City of Easthampton - Anaerobic Digestion Feasibility Study Prepared For: City of Easthampton, Massachusetts May 2014 Prepared with Support from the Tighe&Bond Executive Summary Executive Summary With recent changes to the market for solar PV and the slower adoption of land-based wind in New England, Massachusetts has placed an increasing focus on anaerobic digestion (AD) as a critical piece of the state’s clean energy future. Anaerobic digestion is a biological process during which microorganisms break down organic material in the absence of oxygen to produce biogas containing a high percentage of methane. The methane can then be used to generate electricity and/or heat. Depending on the type of digester and feedstock, additional useful outputs may be produced, such as a soil amendment and compost. AD technology qualifies as a renewable energy technology through the state’s RPS, and various agencies and offices including the Department of Environmental Protection (MassDEP), the Massachusetts Clean Energy Center (MassCEC), and Department of Energy Resources (DOER) have established funding programs to help advance the deployment of AD projects in the state. In addition to its clean energy benefits, there are other drivers for AD related to solid waste and materials management. MassDEP’s 2010-2020 Massachusetts Solid Waste Master Plan calls for the aggressive diversion of food waste and other organic materials from the solid waste stream. The state’s pending Organic Waste Ban (scheduled to take effect October 2014), will prohibit the disposal of commercially generated organic materials at landfills. With the increased opportunities for AD in Massachusetts, the City of Easthampton has been approached by numerous private developers with interest in developing an AD project at the City’s Ferry Street wastewater treatment facility (WWTF). An AD project at the WWTF has the potential to result in numerous benefits for the City, including: Generation of local, renewable energy Avoided cost savings for electricity and heat at the WWTF Avoided cost savings for wastewater sludge disposal and dewatering Potential revenue through lease payments Beneficial use of source-separated organic materials that formerly were disposed of at landfills To better understand the technical and economic issues associated with such a project, the City engaged with Tighe & Bond to conduct a comprehensive Feasibility Study of the project. The Feasibility Study has been funded with a grant from the MassCEC, through its Organics to Energy (OtE) program. The Feasibility Study involves an evaluation of technical, site development, economic, and community impact factors to determine the feasibility of the project. Based on the results of the project, the City may proceed to the next steps of development, which would include further design, permitting, procurement, and construction of the project. Project Site The project site is located at the Easthampton Wastewater Treatment Facility (WWTF), situated at 10 Gosselin Drive off of Ferry Street in Easthampton, MA. The project site consists of two main parcels owned by the City. The WWTF is located on the east parcel, No. 130/24. The area for potential project development is located in the west parcel, No. 130/23, and is an open cleared area of approximately 2.6 acres. The site is currently used for materials storage by the Easthampton Department of Public Works (DPW). The parcel City of Easthampton - Anaerobic Digestion Feasibility Study E-1 Tighe&Bond Executive Summary was formerly associated with the adjoining J. P. Stevens Mills textiles complex, which operated a textile production mill in the late 1920s until 1960s. The site was used for disposal of materials from the former textiles production operations until approximately 1969. Since that time, the site has been inactive. Summary of Evaluations The Feasibility Study report documents the data, assumptions, calculations and research used to support conclusions on technical and economic feasibility of an AD project at the Easthampton WWTF. For the purpose of this Executive Summary, the key findings and recommendations are provided below. Site Assessment The first step of the project involved an assessment of existing site conditions to determine any potential constraints or fatal flaws to the siting of an AD project. The analysis is based on a review of desktop and online information, plans and information provided by the City of Easthampton, and information collected on-site. The Site Assessment also includes a review of the site’s existing electrical and thermal demand, and an assessment of existing electrical, heating, and other infrastructure. The results of the detailed site assessment are provided in Sections 2 and 3 of the Feasibility Study. Physical Characteristics: The facility is accessed from Gosselin Drive from Ferry Street just east of the Easthampton Water Tower. The WWTF and operations consumes a majority of the parcel. The area to the west of the WWTF is currently being used by Sewer Department as a stockpile and staging area for current projects. According to City personal, this is the preferred location for a potential AD facility. The site is very suitable for the proposed project, since