ࡱ> 5@ bjbj22 XX8ppp=|4(\\\ <<<<<<<$7@RB<p}@<\\!=X\p\<<Cj9:6p\\x =k=g=T=jaCU aCd\\aCppexz W S eee<<ZGDBu"G DRAFT REPORT TO STAKEHOLDERS FROM BUILDINGS, FACILITIES & MANUFACTURING WORKING GROUP Date: To: GHG Stakeholder Advisory Group From: Buildings, Facilities & Manufacturing Working Group Re: Recommendations regarding Options to reduce GHG emissions from Buildings, Facilities, Manufacturing  The purpose of this memo is to report to the Stakeholder Group on the work by the Buildings, Facilities & Manufacturing Working Group concerning potential greenhouse gas reduction options related to buildings, facilities and manufacturing in Maine. The Working Group met four times, on January 23, February 26, March 25 and May 26, 2004. During the first meeting, the Working Group reviewed and commented on information then available for developing an inventory and baseline for residential, commercial, and industrial buildings and facilities. At the first meeting the Working Group also reviewed the GHG Options suggested for analysis by the Stakeholder Group and suggested additional options for analysis. At the second through fourth meetings, the Working Group refined the inventory and baseline by providing Maine specific information, developed and refined policy statements, and provided information to estimate potential GHG emissions savings and costs of options. A number of Working Group members put in many hours outside of meetings to develop this information. During the third and fourth meetings, the Working Group evaluated options. The results of this evaluation are set out below. All Working Group Members recommend those options set out under the list of consensus recommendations. The Options are described more fully in the accompanying report. Consensus Recommendation Options NumberNameSaved CarbonCSC1.1 *Energy Efficiency Appliance Standards2.1 *Improved Residential Building Energy Codes 2.3 ?Voluntary Green Building Standards2.6 ?Efficient Use of Oil and Gas: Home Heating2.7 ?Fuel Switching3.1 ?Energy Standards for New Construction/Renovations: State-funded Buildings3.2 ?Promote Energy Efficient Buildings3.3 ?Implement the most cost-effective energy savings in State buildings3.5 ?Load Management3.6 ?Green Campus Initiatives3.7 ?Improve Enforcement of Commercial Building Energy Codes3.8 ?Increase EE in commercial and institutional buildings 3.9 *Procurement Preference4.1 ?Increase Efficiency of Industrial Buildings4.2 ?Participate in Voluntary Industry-Governmental Partnerships4.3 ?Leak Reduction Programs4.4 ?Substitution of High GWP Gases4.5 ?Industrial Ecology/Byproduct Synergy4.6 ?Negotiated Agreements4.7 ?Encourage CHP (commercial, institutional, industrial4.8 ?Specify ASTM specification for portland cement5.1 ?Public Benefit Fund5.4 ?Incentives for Green Power Purchases5.5 ?Natural Gas and Oil Conservation Fund Notes for Table of Consensus Measures: Measure 2.1: Require new buildings or substantial reconstruction to meet the most recent energy code efficiency/performance standards established by the International Code Council and ASHRAE ventilation standards, with effective enforcement, as recommended through the PUC process. The WG reached consensus that this measure should be recommended. The Maine Oil Dealers Association agreed with this recommendation with this clarification: MODA has concerns over the interplay between state oil and gas installation standards and the IECC and ASHRAE standards, which it will address through the PUC process. Table of Non-Consensus Measures (if any) Stakeholders: Meetings Present 1/23 2/26 3/25 5/26 Anderson, Leslie Dead River Company X Anderson, Norm American Lung Association X Barden, Michael Maine Pulp & Paper Association X X X Baston, Doug Northeast by Northwest X X X Butts, John Associated Contractors of Maine Bergeron, Denis Public Utilities Commission X X Burt, Andy Maine Council of Churches X Buxton, Tony Independent Energy Consumers X X X Cox, Shannon Interface Fabrics Groups X X X Greeley, Dudley University of Southern Maine X X X Hall, Dick National Semiconductor X X X Hall, Christopher Maine Chamber of Commerce Hubbell, Brian X X X Jones, Sue Natural Resources Council of Me X X Karagiannes, Mike DEP Air Quality X X X Kraske, Chuck International Paper - Androscoggin X X X Maxwell, David DEP Py, Jamie/ X Aho, Pattie Maine Oil Dealers X X X Stoddard, Michael Environment Northeast X X X Thayer, Ann Dragon Products X X X While, Bill EPA Gosline, Ann Facilitator X X X Lawson, Karen CCAP X X X Note: We will delete Working Group members who do not attend any of the meetings. Maine Greenhouse Gas Action Plan Development Process  SHAPE \* MERGEFORMAT  Building, Facilities, and Manufacturing Greenhouse Gas Reduction Options Center for Clean Air Policy May 19th, 2004 Buildings, Facilities, & Manufacturing (BFM) Assumptions Document as of May 19, 2004 Table of Contents  TOC \o "1-3" 1. Sector Baseline and Cumulative GHG Reduction  PAGEREF _Toc72318308 \h 7 2. Summary Table of Sector Priority Options  PAGEREF _Toc72318309 \h 11 3. Descriptions and Assumptions For Each Sector Option  PAGEREF _Toc72318310 \h 13 BFM 1.1 Energy Efficiency Appliance Standards  PAGEREF _Toc72318311 \h 14 BFM 2.1 Improved Residential Building Energy Codes  PAGEREF _Toc72318312 \h 15 BFM 2.3 Voluntary Green Building Design Standards  PAGEREF _Toc72318313 \h 17 BFM 2.6 Efficient Use of Oil and Gas: Home Heating  PAGEREF _Toc72318314 \h 19 BFM 2.7 Fuel Switching  PAGEREF _Toc72318315 \h 21 BFM 3.1 Energy standards for State and State-funded New Construction/Renovations  PAGEREF _Toc72318316 \h 23 BFM 3.2 Promote Energy Efficient Buildings  PAGEREF _Toc72318317 \h 25 BFM 3.3 Implement the most cost-effective energy savings in State Buildings  PAGEREF _Toc72318318 \h 27 BFM 3.5 Load Management  PAGEREF _Toc72318319 \h 30 BFM 3.6 Green Campus Initiatives  PAGEREF _Toc72318320 \h 31 BFM 3.7 Improve Enforcement of Commercial Energy Codes  PAGEREF _Toc72318321 \h 32 BFM 3.8 Improve Electrical Efficiency in Commercial Buildings  PAGEREF _Toc72318322 \h 34 BFM 3.9 Procurement Preference  PAGEREF _Toc72318323 \h 37 BFM 4.1 Promote Electrical Efficiency Measures in the Industrial Sector  PAGEREF _Toc72318324 \h 38 BFM 4.2 Participate in Voluntary Industry-Government and/or Industry Partnerships  PAGEREF _Toc72318325 \h 40 BFM 4.3 Leak Reduction Programs  PAGEREF _Toc72318326 \h 42 BFM 4.4 Substitution of High GWP Gases  PAGEREF _Toc72318327 \h 43 BFM 4.5 Industrial ecology/by-product synergy  PAGEREF _Toc72318328 \h 45 BFM 4.6 Negotiated Agreements  PAGEREF _Toc72318329 \h 48 BFM 4.7 Encourage Combined Heat and Power  PAGEREF _Toc72318330 \h 50 BFM 4.8 Specify ASTM specification C150 for portland cement  PAGEREF _Toc72318331 \h 53 BFM 5.2 Increase Public Benefit Fund  PAGEREF _Toc72318332 \h 54 BFM 5.4 Incentives for Green Power Purchase  PAGEREF _Toc72318333 \h 55 BFM 5.5 Natural Gas and Oil Conservation Fund  PAGEREF _Toc72318334 \h 57 Appendix 1:  PAGEREF _Toc72318335 \h 58 Potential Building, Facilities, and Manufacturing GHG Reduction Opportunities Edited 12-17-03  PAGEREF _Toc72318336 \h 58 Appendix 2: Proposed Criteria for Assessing and Prioritizing GHG Measures  PAGEREF _Toc72318343 \h 63  1. Sector Baseline and Cumulative GHG Reduction The Building, Facilities, and Manufacturing baseline includes the following GHG emissions from the following source categories in the residential, commercial, and industrial sectors: Carbon dioxide emissions from direct combustion of fossil fuels. Direct combustion of fossil fuels refers to coal, oil and natural gas that is combusted on-site in the residential, commercial, and industrial sector. Methane and nitrous oxide emissions from combustion of fossil fuels at stationary sources (including electricity sector as well as residential, commercial and industrial sectors. Note: Includes methane and nitrous oxide emissions from wood combustion, but emissions from other biomass is not included. Methane emissions from the transmission and distribution of natural gas within the State of Maine. Methane is emitted during oil and gas production, storage, transportation, and distribution. Since there is no oil or gas production in Maine, emissions occur solely through gas transmission and distribution. Major CH4 emission sources from gas transmission pipelines include chronic leaks, fugitive emissions from compressors, compressor exhaust, vents, and pneumatic devices; for gas distribution pipelines, major CH4 emission sources include chronic leaks, meters, regulators and mishaps. Sulfur hexafluoride (SF6) emissions from electric power transmission and distribution systems within the State of Maine. High global warming potential gas (HFC, PFC, and SF6) emissions from substitutes for ozone-depleting substances. High GWP gas emissions result from the following applications: refrigeration & A/C, solvents, foams, aerosols, fire extinguishing. Carbon dioxide emissions from cement production process. CO2 emissions associated with fossil fuel combustion at cement facilities are not accounted for here. They are captured under CO2 emissions from direct combustion of fossil fuels. High GWP gas emissions from semiconductor manufacture. GHG emissions not accounted for in this baseline include: CO2 emissions from wood burning. Biomass is considered to be carbon neutral. Methane emissions from LNG ships cooling gas in ports. GHG emissions from waste treatment plants. These emissions are accounted for in the Solid Waste baseline. The sources of the inventory (1990-2000) emission estimates and the method and sources used to develop the baseline (2000-2020) emissions forecast for these source categories are provided in the Table 1. Table 1: Methodology and Sources for BFM Inventory and BaselineSource CategoryInventory (1990-2000)Baseline (2000-2020)Carbon Dioxide Emissions from Direct Combustion of Fossil FuelsEIA State Energy Data Report, which is reported by fuel type, by sector and collected from the State of Maine. Default values from the US EPA were used to convert fuel use into CO2 emissions.The forecast is based on the New England regional growth forecast for different fuel types by sector from EIAs Annual Energy Outlook 2004. Regional fuel consumption is allocated to Maine as follows: Residential sector: Fuel consumption is allocated using the ratio of Maines population growth to that of the NE region. The Charles Colgan, University of Southern Maine, medium range population forecast was used for Maine based on agreement of Stakeholder Advisory Group. Commercial sector: Fuel consumption is allocated using the ratio of Maines Gross State Product (GSP) to that of the NE region. The Charles Colgan, University of Southern Maine, medium range GSP forecast was used for Maine based on agreement of Stakeholder Advisory Group. Industrial Sector: Hold industrial growth flat at 2000 levels. This was agreed to by the Stakeholder Advisory Group. Default values from the US EPA are used to convert fuel use into CO2 emissionsMethane and nitrous oxide emissions from combustion of fossil fuels in all sectorsEPA Inventory ToolDefault values from the US EPA are used to convert fuel use into CH4 and N2O emissions.Methane emissions from the transmission and distribution of natural gas within the State of Maine. EPA Inventory ToolForecast assumes construction of one new LNG plant in 2010 as per the BFM WG.Sulfur hexafluoride (SF6) emissions from electric power transmission and distribution systems within the State of Maine.EPA Inventory ToolForecast based on historical emission trends. Source CategoryInventory (1990-2000)Baseline (2000-2020)High global warming potential gas (HFC, PFC, and SF6) emissions from substitutes for ozone-depleting substances.EPA Inventory ToolForecast assumes that Maines share of national ODS replacement emissions remains constant over time (based on ratio in the year 2000). Data on national emissions from ODS substitutes are estimated using a complex vintaging model which accounts for equipment turnover, leak rates, charge size, and initial ODS. These estimates are reported in the following document: USEPA, 2000. Estimates of US Emissions from High GWP Gases and the Cost of Reductions. Carbon dioxide emissions from cement production process. Data from Dragon ProductsForecast from Dragon ProductsHigh GWP gas emissions from semiconductor manufacture.Data from National and FairchildForecast based on historical emissions trends. BFM GHG Emissions Inventory and Baseline  K MTCO2E= Thousand metric tonnes of carbon dioxide equivalent emissions BFM GHG Emissions Inventory and Baseline by Sector  Process emissions= See next chart for detail FFC = Fossil fuel combustion K MTCO2E= Thousand metric tonnes of carbon dioxide equivalent emissions GHG Emissions from Industrial Process Gases  K MTCO2E= Thousand metric tonnes of carbon dioxide equivalent emissions 2. Summary Table of Sector Priority Options   3. Descriptions and Assumptions For Each Sector Option Measure:BFM 1.1 Energy Efficiency Appliance Standards  Sector: Residential, Commercial Policy Description: For appliances not covered under federal standards, the state can set minimum levels of efficiency for specific appliances. BAU Policy/Program: Legislation proposed, never passed. LED kits for traffic signals have been purchased to address traffic lights in Maine. