Record of Decision for the Environmental Impact Statement for the Proposed Abengoa Biorefinery Project Near Hugoton, Stevens County, KS (DOE/EIS-0407), 2096-2105 [2011-480]
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Federal Register / Vol. 76, No. 8 / Wednesday, January 12, 2011 / Notices
• February 3, 2011—Mitchell Pauole
Community Center, 90 Ainoa Street,
Kaunakakai, Moloka’i, HI 96748, from
5:30 p.m. to 9 p.m.
¯
• February 5, 2011—Lana‘i High &
Elementary School Cafeteria, 555 Fraser
¯
Avenue, Lana‘i City, HI 96763, from
9:30 a.m. to 3 p.m.
Each scoping meeting will be
conducted in two parts: An informal
‘‘workshop’’ discussion period that will
not be recorded, and a formal
commenting session that will be
transcribed by a court stenographer.
Meeting participants may also have
their comments entered into the record
during the informal portion of the
meetings, on request. Those who do not
arrange in advance to speak may register
at a meeting (preferably at the beginning
of the meeting) and may speak after
previously scheduled speakers. The
presiding officer will establish
procedures to ensure that everyone who
wishes to speak has an opportunity to
do so. Depending on the number of
speakers, the presiding officer may limit
all speakers to a set amount of time
initially and provide additional
opportunities to speak as time permits.
Speakers may also provide written
materials to supplement their
presentations, and such additional
information may be submitted in
writing by the date listed in the DATES
section. Both oral and written comments
will be considered and given equal
weight by DOE and DBEDT.
The formal commenting session will
begin with an overview of the proposed
Wind Phase of the Hawai‘i Interisland
Renewable Energy Program and a
description of the State and Federal
environmental review processes. The
presiding officer will establish the order
of speakers and provide any additional
procedures necessary to conduct the
formal commenting session. Speakers
may be asked questions to help ensure
that DOE and DBEDT fully understand
all suggestions and comments.
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Issued in Washington, DC, on January 7,
2011.
Patricia A. Hoffman,
Assistant Secretary, Office of Electricity
Delivery and Energy Reliability.
[FR Doc. 2011–479 Filed 1–11–11; 8:45 am]
BILLING CODE 6450–01–P
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DEPARTMENT OF ENERGY
Record of Decision for the
Environmental Impact Statement for
the Proposed Abengoa Biorefinery
Project Near Hugoton, Stevens County,
KS (DOE/EIS–0407)
Department of Energy, Office of
Energy Efficiency and Renewable
Energy.
ACTION: Record of Decision.
AGENCY:
The U.S. Department of
Energy (DOE or the Department)
prepared an environmental impact
statement (EIS) (DOE/EIS–0407) to
assess the potential environmental
impacts associated with the proposed
action of providing Federal financial
assistance to Abengoa Bioenergy
Biomass of Kansas, LLC (Abengoa
Bioenergy) to support the design,
construction, and startup of a
commercial-scale integrated biorefinery
to be located near the city of Hugoton
in Stevens County, southwestern Kansas
(the Project). The integrated biorefinery
would use a combination of biomass
feedstocks, such as corn stover and
wheat straw, to produce ethanol and to
generate sufficient electricity to power
the facility and supply excess electricity
to the regional power grid. The Project
site comprises approximately 810 acres
of row-cropped agricultural land. The
biorefinery facilities would be
developed on 385 acres of the Project
site, and the remaining 425 acres would
remain agricultural and act as a buffer
between the biorefinery and the city of
Hugoton.
After careful consideration of the
potential environmental impacts and
other factors such as program goals and
objectives, DOE has decided that it will
provide Federal funding under Section
932 of the Energy Policy Act of 2005
(EPAct 2005) of up to $71 million (2009
dollars), subject to annual
appropriations, to Abengoa Bioenergy
for the Project. A separate decision will
be made regarding a potential loan
guarantee; and if DOE decides to
proceed to consider the loan guarantee,
DOE would consider using the Final
Abengoa Biorefinery EIS to comply with
NEPA review requirements for the loan
guarantee. If DOE determines that the
Final Biorefinery EIS sufficiently
addresses all activities covered by the
loan guarantee, DOE could either issue
a Record of Decision (ROD) deciding to
issue a loan guarantee, or amend this
ROD.
ADDRESSES: The Final EIS is available
on the DOE National Environmental
Policy Act (NEPA) Web site at: https://
nepa.energy.gov/ and on the Abengoa
SUMMARY:
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Biorefinery Project Web site at: https://
www.biorefineryprojecteis-abengoa.com.
This ROD also is available on these Web
sites. Copies of the Final EIS and this
ROD may be obtained from Ms. Kristin
Kerwin, Office of Energy Efficiency and
Renewable Energy, U.S. Department of
Energy, Golden Field Office, 1617 Cole
Blvd., Golden, CO 80401; telephone:
720–356–1564; or fax: 720–356–1650.
FOR FURTHER INFORMATION CONTACT: To
obtain additional information about this
Project, the EIS or the ROD, contact Ms.
Kristin Kerwin by the means specified
above under ADDRESSES. For general
information on the DOE NEPA process,
contact Ms. Carol M. Borgstrom,
Director, Office of NEPA Policy and
Compliance (GC–54), U.S. Department
of Energy, 1000 Independence Avenue,
SW., Washington, DC 20585; telephone:
202–586–4600; fax: 202–586–7031; or
leave a toll-free message at: 1–800–472–
2756.
SUPPLEMENTARY INFORMATION: DOE
prepared this ROD pursuant to the
Council on Environmental Quality
regulations for implementing the
procedural provisions of NEPA [40 Code
of Federal Regulations (CFR) Parts
1500–1508] and the DOE NEPA
regulations (10 CFR Part 1021). This
ROD is based in part on DOE’s Final EIS
for the Proposed Abengoa Biorefinery
Project (DOE/EIS–0407, August 2010).
Background
Under EPAct 2005, Congress directed
DOE to carry out a program to
demonstrate the commercial application
of integrated biorefineries for the
production of biofuels, in particular
ethanol, from lignocellulosic feedstocks.
Federal funding for cellulosic ethanol
production facilities is intended to
further the government’s goal of
rendering ethanol cost-competitive with
gasoline by 2012, and along with
increased automobile fuel efficiency,
reducing gasoline consumption in the
United States by 20 percent within
10 years.
To implement its responsibilities
under EPAct 2005, DOE issued a
funding opportunity announcement in
February 2006 for the design,
construction, and startup of
commercial-scale integrated
biorefineries. In February 2007, the
Department selected Abengoa Bioenergy
and five other applicants for negotiation
of award. Abengoa Bioenergy proposed
an innovative approach to biorefinery
operations that would involve
production of biofuel and energy in the
form of steam that could be used to meet
energy needs and displace fossil fuels,
such as coal and natural gas. The
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proposal also included an integrated
grain-to-ethanol facility.
In January 2009, Abengoa Bioenergy
modified its proposal by omitting the
integrated grain-to-ethanol facility and
including a steam-driven turbine that
would generate sufficient electricity to
power the production facility and
supply excess electricity to the regional
power grid. In addition, Abengoa
applied for a loan guarantee from the
Department’s Loan Guarantee Program
pursuant to Title XVII of EPAct 2005,
and from the U.S. Department of
Agriculture Rural Development
Biorefinery Assistance Program
pursuant to Section 9003 of the Food,
Conservation, and Energy Act of 2008.
The Department of Agriculture Rural
Development was a cooperating agency
in the preparation of the EIS.
DOE considered Abengoa Bioenergy’s
proposed project changes and
concluded that the Project remained
eligible for Federal funding under
Section 932 of EPAct 2005. On August
28, 2009, the Department determined,
however, that it would not proceed with
Abengoa’s request for a DOE loan
guarantee.
On December 22, 2009, after
publication of the Draft Abengoa
Biorefinery Project EIS on September
23, 2009, Abengoa Bioenergy filed a
revised loan guarantee application, and
in March 2010, the Department
determined that the proposed
biorefinery was eligible for
consideration under Title XVII, Section
1703 of EPAct 2005, and requested that
Abengoa submit the Part II portion of its
loan guarantee application. Abengoa
submitted the Part II application on May
14, 2010.
At this time, DOE is not proposing to
issue a loan guarantee for the
construction and startup of the
biorefinery. DOE is reviewing the Part II
submission and, pending the results of
the Part II review, will decide whether
to initiate the due diligence,
underwriting, and negotiation phase of
the loan guarantee process. If DOE
initiates that process with Abengoa,
DOE’s proposed action (that is, to issue
a loan guarantee) would be subject to
NEPA review. If DOE decides to proceed
to consider the loan guarantee, DOE
would consider using the Final
Biorefinery EIS to comply with NEPA
review requirements for the loan
guarantee. If DOE determines that the
Final Biorefinery EIS sufficiently
addresses all activities covered by the
loan guarantee, DOE could either issue
a Record of Decision deciding to issue
a loan guarantee, or amend this Record
of Decision.
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The U.S. Department of Agriculture
Rural Development also considered
Abengoa’s application for a loan
guarantee and did not approve it for
funding in Fiscal Year 2009. Should
Abengoa submit an application for a
loan guarantee in the future, Rural
Development will use DOE’s Final
Biorefinery EIS as part of its evaluation
of project eligibility and sufficiency.
Purpose and Need for Agency Action
EPAct 2005, Section 932, directs the
Secretary of Energy to conduct a
program of research, development,
demonstration, and commercial
application for bioenergy, including
integrated biorefineries that can produce
biopower, biofuels, and bioproducts. In
carrying out a program to demonstrate
the commercial application of integrated
biorefineries, EPAct 2005 authorizes the
Secretary to provide funds to biorefinery
demonstration projects to encourage
(1) the demonstration of a wide variety
of lignocellulosic feedstocks; (2) the
commercial application of biomass
technologies for a variety of uses,
including liquid transportation fuels,
high-value bio-based chemicals,
substitutes for petroleum-based
feedstocks and products, and energy in
the form of electricity or useful heat;
and (3) the demonstration of the
collection and treatment of a variety of
biomass feedstocks. Accordingly, DOE
needs to implement Section 932 of
EPAct 2005 and support advanced
biofuel production pursuant to the
Renewable Fuel Standard established by
the Energy Independence and Security
Act of 2007 (EISA 2007). EISA 2007’s
Renewable Fuel Standard requires the
U.S. Environmental Protection Agency
(EPA) to ensure that transportation fuel
sold or introduced in the United States
contain at least 36 billion gallons per
year of biofuels by 2022, and includes
specific provisions for advanced
biofuels, such as cellulosic ethanol and
biomass-based diesel fuels. Thus, DOE’s
purpose is to demonstrate that
commercial-scale integrated
biorefineries that use a wide variety of
lignocellulosic (second-generation)
feedstocks to produce biofuels, biobased chemicals, and biopower can
operate without direct Federal subsidy
after construction costs are paid, and
that these biorefineries can be easily
replicated.