the site is already engaged in wastewater treatment activities. Environmental and Cultural Resources: There are several jurisdictional inland wetlands and streams located adjacent to and within the project site that are protected pursuant to the Massachusetts Wetlands Protection Act (WPA). The western portion of the project parcel contains area of Estimated or Priority Habitat as mapped by the Natural Heritage and Endangered Species Program (NHESP). Additionally, Potential Vernal Pools are located approximately 250 feet north of the site at the Manhan River and 400 feet southeast of the site. Though there are mapped habitat and vernal pool areas proximate to the site, work is not proposed to occur within these areas and the project is not anticipated to cause any adverse impacts to environmental resources. There are no buildings at the WWTF property or in the immediate vicinity of the project site which are identified as historic properties. However, the project site is located proximate to areas that are included in MHC’s Inventory of the Historic and Archaeological Assets of the Commonwealth which contain MHC Historic Inventoried properties. The entire project is located within a MassDEP Wellhead Protection Area. Zoning: The project site, parcel No. 130/23, is located in the Mixed Use / Mill Industrial (MI) district. Additionally, the site is partially located within mapped 100- year flood plain (flood zone AE), however, it is anticipated that the AD project can be sited outside of the portion of the parcel within the floodplain district. As the entire site is located within a MassDEP approved Wellhead Protection Area (Zone II), it is anticipated that the project will need to comply with the Wellhead Protection related land use restrictions of 310 CMR 22.21(2). Furthermore, since well number City of Easthampton - Anaerobic Digestion Feasibility Study E-2 Tighe&Bond Executive Summary 1087000-07G is approximately less than one-half mile from the project site, it is assumed that the Aquifer Protection District restrictions may apply. Permitting: A summary of anticipated permitting obligations at the local, state, and federal level is provided in the Feasibility Study report. In addition to approvals that may be needed with regard to regulated resource areas at the site, this section of the report also addresses potential permits that may be required regarding air quality, wastewater, and composting and conversion. It is not anticipated that environmental or local land use permitting will be a challenge for the project. Facility Energy Profile: The WWTF currently consumes approximately 690,000 kWh of electricity per year. Over this period, the average monthly consumption was approximately 57,700 kWh with a minimum and maximum monthly consumption of approximately 49,990 kWh and 66,750 kWh respectively. The heating load at the WWTF is currently met through the use of number two fuel oil, liquefied propane (LP) and electric heaters. The total annual heating load of the facility is approximately 840 MMBTU with an average monthly heating load is 70 MMBTU. It was estimated that the WWTP uses 6,000 gallons of number 2 fuel oil and 4,000 gallons of propane annually. Electrical Interconnection: The project site is located within a Western Massachusetts Electric (WMECo) service area, in the West Central Massachusetts ISO-NE load zone. As part of this Feasibility Study, a Distributed Generation Pre- Application form was submitted to WMECo to obtain information about the proposed point of interconnection. Based on information provided by WMECo, power at the WWTF and proposed site is provided by the Gunn Substation located at the intersection of Line and Phelps Street. The voltage at the substation is 22.9kV and is constructed as four wire multi-grounded neutral Wye. The circuit supplying the WWTF is 15A5. It is presumed for purposes of analysis that the ultimate transformer will require a capacity of 1,000 kVA; the existing transformer has a capacity of 300 kVA. Net metering would be accomplished at the secondary voltage of 277/480 Volt four wire Wye. The overall conclusion of the site assessment is that no fatal flaws related to environmental resources, site conditions, or on-site infrastructure exist that would prevent the development of an AD project at the site. The site is very suitable for the proposed project, since the site is already engaged in wastewater treatment activities. However, further coordination with WMECo should occur to determine the scope of a future impact study or whether system upgrades are required to accommodate the proposed project. Feedstock Assessment The Feasibility Study included a consideration of sludge waste generated on-site at the WWTF and off-site food waste. Organic feedstock generators that will be subject to MassDEP’s pending organic waste ban within a 30 mile radius of the proposed AD facility were identified. A radius of 30 miles was selected based on a review of similar studies and experience from similar projects. The estimate of potentially available feedstock was determined based on an analysis of data provided by MassDEP and limited additional research in the vicinity of the project site. Within a 30 mile radius of the Easthampton