HomeMy WebLinkAboutCordova Feasibility Study NVE_burn_pile_preFS 2009Native Village of Eyak
Feasibility Assessment for Biomass Heating
Prepared by:
Dalson Energy
Anchorage, Alaska
September 2009
Delivered to:
Native Village of Eyak
Autumn Bryson, Environmental Coordinator
PO Box 1388
Cordova, Alaska 99574
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Cordova Biomass Energy
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Table of Contents
Page
Introduction 3
Summary 5
Community Information 8
Biomass Energy Narrative 11
Local Feedstock Availability 15
Options 19
Alternative Options 20
Roadmap 21
Resources and Citations 22
Author 23
Cover Photo:
Old Log deck on Eyak Corporation land, on the road toward the Copper River
Delta, where wood samples were taken for testing
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Introduction
Feasibility Assessment for Biomass Heating for Cordova Alaska
Dalson Energy (Consultant) was contracted by the Native Village of Eyak (NVE)
to do a Feasibility Study for Biomass Heating in Cordova.
The Project RFP stated:
“The Community Burn Pile will better serve the community if it is
transitioned from a community dump into local source heating fuel.”
Cordova community burn pile
Further direction from the NVE Executive Director was to specifically assess the
available biomass that can be diverted from the Community Landfill and the
Community Burn Pile that could be used as fuel in a biomass heating system for
a district heat loop in the 2-block square downtown business district.
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Cordova Library and Community Center
Louise Deerfield, Tom Miles and Dave Sharpe assisted Thomas Deerfield with
this report. Dalson staff made two site visits to Cordova, reviewed available data,
took biomass samples for testing, interviewed stakeholders and local authorities,
researched available technologies and case studies, and prepared this report.
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Summary
The principal question asked was: Can Cordova effectively use the community’s
waste wood and cardboard to offset petroleum oil for heating purposes in
community buildings?
Although the literal answer is that it is technically possible to divert waste wood
and cardboard for use as fuel in a heat-producing boiler, the practical answer is
that since Cordova is a relatively small community it does not appear that
sufficient volumes of clean, dry, useable feedstock can be generated in the form
of waste wood and cardboard, used pallets, etc to justify the costs of equipment
and facilities for processing and storing the feedstock, the capital costs of boiler
and emission control systems, and the infrastructure costs to distribute valuable
heat to community buildings.
Cardboard recycle pile at baling plant. Note plastic bags, tarps, foam packing
material in cardboard pile.
(Other bales are aluminum to be shipped out).
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The estimated cost of processing equipment for waste wood, including a suitable
chipper and loader is $125,000 to $250,000. The processing equipment for
cardboard would include a grinder or hammer-mill and cost an estimated
$150,000 to $250,000 (these are not new equipment prices). Add to that the cost
of heated, dry storage during summer months for winter usage, estimate
$50,000, (assuming donated land).
A suitable boiler system that could handle these low-grade materials with
emission-controls and related hardware and software would add another $1M to
1.25M, and distribution infrastructure (to deliver the heat) could add $2M to $3M
if the downtown area is the target. The total estimated cost could be $3.4M to
$5M, not including land.
Location of the boiler would be challenging, as the noise and stack emissions will
present challenges for nearby residences and commercial enterprises. For ideal
efficiency, the boiler system should be located as close as possible to the end
users of the heat produced.
Additionally, each building’s owner would be saddled with the cost of converting
existing (typically oil-fired) heating systems to hydronic heat exchangers. Most of
the buildings are older. Many have not yet done energy audits or energy
efficiency upgrades, a precursor to heating system upgrades.
Installation of a district heat loop in downtown Cordova would involve jack-
hammering concrete sidewalks and alleyways to install insulated pipes, which
inevitably leads to additional work with existing waterlines and other affected
infrastructure. An estimated cost of $2M to $3M may be low.
It should also be noted that it might be difficult to get all the property owners to
commit to the additional costs and disruption of commerce inherent in such
projects, in return for what may appear to be incremental savings.
All things considered, the Consultant recommends against the pursuit of a
biomass energy system for heating downtown Cordova buildings with existing
wastewood and cardboard fuel. There are other recommended energy options
that the community could consider.
A viable community-scale biomass heating system will require harvesting of local
forest feedstock. If the community is willing to include access to a sustainable
source of forest feedstock resources, there are options that have been
successful in other similar communities.