EIS Process
In August 2008, DOE published in the
Federal Register its ‘‘Notice of Intent to
Prepare an Environmental Impact
Statement and Notice of Wetlands
Involvement for the Abengoa
Biorefinery Project near Hugoton, KS’’
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(73 FR 50001), starting a 45-day public
scoping period during which DOE held
a public scoping meeting in Hugoton,
Kansas. In April 2009, DOE re-opened
public scoping and published in the
Federal Register its ‘‘Amended Notice of
Intent to Modify the Scope of the
Environmental Impact Statement for the
Abengoa Biorefinery Project near
Hugoton, KS’’ (74 FR 19543). The
amended notice informed the public
about changes in the Project relevant to
the scope of the ongoing EIS. The
Department conducted a 30-day public
scoping period and held a second public
scoping meeting in Hugoton, Kansas.
During these scoping periods, the
Department received oral and written
comments of the following three types:
Expressions of support for the Project,
statements of no negative environmental
impacts, and requests for additional
information from Federal and state
agencies and members of the public.
On September 23, 2009, DOE
published in the Federal Register its
Notice of Availability for the Draft
Environmental Impact Statement for the
Abengoa Biorefinery Project Near
Hugoton, Stevens County, KS (DOE/EIS–
0407D) (74 FR 48525). DOE’s Notice of
Availability invited the public to
comment on the Draft EIS during a
45-day public comment period, and
described how the public could submit
oral and written comments on the Draft
EIS. DOE’s Notice also announced a
public hearing, which DOE conducted
in Hugoton, Kansas on October 21,
2009. On September 25, 2009, EPA
listed the Draft Abengoa Biorefinery
Project EIS in its weekly notice of
availability (74 FR 48951).
The Department received
approximately 40 comments from six
commenters during the public comment
period. DOE prepared a commentresponse chapter for the Final
Biorefinery EIS (Chapter 10), which
provides each comment and DOE’s
response. One commenter reiterated
comments submitted during public
scoping, and another commenter
submitted suggestions regarding regionspecific studies for corn stover removal
and runoff index scores for agricultural
lands. One commenter recommended
that the proposed transmission line be
designed to protect migratory birds and
raptors. A few commenters expressed
concern about landfill management of
refinery waste. A couple of commenters
expressed support for the Project. One
commenter submitted a number of
comments regarding the impacts of
biomass harvest on soil sustainability,
potential impacts to groundwater, the
timeframe for construction of the grainto-ethanol facility, the use of the latest
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biorefinery design for the air quality
analysis, the site selection process, and
the reliance on irrigated corn crops.
DOE issued the Final EIS and on
August 20, 2010, EPA listed the Final
Abengoa Biorefinery Project EIS in its
weekly notice of availability (75 FR
51458). The Final EIS reflects changes
resulting from public comments, and,
accordingly, the responses in the
comment-response chapter identify
sections of the Final EIS to which
changes have been made. The Final EIS
also reflects changes based on new and
updated information. Substantive
changes in the Final EIS are indicated
by vertical change bars shown in the
margins. DOE received one comment on
the Final EIS from EPA, Region VII. EPA
stated that DOE had adequately
addressed the concerns expressed in
EPA’s comments on the Draft EIS.
Proposed Action and Project
Description
DOE’s Proposed Action is to provide
Federal funding of up to $71 million
(2009 dollars), subject to annual
appropriations, to Abengoa Bioenergy to
support the design, construction, and
startup of the biorefinery, whose total
anticipated cost is approximately $685
million (2009 dollars).
The biorefinery would be constructed
on a 385-acre parcel near Hugoton,
Kansas. Abengoa Bioenergy has
optioned an additional 425 acres
immediately east of the biorefinery
parcel, between the biorefinery and the
Hugoton city limits, as a buffer area. The
optioned parcel would continue to be
used as agricultural land, and might be
used to test production of biomass
feedstocks.
The biomass-to-ethanol and -energy
facility proposed by Abengoa Bioenergy
would use lignocellulosic biomass
(biomass) as feedstock to produce
biofuels. Biomass, including corn
stover, wheat straw, milo stubble, mixed
warm season grasses (such as
switchgrass), and other available
materials, would be harvested as
feedstock and fermented to produce
ethanol.
The biorefinery would also produce
biopower, or bioenergy, in the form of
electricity. The bioenergy generation
facilities co-located at the site would
use direct-firing (that is, using the
biomass as a solid fuel in a boiler) to
produce steam. Steam produced in the
biomass boilers would be used for
facility processes and to produce
electricity.
Under the Proposed Action, the
biorefinery would process
approximately 2,500 dry short tons per
day of feedstock, which would be
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obtained from producers within 50
miles of the Biorefinery Project site. The
biorefinery would produce up to 19
million gallons of denatured ethanol per
year and 125 megawatts of electricity.
Seventy-five megawatts of electricity
would be sold commercially.
Construction of the biorefinery would
take approximately 18 months and
would require infrastructure
improvements, such as construction of
site roads that would tie to Rural Road
P, a 1.5-mile-long electrical
transmission line, and an approximately
0.5-mile railroad spur on the Biorefinery
Project site that would tie into the
Cimarron Valley Railroad. Temporary
connections to utilities would include
electricity, cable, telephone, and a
nonpotable water line. Temporary
potable water and sanitary facilities
would be provided onsite until
construction of permanent, onsite
facilities.
Harvested bales of biomass would be
transported to a 10-acre onsite storage
yard or to one of seven offsite storage
sites to be located within 30 miles of the
Biorefinery Project site. Each offsite
storage location would be about 160
acres and would have no permanent
structures. Combined, these sites would
store enough biomass to support
biorefinery operations for up to 1 year.
Bales of corn stover and other biomass
ready to be processed at the biorefinery
would be transported to a bale barn and
sent by conveyor for grinding and
cleaning. The ground feedstock would
then enter the production process or be
stored temporarily in silos onsite. In
addition, wood waste would be used as
boiler fuel to generate electricity. Up to
1,000 tons per day would be brought
from various sources by rail and truck
to the biorefinery.
The ethanol production process
would involve the following steps: (1)
Enzymatic hydrolysis and fermentation,
(2) distillation and dehydration, and (3)
ethanol denaturization and storage.
During hydrolysis and fermentation, the
feedstock would be treated with
enzymes and genetically modified
organisms (enzymatic hydrolysis) to
simultaneously break down the
cellulose and ferment the recovered
sugars. The resulting ‘‘beer,’’ which
would be 4 to 5 percent ethanol at that
point, would then be distilled and
dehydrated to remove water and
residual solids. Distillation would also
destroy genetically modified and other
organisms.
The facility design incorporates two
45,200-gallon-capacity shift tanks to
hold the anhydrous ethanol produced
during each 8-hour shift. The storage
tanks would be enclosed in a bermed
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area to contain spills. Gasoline would be
added to denature the ethanol and make
it unfit for human consumption prior to
temporary storage and loading of the
product into tanker railcars for
shipment.
Solids would be recovered from the
distillation process. Approximately
120,000 dry short tons of solids, referred
to as lignin-rich stillage cake, would be
produced per year. The stillage cake
would be transferred by conveyor to an
onsite third-party lignin producer. After
extracting the lignin, the lignin
producer would return the lignin-poor
stillage cake to the biorefinery and
Abengoa Bioenergy would use it as fuel
for the solid biomass boilers. Until a
lignin extraction facility is built,
Abengoa would burn the lignin-rich
stillage cake as solid fuel in the biomass
boilers. As an option, Abengoa could
use lignin-rich stillage cake as fuel for
the solid biomass boiler during the life
of the biorefinery.
The biomass receiving, grinding, and
storage operations would be an enclosed
system with a high-velocity, positive
pressure collection system to transfer
airborne particles to a dirt loadout tank.
The loadout tank, grinding activities,
and associated transfer points would
have fabric filter dust collectors
(baghouses). Volatile organic matter
released during processing would be
captured in a vent scrubber.
Approximately 1,900 dry short tons
per day of biomass feedstock would be
supplied to the boilers. The biomass
boilers would also burn much of the
waste resulting from ethanol
production, including fines collected
during milling, stillage cake, and syrup
from the distillation process. These
processes would produce approximately
127,000 tons of ash annually. This ash
would contain potassium and
phosphorus and would be marketed to
the contracted feedstock producers as a
soil amendment. If there is no market
for the ash, it would be sent to landfills.
Alternatives
In addition to the Proposed Action,
the EIS analyzes an Action Alternative
and the No Action Alternative.
Action Alternative
Under the Action Alternative, DOE
would provide Federal funding to
support the design, construction and
startup of a biorefinery that would use
a two-stage process to produce
fermentable sugars for bioethanol
production and that would produce
syngas using a gasification system. A
syngas boiler as well as the biomass
boilers would produce steam. Steam
would be used for ethanol production
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processes and electricity production.
Under the Action Alternative, the
biomass boilers and the turbines would
be used to generate electricity solely to
operate the plant and would be smaller
than those for the Proposed Action.
The biorefinery would produce
approximately 12 million gallons per
year of denatured ethanol, 19,000 short
tons per year of lignin-rich stillage cake,
and 20 megawatts of electricity for use
at the facility.
The milling process for the Proposed
Action and Action Alternative is the
same. Once milled, the feedstock would
be pretreated with dilute acid to remove
hemicellulose and pectin (the Proposed
Action is a one stage process and does
not include two pretreatment stages as
does the Action Alternative). It is this
pretreatment step and the subsequent
processing of the fractionated biomass
where the two-stage process differs from
the one-stage process described in the
Proposed Action. After this
pretreatment, two types of hydrolysate
or pretreated biomass would be
processed in two separate steps. One
type contains a hydrolysate primarily
consisting of hemicellulose and pectin,
which would be further saccharified to
fermentable sugars; these simple sugars
would then be fermented to ethanol.