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Set minimum efficiency standards for the following products: ProductSavings in 2010 (GWh or BBtu)Savings in 2020 (GWH or BBtu)Unit Savings (kWh or therm)Lifetime (years)Incremental Cost * ($) Dry type transformers6.919.316.6kWh/kva303/kvaCommercial refrigerators & freezers1.22430929Exit signs3.710.32232520Traffic signals1.73.14311085Torchiere lamps66.9121.72881015Set-Top boxes96.796.7 5 Unit heaters (therm savings)63.8179.726819276Commercial Clothes Washers1.21.81978200Source: ENE, Communication with M Stoddard; NEEP, 2003. The estimates in this table are in the NEEP report Energy Efficiency Standards: A Low Cost, High Leverage Policy for Northeast States. Appendix A of the report cites sources. * Note: Incremental costs are difficult to calculate because there is almost always a range of products with varying prices. All of these appliances can be regulated by the state, and do not require a federal waiver. GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2E)<0.01<0.01Indirect Emission Reductions (000 MTCO2E)*84.3128.7Total Emission Reductions (000 MTCO2E)84.3128.7Cost Effectiveness ($/MTCO2E)-82Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. CO2 emission savings estimates will differ from NEEP analysis because the electricity emission factor differs. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 2.1 Improved Residential Building Energy Codes  Sector: Residential Policy Description: Require new buildings or substantial reconstruction to meet the most recent energy code efficiency/performance standards established by the International Code Council and ASHRAE 6.2 ventilation standards, with effective enforcement, as recommended through the PUC process. BAU Policy/Program: Residential: State-developed code, less stringent than 1992 MEC, mandatory statewide; Voluntary IECC 2000 Maine has held four meetings of the Building Code Working Group starting in March 2003. The purpose of this group is to 1.) Survey stakeholders and determine where they stand on the issues 2.) Determine which code, NFPA or ICC, to adopt 3.) Make recommendations on how the chosen code is going to be implemented and enforced. (Source: www.bcap-energy.org) DPUC Working Group also. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Residential building energy codes are updated every 3 years and adopted by ME 18 months thereafter. Each building energy code revision achieves the same percentage of savings. Includes BFM 2.2 Training and Enforcement of Building Energy Codes Data NeedAssumptionSourceEnergy Savings Fossil Fuel savings per home (IECC 2000 compared to current construction in ME)10%David Weitz, Building Code Assistance Project for Maine PUC public hearing on Nov 25th 2003# of new residential buildings built each year6,760 single family homes Maine-specific data from National Association of Home Builders# of residential buildings that comply with new codes70%EstimatedCostsIncreased cost for enforcement $150,000 EstimateIncreased cost for training$200,000Based on programs in Texas and New Hampshire that provide training on residential codes and produce and distribute video recordings Potential Barriers/Issues: Avoid conflict with building rehab code GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)24.265.2Indirect Emission Reductions (000 MTCO2)*0.61.6Total Emission Reductions (000 MTCO2)24.764.1Cost Effectiveness ($/MTCO2)-35Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 2.3 Voluntary Green Building Design Standards Sector: Residential Policy Description: Promote voluntary high efficiency and sustainable building standards that builders can follow (e.g., Energy Star, LEED residential building standard as it becomes available, Built GreenTM). In addition to an energy efficiency requirement, require procurement standard for concrete containing up to 20% recovered mineral component. Also promote energy efficiency mortgages, energy improvement mortgages and location efficient mortgages. BAU Policy/Program: None Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionSource# of new homes built in ME6,760 single family homes Maine-specific data from National Association of Home Builders# of new homes meeting higher standard10% per yearEstimated Savings between Energy Star and standard construction (based on proposed RES code for Maine)15%EPA; based on definition of Energy Star Home (ENERGY STAR qualified homes are independently verified to be at least 30% more energy efficient than homes built to the 1993 national Model Energy Code or 15% more efficient than state energy code, whichever is more rigorous.)Incremental Cost between Energy Star and standard construction $2100/home Connecticut Light and Power Note: Price varies depending on house size, prevailing construction practices, availability of equipment, etc. For example, an Energy Star labeled home can actually be less expensive to build than its non-Energy Star counterpart (i.e., good insulation, high performance windows, etc. can lower the heating and cooling loads so much that smaller and less expensive HVAC equipment and more compact duct runs are able to be installed, saving significant first costs.)Residential Concrete Consumption380,000 to 400,000 cubic yards in 2003 PCA Portland Cement and Construction Forecast for Maine.Incremental Cost between concrete and slab0Dragon Products - Slag is comparable in cost to cement Owning (i.e., mortgage amortization) and operating (i.e., utility bills) an Energy Star labeled home costs less than owning and operating a non-Energy Star labeled home. This is because we do not recommend energy-saving measures unless the amortized cost of implementing those measures is less than the utility bill savings resulting from them. Source: EPA Energy Star Homes GHG emission savings are estimated assuming BFM 2.1 (Improved Residential Building Codes) is implemented. A procurement standard for concrete containing a minimum of 20% slag would result in a CO2 savings of over 20,000 short tons per year of direct and indirect emissions (18,144 metric tons). GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)23.427.8Indirect Emission Reductions (000 MTCO2)*0.10.2Total Emission Reductions (000 MTCO2)23.4528.0Cost Effectiveness ($/MTCO2)-45Direct Emissions: On-site emission reductions Indirect Emissions: Emission reductions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. Note: Emission reductions from a procurement standard for concrete are included in the table under direct emissions reductions eventhough reductions will have both direct and indirect impact. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 2.6 Efficient Use of Oil and Gas: Home Heating Sector: Residential Policy Description: Provide incentives for EE retrofits or upgrades for home heating equipment, hot water heaters, programmable thermostats BAU Policy/Program: LIHEAP, WAP, REACH Central Heating Improvement (CHIP) Programs for low-income residents. (Energy Advisors, LLC, 2003) Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionSourcesOil Furnaces/Boilers# operating at or below 60% AFUE 15%Expert judgementEnergy savings associated with replacing 60% AFUE furnace with Energy Star oil Furnace (90% AFUE) 24.25 MMBTU/furnaceCalculated based on 20% efficiency increase and avg 80.8 MMBTU/household for space heating Estimated cost of conventional oil furnace $2000EPAEstimated cost of Energy Star oil furnace$2700Consumer Energy Council of America (2001) Market penetration2%EstimatedNatural Gas Furnaces# operating at or below 60% AFUE 15%Expert JudgementEnergy savings associated with replacing 60% AFUE furnace with Energy Star natural gas furnace (90% AFUE)25.25 MMBTU/furnaceCalculated based on 20% efficiency increase and avg 80.8 MMBTU/household for space heatingEstimated cost of conventional natural gas furnace$2000EPA Energy StarEstimated cost of Energy Star natural gas furnace$2500EPA Energy StarMarket Penetration2%EstimatedIntegrated hot water heater Average energy factor of stand alone water heater more than 10 years old50%USDOE Building Technologies ProgramEnergy factor of new integrated hot water heater88%USDOE Building Technologies ProgramCost of installation900USDOE Building Technologies ProgramMarket Penetration2% of oil heated homes; 2% natural gas heated homesAssume install with furnace replacementSet-back ThermostatEnergy Savings per year5%EPA (Ranges from 5 to 30%)- Energy Star requires 2 programs with 4 settings eachCost  $195EPA (product cost ranges from 40-120; installation charge of 25-75)Market Penetration2% of oil heated homes; 2% natural gas heated homesAssume install Energy Star Programmable Thermostat with boiler replacementPercentage of Homes by Heating Fuel TypeOil80%US Census, 2000Natural Gas8%US Census, 2000Electricity4%US Census, 2000Number of homes in ME518,200US Census, 2000 Note: This option may potentially be funded through BFM 5.5 Subgroup (Pattie Aho, Jamie Py, Michael Stoddard, Brian Hubbell) considering measure Maine Oil Dealers Recommended Improvements to Oil Heat Systems Recommended ImprovmentEstimated SavingsHeating System Tune2 to 10%Reduced firing rate or nozzle reduction 6 to 10%Reduced temperature of circulating water/furnace air5 to 12 %Pipe and duct insulation 5 to 10%Flame retention head burner 15 to 20%New high-efficiency hot water boiler 20 to 40%New high-efficiency warm air furnace 20 to 40%Source: Maine Oil Dealers web site- www.meoil.com . GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)29.339.1Indirect Emission Reductions (000 MTCO2)*0.00.0Total Emission Reductions (000 MTCO2)29.339.1Cost Effectiveness ($/MTCO2)-6Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 2.7 Fuel Switching Sector: Residential Policy Description: Under development by subgroup (Jamie Py, Michael Stoddard, Dudley Greeley) BAU Policy/Program: None Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)Indirect Emission Reductions (000 MTCO2)*Total Emission Reductions (000 MTCO2)Cost Effectiveness ($/MTCO2)Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.1 Energy standards for State and State-funded New Construction/Renovations  Sector: Commercial and Institutional Policy Description: New construction as well as major renovations of all building projects that receive some state funding (state facilities, local schools, etc.) are required to be at least 20% more efficient than required by the then current state energy codes. (Savings achieved under this measure will be included in the baseline. It applies to both State-owned and State-leased buildings.) BAU Policy/Program: The State of Maine has recently passed two pieces of legislation regarding this issue: 1) The Development of optimal energy efficiency in state-funded construction and substantial renovations (requires buildings be designed and built to standards of energy efficiency that are always at least 20% higher than the minimum energy standards required by the then current state energy codes; see Title 5, Chapter 153, Section 1764-A), and 2) Construction of schools (amends rules on construction of new schools to require that all construction proposals must be based on the most energy and environmentally efficient designs per the statute). Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionsSourcesTotal sq ft of state-funded buildings built each year204,750Maine Bureau of General ServicesTotal sq ft of state-funded buildings renovated 131,250Maine Bureau of General ServicesTotal sq ft of schools built each year384,750Maine Bureau of General ServicesRequirement by State of Maine for energy savings compared to minimum energy standards required by current state energy codes20%Maine EOIncremental cost$3/sq ftKatz et al. (2003)  estimates 3-5 $/sq ft. D Baston thinks it should be more toward the lower range like $2/sq ft based on NJ study GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)1.84.8Indirect Emission Reductions (000 MTCO2)*5.315.0Total Emission Reductions (000 MTCO2)7.119.9Cost Effectiveness ($/MTCO2)-12Direct Emissions: On-site emission reductions Indirect Emissions: Emission reductions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.2 Promote Energy Efficient Buildings  Sector: Commercial Policy Description: Encourage privately financed new construction and renovation to be high performance buildings by certifying to 20% above existing code. BAU Policy/Program: None Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedAssumptionSourceNumber of commercial buildings built each year2,184CT data scaled to ME. CMP does not have better data. Texas A&M University estimate of 3,650 nonresidential building permits issued in Maine in 1995. No better data available at this time.Market penetration2%Estimate based on penetration rate of similar programs implemented elsewhere (CT)Energy Savings compared with then current code20%As per recommendationAverage energy intensity for non-governmental buildings Electricity13.4 kWh/sq ftEIA CBECS (1999) Natural Gas43.1 cu ft/sq ftEIA CBECS (1999) Oil0.18 gallons/sq ftEIA CBECS (1999)Incremental Cost$3/sq ftKatz et al. (2003) estimates 3-5 $/sq ft. D Baston thinks it should be more toward the lower range like $2/sq ft based on NJ study Note: This option may potentially be funded through BFM 5.1 GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)1.43.7Indirect Emission Reductions (000 MTCO2)*2.97.5Total Emission Reductions (000 MTCO2)4.311.3Cost Effectiveness ($/MTCO2)-19Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.3 Implement the most cost-effective energy savings in State Buildings Sector: Government Agency Buildings Policy Description: Implement most cost-effective energy savings in state buildings by taking advantage of existing mechanisms (see BAU Policy/Program). BAU Policy/Program: 25% energy reduction goal by 2010 (relative to 1998 baseline) added to Energy Conservation Building Act for Public Buildings. This legislation established a pilot program to seek to achieve that level of energy savings in ten facilities of over 40,000 square feet. Under the pilot program, energy savings are to be achieved through performance contracts with energy service companies. LD845 Climate Change: This bill requires new sources of greenhouse gases to be reported to the Department of Environmental Protection. It also requires the department to create an inventory of greenhouse gas emissions associated with state-owned facilities and state-funded programs and to create a plan for reducing those emissions. The Maine Public Utilities Commission and the Maine Department of Administrative and Financial Services (DAFS) developed a Memorandum of Understanding (MOU) to improve the energy efficiency of State buildings. The program will fund renovations that enhance electrical efficiency. It will also fund an energy survey of all state buildings to identify opportunities for energy efficiency. Under the MOU, DAFS identifies potential projects and Efficiency Maine reviews the proposed projects for cost effectiveness. If the projects are cost effective, they are developed and managed by DAFS and financed through mechanism through Maine PUC to DAS. Pilot program for biodiesel. Existing mechanisms including: 1. Third party financing of energy efficiency improvements in existing state buildings/facilities PL 1985, ch. 128 5M.R.S.A. 1767 Any department or agency of the State, subject to approval of the Bureau of Public Improvements, may enter into an agreement with a private party such as an energy service or 3rd-party financing company for the design, installation, operation, maintenance and financing of energy conservation improvements at state facilities. [1985, c. 128 (new).] Any department or agency of the State, subject to approval by the Bureau of Public Improvements, at the termination of the agreement with the private party pursuant to this section, may acquire, operate and maintain the improvement, may renew the agreement with the private party or may make an agreement with another private party to operate and maintain the improvement. [1985, c. 128 (new).] All agreements made with private parties as contemplated in this section shall be subject to review by a subcommittee of the joint standing committee of the Legislature having jurisdiction over appropriations and financial affairs. [1985, c. 128 (new).] 2. Third party financing of energy efficiency improvements PL 1999, ch. 35, 5 M.R.S.A. 1770 1. Goal. The Legislature finds it is in the best interests of the State to significantly reduce its energy consumption to the extent possible without interfering with other goals, plans and policies of the State. The energy reduction goal, referred to in this section as the "goal," for facilities owned by the State is, by 2010, a 25% reduction in energy consumption relative to baseline consumption in 1998, as long as the achievement of the goal is accomplished in a manner that: A. Is consistent with all applicable laws; and [1999, c. 735, 1 (new).] B. Does not interfere with other goals, plans or policies of the State. [1999, c. 735, 1 (new).] For purposes of this subsection, "facilities owned by the State" includes all facilities that consume energy and that are owned by the legislative, judicial or executive branches of government, any state department, agency or authority, the University of Maine System or the Maine Community College System. 3. Improvements in efficiency to new buildings - Consider life cycle energy costs in state owned buildings 5 M.R.S.A. 1762 Consider life cycle energy costs in state leased builidngs 5 M.R.S.A. 1763. No public improvement, as defined in this chapter, public school facility or other building or addition constructed or substantially renovated in whole or in part with public funds or using public loan guarantees, with an area in excess of 5,000 square feet, may be constructed without having secured from the designer a proper evaluation of life-cycle costs, as computed by a qualified architect or engineer. The requirements of this section with respect to substantial renovation shall pertain only to that portion of the building being renovated. Construction shall proceed only upon disclosing, for the design chosen, the life-cycle costs as determined in section 1764 and the capitalization of the initial construction costs of the facility or building. The life-cycle costs shall be a primary consideration in the selection of the design. As a minimum, the design shall meet the energy efficiency building performance standards promulgated by the Department of Economic and Community Development. 4. Improvements in efficiency to new buildings - Include an energy-use target that esceeds by at least 20% the energy efficiency standards in effect for commercial and institutional buildings 5 M.R.S.A. 1764-A The Bureau of General Services, in consultation with the Energy Resources Council and the Public Utilities Commission, shall by rule require that all planning and design for the construction of new or substantially renovated state-owned or state-leased buildings and buildings built with state funds, including buildings funded though state bonds or the Maine Municipal Bond Bank: A. Involve consideration of architectural designs and energy systems that show the greatest net benefit over the life of the building by minimizing long-term energy and operating costs; [2003, c. 497, 1 (new); 5 (aff).] B. Include an energy-use target that exceeds by at least 20% the energy efficiency standards in effect for commercial and institutional buildings pursuant to Title 10, section 1415-D; and [2003, c. 497, 1 (new); 5 (aff).] C. Include a life-cycle cost analysis that explicitly considers cost and benefits over a minimum of 30 years and that explicitly includes the public health and environmental benefits associated with energy-efficient building design and construction, to the extent they can be reasonably quantified. [2003, c. 497, 1 (new); 5 (aff).] Rules adopted pursuant to this section apply to all new or substantially renovated state-owned or state-leased buildings and buildings built with state funds, including buildings funded through state bonds or the Maine Municipal Bond Bank, regardless of whether the planning and design for construction is subject to approval by the department. Rules adopted pursuant to this section may provide for exemptions, waivers or other appropriate consideration for buildings with little or no energy usage, such as unheated sheds or warehouses. The Bureau of General Services shall adopt rules pursuant to this section by July 1, 2004. Rules adopted pursuant to this section are routine technical rules as defined in Title 5, chapter 375, subchapter 2-A Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionSourceState Agency Fuel Consumption Electricity127,384 MWhEnergy Advisors, LLC Natural Gas90,025 MMBTUEstimated using government to commercial sector electricity share Oil643,062 MMBTUEstimated using government to commercial sector electricity shareGovernment building share of commercial sector electricity consumption3%Energy Advisors, LLCReduction in state energy use by 20107%1% per year above current regulation; Savings associated with regulation accounted for in baselineReduction in state energy use by 202017%1% per year above current regulation; Savings associated with regulation accounted for in baselineCosts $0.3/kWhBased on Maine Efficiency results from State Building Program; Consistent with cost estimates in Optimal Study GHG Emission and Cost per tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)3.59.1Indirect Emission Reductions (000 MTCO2)*4.412.0Total Emission Reductions (000 MTCO2)7.921Cost