WWTF, there are approximately 263 institutional/ commercial entities that are expected to be subject to the one ton per week limit for the expected waste ban (i.e. generating 50 tons a year or more) that cumulatively City of Easthampton - Anaerobic Digestion Feasibility Study E-3 Tighe&Bond Executive Summary generate approximately 69,290 tons a year assuming an estimated percentage of contamination specific to each generator category. The characteristics of organic waste generated by commercial and industrial sources vary considerably both across generator sectors and within the sectors themselves. The report provides the general waste characteristics by industry sector including typical moisture content, contamination levels, and types. The Feasibility Study also included a discussion of potential options for the management and disposal/reuse of the digestate from each the AD process. Estimates of liquid and high solids digestate were provided. The digestate management and reuse scenario will ultimately be decided by the project developer. Technical and Financial Analysis Based on the identification of potentially available feedstock, and the quantity and characteristics of this material, a system size and type was identified for the Feasibility Study evaluation. Following an analysis to determine the suitability and composition of the SSOM, the following volumes of feedstock were modeled for the AD system: 48 tons per day (TPD) food waste and 4.9 TPD dewatered sludge. While the Feasibility Study necessarily established a potential system size based on project site constraints and the potential availability of feedstock materials, it should be noted that the report does not represent a specific recommendation of a particular system size, type, or configuration. It is anticipated that if the City issues a solicitation for the project, it will allow respondents a level of flexibility with regard to project size and type. Based on the feedstock inputs to each system, it was estimated that the 600 kW AD system could produce 7,500 ft3/hr of biogas. The biogas generated by the AD project can be used to generate electricity and heat. Current electricity and thermal consumption data for the Easthampton WWTF was reviewed to determine current demands. For the purpose of the study, we elected to model a reciprocating engine cogeneration system that would use the biogas generated through the AD process. For the 600 kW system, it was estimated that 4,222 MWh of electricity would be produced annually. Based on current electrical consumption at the WWTF, the project can offset a significant amount of electrical demand. The cogeneration system will generate a significant amount of waste heat, even after diverting a portion of it to the digesters and accounting for downtime for system maintenance. The excess heat generated by the cogeneration system can be used for space heating at the WWTF if an interconnection between the AD facility and the heating plant is made. The preliminary analysis shows that the unit can meet the majority of WWTF’s heating demand; however during periods of cold weather or system downtimes it is expected that the facility would require supplemental heating. Economic Assessment The Feasibility Study included a life-cycle cost analysis completed for two project scenarios: a project that would be developed, owned and operated by the City and one that would be developed, owned, and operated by a private entity. The analysis included development of an economic pro forma for each scenario that incorporates project costs, financing mechanisms and incentives, and potential post-construction revenue. Costs include capital equipment; site development, design, and permitting; operations and maintenance; taxes; and financing. Revenue includes tax and other incentives; sale of Renewable Energy Credits, Alternative Energy Credits, CHP Rebates; and tipping fee from the feedstock. In the private developer scenario, it was assumed that the City would enter into a Power City of Easthampton - Anaerobic Digestion Feasibility Study E-4 Tighe&Bond Executive Summary Purchase Agreement with the developer for the electricity and Thermal Purchase Agreement to supply the WWTF’s thermal load. Under the City-owned scenario, the City of Easthampton would incur the cost of design, construction, and operation and maintenance of the project. In the private developer scenario, the developer would develop, own, and operate the AD facility through a PPA and/or lease agreement with the City. The same system size and associated capital costs were modeled for both scenarios. Food waste tipping fee revenue remained constant between both scenarios. Note that the pro forma was completed from the perspective of the private developer to gauge the financial performance of the project. The economic pro forma analysis shows that as modeled, only the publicly owned scenario is economically viable. Key differences between the two models include energy cost savings revenue to the City in the public scenario, and the impact of tax payments in the private scenario. Additionally, compared to other renewable energy technologies that can benefit from federal tax credits of 30% of capital costs, this credit is only 