The second type includes the celluloserich, lignin-rich fiber hydrolysate,
which would be further processed with
enzymes to produce simple sugars that
would be simultaneously fermented to
ethanol. Each separate step produces
beers containing between 4 and 5
percent ethanol and both beers would
be conveyed to distillation operations
for purification. Volatile organic matter
released during both of these processes
would be captured in a vent scrubber.
Approximately 71,000 dry short tons
per year of soluble and insoluble solids
would be recovered from the bottom of
the distillation column. The soluble
solids would be concentrated to a thin
stillage syrup in an evaporator and
would be combusted in the biomass
boilers. About 130 dry short tons per
day of insoluble, lignin-rich stillage
cake would be transferred to an onsite
processing facility for extraction of
lignin. After the lignin was extracted,
the lignin producer would return the
lignin-poor stillage cake to the
biorefinery, and Abengoa Bioenergy
would use it as fuel for the solid
biomass boiler. Until a lignin extraction
facility is built, Abengoa would burn the
lignin-rich stillage cake as solid fuel in
the biomass boiler. If recovery of lignin
is not economically feasible, the ligninrich stillage cake would be used as fuel
in the biomass boiler.Denaturing the
produced ethanol and loadout for the
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Proposed Action and Action Alternative
would be the same.
Syngas produced in the gasification
plant under the Action Alternative
would be used to operate a fire-tube
boiler to produce steam. A small
biomass solids boiler would also
produce steam to power the biorefinery
process operations only. Steam would
be used to operate a small turbine that
would produce 20 megawatts of power.
No-Action Alternative
Under the No-Action Alternative,
DOE would not provide Federal funding
to Abengoa Bioenergy to support the
design, construction, and startup of a
biorefinery. Abengoa would not build a
biorefinery and the biorefinery parcel
would remain agricultural land. The
Department recognizes, however, that
Abengoa could pursue alternative
sources of capital for development of
the biorefinery.
Potential Environmental Impacts of the
Proposed Action
In making its decision, DOE
considered the environmental impacts
of the Proposed Action, Action
Alternative, and the No-Action
Alternative on potentially affected
resource areas. These include: land use;
air quality; hydrology; biological
resources; utilities, energy, and
materials; wastes, byproducts, and
hazardous materials; transportation;
aesthetics; socioeconomics; cultural
resources; health and safety; and
environmental justice. DOE also
considered potential impacts on these
resources from accidents and acts of
sabotage. No wetlands would be filled
and no floodplains would be affected.
The EIS also considered cumulative
impacts, that is, impacts from the
Project combined with those from other
past, present, and reasonably
foreseeable future actions. The
following sections discuss the potential
impacts.
Land Use
Operation of the biorefinery would
require approximately 880,000 dry short
tons of lignocellulosic feedstock per
year. Abengoa Bioenergy anticipates
that, at the start of operations, the
primary feedstock would be corn stover,
with secondary feedstocks consisting of
grain sorghum stover, wheat straw, and
mixed warm season grasses.
Approximately 20 percent of the total
feedstock demand would consist of corn
stover for cellulosic ethanol production,
with the remaining 80 percent
consisting of any combination of
feedstocks for bioenergy production.
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DOE conservatively estimates that the
total annual demand for crop residue by
the biorefinery would equal about 60
percent of the targeted crop residues
that could be sustainably removed from
the 50-mile region surrounding the
Biorefinery Project site. The demand for
corn residue for ethanol production
would be about 20 percent of the
amount that could be sustainably
removed from irrigated corn acreage.
Thus, production of targeted crop
residues exceeds biorefinery demand
and Abengoa would have flexibility in
feedstock procurement. DOE anticipates
the demand for crop residue by the
biorefinery would have a negligible
impact on changes in land use type,
including use of lands in the
Conservation Reserve Program, because
there would be no incentive to alter
land use type for the purpose of meeting
demand.
Over time, it is anticipated that mixed
warm season grasses (such as
switchgrass) would replace corn residue
as the primary feedstock for producing
ethanol resulting in (1) beneficial
environmental impacts where marginal
cropland was converted, and (2)
minimal environmental changes where
land use types such as nonharvested
cropland, former Conservation Reserve
Program acreage, and pasture were
converted. The beneficial environmental
impacts of converting marginal cropland
to mixed warm season grasses are
related to establishment of a crop that is
resistant to many pests and plant
diseases; uses relatively less water,
fertilizer, and pesticides; and establishes
deep roots that store carbon in the soil.
Increased mixed warm season grasses
production would not be expected to
result in an adverse impact to land
enrolled in the Conservation Reserve
Program.
Contracts between Abengoa Bioenergy
and producers of biomass would
include a requirement that crop residues
would be harvested in accordance with
U.S. Department of Agriculture
guidelines for minimizing wind erosion.
DOE concludes that, on a regional basis,
removing crop residue following these
guidelines would have a negligible
adverse impact on soil organic matter
content. On a field-by-field basis, crop
residue removal would have a negligible
to minor adverse impact on soil organic
matter content. Any adverse impact to
soil organic matter content would be
limited to land for which the producer
was compensated for residue removal.
Development of the biorefinery would
result in the irreversible conversion of
385 acres from agricultural to industrial
use. The Proposed Action is consistent
with existing land use and zoning at the
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Project site. The reduction in irrigated
farmland associated with the water
rights Abengoa Bioenergy would
transfer to industrial use at the
biorefinery would be a negligible change
in regional irrigated cropland.
Air Quality
Construction of the biorefinery would
cause emissions from various activities
including use of heavy diesel-operated
equipment, disturbance of the soil,
grading activities, material transport,
and material handling. These activities
would be short term or intermittent in
nature and would only occur during the
18-month construction phase. Best
management practices would be
employed to minimize these emissions.
Concentrations of criteria pollutants
estimated to be released during
operation of the biorefinery would be
well below the National Ambient Air
Quality Standards. The estimated
concentrations from the biorefinery,
combined with ambient background
concentrations of pollutants in the
region, are about 67 percent of the
National Ambient Air Quality Standard
for 24-hour PM10, 12 percent for
nitrogen dioxide, and less than 10
percent of the standard for other
pollutants. DOE concludes that air
emissions would not harm human
health and the environment.
The biorefinery also would be a
source of greenhouse gases, with carbon
dioxide the most abundant. The boilers
would be the main source of the
greenhouse gases carbon dioxide,
methane, and nitrous oxide. Biomass
fermentation and distillation processes
also would emit carbon dioxide. The
total emissions of carbon dioxide
equivalents (used to represent the
contribution of all gases) from operation
would be 3.61 million tons per year.
According to the DOE Energy
Information Administration, the total
U.S. greenhouse gas emissions in 2008
was 7,775 million tons of carbon
dioxide equivalents, with 6,409 million
tons of the total from energy-related
carbon dioxide. The projected
greenhouse gas emissions from the
biorefinery would be 0.046 percent of
the total U.S. carbon dioxide equivalent
value.
Although the biorefinery would be a
source of greenhouse gas emissions,
operation of the biorefinery would
provide a net reduction in greenhouse
gas emissions when considering the
emissions produced during the lifecycle
of ethanol production and use relative
to the lifecycle of gasoline production
and use. To determine the level of
greenhouse gas reduction from the
Proposed Action, DOE used the
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Greenhouse gases, Regulated Emissions,
and Energy use in Transportation
(GREET) Model, developed by DOE’s
Argonne National Laboratory. The
GREET Model examines ‘‘well-to-wheel’’
fuel lifecycles by considering factors
such as producing raw materials for
fuels, refining the raw materials into
fuels, and using the fuel in vehicles.
The Abengoa Biorefinery Project
would reduce greenhouse gas emissions
not only by producing a fuel that
displaces gasoline, but also by
producing power that displaces
electricity from other electricity
generating sources. The GREET Model
combines these reductions and other
factors into a single metric to express
the net effect on lifecycle greenhouse
gas emissions relative to a baseline
scenario in which the biorefinery is not
built. Because the majority of the
electricity the biorefinery would
produce would be exported rather than
used for biorefinery operations, the
greenhouse gases displaced by the
biorefinery would be larger than the
greenhouse gases emitted by biorefinery
operations, thus causing a decrease in
greenhouse gas emissions that exceeds
100 percent. As a comparison, if only
enough electricity was produced to run
the biorefinery (none would be sold to
the grid), the percent reduction under
the Proposed Action would be 69
percent as compared with the baseline
where the biorefinery is not built and
passenger vehicles use 100 percent
conventional or reformulated gasoline.
Hydrology
Wastewater, petroleum products, and
hazardous chemicals would be
generated by the biorefinery. Planned
releases of wastewater would be limited
to the non-contact wastewater that
would be used for irrigation of the
buffer area. Petroleum products and
hazardous chemicals used during
construction and operations would be
managed within secondary containment
on the site, and there are no surface
waters in the nearby area that would be
affected by accidental releases.
Disturbed and built-up land areas
would result in increased runoff; this
runoff would be directed to natural low
areas within the biorefinery parcel.
Changes in infiltration would be minor
and likely would be limited to small
changes in the exact locations where
infiltration would occur. Alterations to
surface water drainage would be limited
to minor changes within the 385-acre
parcel and possibly within the buffer
area. Natural low areas where runoff
accumulates would not be altered. The
Department concludes the potential for
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adverse impacts to surface waters from
the Proposed Action is negligible.
Construction of the biorefinery would
require approximately 220 acre-feet of
water, and operations would require
about 2,900 acre-feet of water per year.
DOE estimates that an additional 46
acre-feet of groundwater would be
withdrawn per year by the city of
Hugoton to meet the domestic needs of
biorefinery workers, bringing the total
annual estimated demand to support the
biorefinery to approximately 2,950 acrefeet per year.
Abengoa Bioenergy has optioned
existing irrigation water rights from
eight wells to meet the water demand
for construction and operation of the
biorefinery under the Proposed Action.
The maximum permitted withdrawal
associated with those water rights is
about 7,240 acre-feet per year, and the
total volume discharged from those
wells in 2008 was about 4,380 acre-feet.
Thus, use of those water rights for
operation of the biorefinery would
result in a reduction of more than 4,290
acre-feet compared with the permitted
annual volume, and a reduction of more
than 1,430 acre-feet compared with
withdrawals during 2008. DOE
concludes that operation of the
biorefinery would result in a beneficial
decrease in groundwater withdrawals
from the High Plains aquifer.