Effectiveness ($/MTCO2)-37Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.5 Load Management  Sector: Commercial Policy Description: Sub-group working on language (Tony, Mike, Denis, Dick) BAU Policy/Program: None Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)0.00.0Indirect Emission Reductions (000 MTCO2)*Total Emission Reductions (000 MTCO2)Cost Effectiveness ($/MTCO2)Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.6 Green Campus Initiatives Sector: Commercial Policy Description: Promote a Green Campus Initiative with all Maine Colleges, Universities, Private/Secondary Schools with Campus to minimize environmental impact. BAU Policy/Program: Currently underway (USM, Others) Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionSourceDuration of Proposed Program5 yearsEstimatedMarket Size27 colleges and universities with 52,441 student enrollmentDepartment of EducationAverage $/student for energy$265/StudentBased on University of Southern Maine% of Market enrolled in program each year5%EstimatedAverage electricity savings15%Communication with Clean Air-Cool PlanetAverage fossil fuel reductions20%Communication with Clean Air-Cool PlanetCost$0.3/kWhBased on Maine Efficiency results from State Building Program; Consistent with cost estimates in Optimal Study Note: This option may potentially be funded through BFM 5.2 GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)7.720.6Indirect Emission Reductions (000 MTCO2)*3.39.3Total Emission Reductions (000 MTCO2)11.029.8Cost Effectiveness ($/MTCO2)-18Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.7 Improve Enforcement of Commercial Energy Codes  Sector: Commercial Policy Description: Improve enforcement of the requirement that new construction and substantial renovations of commercial buildings meet the most recent energy code efficiency/performance standards established by the International Code Council. BAU Policy/Program: Commercial: ASHRAE/IESNA 90.1-2001, mandatory statewide (includes all institutional buildings such as schools and hospitals); can COM check -EZ to show compliance (Most up to date). Legislature must pass "housekeeping legislation" whenever the State wants to update to the most recent building energy codes. (Located in MRSA Title 10, Part 3, Chapt. 214, Section 1415-D: Mandatory standards for commercial and institutional construction.) Bill being held DPUC-7 Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Upgrades to commercial building code included in baseline. Data NeedAssumptionSourceAnnual Commercial Savings Oil savings 5%EERE Natural gas savings 5%EERE Electricity savings 5%EERENew commercial buildings built each year2,184CT data scaled to ME. CMP does not have better data. Texas A&M University estimate of 3,650 nonresidential building permits issued in Maine in 1995. No better data availableNumber of commercial buildings that comply with new codes if enforced15%D. Baston estimates compliance will move from 70 to 85%CostsCost for enforcement$150,000Based on Residential Code EstimatesCost for training$200,000Based on Residential Code Estimates Potential Barriers/Issues: Avoid conflict with Rehab code GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)2.67.0Indirect Emission Reductions (000 MTCO2)*9.326.6Total Emission Reductions (000 MTCO2)12.033.6Cost Effectiveness ($/MTCO2)-61Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.8 Improve Electrical Efficiency in Commercial Buildings  Sector: Commercial Policy Description: Improve electrical efficiency in commercial buildings BAU Policy/Program: Efficiency Maine C&I Program, available to businesses with > 50 FTEs, includes three components (1) business practices training, (2) information and end-use training opportunities, and (3) financial grants to assist in the purchase of EE equipment. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Optimal Energy Study for Public Advocate looks at electrical energy savings potential and cost for the following commercial and institutional sector measures: Efficient Lighting Efficient Air Conditioning Building System Controls Enhanced Envelope Measures Efficient Appliances High Efficiency Motors Variable Frequency Drives High Efficiency Refrigerators Estimates for MWh of savings by year and measure are shown in the table below. These estimates exclude the MWh savings estimated from these measures under the current Efficiency Maine funding (which are assumed to be in the baseline).  Source: Optimal Energy Study Note: This option may be potentially funded through BFM 5.2 GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)0.00.0Indirect Emission Reductions (000 MTCO2)*181.9250.8Total Emission Reductions (000 MTCO2)181.9250.8Cost Effectiveness ($/MTCO2)-139Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 3.9 Procurement Preference  Sector: Buildings Facilities and Manufacturing Policy Description: Specify procurement preference for concrete and concrete products that contain a minimum of 20% of ground granulated blast furnace slag for publicly funded projects, as long as this is cost-effective. BAU Policy/Program: ASTM specifies standards for the inclusion of slag to concrete. MDOT specifications allow for the inclusion of slag in concrete. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Slag is derived from a by-product of the steel industry. It is processed and grounds to meet strict specifications and sold as a cementitious (cement-like) product. Slag has cementitious properties and can be used to offset a portion of the cement used in concrete mixtures. How much can be offset is dependent on season (winter/summer), set requirements and other factors. 550 lbs cement is used per yard of concrete (average) Approximately, 880,000 cubic yards of concrete for all applications in Maine in 2003. (based on data from USGS for Cement consumption) Approximately 315,000 to 350,000 cubic yards of concrete used for public buildings, structures, and transportation. Use of 20% slag as a replacement for cement yields savings of approximately 18,000 to 20,000 tons of CO2 per year. This is a conservative estimate based on slag. Use of other recycled mineral components such as fly ash or silica fume may be different. Slag usage may be higher (30 to 40%) and result in higher CO2 savings. Concrete consumption includes commercial, residential, industrial and government consumption. Transportation accounts for approximately 215,650 cubic yards (PCA Construction Forecast, February 2004). Approximately 22,000 tons of slag was used in concrete in 2003 for all uses. Slag is comparable in cost to cement. Availability may be limited. May require a capital investment of additional silo storage for some suppliers. EPA procurement guidelines for recovered materials: HYPERLINK "http://www.access.gpo.gov/nara/cfr/waisidx_03/40cfr247_03.html"http://www.access.gpo.gov/nara/cfr/waisidx_03/40cfr247_03.html GHG Emission and Cost Estimates: 20102020Direct Emission Reductions (000 MTCO2)1818Indirect Emission Reductions (000 MTCO2)* 0 0Total Emission Reductions (000 MTCO2)1818Cost Effectiveness ($/MTCO2)0Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.1 Promote Electrical Efficiency Measures in the Industrial Sector Sector: Industrial Policy Description: Offer financial incentive/rebates for EE improvements taken at ME industries. Can include: Tax incentives, such as Investment Tax Credit or shortened depreciation periods for installation of energy efficient systems and equipment Creative financing mechanisms Rebates Grants Technical assistance Training Interruptible power programs Real time pricing BAU Policy/Program: Efficiency Maine has established a new Commercial and Industrial Program for Maine businesses that provides a combination of services, including energy efficiency information and training, business practice assistance, and direct financial incentives in the form of grants. The components of the program are designed to encourage businesses to adopt energy efficient business practices, to include consideration of energy costs and energy efficiency in their business decisions, and to purchase and install energy efficient products. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Note: This option may potentially be funded through BFM 5.2 Optimal Energy Study for Public Advocate looks at electrical energy savings potential and cost for the following industrial sector measures: Efficient Lighting Efficient Ventilation and Cooling Efficient Process Controls Building System Controls Variable Frequency Drives High Efficiency Air Compressors Estimates for MWh of savings by year and measure are shown in the table below. These estimates exclude the MWh savings estimated from these measures under the current Efficiency Maine funding (which are assumed to be in the baseline).  Source: Optimal Energy Study GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)00Indirect Emission Reductions (000 MTCO2)*156.5207.1Total Emission Reductions (000 MTCO2)156.5207.1Cost Effectiveness ($/MTCO2)-30Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.2 Participate in Voluntary Industry-Government and/or Industry Partnerships  Sector: Commercial, Industrial Policy Description: Recognize voluntary programs and reward actions in the appropriate sectors. While some programs already exist at the national level, there may also be an opportunity to develop additional programs in Maine. BAU Policy/Program: Several programs already exist at the national level: EPA Climate Leaders, DOE Industries of the Future (Maine Industries of the Future currently includes pulp and paper, secondary wood, and metals industry), EPA Energy Star Benchmarking Program, DOE Rebuild America; Maine STEP-UP program, Carbon Challenge, Climate Vision Clean Air-Cool Planet program highlights include MOUs with Star supermarket, Timberland company, Toms of Maine, Oakhurst Dairy, Poland Spring, York hospital Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: DOEs suggestions for expanding Maine participation in IOF: Include agriculture and plastics and potentially welding Additional publicity The Maine legislature might consider creating a mini state grant program that could provide funds to Maine businesses for feasibility studies to determine whether to adopt new energy-efficient technologies. Discuss energy and EE technologies as part of technology cluster project The Maine Smart Tracks for Exceptional Performers and Upward Performers, or STEP-UP, Program offers recognition and other incentives to businesses interested in implementing sustainable practices. Alan Auto (Portland), Bath Iron Works (Bath), Fairchild Semiconductor (South Portland), Interface Fabrics Group (Guilford), Moss, Inc. (Belfast), NorDx (Scarborough) and Poland Springs Bottling Company (Hollis). College of the Atlantic (Bar Harbor), CYRO Industries (Sanford), National Semiconductor of Maine (South Portland) and Naturally Potatoes (Mars Hill). Quantification assumes subset of companies in Maine representing 10% of GHG emissions reduce GHG emissions by 15% in 2010 and 25% in 2020 compared to 2000 levels. (Based on commitments under EPA Climate Leaders Program; e.g., Interface and International Paper have pledged similar reductions as those assumed for 2010) Industrial sector direct emissions in 2000 = 2,300,000 Metric Tonnes GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)34.557.5Indirect Emission Reductions (000 MTCO2)*00Total Emission Reductions (000 MTCO2)34.557.5Cost Effectiveness ($/MTCO2)NEDirect Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.3 Leak Reduction Programs Sector: Industrial Policy Description: Reduce methane leaks from natural gas systems, reduce HFC leaks from refrigeration, motor vehicle air conditioning, etc. BAU Policy/Program: Existing federal programs to reduce methane leaks from natural gas pipelines, SF6 from electricity substations Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedsAssumptionSourceIncreased participation in EPA Natural Gas StarNAParticipation in SF6 Electrical Utility100% of Maine Electric utilities are participating currently in EPAs SF6 reduction program. No additional savings achievable.CMPODS substitute emissions from refrigeration and A/C67%US EPA based on national statisticsHFC emissions from stationary refrigeration40%USEPA based on national statisticsMarket penetration5% per yearEstimatedHFC leak reduction potential for stationary refrigerants5%US EPANA: Data not available at this time GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)1.29.0Indirect Emission Reductions (000 MTCO2)*N/AN/ATotal Emission Reductions (000 MTCO2)1.29.0Cost Effectiveness ($/MTCO2)1.2Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.4 Substitution of High GWP Gases Sector: Industrial Policy Description: Substituting other gases for high GWP gases is a viable option as long as environmental, health, safety, and performance requirements can be met. BAU Policy/Program: None. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Alternative Refrigerants Ammonia. Ammonia, primarily used in water cooled chillers, has excellent thermodynamic properties and can be used in many types of systems. However, it must be used carefully, because it is toxic and slightly flammable. Building and fire codes restrict the use of ammonia in the urban areas of the United States and many other countries. (EPA, 2001) Hydrocarbons. Hydrocarbons have thermodynamic properties that make them good refrigerants; however, their high flammability causes concern for safety. Hydrocarbon refrigerant use is generally restricted by U.S. safety codes, with the exception of industrial refrigeration(EPA, 2001). Carbon Dioxide. Carbon dioxide has been investigated for use primarily in mobile air-conditioning systems and refrigerated transport. (EPA, 2001) Alternative Solvent Fluids In electronics, metal, and some precision cleaning end uses, alternative organic solvents with lower GWPs are being manufactured and integrated into the industry. Some of these solvents, such as HFCs, HFEs, hydrocarbons, alcohols, volatile methyl siloxanes, brominated solvents, and non-ODS chlorinated solvents, can be used as alternatives to PFC/PFPEs, CFCs, and HCFCs. Non-HFC Blowing Agents Hydrocarbons (HC) Hydrocarbons such as propane and butane are alternatives to HFCs. HCs are inexpensive and have lower GWP impacts relative to HFCs. However, key technical issues associated with hydrocarbons are: flammability, VOCx, and performance. Liquid Carbon Dioxide (LCD). Foams blown with CO2 might suffer from lower thermal conductivity, lower dimensional stability, and higher density versus HCFC blown foams. To overcome these limitations, CO2 can be blended with hydrocarbons or HFCs. Water-Blown (in situ) Carbon Dioxide (CO2/water). During manufacturing, no ODP or high GWP gases are emitted, and there are limited health and safety risks during processing. However, foams produced using CO2/water are subject to the same performance limitations discussed for LCD-blown foams Lower-GWP HFC Substitution. Manufactures can reduce their emissions on a carbon basis by switching from a blowing agent with a high GWP to one with a lower GWP, but any associated energy penalties must also be considered. GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)NENEIndirect Emission Reductions (000 MTCO2)*NENETotal Emission Reductions (000 MTCO2)NENECost Effectiveness ($/MTCO2)NENEDirect Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.5 Industrial ecology/by-product synergy Sector: Industrial Policy Description: Two recommendations are as follows: (1) Amend Liability Clause as per recommendation of Beneficial Use Stakeholder Group: Although beneficial use and recycling of solid waste rank at the top of Maines waste management hierarchy, these activities have languished in recent years. This slackening in beneficial use activity can be attributed, in part, to the mere stigma assigned to the term solid waste and the fear of potential end users and handlers of the liability that might be imposed, even years later, despite their lawful reuse of the waste. The proposed bill developed by the Maine Beneficial Use Stakeholder Group was intended to promote and encourage beneficial use and recycling of solid waste by providing liability protection under relevant State laws to persons who engage in such activities in accordance with a permit or exemption: An Act to Promote Beneficial Reuse of Solid Waste Be it enacted by the People of the State of Maine as follows: Sec. 1. 38 M.R.S.A. 1304, Sub- 18 is enacted to read: Liability protection for beneficial use. Any person who is engaged in a beneficial use activity or generates, handles or uses a solid waste that has been licensed or exempted from licensing under the Departments beneficial use or recycling regulations may not be deemed a responsible party and is not subject to Department orders or other enforcement proceedings or otherwise responsible under Sections 568; 570; 1304, subsection 12; 1318-A; 1319-J; 1361 to 1367 or 1371 for the use of the solid waste, provided such person has used the waste or conducted the activity in accordance with a Department license or exemption and relevant Department laws, as applicable. (2) Continue funding pilot project with the University of Maine to establish a Recycled Resource Center BAU Policy/Program: Beneficial Use is Maines Industrial Ecology program and is regulated under Chapter 418. Agronomic Use of waste materials is a similar program and is not discussed here. DEP convened a multi-year stakeholder process with the task of reviewing issues related to beneficial use with the overall goal of increasing beneficial use in Maine. The stakeholders group funded a pilot project through the University of Maine to compile data related to beneficial use of certain materials. This site resides at  HYPERLINK "http://useit.umeciv.maine.edu" http://useit.umeciv.maine.edu. The group also developed educational and presentational materials for trade shows and other presentations. Finally, the group proposed legislation that was based on the successful brownfields program (VRAP) that called for limiting the liability of the material suppliers, the material processor and the ultimate beneficial user of the material. CURRENT PROJECTS Waste Derived Fuels Tire Derived Fuel (TDF) Tires from Maines tire dumps were shredded using bond money and then distributed for beneficial use. About half of Maines waste pile tires went to TDF the other half went to geotechnical applications. One passenger tire is the equivalent of 280,000 to 300,000 BTUs. Tire chips are 10-12,000 BTUs/lbs. Approximately 1.2 million new waste tires are generated in Maine every year. Three facilities in Maine are burning TDF. These are chipped tires or tire shreds. Whole tires are advantageous in that they do not require additional energy to process the tire to chips. Construction and Demo Debris as Fuel (demo chips) Demo chips consist of ground wood wastes including pallet wood, painted wood, etc. It excludes pressure treated. BTU values are approximately 7,500 BTUs/lbs. This is higher than biomass as the wood waste typically has lower moisture content. Several plants in Maine are burning demo chips in biomass boilers. Gates Formed Fiber Waste This is felted non-woven polyester fiber. The material has a BTU value of approximately 15,000 BTUs/lbs. One plant in Maine is burning a small amount of this waste. Pioneer Plastics Pioneer produces laminate trimmings as well as a fine dust. The trimmings have a BTU value of 8,200 BTU/Lbs. These have been burned for fuel at one facility, but the project has been discontinued. Biodiesel from used fryolater oil - Current operated on a small scale at the Chewonki Foundation, there is an effort to evaluate the potential for a commercial scale operation in Maine. Methane Gas from Landfills One potential pilot project. Pulp & paper sludge - Large quantities of primary and secondary sludge are generated by pulp & paper facilities. Most ends up landfilled or burned as a low heat value fuel. Methane collection from landfills is cost-prohibitive due to the low permeability. Technologies to ferment the sludge and collect the resulting ethanol are being developed by the Lynd Group at Dartmouth College in NH. The ethanol can be marketed as biomass-derived fuel and the amount of sludge being landfilled would be significantly reduced. Other processes are being developed to take residual biomass streams from the pulp & paper industry to create high heat value fuels or other useful products. Raw Material Substitution Dragon Cement Dragon takes a variety of materials for use in the cement manufacturing process. Lime mud is a by-product of the paper making process and is an alternative calcium source to limestone. (Use of lime mud reduces direct process GHG emissions from Dragons cement manufacture.) Fly ash from coal-fired power plants supplies aluminum and silica as well as BTU value. Spent foundry sand is from Enterprise Foundry in Lewiston and supplies silica. Oil Contaminated Soil from leaking tanks and spills provides a silica replacement. Fly Ash, Ground Granulated Blast Furnace Slag and Silica Fume as a cement replacement in concrete. Masonite in Lisbon Falls used wood chips soaked in black liquor as part of their process although this may have been discontinued. Waste Utilization Stabilized Dredge Spoils as structural fill dredge spoils may be stabilized with cement or cement kiln dust (a waste product) to reduce the moisture content and to increase the workability of the material. Use on site replaces use of virgin fill material. Scrap Tires for geotechnical applications - Tires are also used in many geotechnical applications and replace virgin materials in use as lightweight fill. Tires projects completed in Maine include the new Portland Jetport interchange and the Brunswick-Topsham bypass. Commercial Paving and Recycling - Commercial produces a variety of products using recycled waste material. Crushed concrete is used as a recycled aggregate, Asphalt shingles as bituminous asphalt mix, contaminated soils are treated and used as recycled soil products International Paper has produced a flowable fill (low strength concrete mixture) from ash, paper mill waste and lime wastes. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Estimates of potential not available at this time. GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)NENEIndirect Emission Reductions (000 MTCO2)*NENETotal Emission Reductions (000 MTCO2)NENECost Effectiveness ($/MTCO2)NENEDirect Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.6 Negotiated Agreements Sector: Industrial Policy Description: Include GHG reduction projects as acceptable Supplemental Environmental Project (SEP). A SEP is an environmentally beneficial project that a company performs in exchange for a reduction in penalty associated with violation of an environmental regulation or statute, but it is in addition to the actions necessary to bring the company into compliance. BAU Policy/Program: LD845 Climate Change: This bill requires new sources of greenhouse gases to be reported to the Department of Environmental Protection. The bill also requires the department to enter into carbon emission reduction agreements with nonprofit organizations and businesses. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: EPA has set out eight categories of projects that can be acceptable SEPs. To qualify, a SEP must fit into at least one of the categories. The following six seem to be the categories where reducing GHGs can be worked in. (Original numbering from the EPA webpage has been preserved.): 2. Pollution Prevention: These SEPs involve changes so that the company no longer generates some form of pollution. For example, a company may make its operation more efficient so that it avoids making a hazardous waste along with its product. 3. Pollution Reduction: These SEPs reduce the amount and/or danger presented by some form of pollution, often by providing better treatment and disposal of the pollutant. 4. Environmental Restoration and Protection: These SEPs improve the condition of the land, air or water in the area damaged by the violation. For example, by purchasing land or developing conservation programs for the land, a company could protect a source of drinking water. 6. Assessments and Audits: A violating company may agree to examine its operations to determine if it is causing any other pollution problems or can run its operations better to avoid violations in the future. These audits go well beyond standard business practice. [Detailed energy audits would fit this and reduce GHGs.] 7. Environmental Compliance Promotion: These are SEPs in which an alleged violator provides training or technical support to other members of the regulated community to achieve, or go beyond, compliance with applicable environmental requirements. For example, the violator may train other companies on how to comply with the law. [Violators could train other companies on ways to reduce GHGs. Could include training similar companies on ways to reduce high GWP process gases.] 8. Other Types of Projects: Other acceptable SEPs would be those that have environment merit but do not fit within the categories listed above. These types of projects must be fully consistent with all other provisions of the SEP Policy and be approved by EPA. GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)NENEIndirect Emission Reductions (000 MTCO2)*NENETotal Emission Reductions (000 MTCO2)NENECost Effectiveness ($/MTCO2)NENEDirect Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.7 Encourage Combined Heat and Power/ EW 1.8 Sector: Electricity Generation Policy Description: Reduce barriers and implement programs to increase CHP in the state. CHP is a high efficiency method of DG that utilizes both the steam (or heat) and electricity produced by the electricity generating process, rather than just the electricity. Efficiency can be 2-3 times that of systems not utilizing the heat produced. (For example, an older stand-alone fossil fuel utility powerplant will have a thermal efficiency of about 30%. A new gas turbine,also a stand-alone, will have a thermal efficiency of 50%. CHP, regardless of fuel, will enjoy a thermal eficiency of 85 to 90%.) BAU Policy/Program: (CHP units of at least 70% efficiency )are included as eligible efficient sources under the state Renewable Resource Portfolio Requirement (for a description of this state program see Renewable Portfolio Standards [RPS] measure above). Data Needs, Sources & Assumptions for GHG Savings and Cost Estimates: The promotion of CHP is a fundamental issue for our society. CHP is not a tool or a technology; CHP results only from the watershed determination that the foundation of an efficient electric grid is the most complete use of the energy potential of all thermal generation. Development of our full CHP potential will produce a grid with more distributed and less centralized generation, generation less dependent on economies of scale, more shared or district heating in communities and industrial parks, less transmission investment and greater grid stability and reliability . Several policies can promote CHP in Maine: Protection of the Consumer Right to Self-Generate Behind the Meter: Maine law recognizes self-generation, but the right is threatened in several ways. First, some have attempted to require consumers that self-generate to pay transmission charges to utilities even though the electricity generated never uses the utility grid. This proposal was defeated in New England but approved in the West and Midwest. The risk of such a policy is a disincentive to CHP, as such utility charges would penalize CHP and make it uneconomic. Maines PUC, Public Advocate and other public officials must be required to oppose such policies in Maine, New England and at the federal level. Second, others have proposed that those who self-generate pay excessively for backup power from the grid used during scheduled and unscheduled maintenance. Backup power rates should be based on the probability of the need for backup service, and should not be designed to discourage CHP and require greater grid use, as has often been the case. The PUC should be required to ensure backup rates do not discourage CHP. Third, Maines PUC and other public officials should be required to oppose exit fees in any form. Exit fees were proposed during electric restructuring to discourage the use of CHP and to provide guaranteed payments to utilities for service not taken by larger customers. Customers should pay only those costs they agree to assume, or which are for service actually taken. Other devices, such as exit fees, are inconsistent with our regulatory model for utilities and strongly discourage the movement to more efficient consumption or conservation, such as CHP. The NEPOOL Minimum Grid Interconnection Standard Must be Maintained. After a long and expensive legal battle waged by Champion International, a Maine CHP located in Bucksport ( now International Paper), the Federal Regulatory Energy Commission (FERC), adopted a simple and easy policy for allowing the interconnection of powerplants to the electric grid. The policy is now used in most regions of the nation, but is opposed by some large electric utilities, including some in New England. The policy allows interconnection without expanding the grid beyond what is necessary to ensure its reliabillity and stability for consumers and generators. Repeal of the policy essentially would require owners of CHP (and other generators) which export to the grid at all to build additions to the grid that are unnescessary. The policy not only helps CHP, but also lowers electricity costs. Permitting Must Recognize the Benefits of CHP. Present federal and state air permitting policies do not contain recognition of the societal benefits of CHP. For example, most air analyses focus on the amount and kind of pollutants emitted by a source, rather than also considering the efficiency of the use of fuel . Clearly the efficiency of CHP lowers total societal pollution. But, since CHP meets both electricity and heat needs at a given location, CHP requires more emissions at the site than if only heat or electricity were produced. This increment of emissions stresses the permitting system when, if both heat and power were considered, it would not. The effect of current permitting policies is to encourage the centralized generation of electricity, usually at far lower efficiencies than when CHP is used, because the incremental electricity production requires no permitting, unless an entirely new plant is required. The granting of emissions credits may also be useful. A more positive step, however, is to incorporate the efficiency of energy use (and the benefits of CHP) into all state and local permitting, so as to provide an incentive to new building construction and air system renovation to consider CHP. This can only occur by use of a broader societal perspective on total energy use. The current disaggregation of land , air and water use from energy use is unrealistic and harmful to the environment.) 4) Financial Incentives--- could be any of many available for other purposes. Policy Options for CHP Development: This analysis does not identify which option would be used to obtain the required level of CHP penetration. There are several methods that can be employed. Interconnection standards are technical guidelines governing the linking of the CHP unit to the grid. In some cases they may be difficult to meet, and may thus serve as barriers to new CHP. Developing uniform and consistent interconnection standards can allow units to be connected to the electricity grid faster and reduce the cost of interconnection. Stand-by fees are charged by utility companies to provide back-up or stand-by electricity in the event of power loss or to supplement generation. The cost of ensuring the availability of stand-by power can be as high as the cost of buying the electricity directly from the grid. Lowering standby fees can therefore promote CHP development. Other methods include the awarding of emission reduction credits to CHP units for emission reductions realized as a result of their high efficiency; consumer choice, which allows electricity customers to purchase CHP-generated electricity; and direct subsidies, provided to CHP units on a per unit, efficiency or energy production basis, which can improve the depreciation allowance for CHP equipment. Several efforts to increase generation from CHP are already under way. The RAP model rule, developed in 2002, seeks to establish uniform and appropriate emission standards for new distributed generation (DG) and to streamline the permitting process (see  HYPERLINK "http://www.eea-inc.com/rrdb/DGRegProject/modelrule.html" http://www.eea-inc.com/rrdb/DGRegProject/modelrule.html). The Distributed Generation Interconnection Collaborative issued a report titled Proposed Uniform Standards for Interconnecting Distributed Generation in Massachusetts which describes a starting point for DG interconnection of various sized units located on both radial and secondary network systems within Massachusetts (see  HYPERLINK "http://dg.raabassociates.org/Articles/DG%20Report.Final.doc" http://dg.raabassociates.org/Articles/DG%20Report.Final.doc). Massachusetts has also issued D.T.E. 02-38. requesting comments on four issues: (1) whether current distribution company interconnection standards and procedures in Massachusetts act as a barrier to the installation of distributed generation; (2) whether current distribution company standby service tariffs act as a barrier to the installation of distributed generation; (3) what the role of distributed generation is with respect to the provision of service by Massachusetts distribution companies; (4) what other issues are appropriate for the Department to consider (see  HYPERLINK "http://www.state.ma.us/dpu/electric/02-38/103order.pdf" http://www.state.ma.us/dpu/electric/02-38/103order.pdf and  HYPERLINK "http://www.state.ma.us/dpu/electric/02-38/81necacom.pdf" http://www.state.ma.us/dpu/electric/02-38/81necacom.pdf). (BUXTON comments on Modeling: I have no way to quarrel with these numbers, but I wonder how dependent they are on perceptions of the path of distributed generation technology. For example, if it becomes possible for the McDonalds to CHP with natural gas, as has frequently been discussed, that takes the usage down to the 200 kw level and opens apartment houses, smaller office buildings, etc, up for CHP. By 2008, we ought to be capable of this. I would estimate 30,000 200kw customers in Maine at about 1000 mw of consumption. Dennis may have better estimates. Also, CHP will develop from large to small, and will be lumpy, like all capitial investment)). For modeling analysis, following assumptions were made: Total potential capacity (MW) provided by Energy and Environmental