10% for AD/CHP. While the pro forma assumed the private project could benefit from accelerated depreciation, the first year 50% bonus was not considered. In general, the results of the economic analysis point to several key drivers for AD projects; namely project size, tipping fee, digestate management, O&M costs, and the ability to offset electrical and thermal load. Most notably, tipping fee revenue and digestate disposal costs significantly impacted the viability of project modeled in the Feasibility Study. In the private scenario, revenue streams associated with power sales are not significant enough to overcome the relationship between tipping fees/ digestate management costs. The Feasibility Study used conservative assumptions for cost and revenue inputs. The study includes a sensitivity analysis to test cost and revenue assumptions. Given the incentives for AD projects and regulatory drivers for organic material diversion, the initial results of the economic pro forma analysis do not mean that a project is not economically viable at the site. Conclusions and Recommendations This report evaluated the feasibility of the installation of a potential AD system at the City of Easthampton WWTF. The intent of the study was to help the City determine whether the site is suited for an AD project and whether such a project could be technically and economically viable. The analysis modeled a private-development project, in which a private developer would develop, own, and operate the facility; and a City-owned scenario in which the City of Easthampton would be responsible to develop, own, and operate the AD facility. The above factors affecting the feasibility of an AD project at the Easthampton WWTF are summarized in Table E-1, below. As shown on Table E-1, the economic evaluation determined that as modeled in the Feasibility Study only the public scenario is viable. The economics for the publicly owned project are more attractive due to the significant energy cost savings revenue enjoyed by the City. Tighe & Bond employed conservative values in our analysis and assumed revenue would not be produced from the potential reuse of digestate. Should a private developer be able to utilize additional revenue sources or reduce digestate disposal costs, the project economics would improve significantly. City of Easthampton - Anaerobic Digestion Feasibility Study E-5 Tighe&Bond Executive Summary It should be noted that the quantity of food waste available to the project was based on the Draper/Lennon study which provided the most comprehensive data source of available generators in the region. However, the Draper/ Lennon study does not account for current diversion practices. Based on our outreach efforts with regional generators, several commercial and institutional entities have initiated practices to reduce waste generated and/or currently divert their organic waste to other disposal facilities, such as local farms. The sizing and economics of the project are subject to change depending on the quantity of feedstock available. Given the potential benefits of the project to the city and suitability of the site, it is recommended that the project proceeds to the procurement stage to solicit responses from the development community. Recommended next steps to be conducted either by the City or a private developer, and either prior to procurement or as part of project development, include: Confirmation of the availability and composition of feedstock for the project. Confirm status of other AD projects in project area, and determine the potential impact to a project at the Easthampton WWTF. Confirmation of project development costs (including modification to the WWTF and interconnection costs). Additional site evaluation, including topographic survey and geotechnical evaluations prior to design of tanks, footings, and foundations to determine the actual soil characteristics to design the bearing structures accordingly. A formal wetland delineation should occur to confirm wetland boundaries on-site. Confirmation of current heating demand and estimated thermal costs at the WWTF Additional evaluation of water needs for the project, including domestic and fire prevention needs. Consideration of management scenarios and economics associated with digestate from the AD process Further coordination with WMECo with regard to electrical interconnection and remaining capacity on the proximate circuit Pre-permitting consultation with the City of Easthampton to confirm the local zoning permit requirements and consultation with MassDEP to confirm the air quality permitting strategy J:\E\E0702\REPORT\FINAL\Executive Summary_05.14.2014.doc City of Easthampton - Anaerobic Digestion Feasibility Study E-6 Tighe&Bond TABLE E-1 Easthampton WWTF Anaerobic Digestion Project - Overview of Project Feasibility Project Owner: City of Easthampton Ownership Private Developer Ownership Feedstock: WWTF, Sludge & Food Waste WWTF, Sludge & Food Waste Comments: Scenario: 1 2 Factor: Rated Capacity 600 kW 600 kW As the project site is located within a MassDEP approved Zone II, it is anticipated that the Land Use No conflict expected No conflict expected project will need to comply with the Wellhead Protection related land use restrictions of 310 CMR 22.21(2). If the project is considered an extension of Site Plan Review or Special Permit Site Plan Review or Special Permit the WWTF, Site Plan Review is required. If Zoning Approval from Planning Board Approval from Planning Board the project is considered a power plant facility, a Special Permit will be required. East side of operations building. Existing 3 East side of operations building. Existing Electrical Interconnection phase power lines. 