Changes in cropping practices as a
result of the Proposed Action are not
expected to occur. Further, increases in
water withdrawals for agricultural
purposes in Kansas are limited by State
water appropriation regulations,
although increases in Oklahoma and
Colorado may be allowed. Thus, DOE
concludes that changes in water use in
the region resulting from changes in
land use to meet the demand of the
biorefinery for biomass are not expected
to occur.
Any spills of hazardous materials
would be handled in accordance with a
spill prevention, control, and
countermeasures plan, which would
minimize or eliminate potential impacts
to the groundwater quality from
construction and operation of the
biorefinery.
Biological Resources
There are no Federal- or stateendangered and/or threatened species,
candidate species, or state species in
need of conservation present or within
1 mile of the Biorefinery Project site.
DOE concludes that construction and
operation of the biorefinery would have
no impacts on threatened or endangered
species or their designated critical
habitat.
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To construct the biorefinery, the
biorefinery parcel, which is currently
used for dry-land farming, would be
converted to industrial use. There
would be some minor, short-term
adverse impacts to biological resources
from the construction and some minor,
long-term adverse impacts from the
operation of the biorefinery, but these
impacts would affect only common
species on or within 1 mile of the
Biorefinery Project site. The analysis of
potential changes in land use resulting
from the Proposed Action indicated that
conversion of Conservation Reserve
Program lands to tilled cropland from
the Proposed Action is not expected,
and other changes in land use would be
minimal. Thus, DOE does not expect the
Proposed Action to impact biological
resources within the region surrounding
the Project site.
Utilities, Energy, and Materials
Biorefinery workers and their families
would rely on the city of Hugoton water
system, the city of Hugoton sewage
system, and the Stevens County landfill.
The Hugoton water system also would
supply potable water for the biorefinery
facilities. Anticipated demands are well
below the excess capacity of the City
water system. The sewage collection
system in Hugoton has sufficient
capacity to accommodate use of the
system by construction and operations
workers and their families. In addition,
the Stevens County landfill has enough
capacity to handle the increase in solid
waste during construction and
operations due to the influx of workers
and their families living in Hugoton.
The biorefinery would require no
electric power from the regional grid
during operations. Rather, the
biorefinery would supply 75 megawatts
of electricity to the grid during normal
operations, which equals 5.8 percent of
the production capacity in the westerncentral region of Kansas, but only about
0.2 percent of current summer demand
in the Southwest Power Pool. The
amount of natural gas and diesel fuel
required for normal operation of the
biorefinery is approximately 0.1 and
0.05 percent, respectively, of the
amounts of these fuels used in Kansas
and would not adversely impact their
supply and distribution in the region.
The Proposed Action would involve a
commitment of building materials. With
the possible exception of stainless steel,
these materials would be available and
their procurement would not decrease
availability to other users in regional
markets. Components used in stainless
steel production (such as chromium and
nickel) are in high demand and, at
times, affect availability of stainless
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steel. However, the amount of stainless
steel required for construction of the
biorefinery is a very small portion of the
amount that moves through the U.S.
market annually.
Wastes, Byproducts, and Hazardous
Materials
The wastes and byproducts the
biorefinery would produce include
construction wastes, wastewater, solid
biomass boiler ash, distiller’s residual
biomass solids (stillage cake), stillage
syrup, wastewater treatment facility
sludge, lignin, genetically modified
organisms, dirt and fines resulting from
biomass processing, municipal solid
waste, and hazardous waste.
Solid biomass boiler ash and lignin
are byproducts that could be sold to
consumers within the 50-mile region of
influence. Abengoa Bioenergy would
burn stillage cake, dirt and fines from
biomass processing, and genetically
modified organisms in the solid biomass
boilers as part of the Proposed Action.
Domestic and process wastewater would
be treated in the onsite wastewater
treatment facilities, and treated process
wastewater would be recycled in the
ethanol production process. Wastewater
treatment facility sludge would be used
in the boiler fly ash pelletization
process or burned in the solid biomass
boilers. Abengoa would use non-contact
wastewater for crop irrigation on the
buffer area, and would treat, recycle,
and/or dispose of boiler bottom ash,
municipal solid waste, hazardous waste,
and construction debris at permitted
facilities within the region of influence.
The Stevens County landfill would
not have adequate capacity to receive
the construction wastes generated and
maintain its small arid landfill exempt
permit status (limited to 20 tons per
day); revising that permit would be
expensive. The non-recycled
construction waste streams would be
split among other permitted landfills
and transfer stations within 35 miles of
the biorefinery without significantly
affecting their capacity. Less than 1 ton
per day of municipal solid waste would
be generated during the expected 30year operating life of the biorefinery and
would be sent to the Stevens County
landfill. This waste stream would be
about a 3 percent increase to the
landfill’s current waste stream and
would reduce the life of the landfill by
less than 1 year.
The onsite wastewater treatment
facility would treat all process
wastewater generated at the Biorefinery
Project site and would not discharge any
to the Hugoton wastewater system.
Wastewater treated onsite would be
reused in the ethanol production
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process. Wastewater that would not be
recycled and reused in the production
process or treated onsite (non-contact
wastewater) would be produced at a rate
of 370 gallons per minute and would be
used to irrigate biomass crops on the
buffer area. This water would be
conveyed to two 11.5-acre storage ponds
prior to application to the buffer area.
Wastewater treatment facility sludge
would be used in the boiler fly ash
pelletization process or burned in the
solid biomass boilers. Based on an
agronomy study, the chemical
composition of the wastewater and the
anticipated stipulations of a required
discharge permit, DOE does not
anticipate adverse impacts from the
land application of wastewater,
including odor or aesthetic impacts.
Abengoa Bioenergy would have to
modify the facility water balance and
wastewater treatment facility design if
lignin was extracted from the stillage
cake, thereby generating additional
wastewater.
Chemicals required for operation of
the biorefinery would be received by
truck or rail and off-loaded and
transferred by an enclosed chemical
delivery system to storage tanks, silos,
or other chemical storage facilities.
Chemicals would have to be obtained
from outside the region. The demand for
chemicals for the biorefinery would be
an insignificant percentage of the
production in the United States.
The Project would generate 2,000
pounds per year of hazardous waste (for
example, spent solvents, waste ethanol,
and caustics). Those wastes would be
collected and treated/disposed of by
licensed hazardous waste facilities. DOE
does not anticipate adverse impacts
from the handling and disposal of
hazardous wastes generated at the
biorefinery because Abengoa
Bioenergy’s proposed hazardous waste
management practices will be
implemented.
Genetically modified organisms used
in the enzymatic hydrolysis process
would be killed by a heat sterilization
process and would be contained in the
beer column bottoms. The bottoms
stream would be dewatered and the
residual solids sent to the solid biomass
boiler for burning.
The solid biomass boilers would
generate up to 16 tons of bottom ash per
day. The bottom ash would be sent to
the Seward County landfill. Disposal of
the bottom ash at this landfill over the
life of the biorefinery would reduce the
life of permitted landfill space by about
2.2 years. In addition, the solid biomass
boilers would generate up to 350 tons of
fly ash per day. Abengoa Bioenergy
plans to sell the fly ash as a nutrient
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replacement co-product to biomass
producers in the region. If the ash could
not be sold or otherwise used in a
beneficial manner, it would require
disposal at permitted solid waste
disposal facilities. The Stevens County
landfill does not have adequate capacity
to receive this amount of ash without a
permit modification, so this waste
stream would be split among permitted
landfills and transfer stations within 35
miles of the biorefinery. However,
impacts on existing permitted solid
waste disposal facilities could be
problematic if a significant percentage
of the boiler fly ash was not marketable
as a soil amendment byproduct. The
loss of land used for landfill disposal of
solid wastes generated during
construction and operation of the
biorefinery would be an irreversible and
irretrievable loss of resources.
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Transportation
There would be approximately 32,000
truck shipments of materials during
construction, and about 80,000 to
116,000 truck and 1,300 to 6,600 rail
shipments per year during the 30-year
operating period of the biorefinery. DOE
estimates there would be 35 to 41 traffic
fatalities during the 30-year operations
period due to these shipments and the
commuting of workers, the majority (32
to 38) of which would be due to
shipments of biomass, chemicals,
denatured ethanol product, and waste.
For perspective, over the 30-year
operations period, there would be an
estimated 13,400 traffic fatalities in
Kansas and 820 traffic fatalities in the
nine counties surrounding the Project
site.
DOE estimates that 1,075 rail carloads
of denatured ethanol and waste and 211
to 5,554 rail carloads of biomass and
chemicals would be shipped to and
from the biorefinery per year of
operation, which is equivalent to about
49 to 241 additional trains per year.
This would result in an increase in the
approximately 600 trains per year that
travel on the Cimarron Valley Railroad,
but is less than the capacity of 40 to 60
trains per day on that line. Thus, the
additional rail traffic for the Proposed
Action would not adversely affect the
operations of the Cimarron Valley
Railroad.
Increased truck traffic would result in
increased pavement deterioration. For
biomass, chemical, and waste shipments
associated with the Proposed Action,
DOE estimated the annual cost of this
pavement damage to range from
$580,000 to $840,000.
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Aesthetics
DOE considered the potential impacts
of the Abengoa Biorefinery Project on
views in the area surrounding the
Biorefinery Project site and evaluated
how noise and odor from the biorefinery
could affect residents in the area.
Visual Resources—The tallest
structure at the biorefinery considered
under the Proposed Action would be
approximately 115 feet, but many of the
other structures would be 40 feet tall or
less. The biorefinery would be visually
similar to the grain storage silos and
elevators, chemical tanks, and other
structures located adjacent to the
Biorefinery Project site and would be
visible from surrounding vantage points,
such as the city of Hugoton and the
Forewinds Golf Course. The Proposed
Action would require a new 1.5-milelong transmission line that would be
visible from Road P and Road 11 near
the Biorefinery Project site, but would
result in minimal visual impacts to
viewers from a distance.
The biorefinery would operate 24
hours a day, 350 days a year, and thus
would be a source of night lighting.
Noise—Workers would be exposed to
noise during construction from
construction equipment and trucks
traveling to and from the biorefinery
construction site. Workers would also
be exposed to noise from equipment and
biorefinery processes during operations.
Best management practices would be
employed to limit noise, and a hearing
conservation program would be
implemented; therefore, permissible
noise exposure levels are not expected
to be exceeded.
The nearest residence to the
Biorefinery Project site, approximately
0.6 mile away, may experience some
annoyance from construction noise. The
noise level at that distance would be
approximately 56 decibels which is
approximately the same noise level as a
normal conversation.