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The consultants suggest that the community of Cordova, including the City, the
Electrical Co-op, the Native Village of Eyak and the Eyak Corporation, combine
forces and efforts to create a renewable energy plan, starting with an
independent community energy audit and an assessment of available energy
efficiency strategies, as first steps toward more effective utilization of all available
resources.
The feedback from potential funding sources (Alaska Energy Authority, Denali
Commission, USDA Rural Development, etc) is that communities must first
undertake to quantify their energy uses and sources, then “tighten up” their
energy usage with audits and energy efficiency efforts, and then undertake
renewable energy projects—in that order.
At this time, the target should be generating heat to offset heating oil. The
technology for CHP (combined heat and power) systems is not yet viable
for small (<2MWe) community-scale systems for rural Alaska.
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Community Information
Cordova population: 2454
Households: 958
Heating Degree Days: 9565
Existing heating systems: Mostly Oil furnace and some Electric
Cost of fuel oil in Cordova: $3.72 (ISER-UAA 8-15-09)
Cost of fuel oil: $3.28 delivered (300 gallon keep-full service -Shoreside 9/10/09)
Cost of electricity $/kWh: $.20 to .27 (residential -CEC 8/15/09)
Fuel value of Cardboard: 6,000 to 7,000 Btu/Lb Dry
Fuel Value of wood pallets: 6,000 to 8,000 Btu/Lb (dry & clean)
Fuel value of landfill wastewood: 4,500-5,000 Btu/Lb (dry & clean)
City Baler output (cardboard) 50-80 bales/yr (G. Rankin estimate)
Bales are 1.6 cu. yd. (mixed with some foam & plastics)
MSW Bales unsuitable as fuel (mixed content and very high m/c)
Heating Oil cost for City buildings (2008):
(no gallon volumes available)
Fire & EMS: $6,913
Bldg Mntnce: $75,766
Recreation: $18,790
Pool: $115,458
Ski hill: $5,153
Camper Park: $2,952
Harbor Operations: $11,666
Sewer operations: $12,506
Water operations: $18,737
Total: $267,941
Source: Public Works
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Cordova’s historical heating oil usage for individual residential and commercial
buildings has not been gathered and collated by any source that the Consultant
could access. City Public Works provided the data for City buildings. The local
petroleum distributor considers the usage data to be proprietary, and is unwilling
to release data on individual building usage. Several local businesses consulted
were unable to provide information on heating oil usage. One small downtown
business estimated usage at $200-400 per month in winter, but none of those
interviewed were more definitive.
The lack of collated data is not atypical in small rural communities. It points to the
need for a community-wide energy audit.
Typical examples:
1000 square foot home in Cordova climate:
50,000 to 200,000Btu/hr heat load
500-800 gallons heating fuel/year
$1900 – 3,000/yr
2,000 square foot commercial building
150,000 to 300,000 Btu/hr heat load
1500 to 3000 gallons/yr
$5,500 to 11,000/yr
These examples can vary widely depending on building insulation, system
efficiency, etc.
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CORDOVA FAA, ALASKA
Station:(502177) CORDOVA FAA AP
From Year=1949 To Year=2006
Heating Degree Days for Selected Base Temperature (F)
Base Jan. Feb. Mar. Apr. May Jun. Jul. Aug. Sep. Oct. Nov. Dec. Annual
65F 1282 1069 1087 840 640 427 335 352 508 788 1033 1206 9565
Heating Degree Day units are computed as the difference between the base
temperature and the daily average temperature. (Base Temp. - Daily Ave.
Temp.) One unit is accumulated for each degree Fahrenheit the average
temperature is below the base temperature.
Heating Degree Days
- Average of all heating degree-day units recorded for the day of the year.
Source: Western Regional Climate Center
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Biomass Energy Narrative
Woody biomass has become a significant fuel alternative across North America,
especially in rural and off-road communities in Alaska. The escalating costs of
petroleum fuels combined with additional transportation costs make locally
available fuel feedstocks more economically attractive. In addition, the use of
locally available fuel feedstocks creates local jobs for harvesting, gathering or
processing, and in many cases contributes to cleaner air by avoiding the open-air
burning of these materials.
Open air burning of waste wood, forest residues and other combustibles is the
least effective and most hazardous method of combustion. Especially in wet rainy
climates, full combustion is not possible; therefore particulates and other
emissions are high. In many jurisdictions, open air burning is legally restricted,
and regulations for burn piles require controlled access, staffing and monitoring.