3 phase power lines. Thermal Interconnection Interconnect with WWTF Interconnect with WWTF 50 Tons Per Day Food Waste 50 Tons Per Day Food Waste Feedstock Assumed for System 10,000 Gallons Sludge 10,000 Gallons of Sludge Estimated Biogas Production (ft3/hr) 7,500 7,500 Estimated Annual Electrical Generation 4,222 4,222 (MWh) Estimated Annual Thermal Generation 11,000 11,000 (MMBTU) Estimated Digestate Production: Dewatered Digestate (tons/day) 14.5 14.5 Liquid Digestate (gallons/day) 16,800 16,800 Environmental Factors: Must submit Project Notification Form to Historic and/or Cultural Resources Minimal/No Impact Minimal/No Impact Massachusetts Historical Commission. Project not located within the limits of mapped Natural Heritage and Endangered Rare Species No impact No impact Species Program (NHESP) Estimated Habitats for Rare Wildlife or Priority Habitats for Rare Species. Order of Conditions from Conservation Wetlands Minimal Minimal Commission/Determination of Applicability likely required. Comprehensive Plan Approval required from MassDEP may require modeling and comprehensive evaluation. Will require Permitting Requirements Moderate Permitting Effort Moderate Permitting Effort MassDEP approval to accept organic waste and local approval via the Industrial Pretreatment Program. Economic Factors: Est. Capital Cost $5,408,500 $5,408,500 Est. O&M Cost $214,579 $214,579 Financial Viability: IRR (leveraged) 11.5% N/A NPV (leveraged) $1,189,644 -$3,075,890 Payback Period (yrs, leveraged) 8.4 47.8 Economic Feasibility YES NO J:\E\E0702\REPORT\Tables\overview of feasibility_table_03142014.xlsx S S T T N N E E T T N N O O C C Table of Contents Tighe&Bond Executive Summary 1 Introduction 1.1 Site Location & History ....................................................................1-2 1.2 Project Description .........................................................................1-2 1.3 Feasibility Study Overview ...............................................................1-3 2 Detailed Site Assessment 2.1 Physical Characteristics ...................................................................2-1 2.2 WWTF Facility ................................................................................2-1 2.3 Historical Environmental Site Assessment Issues ................................2-2 2.4 Environmental and Cultural Resources ..............................................2-3 2.4.1 Historic and/or Cultural Resources .......................................... 2-3 2.4.2 Rare Species........................................................................ 2-4 2.4.3 Wetlands ............................................................................. 2-4 2.4.4 Protected Open Space/ Drinking Water Resources .................... 2-5 2.5 Zoning ..........................................................................................2-5 2.6 Constraints Map .............................................................................2-7 2.7 Regulatory Assessment ...................................................................2-7 2.7.1 Air Quality ........................................................................... 2-7 2.7.2 Anaerobic Digestion Permitting .............................................. 2-8 2.7.3 Wastewater Discharge Permitting ........................................... 2-8 2.7.4 Wastewater Treatment Facility Permitting ............................... 2-9 2.7.5 Solid Digestate Disposal/Reuse ............................................ 2-10 3 Facility Profile - Utilities 3.1 Existing Electrical/Heating Infrastructure ...........................................3-1 3.2 Facility Energy Profile .....................................................................3-1 3.3 Electrical Interconnection ................................................................3-3 3.4 Thermal Interconnection .................................................................3-4 4 Feedstock Availability 4.1 WWTF Sludge ................................................................................4-1 4.2 Food Waste ...................................................................................4-2 4.2.1 Food Waste Analysis Methodology .......................................... 4-2 4.2.2 Potentially Available Food Waste ............................................ 4-3 4.2.3 Feedstock Characteristics by Sector ........................................ 4-3 4.2.4 Generator Outreach .............................................................. 4-6 4.2.5 Competing Facilities.............................................................. 4-7 4.3 Summary of Feedstock Characterization ............................................4-8 5 Technical Analysis i
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