In addition to being temporary, EPA
states that this noise level should not
interfere with daily activities such as
conversation, working, or recreation. As
such, the impact would be small. At 0.6
mile, noise from wood hog operations
could be distinguishable from other
background sources of noise. Noise from
biorefinery operations would attenuate
to below background levels beyond 0.6
mile. Therefore, except for the residence
at the northwest property boundary,
DOE does not anticipate impacts to
members of the public from
construction or operation of the
biorefinery due to noise.
During construction, there would be
about 70 truck shipments to the
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biorefinery site per day, or about one
truck arriving every 12 minutes
(assuming all traffic occurs from 7 a.m.
to 9 p.m.). During operations, 202 trucks
per day are expected (one truck every 4
minutes). The routes taken by those
trucks through and around Hugoton
would vary, but it is anticipated that at
least 50 percent of the traffic (one truck
every 8 minutes during operations)
would use the truck bypass and affect
two residences along Road Q. Along a
route that passes the Stevens County
Hospital, several schools, and places of
worship, trucks are anticipated to pass
at a rate of one every 21 minutes during
operations. Noise from these passing
trucks would frequently interfere with
outdoor conversations and cause
annoyance indoors. Rail traffic would
increase by about 255 trains per year.
Most of the rail shipments would carry
wood waste and are expected to occur
on weekdays during normal working
daylight hours.
Odor—Odors may result from
emissions of volatile organic
compounds, including ethanol, and
hazardous air pollutants, and from
nitrogen dioxide and sulfur dioxide.
Engineered controls implemented to
minimize these emissions would reduce
odors from the biorefinery. Air
dispersion modeling indicates that no
odorous compounds would be detected
at the biorefinery parcel fence line or
offsite locations where the public would
commonly be located. Therefore, DOE
anticipates no impacts to the public
from the release of odorous compounds.
Socioeconomics
DOE evaluated the potential impacts
of construction and operation of the
biorefinery on socioeconomic variables,
including population and housing,
employment and income, taxes, and
public services, in Stevens County and
the three surrounding counties; that is,
Morton and Seward counties in Kansas
and Texas County in Oklahoma.
The Proposed Action would require
256 workers at the peak of construction.
About 190 of those positions likely
would be filled by people who would
migrate into the four-county region,
which would result in a temporary
increase in the population in the region
of less than 1 percent and would have
little impact on the availability or cost
of housing or on public services. In
addition to the jobs directly associated
with the construction of the biorefinery,
88 indirect jobs are expected to be
created during the peak period of
construction. DOE estimates that during
construction, there would be about 110
additional students enrolled in local
school districts. This represents a 1.0
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percent increase in enrollment in the
region. During the 12-month period of
the most-intense construction activity,
the region could experience an
approximately $17-million infusion of
earnings, which equals about 1 percent
of the 2006 per capita income in the
region.
The anticipated life of the biorefinery
is 30 years, during which it would
employ 43 people. This would result in
a regional increase in the local
population of less than 0.1 percent, and
would have little or no impact on
housing, public services, or educational
services. During operations, the region
would experience an annual $4.4
million infusion in earnings. In
addition, 23 indirect jobs are expected
to be created during the operations
phase.
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Cultural Resources
No properties listed on the National
Register of Historic Places are within or
on properties adjoining the Biorefinery
Project site. Based on DOE review of
published information, coordination
with the State Historic Preservation
Officer, and the results of a Phase I/II
investigation of a 160-acre portion (areas
investigated were coordinated with the
State Historic Preservation Officer) of
the Project site, construction and
operation of the biorefinery would not
result in adverse impacts to Statepreserved or National Historic Register
sites, sites of prehistoric or early historic
occupation, or historic resources of local
significance. When selected, offsite
biomass storage locations will be
evaluated for cultural resources in
coordination with the Kansas State
Historical Preservation Office to ensure
no adverse impacts.
Health and Safety
DOE estimated health and safety
impacts to workers from industrial
hazards using incidence rates for 2007
for both nonfatal occupational injuries
and occupational fatalities from the U.S.
Department of Labor, Bureau of Labor
Statistics. Members of the public would
not be located within the Biorefinery
Project site and would not be affected by
industrial hazards at the biorefinery.
The potential for adverse impacts to
health and safety from the Proposed
Action would be very minor. During
construction, the industrial health and
safety impacts to workers are estimated
to be 14 total recordable cases (that is,
work-related deaths, illnesses, or
injuries that result in the loss of
consciousness, days away from work
restricted work activity or job transfer,
or required medical treatment beyond
first aid), 7 days away from work, and
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0.026 fatality. During operations, the
total annual industrial health and safety
impacts to workers from all operations
at the biorefinery (such as, ethanol
manufacturing, milling and grinding
operations, and electric power
generation) are estimated to be 2.7 total
recordable cases, 0.94 day away from
work, and 0.0014 fatality. Based on
these results, DOE concludes that a
fatality would be unlikely. No adverse
health impacts to members of the public
from air emissions under normal
operations are anticipated.
Facility Accidents and Sabotage
Based on the operational history of
existing ethanol plants, DOE concludes
that the hazards of ethanol production
to members of the public are minor, and
that accidents during biorefinery
operations are not likely to result in
permanent health effects to offsite
members of the public. In some accident
scenarios, such as the failure of an
ethanol or gasoline storage tank,
workers could be injured or killed
depending on the location of the worker
at the time of the event.
DOE considered the most hazardous
intentional destructive act to be the
deliberate destruction of a toxic
chemical storage tank. The
consequences of such an act would be
similar to the accidental failure of a
toxic chemical tank and would be
limited to injury and, in unlikely
circumstances, death to nearby workers.
Environmental Justice
No impacts to communities with high
percentages of minority or low-income
populations were identified that would
exceed those identified for the general
population. In addition, during the
scoping process, DOE identified no
unique exposure pathways, sensitivities,
or cultural practices that would result in
different impacts on minority or lowincome populations. Disproportionately
high and adverse impacts would be
unlikely as a result of the Proposed
Action.
Potential Impacts of the Action
Alternative
Under the Action Alternative, the
environmental impacts would be similar
to those of the Proposed Action. For
most resource and subject areas, there
are no or minor differences between
those alternatives. Differences exist
between the alternatives for the
following resource and subject areas.
Air Quality—The Proposed Action
would result in a greater reduction in
greenhouse gas emissions (340 percent)
than the Action Alternative (39 percent)
by producing more fuel with biomass-
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derived ethanol and producing more
electricity from biomass.
Utilities—The Proposed Action would
produce and sell electricity in excess of
that required to operate the biorefinery
equal to about 5 percent of the
production capacity in west-central
Kansas. The Action Alternative would
produce less electricity and would
require electrical power from the
regional grid to operate the biorefinery
equal to about 1 percent of the
combined production capacity of two
suppliers in the region.
Transportation—The Proposed Action
would require substantially more truck
shipments than the Action Alternative
during operations; thus, the number of
traffic accidents and amount of road
damage would be proportionally greater
under the Proposed Action.
Noise—For operations, because there
would be more truck shipments for the
Proposed Action, local residents would
experience noise from truck shipments
more frequently under the Proposed
Action than under the Action
Alternative.
Socioeconomics—Approximately 10
percent more workers would be
employed at the biorefinery under the
Proposed Action, and more earnings
would be infused in the local economy.
Under the Action Alternative, the
biorefinery would produce 33 percent
less ethanol [12 million gallons (45
million liters)] and 80 percent less
biopower (20 megawatts) than under the
Proposed Action. In addition, less
salable byproducts, such as lignin and
lignin-rich stillage cake, would be
produced under the Action Alternative.
Potential Impacts of the No-Action
Alternative
Under the No-Action Alternative,
none of the adverse impacts identified
above for the two action alternatives (for
example, emissions of air pollutants,
use of land for disposal of solid wastes,
increase in truck traffic, and associated
increase in accidents and noise) or
beneficial impacts (for example,
increased employment, decrease in
groundwater use, and increase in the
electrical production capacity for the
region) would occur. Further, the
benefits that would be gained from the
development, demonstration, and
commercial operation of an integrated
biorefinery that uses lignocellulosic
feedstocks would not be realized. In
addition, no benefits would be realized
from the development of a renewable
energy system that would reduce air
pollutants and sequester emissions of
greenhouse gases. For example, the
reductions in greenhouse gas emissions
estimated to occur if the Proposed
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Action were implemented would not be
realized with the continued use of
gasoline instead of biofuel and no
generation of biopower.
Environmentally Preferred Alternative
The Proposed Action and Action
Alternative would result in both
beneficial and adverse potential
environmental impacts (summarized
above and in Table 2–2 of the EIS).
Potential beneficial impacts include
those associated with reductions in
greenhouse gas emissions and a
decrease in water withdrawals; adverse
impacts include those associated with a
substantial increase in transportation
activity and minor impacts from air
emissions. On balance, DOE regards the
No-Action Alternative, which would
result in no change in existing
environmental conditions, as the
environmentally preferred alternative.
mstockstill on DSKH9S0YB1PROD with NOTICES
Decision
DOE has decided to implement the
Proposed Action to provide Federal
funding of up to $71 million (2009
dollars), subject to annual
appropriations, to Abengoa Bioenergy
Biomass of Kansas, LLC (Abengoa
Bioenergy) to support the design,
construction, and startup of the
Abengoa Biorefinery Project. DOE has
also decided to adopt the mitigation
measures discussed in the Final
Abengoa Biorefinery EIS and
summarized below under ‘‘Mitigation’’.
Basis of Decision
DOE’s decision is based on the
importance of achieving the objectives
of the EPAct 2005 and careful review of
the potential environmental impacts
presented in the Final Biorefinery EIS.
This Project will support advanced
biofuel production pursuant to the
Renewable Fuel Standard established by
EISA 2007, which requires EPA to
ensure that transportation fuel sold or
introduced into commerce in the United
States contain at least 36 billion gallons
per year of biofuels by 2022. It provides
an opportunity to demonstrate that
commercial-scale integrated
biorefineries that use a wide variety of
lignocellulosic (second-generation)
feedstocks to produce biofuels and
biopower can operate without direct
Federal subsidy after construction costs
are paid, and that these biorefineries can
be easily replicated.