Alaska Department of Environmental Conservation has fact sheets on
rural waste management and open air burning at this link:
www.dec.state.ak.us/eh/sw/April%202009%20Factsheets/Working/Factsheet%2
0HTMLs/2Rural%20Issues.html
The use of waste wood from landfill diversion, combustible MSW (municipal solid
waste), and C&D (construction and demolition) debris can be a valuable source
of fuel, however the volumes required and the necessity for clean and dry fuel
(for biomass furnaces/boilers) create a challenging situation, unless they are a
supplement to a larger sustainable source of fuel feedstock for small
communities.
Typically, communities under 20,000 in population usually do not generate
sufficient volumes of these waste materials to justify the capital costs of the
systems needed to gather, store and process the materials, burn it in clean-
burning boilers and distribute the heat in district heat loops.
The principal heating fuel in Cordova for both residences and business buildings
is fuel oil, delivered locally by tanker truck from Shoreside Petroleum Company,
and stocked in individual oil tanks. The furnaces, boilers and other stoves that
burn the fuel oil are usually electric fan-forced heated-air systems. A few are
hydronic, where heated water (or other liquid) runs through radiant heat tubing,
radiators or heat exchangers.
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Biomass heating systems fit into two typical categories: the first is stoves or
fireplaces that heat space directly through convection and radiation, and typically
burn cordwood or pellets. The second category is hydronic systems where the
stove, furnace or boiler burns cordwood, woodchips or pellets to heat liquid that
is distributed to radiant piping, radiators or heat exchangers. Community scale
hydronic systems, called district heating loop systems, (common in Europe), are
usually large boilers that supply hot liquid to several or many buildings,
sometimes a whole village or town.
Biomass fuel systems fit into three general categories, by the fuel type:
Solid chunks (cordwood),
Chipped or ground (hogged) material, and
Densified (pellets, bricks, pressed logs or pucks).
System application is typically determined by size of heat load.
Loads up to 1MM Btu/Hr often use cordwood or pellet systems.
Loads over 1MMBtu/Hr often use woodchip boilers.
Loads over 10MMBtu/Hr (Industrial-scale) systems often use hog-fuel
(lower-grade feedstock) and require additional particulate and emission
controls.
These are only rules of thumb, and do not take into account all local parameters.
Cordwood systems are more labor intensive, have lower capital cost and
are less complex. Multiple cordwood boilers can be stacked to meet
higher heat loads.
Woodchip systems can be more automated and less labor intensive, but
require more upstream equipment (chippers, loaders, augers, etc) and
significantly higher capital costs.
Pellet systems are the most automated, and have lower capital costs,
however they require access to competitively priced pellet fuel.
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System Feedstock requirements are determined by three parameters:
Building heat load
BTU content of the fuel
Efficiency of the boiler system
Building heat loads are determined by square footage, orientation and usage, as
well as energy efficiency factors like insulation, moisture barriers and air leakage.
BTU content of biomass fuels is reduced by moisture content (MC). The
reduction is mathematically equal; 30% MC means 30% reduction in BTU value.
Typically wet or unseasoned wood makes poor fuel.
Biomass boiler efficiency varies from <60% to 80% (manufacturer’s claims), and
is strongly affected by the BTU value and MC of the fuel.
Emissions from Woody Biomass combustion
In comparison to other fuels (coal, natural gas, and oil), wood has low nitrogen
oxides (NOx); carbon monoxide (CO, a product of incomplete combustion); sulfur
dioxide (SO2); and mercury (Hg) emissions. Effective methods of particulate
control have been developed to remove most of the particles from the exhaust air
of wood combustion facilities. In addition, unlike fossil fuels, wood is a carbon-
neutral source of energy, meaning it does not increase the amount of carbon
dioxide, a greenhouse gas, cycling through the atmosphere.
MSW Incineration for heat recovery
One suggested application was the burning of combustible waste diverted from
the MSW and trash waste stream at the Cordova baler plant. The baler location
is separate from principal residential districts and any heat produced could be
used on-site for heating the building.
A differentiation must be made between a waste wood burner and a MSW waste
incinerator. Following is a discussion of the typical issues associated with waste
incinerators. The option for a waste wood burner is below in the section called
Alternative options
Heat recovery from waste incinerators is often considered as an approach for
reducing waste management costs, in large volume situations. Rule of thumb
parameters describe the volume from communities of at least 20,000 population
are required to justify the costs of MSW incineration equipment and
infrastructure.
The feasibility of recovering heat from an incinerator depends on a number of
site-specific factors. In general, for heat energy recovery to be economically
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feasible, large quantities of waste need to be burned near the locations where
the large quantities of heat are needed.