Analysis (EEA). This potential represents the technical potential only, and does not evaluate economic potential. EEA has emphasized that this is an extremely rough estimate. However, a study by Onsite Sycom (The Market and Technical Potential for Combined Heat and Power in the Commercial/ Institutional Sector) estimates the total commercial CHP technical potential in Maine to be 300 MW. The EEA estimate of 411 MW is reasonably close to this value, so the total potential estimated by EEA has been used. Only a portion of the technical potential will be economically viable. It has therefore been assumed that only 20% of the total technical potential could be developed, and a level of 130 MW of additional CHP penetration was modeled with NEMS. 82 MW would be in the commercial sector, 46 MW in the industrial sector. Policy begins in 2008, with the full 130 MW online in that year and continuing through 2020. All CHP units assumed to be fired by natural gas Fuel input of stand-alone boilers replaced assumed to be 1/2 gas, 1/2 oil (Btu basis). Oil is assumed to be distillate in commercial sector and residual in industrial. Efficiency of stand-alone boilers assumed to be 80% CHP units assumed to have following characteristics: Economic SectorParameterCommercialIndustrialSystem assumption200 kW micro-turbine5MW combustion turbineElectrical efficiency36%28%Heat efficiencyFraction of fuel energy input27%45%Capital cost$/kW$1,415$966Source : Assumptions to NEMS model, Annual Energy Outlook 2004 GHG Emission and Cost per Tonne Estimates: Under development by ESW WG 20102020Direct Emission Reductions (000 MTCO2)Indirect Emission Reductions (000 MTCO2)*Total Emission Reductions (000 MTCO2)Cost Effectiveness ($/MTCO2)Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on NEMs Model Results 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 4.8 Specify ASTM specification C150 for portland cement Sector: Manufacturing Policy Description: Specify ASTM (American Society for Testing and Materials ) specification C150 for Portland cement rather than AASHTO (American Association of State Highway Officials). BAU Policy or Program: MEDOT currently specifies AASHTO specifications. ASTM is the American Society for Testing and Materials, the largest voluntary standard development system in the world. The manufacturing of portland cement is outlined in ASTM standard C150. ASTM C 150 was recently amended to allow for the inter-grinding of up to 5% limestone in Portland cement while maintaining all performance specifications. The amended specification lowers the overall carbon intensity of the portland cement. This standard is consistent with standards already in place in Mexico and Canada. EPA supports this revised standard due to the potential for CO2 reductions. The ASTM standards Board is currently working to harmonize the revised standard with existing AASHTO (American Association of State Highway Officials) standards, which do not recognize this amended standard. Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates Approximately 450,000 tonnes of cement were produced in Maine in 2003. If Maine and the surrounding states adopt the ASTM standard C 150, up to 5% limestone can be introduced in the final grind of cement as long as all other performance standards are met. Based on experiences from Canada and European cement manufacturers, a conservative figure that 2.5% limestone addition is possible. This results in a reduction of approximately 10,000 tonnes of CO2.(reported in metric tonnes) Reduction in emissions is directly related to cement production. Revise estimates based on cement production in 2010 and 2020. There are no cost implications for adopting the revised standard. The Working Group reviewed a two-page letter from the U.S. EPA to the ASTM Committee C01 on Cement. The letter supports the modification of ASTM standard C 150 allowing up to 5% limestone intergrading in portland cement. GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)1010Indirect Emission Reductions (000 MTCO2)*Total Emission Reductions (000 MTCO2)1010Cost Effectiveness ($/MTCO2)<0Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 5.2 Increase Public Benefit Fund Sector: Residential, Commercial, Industrial Policy Description: Increase surcharge on electricity and/or fossil fuel provides funding for EE measures BAU Policy/Program: Efficiency Maine is funded by electricity consumers and administered by the Maine Public Utilities Commission (current funding level ~$16 million per year); no sunset date Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedAssumptionSourceElectricityFunds collected beyond BAU 2005-2020$ 15 MillionEstimated2003 Efficiency Maine Program Costs$2,921,000Efficiency Maine Annual Report 20032003 Annual Participant Benefits$370,150Efficiency Maine Annual Report 2003Savings (1st year)4,837 t CO2Efficiency Maine Annual Report 2003Lifetime of savings15 yearsCT C&LM Fund Do not include in total in total as it potentially double counts savings estimated in BFM 3.7 and BFM 4.1 GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)0.00.0Indirect Emission Reductions (000 MTCO2)*2571Total Emission Reductions (000 MTCO2)2571Cost Effectiveness ($/MTCO2)-55Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 5.4 Incentives for Green Power Purchase Sector: Residential, Commercial and Institutional, Industrial Policy Description: To promote and encourage the deployment of renewable energy resources in the region (beyond RPS requirements) by Maine businesses, municipalities, institutions, and households, (1) Maine ratepayers should have the choice of determining where their power comes from through a green offering(s). (2) Government should have requirement (3) PV buy down program. BAU Policy/Program: Maine Renewable Energy is now offering on a limited basis to residential and small commercial customers in either the CMP or Bangor Hydro service territories electricity that is 100% renewable / 100% from Maine; Maine Technologies Institute coordinates Renewable Resource Fund with the State Planning Office- $70,000 for R&D at colleges, pilot program; Government lead by example- purchase 50% electricity from RE Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: ESW WG has evaluated and quantified government requirement for green power purchases (policy option 2 above). 50% by 2010; 60% by 2020. ESW WG has evaluated and quantified rooftop residential solar (potential overlap with policy option 3 above, which is under development and not included in quantification below). Data NeedAssumptionSourcesGreen power purchase goal in 20101% of total residential electricity demandAverage participation nationally in green pricing programs (NREL, Status of Green Power Marketing in US)Green power purchase goal in 20203% of total residential electricity demandLeading programs achieved 3-5% participation (NREL)Maine residential electricity demand in 20104,810,000 MWhProjection based on Tellus Modeling Maine residential electricity demand in 20205,620,000 MWhProjection based on Tellus ModelingIncremental cost of green pricing program0.029$/kWhAverage price premium for utility green pricing programs is 0.029$/kWh (NREL). Includes cost of marketing program. Maine Renewable Energy estimates incremental cost for RE to be 0.015$/kWh.  GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)00Indirect Emission Reductions (000 MTCO2)*22.7485.1Total Emission Reductions (000 MTCO2)22.7485.1Cost Effectiveness ($/MTCO2)57Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation * Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Measure:BFM 5.5 Natural Gas and Oil Conservation Fund Policy Description: Establish surcharge on fossil fuel to provide funding for EE measures BAU Policy/Program: None Data Needs, Sources & Assumptions for Preliminary GHG Savings and Cost Estimates: Data NeedAssumptionSourceNatural GasFunds collected beyond BAU 2005-2020$0.6 MillionAssumes 7 cents per MCFAverage Savings per $ for first year1MCF/ $29VT gas program- Is there a better source (D Baston); NJ about half as cost effective (DB). Lifetime of savings15 yearsCT C&LM FundOilFunds collected beyond BAU 2005-2020$4.5 MillionAssumes 1cent per gallon chargeSavings per $164 barrels/$VT gas program- Is there a better source (D Baston)Lifetime of Savings15 yearsCT C&LM Fund GHG Emission and Cost per Tonne Estimates: 20102020Direct Emission Reductions (000 MTCO2)76.6204.4Indirect Emission Reductions (000 MTCO2)*00Total Emission Reductions (000 MTCO2)76.6204.4Cost Effectiveness ($/MTCO2)-34Direct Emissions: On-site emission reductions Indirect Emissions: Emissions at the site of electricity generation Indirect Emissions are based on a projection of the marginal NEPOOL emission factor. 000 MTCO2 = Thousand metric tonnes of carbon dioxide equivalent MTCO2= Metric tonnes of carbon dioxide equivalent Appendix 1: Potential Building, Facilities, and Manufacturing GHG Reduction Opportunities Edited 12-17-03 The following notation was used in the table below: *Options that were popular choices in other states, potentially high Maine GHG reduction options, or both (originally denoted by CCAP, reviewed by Stakeholders *? For *d options to which at least one member of the Stakeholder Advisory Group expressed uncertainty about it being important in Maine *! For options not previously marked with a *, which at least one member of the Stakeholder Advisory Group thought should be a priority Some additional comments from stakeholders are highlighted in the list Status Legend: NI: Not Identified for pursuit by Working Group or Stakeholder Advisory Group, but included in CCAPs original list of GHG mitigation options D: Dropped. Originally selected for evaluation and consideration by Stakeholder Group or Working Group, but dropped by the Working Group. C: Combined with another option (list which option) R: Referred to another working group (name working group) F: Future technology. Technology not commercially viable at present, but flagged for monitoring and possible future pursuit. WG: Working Group proposing this option Residential Sector GHG Reduction Opportunities1Improve Energy Efficiency (EE) of AppliancesStatus1.1*Energy Efficiency Appliance Standards - For appliances not covered under federal standards, the state can set minimum levels of efficiency for specific appliances.WG1.2Tax Incentives for EE AppliancesNI1.3Discounts/Rebates on Energy Star ProductsNI1.4Contractor Education: Proper sizing of HVAC Proper sizing of air ducts and other components of heating, ventilation and air conditioning systems can significantly reduce the size and energy requirements of furnaces and air conditioning units.NI1.5Consumer Education: Selection, Alternate appliance choices Educate consumers about the lifetime savings achieved over appliance lifetime by appliances that consume less energy.NI1.6Bulk Purchasing Program - Bulk procurement can reduce the cost of energy efficient appliances or renewable technologies.NI1.7Promote Appliance RecyclingNI1.7.aAppliance recycling pick-up program Program to collect and recycle old residential appliances, rather than send them to junkyards/landfills.NI1.7.bReduce secondary market for used appliances Create incentives for residential customers to discard old appliances when new ones are purchased, rather than selling the old appliance or running both the new and old appliance (e.g. air conditioners or refrigerators). Other states have offered a bounty rebate to residents who buy a new window AC unit and turn in the old unit to the state for disposal.NI2Incentives to Technology Providers2.1R&DNI2.2Incentives to manufacturers (regional) Cross