The Project would reduce greenhouse
gas emissions not only by producing a
fuel that displaces gasoline, but also by
producing power that displaces
electricity from other electricity
generating sources. In addition, this
Project would have economic benefits in
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17:25 Jan 11, 2011
Jkt 223001
the region. The Project would require
256 workers at the peak of construction
and during the 12-month period of the
most-intense construction activity, the
region could experience an
approximately $17-million infusion of
earnings. Over the anticipated life of the
biorefinery of 30 years, it would employ
43 people and the region would
experience an annual $4.4 million
infusion in earnings.
To meet the mandates of the EPAct
2005 and other governing policies, it is
in the best interest of DOE to select and
fund the most technologically and
economically viable alternative.
Production of more ethanol and
production of biopower would make the
Proposed Action a more economically
viable alternative than the Action
Alternative. The Proposed Action,
therefore, better meets the direction of
Section 932(d)(2) of EPAct 2005, which
directs the Secretary of Energy to select
only proposals that ‘‘demonstrate that
the project will be able to operate
profitably without direct Federal
subsidy after initial construction costs
are paid.’’ In addition, the Proposed
Action more fully supports the intent of
the Section 932(d)(1) of EPAct 2005 to
encourage the commercial application
of biomass technologies for a variety of
uses, including high-value bio-based
chemicals and energy in the form of
electricity and useful heat. For these
reasons, DOE determined the Proposed
Action more fully meets its purpose and
need, and has decided to implement the
Proposed Action.
This decision incorporates all
practicable means to avoid or minimize
environmental impacts. DOE plans to
review annual monitoring reports to
assess the environmental impacts
predicted in the EIS and the
implementation of appropriate
avoidance and mitigation measures.
Mitigation
DOE’s decision incorporates best
management practices and additional
measures to avoid or minimize adverse
environmental impacts during the
design, construction, and operation of
the Project. DOE will require Abengoa
Biorefinery to implement the best
management practices outlined in
Chapter 6, Section 6.1, of the Final
Biorefinery EIS, for the following
resource areas: land use; air quality;
geology and soils; surface water;
groundwater; biological resources;
utilities, energy, and materials; wastes
and hazardous materials; visual
resources; noise; odor; cultural
resources; and health and safety.
DOE regards mitigation measures as
activities or actions that would be above
PO 00000
Frm 00024
Fmt 4703
Sfmt 4703
and beyond (in addition to) best
management practices. DOE requires
that the participants comply with all
applicable Federal, state, and local
environmental laws, orders, and
regulations. Mitigation measures beyond
those specified in permit conditions
will be addressed in a mitigation action
plan (MAP) that DOE will prepare
pursuant to 10 CFR 1021.331. The MAP
will explain how the mitigation
measures will be planned,
implemented, and monitored and is an
adaptive management tool. Mitigation
conditions in it will be removed if
equivalent conditions are otherwise
established by permit, license, or law, as
compliance with permit, license or
regulatory requirements are not
considered mitigation activities subject
to DOE control and are therefore not
included in MAPs.
DOE will ensure that commitments in
the ROD are incorporated into DOE’s
Cooperative Agreement with Abengoa
Bioenergy. The MAP and annual
monitoring reports will be available on
the DOE NEPA Web site (https://
www.nepa.energy.gov) and the DOE
Golden Field Office Web site (https://
www.eere.energy.gov/golden/
Reading_Room.aspx). DOE will make
copies of the MAP available for
inspection in appropriate locations (e.g.,
local library or DOE reading rooms) for
a reasonable time. The Department also
will provide copies of the MAP and
annual reports upon request.
In the Final EIS, DOE stated that
mitigation measures for the following
resource areas were being considered:
air quality, biological resources, visual
resources, odor, socioeconomics, wastes
and hazardous materials, and
transportation. Upon consideration of
the findings presented in the Final EIS,
DOE has determined that no mitigation
is required for air quality, odor, or
socioeconomic impacts. The required
implementation of air quality best
management practices presented in
Section 6.1 will adequately minimize
impacts and therefore no additional
mitigation is required. While the EIS
concludes that odor may result from
emissions of volatile organic
compounds, it also concludes, based on
air dispersion modeling, that there are
no anticipated impacts to the public
from the release of odorous compounds
and therefore no mitigation is required.
The EIS concludes that the impacts to
community services would be
temporary and not likely to place an
undue demand on community services,
and therefore no mitigation is required.
Biological Resources Mitigation.
While the EIS concludes that DOE does
not expect the Proposed Action to
E:\FR\FM\12JAN1.SGM
12JAN1
mstockstill on DSKH9S0YB1PROD with NOTICES
Federal Register / Vol. 76, No. 8 / Wednesday, January 12, 2011 / Notices
impact biological resources (including
threatened and endangered species)
within the region or the Project site,
DOE acknowledges that the new
transmission line should be designed to
minimize impacts to raptors and
migratory birds. At this time it is
uncertain whether Abengoa or Pioneer
Electric Cooperative, Inc. (Pioneer
Electric) will be responsible for the
design and construction of the new
transmission line, or if an existing
transmission line will be upgraded by
Pioneer Electric to serve the biorefinery.
If Abengoa is responsible for the design
and construction of the transmission
line, DOE will require that the line be
designed and constructed to minimize
the risk of electrocution to raptors and
migratory birds. If Pioneer Electric is
responsible for the design and
construction of the new transmission
line or the upgrade of the existing line,
DOE will have no authority to impose
mitigation measures. However, a
transmission line constructed or
upgraded by Pioneer Electric would be
subject to additional NEPA review by
the U.S. Department of Agriculture
Rural Utilities Service (RUS). Further,
Pioneer Electric would follow RUS
standards for design and construction of
transmission lines, which include
consideration of raptors and migratory
birds.
Visual Resources Mitigation. The
buffer area will only be used for
agricultural activities, thereby
maintaining the current visual status of
this area. To minimize visual impacts
from nighttime light, the biorefinery
will have the minimum amount of
downward-facing or directional lighting
necessary for safe operation.
Wastes and Hazardous Materials
Mitigation. Abengoa will develop and
implement a waste management plan for
construction and operation of the
biorefinery. Abengoa will also develop
and implement a contingency plan for
alternative beneficial uses of the solid
biomass boiler fly ash in the event that
the waste management plan is not
effective.
Transportation Mitigation. To the
extent practicable, Abengoa will stagger
workforce schedules to minimize traffic
delays and congestion. Abengoa will
develop safety-based criteria to be used,
in part, to select carriers, including
elements of the Federal Motor Carrier
Safety Administration regulations, as
well as provisions for drivers to be paid
hourly and receive bonuses for accidentfree driving, mandatory safety training,
and avoidance of teen-age drivers and
drivers having less than 5-years
experience. Abengoa will require
carriers and drivers to meet the Federal
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17:25 Jan 11, 2011
Jkt 223001
Motor Carrier Safety Administration
regulations. In addition, to the extent
practicable, Abengoa will maximize the
use of rail shipments to and from the
Project site and will ensure the onsite
rail system does not block railroad
crossings near the site.
Issued in Washington, DC, on the 15th day
of December 2010.
Cathy Zoi,
Assistant Secretary, Energy Efficiency and
Renewable Energy, Department of Energy.
[FR Doc. 2011–480 Filed 1–11–11; 8:45 am]
BILLING CODE 6450–01–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–SFUND–2010–0437; FRL–9251–3]
Agency Information Collection
Activities; Submission to OMB for
Review and Approval; Comment
Request; Notification of Episodic
Releases of Oil and Hazardous
Substances (Renewal); EPA ICR No.
1049.12, OMB Control No. 2050–0046
Environmental Protection
Agency (EPA).
ACTION: Notice.
AGENCY:
In compliance with the
Paperwork Reduction Act (PRA) (44
U.S.C. 3501 et seq.), this document
announces that an Information
Collection Request (ICR) has been
forwarded to the Office of Management
and Budget (OMB) for review and
approval. This is a request to renew an
existing approved collection. The ICR,
which is abstracted below, describes the
nature of the information collection and
its estimated burden and cost.
DATES: Additional comments may be
submitted on or before February 11,
2011.
SUMMARY:
Submit your comments,
referencing Docket ID No. EPA–HQ–
SFUND–2010–0437, to (1) EPA online
using https://www.regulations.gov (our
preferred method), by e-mail to
superfund.docket@epa.gov, or by mail
to: EPA Docket Center, Environmental
Protection Agency, Superfund Docket,
Mailcode 28221T, 1200 Pennsylvania
Ave., NW., Washington, DC 20460, and
(2) OMB by mail to: Office of
Information and Regulatory Affairs,
Office of Management and Budget
(OMB), Attention: Desk Officer for EPA,
725 17th Street, NW., Washington, DC
20503.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Lynn Beasley, Office of Emergency
Management, Mailcode 5104A,
Environmental Protection Agency, 1200
PO 00000
Frm 00025
Fmt 4703
Sfmt 4703
2105
Pennsylvania Ave., NW., Washington,
DC 20460; telephone number: 202–564–
1965; fax number: 202–564–8444;
e-mail address: beasley.lynn@epa.gov.
SUPPLEMENTARY INFORMATION: EPA has
submitted the following ICR to OMB for
review and approval according to the
procedures prescribed in 5 CFR 1320.12.
On June 28, 2010 (75 FR 36653), EPA
sought comments on this ICR pursuant
to 5 CFR 1320.8(d). EPA received no
comments. Any additional comments on
this ICR should be submitted to EPA
and OMB within 30 days of this notice.
EPA has established a public docket
for this ICR under Docket ID No. EPA–
HQ–SFUND–2010–0437, which is
available for online viewing at https://
www.regulations.gov, or in person
viewing at the Superfund Docket in the
EPA Docket Center (EPA/DC), EPA
West, Room 3334, 1301 Constitution
Ave., NW., Washington, DC. The EPA/
DC Public Reading Room is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The
telephone number for the Reading Room
is 202–566–1744, and the telephone
number for the Superfund Docket is
202–566–0276.
Use EPA’s electronic docket and
comment system at
www.regulations.gov, to submit or view
public comments, access the index
listing of the contents of the docket, and
to access those documents in the docket
that are available electronically. Once in
the system, select ‘‘docket search,’’ then
key in the docket ID number identified
above. Please note that EPA’s policy is
that public comments, whether
submitted electronically or in paper,
will be made available for public
viewing at www.regulations.gov as EPA
receives them and without change,
unless the comment contains
copyrighted material, confidential
business information (CBI), or other
information whose public disclosure is
restricted by statute. For further
information about the electronic docket,
go to https://www.regulations.gov.