Therefore, a major concern is locating the incinerator as close as possible to the
facilities that will use the recovered heat. In general, increasing the distance the
hot water has to travel also increases the cost of the insulated piping, the amount
of energy required to pump the water, and the amount of heat that is lost in
transit. The cost of arctic pipe including installation is estimated at $100 per foot.
So, every additional 10 feet of pipe adds $1,000 to the price of the system.
In addition to the incinerator and insulated arctic pipe, such a system might
include the following components:
Heat recovery system at the incinerator, including a boiler, inducer fan,
bypass system, breeching and stack pieces, and the control system.
$250,000
Heat distribution system at the facility, including a heat exchanger, pump,
expansion tank, piping, valves, fittings, and controls.
$15,000
Engineering design (15%)
Contingency (15%)
Estimated total cost $350,000
(not including the incinerator or distribution piping).
Operation and maintenance (O&M) requirements for a MSW incinerator heat
recovery system are higher than conventional biomass systems, due to the
mixed quality of the feedstock. Costs would include labor for general
maintenance and periodic cleaning of the fire tubes, the electrical power to run
the circulating pumps, the cost of replacement parts, and the cost of rebuilding
the heat exchangers approximately every 10 years.
For environmentally sound MSW incineration, highly specialized personnel
must service air pollution control equipment regularly. Monitoring
equipment is costly and requires aggressive maintenance and servicing by
trained technicians. When incineration is done in a manner that has low
adverse health and environmental impacts it is expensive. When it is done
poorly (with low financial costs) it can be expensive in terms of human
health and environmental impacts.
United Nations Environment Programme
Division of Technology, Industry and Economics
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Local Feedstock Availability
The City of Cordova has no accurate historical volume data on the community
burn pile, as it is effectively unregulated. Community members (or anyone else)
can drop off material there at all hours, since it is not fenced or gated, and have
only a sign to remind them of the rules.
Cordova Burn pile site
Its location outside town is ideal for avoiding complaints from nearby residences
or businesses, however that isolation also leads to some abuse of the site rules.
Toxic combustibles and non-combustible material are dumped at the site, and
require periodic cleanup by City staff.
A recent study of burn pile use did not establish total volumes, but did estimate
that 38% of the material dumped at the burn pile was unburnable items. The list
of items dumped at the burn pile included tires, plastic, metal, fishnets, glass and
household garbage.
Cordova burn pile assessment; Native Village of Eyak, 2008
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Effective diversion of appropriately clean and dry combustible material from the
burn pile would necessitate regulated access. Fencing and a gate, with operating
hours that were manned by City staff, could result in more accurate estimates of
the quantities of appropriate biomass boiler material.
Cordova Community Burn pile Sign
Other communities have installed chippers and chip vans at landfill sites to
process clean dry usable waste combustibles. Significant volumes of material are
necessary to justify the capital costs of equipment, plus labor and M&O costs for
the operations.
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Baler Plant
The Cordova Baler plant compresses unsorted MSW (municipal solid waste) into
bales for burial at the landfill. Unsorted MSW is not appropriate fuel for small
community-scale energy systems.
Cardboard is also baled at the plant, in quantities estimated by the operator at
50-80 bales per year (@ 400 pounds total 10-16 tons year). Cardboard can be a
relatively good fuel source, however processing is more complex and expensive
than wood. To be suitable as fuel, the cardboard must be clean, dry and
uncontaminated by plastics, foam packing, etc. The volumes of cardboard fuel
required to justify the capital and operating costs of a suitable system are orders
of magnitude greater than what is available in Cordova.
Log Decks on Eyak Corporation Land
There remain several significant log decks from old logging operations
approximately 20 years ago. Wood loses Btu value over time, typically at a rate
of 3% to as much as 10% per year, for whole decked logs. However, moisture
and oxidation are the primary causes of the losses, so logs that are protected
can retain a significant amount of their heating value over many years.
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Although most of the wood from the exterior of these log decks is of little value,
some of the logs inside the piles have been protected from rain and oxidization.
(see photo on report cover)
Samples were cut from protected logs inside an old log deck on Eyak
Corporation Land near the airport, in July 2009, and sent for analysis to a
certified testing lab.