cutting for all GHG sectorsNI3Improve EE and SustainableEEE Design of Buildings3.1*Improved Building Codes (revisit every 3 years) - Require buildings to meet the most recent Energy Code efficiency/performance standards established by the International Code Council. (Avoid conflict with Rehab code)WG3.2*!Training (builders, code officials, architects etc.) and Enforcement of Building CodesC with 3.13.3EPA Energy Star Homes - This program provides rebates for the purchase of newly constructed homes meeting higher efficiency standards established by the U.S. EPA and DOE Energy Star Program.C with 3.43.4*!Voluntary Green Building Design Standards Create voluntary high efficiency and sustainable building standards (recycled material, low VOC content, low embodied energy construction materials, etc.) that builders can follow. Buildings meeting the standards can have a seal of approval or other type of recognition (e.g., LEED).WG3.5Mandatory "Green" Standards for New Construction/ RenovationsNI3.6*Energy Efficiency Mortgages - Energy Efficient Mortgages allow purchasers to borrow a larger mortgage when purchasing an Energy Star home. Energy Improvement Mortgages allow owners to borrow money for energy efficiency improvements on their homes, or to upgrade the energy efficiency of a home before purchasing.C with 3.43.7Financial incentives for contractors, builders, homeownersNI3.8Increased marketing of existing programsNI3.9White Roofs and Rooftop Gardens Reflect sunlight and shade roofs to reduce air conditioning energy requirements.NI3.10Landscaping Well-planned landscaping with trees for shade and evergreens/hedges to block wind reduce a buildings heating and cooling requirements.NI3.11*Education to homeowners Educate homeowners energy efficiency and sustainable design retrofits, renovations and new construction options.R: Education WG4Improve Energy Management4.1Energy Audits Assess a homes energy use, and areas where energy is being wasted.NI4.1.aWeatherizationNI4.1.bBlower door testingNI4.2Training of Building OperatorsNI4.3Efficient Use of Oil and GasWG4.3.aImprove building envelope windows, insulation, etc.NI4.3.b*Heating WG4.3.cDHWWG4.3.dCookingNI4.3.ePumping well waterNI4.3.fFuel Switching to less carbon-intensive fuelsWG4.4Efficient Use of ElectricityNI4.5*Educate residents/ public/ children R Education WG4.5.aMarketing ProgramsNI4.5.bIntroduce in School Curriculum NI4.6Advanced metering Provides real or near real-time electricity consumption data. Combined with time-of-use rates, creates incentive for residential electricity load management and conservation.NI4.7Load Management With advanced meters and time-of-use rates in place, residential electricity customers can manage their energy use to reduce consumption during peak daytime rates, thereby saving money.WG4.8Time-of-Use (TOU) Rates Time-of-use rates for electricity, a market mechanism charging customers more during daytime peak periods and less during off-peak periods. Provides incentive for residential customers to save money by shifting some energy consuming tasks (such as laundry) to off-peak periods.NISee also "Comprehensive Programs" Commercial Sector GHG Reduction Opportunities1Improve Energy Efficiency (EE) of Equipment and Appliances1.1*EE Equipment and Appliance Standards - For appliances not covered under federal standards, the state can set minimum levels of efficiency for specific appliances.WG1.2Tax Incentives for EE Equipment and AppliancesNI1.3Discounts on Energy Star ProductsNI1.4Bulk Purchasing Program - Bulk procurement can reduce the cost of energy efficient appliances or renewable technologies.NI2Energy Efficient Buildings2.1*Improved Building Codes - Require buildings to meet the most recent Energy Code efficiency/performance standards established by the International Code Council.WG2.2Training (Builders, Code Officials, Architects etc.) and Enforcement of Building CodesC: 2.12.3Voluntary Green Building Design Standards WG2.4*"Green" Standards for New Construction/ RenovationsWG2.4.aMandatory standards for state buildings Construction and renovations receiving any state funding should meet higher energy efficiency/performance standards.WG2.4.bMandatory standards for schools - Construction and renovations receiving any state funding should meet higher energy efficiency/performance standards.NI2.5*Incentive payment for green buildings Provide incentives for privately financed new construction and renovation to meet higher energy efficiency performance standards than standard construction.C: 2.32.6White Roofs and Rooftop Gardens Designed to reduce solar heat gain and thereby reduce air conditioning electricity needs.NI2.7*State-wide EE Goals and Reporting for Government Buildings - A program to encourage measurement and tracking of energy consumption, strategic planning and benchmarking against other buildings.WG3Improve Energy Management3.1Energy AuditsNI3.2Building RecommisioningNI3.3Training of Building Operators - Training building operators in how to maximize the efficiency of their buildings will decrease energy use if operators apply what they learned.NI3.4Efficient Use of Oil and GasNI3.4.aBuilding Shell Windows, insulation, etc.NI3.4.bHeatingNI3.4.cDHWNI3.5Efficient Use of ElectricityWG3.5.aLightingWG3.5.bA/CWG3.5.cVentilationWG3.5.dPumps/motorsWG3.6*Shared Savings Program for Government Agencies - Allows a state agency to keep a portion of the energy savings realized when the agency makes energy efficiency improvements to a building. C:2.73.7Fuel Switching to less carbon-intensive fuels such as natural gas, biodiesel, etc.WG3.8*Load ManagementWG3.9*!Green campus initiative already begun.WG4Promote RecyclingNISee also "Comprehensive Programs" Industrial Sector GHG Reduction Opportunities1Industrial Energy Efficiency (EE), Management, and Conservation 1.1Efficient Use of Oil and GasNI1.1.aBoilersNI1.1.bUpgrade to steam systemNI1.1.cProcess-specific equipmentNI1.1.dBuilding Envelope Windows, insulation, etc.C:2.11.2Efficient Use of ElectricityWG1.2.aPumpsWG1.2.bMotorsWG1.2.cLightingWG1.2.dCoolingWG1.3Optimization of Compressed air systemsC: 1.21.4EE process improvementsC: 1.21.5Shut-it off program (curtailment) Financial incentive for industrial electricity customers to cut demand during peak/emergency demand periods for the local utility. NI1.6Energy Management TrainingNI1.7R&D of new technologiesNI1.8*Financial incentives - Offer incentive rebates for energy efficiency improvements.C: 1.21.9EducationR: Education WG2Reduction in Process Gases2.1*Participate in Voluntary Industry-Government PartnershipsWG2.2*Leak Reduction ProgramsWG2.3Process Changes/ OptimizationNI2.4Capture, Recovery and Recycling of Process GasesC: 2.22.5New EquipmentNI2.6*!Substitution of High GWP Gases Substitute high global warming potential (GWP) gases with appropriate substitutes depending on application (e.g., CO2, ammonia).WG3Supply Side Measures3.1*Encourage Combined Heat and Power Combined heat and power is a high efficiency method of distributed generation that utilizes both the steam and electricity produced from the electricity generating process, rather than just the electricity. Efficiency can be 2-3 times that of systems not utilizing the heat produced.WG (R: ESW WG)4Other programs4.1*!Industrial ecology/ by-product synergy Programs to link the by-products from one industry with use as the feedstock for other industries.WG4.2*!Negotiated Agreements - To promote GHG reductions in particular sectors, a state government may enter into direct voluntary or negotiated agreements with industries or industrial sectors. Legislation requires (need to develop metrics)WG4.3Cap and TradeNISee also Comprehensive ProgramsComprehensive Programs for Residential, Commercial and Industrial Sectors GHG Reduction 1.1Mandatory Reporting of Fuel Use, GHG EmissionsNI1.2State-wide Energy Efficiency/GHG Emission Reduction GoalsC:2.71.3*Government Agency Requirements and GoalsC: 2.71.4*Public Benefit Funds Funds created by a surcharge on electricity, natural gas or oil sales that are used to fund demand side energy efficiency and conservation programs.WG1.5Negotiated AgreementsWG1.6Environmentally Friendly ProcurementWG1.7Small-source aggregationNI1.8Supply-Side Measures1.8.aNet-metering - Allows the electric meters of customers with generating facilities to turn backwards when the generators are producing energy in excess of the customers' demand, enables customers to use their own generation to offset their consumption over a billing period.NI1.8.bEncourage Green Power PurchasesWG1.8.cIncentives for Renewable Energy ApplicationsC: 1.8b Appendix 2: Proposed Criteria for Assessing and Prioritizing GHG Measures PRIMARY CRITERIAIndicators that would be assessed by CCAP to the extent possible using the best available data for each option.GHG Impact Total annual GHGs reduced in relevant target years in carbon equivalents. This is typically expressed as an average annual level of projected MMTCE reduction in a given year beyond baseline emissions. GHG impacts must be quantified in order to aggregate measures toward a numerical target.Cost-Effectiveness Direct net cost divided by the GHG impact (expressed in dollars per metric ton of carbon equivalent) and is typically expressed in a given year as an average annual value over the life of the action. Costs may be expressed as a range.SECONDARY CRITERIAIndicators that would be assessed by CCAP, the Working Groups, or both when relevant for a particular option using best available data. These impacts may not be readily quantifiable.Ancillary Environmental Impacts Environmental impacts other than GHG emissions reductions, including public health and ecosystem impacts from changes in air quality or other environmental indicators. These impacts may not be readily quantifiable.Ancillary Economic Impacts Economic impacts other than direct costs or benefits of GHG reduction actions (e.g. economic development, cost savings for other actions). These impacts may not be readily quantifiable.Equity Effects Measure disproportionately affects a population, sector or a region of the state or affects the states competitive position relative to other states. These impacts may not be readily quantifiable.Public and Political Support/Concern Expected support and or concern from the general public and from policymakers. These impacts may not be readily quantifiable.Feasibility Ease of implementation and administration by implementing parties. These impacts may not be readily quantifiable.Compatibility Measure reinforces or enhances the effectiveness of other policy programs, or is required for other measures to work. These impacts may not be readily quantifiable.Transferability to Other States/NationallyEase of duplication of measure in other states and or national and international policies. These impacts may not be readily quantifiable.  Estimates of thousands of tonnes in 2020.  Estimate appears to be conservative based on 18% reduction cited in Xenergy (2001), Impact Analysis of the Massachusetts 1998 Energy Code Revisions  Costs and Financial Benefits of Green Buildings: A Report to Californias Sustainable Building Task Force (October 2003). Costs based on 33 green buildings compared to conventional designs for those buildings. The average premium was slightly less than 2% or $3-5/sq ft.  Costs and Financial Benefits of Green Buildings: A Report to Californias Sustainable Building Task Force (October 2003). Costs based on 33 green buildings compared to conventional designs for those buildings. The average premium was slightly less than 2% or $3-5/sq ft. 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