Title: Notification of Episodic
Releases of Oil and Hazardous
Substances (Renewal).
ICR numbers: EPA ICR No. 1049.12,
OMB Control No. 2050–0046.
ICR Status: This ICR is scheduled to
expire on January 31, 2011. Under OMB
regulations, the Agency may continue to
conduct or sponsor the collection of
information while this submission is
pending at OMB. An Agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information, unless it displays a
currently valid OMB control number.
The OMB control numbers for EPA’s
E:\FR\FM\12JAN1.SGM
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Agencies
[Federal Register Volume 76, Number 8 (Wednesday, January 12, 2011)]
[Notices]
[Pages 2096-2105]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-480]
-----------------------------------------------------------------------
DEPARTMENT OF ENERGY
Record of Decision for the Environmental Impact Statement for the
Proposed Abengoa Biorefinery Project Near Hugoton, Stevens County, KS
(DOE/EIS-0407)
AGENCY: Department of Energy, Office of Energy Efficiency and Renewable
Energy.
ACTION: Record of Decision.
-----------------------------------------------------------------------
SUMMARY: The U.S. Department of Energy (DOE or the Department) prepared
an environmental impact statement (EIS) (DOE/EIS-0407) to assess the
potential environmental impacts associated with the proposed action of
providing Federal financial assistance to Abengoa Bioenergy Biomass of
Kansas, LLC (Abengoa Bioenergy) to support the design, construction,
and startup of a commercial-scale integrated biorefinery to be located
near the city of Hugoton in Stevens County, southwestern Kansas (the
Project). The integrated biorefinery would use a combination of biomass
feedstocks, such as corn stover and wheat straw, to produce ethanol and
to generate sufficient electricity to power the facility and supply
excess electricity to the regional power grid. The Project site
comprises approximately 810 acres of row-cropped agricultural land. The
biorefinery facilities would be developed on 385 acres of the Project
site, and the remaining 425 acres would remain agricultural and act as
a buffer between the biorefinery and the city of Hugoton.
After careful consideration of the potential environmental impacts
and other factors such as program goals and objectives, DOE has decided
that it will provide Federal funding under Section 932 of the Energy
Policy Act of 2005 (EPAct 2005) of up to $71 million (2009 dollars),
subject to annual appropriations, to Abengoa Bioenergy for the Project.
A separate decision will be made regarding a potential loan guarantee;
and if DOE decides to proceed to consider the loan guarantee, DOE would
consider using the Final Abengoa Biorefinery EIS to comply with NEPA
review requirements for the loan guarantee. If DOE determines that the
Final Biorefinery EIS sufficiently addresses all activities covered by
the loan guarantee, DOE could either issue a Record of Decision (ROD)
deciding to issue a loan guarantee, or amend this ROD.
ADDRESSES: The Final EIS is available on the DOE National Environmental
Policy Act (NEPA) Web site at: https://nepa.energy.gov/ and on the
Abengoa Biorefinery Project Web site at: https://www.biorefineryprojecteis-abengoa.com. This ROD also is available on
these Web sites. Copies of the Final EIS and this ROD may be obtained
from Ms. Kristin Kerwin, Office of Energy Efficiency and Renewable
Energy, U.S. Department of Energy, Golden Field Office, 1617 Cole
Blvd., Golden, CO 80401; telephone: 720-356-1564; or fax: 720-356-1650.
FOR FURTHER INFORMATION CONTACT: To obtain additional information about
this Project, the EIS or the ROD, contact Ms. Kristin Kerwin by the
means specified above under ADDRESSES. For general information on the
DOE NEPA process, contact Ms. Carol M. Borgstrom, Director, Office of
NEPA Policy and Compliance (GC-54), U.S. Department of Energy, 1000
Independence Avenue, SW., Washington, DC 20585; telephone: 202-586-
4600; fax: 202-586-7031; or leave a toll-free message at: 1-800-472-
2756.
SUPPLEMENTARY INFORMATION: DOE prepared this ROD pursuant to the
Council on Environmental Quality regulations for implementing the
procedural provisions of NEPA [40 Code of Federal Regulations (CFR)
Parts 1500-1508] and the DOE NEPA regulations (10 CFR Part 1021). This
ROD is based in part on DOE's Final EIS for the Proposed Abengoa
Biorefinery Project (DOE/EIS-0407, August 2010).
Background
Under EPAct 2005, Congress directed DOE to carry out a program to
demonstrate the commercial application of integrated biorefineries for
the production of biofuels, in particular ethanol, from lignocellulosic
feedstocks. Federal funding for cellulosic ethanol production
facilities is intended to further the government's goal of rendering
ethanol cost-competitive with gasoline by 2012, and along with
increased automobile fuel efficiency, reducing gasoline consumption in
the United States by 20 percent within 10 years.
To implement its responsibilities under EPAct 2005, DOE issued a
funding opportunity announcement in February 2006 for the design,
construction, and startup of commercial-scale integrated biorefineries.
In February 2007, the Department selected Abengoa Bioenergy and five
other applicants for negotiation of award. Abengoa Bioenergy proposed
an innovative approach to biorefinery operations that would involve
production of biofuel and energy in the form of steam that could be
used to meet energy needs and displace fossil fuels, such as coal and
natural gas. The
[[Page 2097]]
proposal also included an integrated grain-to-ethanol facility.
In January 2009, Abengoa Bioenergy modified its proposal by
omitting the integrated grain-to-ethanol facility and including a
steam-driven turbine that would generate sufficient electricity to
power the production facility and supply excess electricity to the
regional power grid. In addition, Abengoa applied for a loan guarantee
from the Department's Loan Guarantee Program pursuant to Title XVII of
EPAct 2005, and from the U.S. Department of Agriculture Rural
Development Biorefinery Assistance Program pursuant to Section 9003 of
the Food, Conservation, and Energy Act of 2008. The Department of
Agriculture Rural Development was a cooperating agency in the
preparation of the EIS.
DOE considered Abengoa Bioenergy's proposed project changes and
concluded that the Project remained eligible for Federal funding under
Section 932 of EPAct 2005. On August 28, 2009, the Department
determined, however, that it would not proceed with Abengoa's request
for a DOE loan guarantee.
On December 22, 2009, after publication of the Draft Abengoa
Biorefinery Project EIS on September 23, 2009, Abengoa Bioenergy filed
a revised loan guarantee application, and in March 2010, the Department
determined that the proposed biorefinery was eligible for consideration
under Title XVII, Section 1703 of EPAct 2005, and requested that
Abengoa submit the Part II portion of its loan guarantee application.
Abengoa submitted the Part II application on May 14, 2010.
At this time, DOE is not proposing to issue a loan guarantee for
the construction and startup of the biorefinery. DOE is reviewing the
Part II submission and, pending the results of the Part II review, will
decide whether to initiate the due diligence, underwriting, and
negotiation phase of the loan guarantee process. If DOE initiates that
process with Abengoa, DOE's proposed action (that is, to issue a loan
guarantee) would be subject to NEPA review. If DOE decides to proceed
to consider the loan guarantee, DOE would consider using the Final
Biorefinery EIS to comply with NEPA review requirements for the loan
guarantee. If DOE determines that the Final Biorefinery EIS
sufficiently addresses all activities covered by the loan guarantee,
DOE could either issue a Record of Decision deciding to issue a loan
guarantee, or amend this Record of Decision.
The U.S. Department of Agriculture Rural Development also
considered Abengoa's application for a loan guarantee and did not
approve it for funding in Fiscal Year 2009. Should Abengoa submit an
application for a loan guarantee in the future, Rural Development will
use DOE's Final Biorefinery EIS as part of its evaluation of project
eligibility and sufficiency.
Purpose and Need for Agency Action
EPAct 2005, Section 932, directs the Secretary of Energy to conduct
a program of research, development, demonstration, and commercial
application for bioenergy, including integrated biorefineries that can
produce biopower, biofuels, and bioproducts. In carrying out a program
to demonstrate the commercial application of integrated biorefineries,
EPAct 2005 authorizes the Secretary to provide funds to biorefinery
demonstration projects to encourage (1) the demonstration of a wide
variety of lignocellulosic feedstocks; (2) the commercial application
of biomass technologies for a variety of uses, including liquid
transportation fuels, high-value bio-based chemicals, substitutes for
petroleum-based feedstocks and products, and energy in the form of
electricity or useful heat; and (3) the demonstration of the collection
and treatment of a variety of biomass feedstocks. Accordingly, DOE
needs to implement Section 932 of EPAct 2005 and support advanced
biofuel production pursuant to the Renewable Fuel Standard established
by the Energy Independence and Security Act of 2007 (EISA 2007). EISA
2007's Renewable Fuel Standard requires the U.S. Environmental
Protection Agency (EPA) to ensure that transportation fuel sold or
introduced in the United States contain at least 36 billion gallons per
year of biofuels by 2022, and includes specific provisions for advanced
biofuels, such as cellulosic ethanol and biomass-based diesel fuels.
Thus, DOE's purpose is to demonstrate that commercial-scale integrated
biorefineries that use a wide variety of lignocellulosic (second-
generation) feedstocks to produce biofuels, bio-based chemicals, and
biopower can operate without direct Federal subsidy after construction
costs are paid, and that these biorefineries can be easily replicated.
EIS Process
In August 2008, DOE published in the Federal Register its ``Notice
of Intent to Prepare an Environmental Impact Statement and Notice of
Wetlands Involvement for the Abengoa Biorefinery Project near Hugoton,
KS'' (73 FR 50001), starting a 45-day public scoping period during
which DOE held a public scoping meeting in Hugoton, Kansas. In April
2009, DOE re-opened public scoping and published in the Federal
Register its ``Amended Notice of Intent to Modify the Scope of the
Environmental Impact Statement for the Abengoa Biorefinery Project near
Hugoton, KS'' (74 FR 19543). The amended notice informed the public
about changes in the Project relevant to the scope of the ongoing EIS.
The Department conducted a 30-day public scoping period and held a
second public scoping meeting in Hugoton, Kansas. During these scoping
periods, the Department received oral and written comments of the
following three types: Expressions of support for the Project,
statements of no negative environmental impacts, and requests for
additional information from Federal and state agencies and members of
the public.