Lab Test results:
Species: Hemlock
M/C: 57%
Ash: .08%
Volatile Matter: 34.68% wet
82.09% dry
BTU/LB: 3620 wet
8571 dry
Estimates made by visual inspection of several log decks indicate that 25% to
40% of the wood is still valuable as fuel feedstock. Considerable effort will be
required to remove the exterior layers of logs, to access the better material
interior to the piles. It is strongly suggested that this operation be undertaken
soon, as the losses continue and more logs lose all significant value every year.
Alder
There are also considerable amounts of alder grown in around the log decks and
along the roads leading to them. It is conceivable that this material could be
added to the list of available feedstock. The harvesting would almost certainly
need to be manual, as the material is too small for feller-buncher equipment and
the land too rocky, soft and uneven for mower-style equipment.
It would be interesting to experiment with the idea of hand harvesting and
immediate chipping into rolling chip vans or trucks. Similar operations are
common in Latin America and Northern Europe. This idea was discussed with
local Forest Service staff, and considered plausible.
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Options
A community scale biomass heating system or systems could be deployed in
Cordova for specific buildings, such as the planned Cordova Center, the hospital,
school or firehouse. The key requirement is a long-term sustainable supply of
woody biomass fuel feedstock, from the forests near Cordova.
The planned Cordova Center building’s proximity to the community pool and City
Hall point to the opportunity for a multi-building system, with a mini-district heat
loop of approximately 1-4MMBtu, which could be either cordwood (if smaller
<1MMBtu) or woodchip boiler system.
That location in the center of town, below downtown shops and surrounded by
businesses may be challenging for smokestack considerations. Even the
cleanest burning biomass boilers occasionally emit excess smoke, usually at
startup and if ever stoked with wet fuel.
If a biomass heating system is to be considered for the planned Cordova Center,
it is strongly suggested that the pre-design planning incorporate the biomass
system. It is much less expensive to incorporate auxiliary heating systems in pre-
construction planning than to attempt integration on existing buildings.
There are many examples of successful deployments of small to medium-scale
biomass heating systems in Montana (Fuels for Schools), Craig and Tanana in
Alaska, and projects planned for Tok and Delta Junction.
A recent study done for the Talkeetna School indicated a 250 cord per year
cordwood system would displace up to 90% of the heating oil used for a 50,000
square foot school. The acreage required was estimated at 16 acres per year, at
20 tons/acre.
Northern Economics, Inc. Su Valley High School: Wood Heat Analysis. Prepared for
Matanuska Susitna Borough. September 2009.
The challenges to a woody biomass heating system include establishing a
sustainable supply of feedstock, matching technology and capital cost to
available human and financial resources, and identifying an appropriate site near
end users.
According to the Port Graham Biomass Feasibility Study, there are approximately
250,000 tons of woody biomass within ¼ mile of that community. They estimated
that 5,000 tons a year could be sustainably harvested on a 50-year rotation.
1,000 to 2,000 tons per year is an amount likely required for a village-scale
biomass heating system.
Port Graham Village Council, Final Report Potential Biomass District Energy Production
in Port Graham, Alaska, May 2008
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Alternative Options
A small, manually fed “waste wood burner” furnace could be considered for “shop
heat” at the baler plant. Several versions of shop heaters in the range of 250,000
Btu per hour are available, and typically sold for about $8-10,000.
This type of heater could burn waste wood, broken pallets, etc that could be
separated out of the waste stream manually by shop staff.
A typical example is the 250,000 Btu furnace from Biomass Combustion Systems
(Massachusetts), designed for commercial and industrial facilities 5,000 square
feet and smaller, (open rooms) The all-steel, hot-air furnaces are chunk-wood
burners compatible with wood scrap such as truss, pallets, saw mill and recycling
and other wood waste, according to the company. The price tag for these
furnaces is $9,000, not including taxes, shipping or installation.
(There are many vendors and versions of these burners, this is only an example)
The Cordova Forest Service is planning forest-thinning operations for 2010.
NVE is planning Moose habitat enhancement projects (alder removal).
The DOT has ongoing road clearing operations that result in Alder cutting.
The airport operations regularly clear land for flight approach clearing.
All of these operations could be included in a biomass energy fuel source
program, however the base amount will, as stated previously, necessarily be
from nearby forestland.
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Roadmap
Find out how much you need and how much you waste, plug the
holes, and then find better ways to create what you need.
From an anonymous “old energy sage”
In many communities similar to Cordova, a community-wide energy audit,
followed by an energy efficiency program to eliminate waste, have been shown to
be effective (and necessary) first steps toward improved stewardship of local
resources. The process also builds local awareness and sense of community
effort.
