rights to the offset project, or has been granted the right to act on behalf of a party that holds the legal rights to the offset project.
I understand that eligibility for the award of CO2 offset allowances under the CO2 Budget Trading Program is contingent on meeting the requirements of the CO2 Budget Trading Program. I authorize the Department or its agent to audit this offset project for purposes of verifying that the offset project, including the monitoring and verification plan, has been implemented as described in the consistency application that was the subject of a consistency determination by the Department.
I understand that this right to audit shall include the right to enter the physical location of the offset project and to make available to the Department or its agent any and all documentation relating to the offset project at the Department's request. I submit to the legal jurisdiction of the State of Delaware."
12/11/18
7 Del. Admin. Code § 1147-10.0
22 DE Reg. 511 (12/1/2018) (Final)