An independent energy audit could gather and collate all energy inputs for the
entire community, residential, commercial, municipal and industrial. The full
disclosure of energy usage and costs is usually eye-opening for the community.
It is important to get an independent energy auditor, not financially connected to
a utility, energy system vendor or specific technology.
Quantification also leads to recognition of opportunities for increased efficiency.
Every community has waste and inefficiencies. Escalating costs drive the interest
in alternatives. Comparing local patterns of usage and costs to other
communities usually leads to a call for greater attention.
Energy efficiency programs come next, and are the low-hanging fruit of energy
alternatives. Insulation, building envelope tightening, ducting and ventilation
upgrades, and burner efficiency upgrades are usually cheap compared to new
systems. Often the payback for these efficiency upgrades is very quick.
The accomplishment of these steps: an energy audit and energy efficiency
program, will help build the necessary community spirit and cohesion necessary
to make the next step to renewable energy projects. These steps are also
requisite to gaining grant funding for renewable energy projects.
A community-scale biomass energy project will require community involvement
and collaboration. The Eyak Corporation forestlands are the apparently best
source for a sustainable supply of woody biomass in the volumes required.
Locally produced wastewood, pallets, etc can supplement the forest biomass.
The costs, the collaboration and the process to accomplish this are significant,
and will require the dedication of a community champion (advocate) with the
backing of the community.
Cordova has the resources to accomplish these projects.
The requisite community commitment is the next step.
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Resources
Consulted/interviewed for this report:
Autumn Bryson, NVE
Scott Madison, NVE
Mark King, NVE
Jason Borer, Eyak Corporation
Luke Borer, Forester
Clay Koplin, Cordova Electric Co-op
Charles Sink, Chugachmiut
Nathan Lojewski, Chugachmiut
Theresa Benson, USFS
Bob Behrends, USFS
Bruce Campbell, USFS
Steve Patterson, USFS
Ray Koleser, USFS
Martin Moe, Cordova Chamber of Commerce
Jim Nygaard, Cordova School District
Tom Cohenour, City Public Works
Todd Cook, City Public Works
Greg Rankin, City Baler plant & Landfill
Doug Pettit, local businessman
Bruce Lechner, Shoreside Petroleum
Jim Baumgartner, Alaska DEC
Alaska Energy Authority
Denali Commission
USDA Rural Development
ISER UAA
Institute of Social & Economic Research - University of Alaska Anchorage
Burning Garbage and Land Disposal in Rural Alaska; Alaska Energy Authority
And Alaska Department of Environmental Conservation; Emswiler & Crimp
May 2004
http://www.akenergyauthority.org/AEAdocuments/BurningGarbage.pdf
Northern Economics, Inc. Su Valley High School: Wood Heat Analysis. Prepared for
Matanuska Susitna Borough. September 2009.
Port Graham Village Council: Final Report Potential Biomass District Energy Production
in Port Graham, Alaska, May 2008
Native Village of Eyak; Cordova Burn Pile Assessment, Summer 2008
BBI International, AURI AITKIN COUNTY, MN; BIOMASS UTILIZATION
ASSESSMENT, June 2009
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Consultant/Author of this report:
Dalson Energy is a Renewable Energy Consulting and Emerging Technology
Research firm based in Anchorage. Dalson staff and partners have decades of
experience in construction project management, project development consulting
and renewable energy technology research. Dalson teams with licensed
engineers, architects and designers in Alaska, Canada and Lower 48.
Dalson Energy has worked with Alaska Energy Authority, Alaska Center for
Energy & Power, University of Alaska Fairbanks, Washington State CTED
(Community Trade & Economic Development) and California Energy
Commission on biomass energy technology research.
Dalson’s President, Thomas Deerfield, has been involved in biomass energy
RD&D since 2001, winning and managing grants from NREL (National
Renewable Energy Labs), USFS (US Forest Service), and CEC (California
Energy Commission). He has managed the field-testing of biomass CHP
systems, including the first grid-connected biomass gasification CHP system in
the US. (budget $1.2M, finalized 2007)
Thomas founded Shasta Energy Group (SEG), a 501c3 nonprofit, and managed
wind energy research, biomass energy feasibility studies, energy efficiency for
buildings, and Hydronic heating system research design and development
(RD&D). He also initiated a rural economic development think tank and has
engaged his writing skills to assist many other renewable energy project
initiatives.
Thomas Deerfield
Dalson Energy
Anchorage, AK
907-277-7900