On September 23, 2009, DOE published in the Federal Register its
Notice of Availability for the Draft Environmental Impact Statement for
the Abengoa Biorefinery Project Near Hugoton, Stevens County, KS (DOE/
EIS-0407D) (74 FR 48525). DOE's Notice of Availability invited the
public to comment on the Draft EIS during a 45-day public comment
period, and described how the public could submit oral and written
comments on the Draft EIS. DOE's Notice also announced a public
hearing, which DOE conducted in Hugoton, Kansas on October 21, 2009. On
September 25, 2009, EPA listed the Draft Abengoa Biorefinery Project
EIS in its weekly notice of availability (74 FR 48951).
The Department received approximately 40 comments from six
commenters during the public comment period. DOE prepared a comment-
response chapter for the Final Biorefinery EIS (Chapter 10), which
provides each comment and DOE's response. One commenter reiterated
comments submitted during public scoping, and another commenter
submitted suggestions regarding region-specific studies for corn stover
removal and runoff index scores for agricultural lands. One commenter
recommended that the proposed transmission line be designed to protect
migratory birds and raptors. A few commenters expressed concern about
landfill management of refinery waste. A couple of commenters expressed
support for the Project. One commenter submitted a number of comments
regarding the impacts of biomass harvest on soil sustainability,
potential impacts to groundwater, the timeframe for construction of the
grain-to-ethanol facility, the use of the latest
[[Page 2098]]
biorefinery design for the air quality analysis, the site selection
process, and the reliance on irrigated corn crops.
DOE issued the Final EIS and on August 20, 2010, EPA listed the
Final Abengoa Biorefinery Project EIS in its weekly notice of
availability (75 FR 51458). The Final EIS reflects changes resulting
from public comments, and, accordingly, the responses in the comment-
response chapter identify sections of the Final EIS to which changes
have been made. The Final EIS also reflects changes based on new and
updated information. Substantive changes in the Final EIS are indicated
by vertical change bars shown in the margins. DOE received one comment
on the Final EIS from EPA, Region VII. EPA stated that DOE had
adequately addressed the concerns expressed in EPA's comments on the
Draft EIS.
Proposed Action and Project Description
DOE's Proposed Action is to provide Federal funding of up to $71
million (2009 dollars), subject to annual appropriations, to Abengoa
Bioenergy to support the design, construction, and startup of the
biorefinery, whose total anticipated cost is approximately $685 million
(2009 dollars).
The biorefinery would be constructed on a 385-acre parcel near
Hugoton, Kansas. Abengoa Bioenergy has optioned an additional 425 acres
immediately east of the biorefinery parcel, between the biorefinery and
the Hugoton city limits, as a buffer area. The optioned parcel would
continue to be used as agricultural land, and might be used to test
production of biomass feedstocks.
The biomass-to-ethanol and -energy facility proposed by Abengoa
Bioenergy would use lignocellulosic biomass (biomass) as feedstock to
produce biofuels. Biomass, including corn stover, wheat straw, milo
stubble, mixed warm season grasses (such as switchgrass), and other
available materials, would be harvested as feedstock and fermented to
produce ethanol.
The biorefinery would also produce biopower, or bioenergy, in the
form of electricity. The bioenergy generation facilities co-located at
the site would use direct-firing (that is, using the biomass as a solid
fuel in a boiler) to produce steam. Steam produced in the biomass
boilers would be used for facility processes and to produce
electricity.
Under the Proposed Action, the biorefinery would process
approximately 2,500 dry short tons per day of feedstock, which would be
obtained from producers within 50 miles of the Biorefinery Project
site. The biorefinery would produce up to 19 million gallons of
denatured ethanol per year and 125 megawatts of electricity. Seventy-
five megawatts of electricity would be sold commercially.
Construction of the biorefinery would take approximately 18 months
and would require infrastructure improvements, such as construction of
site roads that would tie to Rural Road P, a 1.5-mile-long electrical
transmission line, and an approximately 0.5-mile railroad spur on the
Biorefinery Project site that would tie into the Cimarron Valley
Railroad. Temporary connections to utilities would include electricity,
cable, telephone, and a nonpotable water line. Temporary potable water
and sanitary facilities would be provided onsite until construction of
permanent, onsite facilities.
Harvested bales of biomass would be transported to a 10-acre onsite
storage yard or to one of seven offsite storage sites to be located
within 30 miles of the Biorefinery Project site. Each offsite storage
location would be about 160 acres and would have no permanent
structures. Combined, these sites would store enough biomass to support
biorefinery operations for up to 1 year. Bales of corn stover and other
biomass ready to be processed at the biorefinery would be transported
to a bale barn and sent by conveyor for grinding and cleaning. The
ground feedstock would then enter the production process or be stored
temporarily in silos onsite. In addition, wood waste would be used as
boiler fuel to generate electricity. Up to 1,000 tons per day would be
brought from various sources by rail and truck to the biorefinery.
The ethanol production process would involve the following steps:
(1) Enzymatic hydrolysis and fermentation, (2) distillation and
dehydration, and (3) ethanol denaturization and storage. During
hydrolysis and fermentation, the feedstock would be treated with
enzymes and genetically modified organisms (enzymatic hydrolysis) to
simultaneously break down the cellulose and ferment the recovered
sugars. The resulting ``beer,'' which would be 4 to 5 percent ethanol
at that point, would then be distilled and dehydrated to remove water
and residual solids. Distillation would also destroy genetically
modified and other organisms.
The facility design incorporates two 45,200-gallon-capacity shift
tanks to hold the anhydrous ethanol produced during each 8-hour shift.
The storage tanks would be enclosed in a bermed area to contain spills.
Gasoline would be added to denature the ethanol and make it unfit for
human consumption prior to temporary storage and loading of the product
into tanker railcars for shipment.
Solids would be recovered from the distillation process.
Approximately 120,000 dry short tons of solids, referred to as lignin-
rich stillage cake, would be produced per year. The stillage cake would
be transferred by conveyor to an onsite third-party lignin producer.
After extracting the lignin, the lignin producer would return the
lignin-poor stillage cake to the biorefinery and Abengoa Bioenergy
would use it as fuel for the solid biomass boilers. Until a lignin
extraction facility is built, Abengoa would burn the lignin-rich
stillage cake as solid fuel in the biomass boilers. As an option,
Abengoa could use lignin-rich stillage cake as fuel for the solid
biomass boiler during the life of the biorefinery.
The biomass receiving, grinding, and storage operations would be an
enclosed system with a high-velocity, positive pressure collection
system to transfer airborne particles to a dirt loadout tank. The
loadout tank, grinding activities, and associated transfer points would
have fabric filter dust collectors (baghouses). Volatile organic matter
released during processing would be captured in a vent scrubber.
Approximately 1,900 dry short tons per day of biomass feedstock
would be supplied to the boilers. The biomass boilers would also burn
much of the waste resulting from ethanol production, including fines
collected during milling, stillage cake, and syrup from the
distillation process. These processes would produce approximately
127,000 tons of ash annually. This ash would contain potassium and
phosphorus and would be marketed to the contracted feedstock producers
as a soil amendment. If there is no market for the ash, it would be
sent to landfills.
Alternatives
In addition to the Proposed Action, the EIS analyzes an Action
Alternative and the No Action Alternative.
Action Alternative
Under the Action Alternative, DOE would provide Federal funding to
support the design, construction and startup of a biorefinery that
would use a two-stage process to produce fermentable sugars for
bioethanol production and that would produce syngas using a
gasification system. A syngas boiler as well as the biomass boilers
would produce steam. Steam would be used for ethanol production
[[Page 2099]]
processes and electricity production. Under the Action Alternative, the
biomass boilers and the turbines would be used to generate electricity
solely to operate the plant and would be smaller than those for the
Proposed Action.
The biorefinery would produce approximately 12 million gallons per
year of denatured ethanol, 19,000 short tons per year of lignin-rich
stillage cake, and 20 megawatts of electricity for use at the facility.
The milling process for the Proposed Action and Action Alternative
is the same. Once milled, the feedstock would be pretreated with dilute
acid to remove hemicellulose and pectin (the Proposed Action is a one
stage process and does not include two pretreatment stages as does the
Action Alternative). It is this pretreatment step and the subsequent
processing of the fractionated biomass where the two-stage process
differs from the one-stage process described in the Proposed Action.
After this pretreatment, two types of hydrolysate or pretreated biomass
would be processed in two separate steps. One type contains a
hydrolysate primarily consisting of hemicellulose and pectin, which
would be further saccharified to fermentable sugars; these simple
sugars would then be fermented to ethanol. The second type includes the
cellulose-rich, lignin-rich fiber hydrolysate, which would be further
processed with enzymes to produce simple sugars that would be
simultaneously fermented to ethanol. Each separate step produces beers
containing between 4 and 5 percent ethanol and both beers would be
conveyed to distillation operations for purification. Volatile organic
matter released during both of these processes would be captured in a
vent scrubber.
Approximately 71,000 dry short tons per year of soluble and
insoluble solids would be recovered from the bottom of the distillation
column. The soluble solids would be concentrated to a thin stillage
syrup in an evaporator and would be combusted in the biomass boilers.
About 130 dry short tons per day of insoluble, lignin-rich stillage
cake would be transferred to an onsite processing facility for
extraction of lignin. After the lignin was extracted, the lignin
producer would return the lignin-poor stillage cake to the biorefinery,
and Abengoa Bioenergy would use it as fuel for the solid biomass
boiler. Until a lignin extraction facility is built, Abengoa would burn
the lignin-rich stillage cake as solid fuel in the biomass boiler. If
recovery of lignin is not economically feasible, the lignin-rich
stillage cake would be used as fuel in the biomass boiler.Denaturing
the produced ethanol and loadout for the Proposed Action and Action
Alternative would be the same.
Syngas produced in the gasification plant under the Action
Alternative would be used to operate a fire-tube boiler to produce
steam. A small biomass solids boiler would also produce steam to power
the biorefinery process operations only. Steam would be used to operate
a small turbine that would produce 20 megawatts of power.
No-Action Alternative
Under the No-Action Alternative, DOE would not provide Federal
funding to Abengoa Bioenergy to support the design, construction, and
startup of a biorefinery. Abengoa would not build a biorefinery and the
biorefinery parcel would remain agricultural land. The Department
recognizes, however, that Abengoa could pursue alternative sources of
capital for development of the biorefinery.
Potential Environmental Impacts of the Proposed Action
In making its decision, DOE considered the environmental impacts of
the Proposed Action, Action Alternative, and the No-Action Alternative
on potentially affected resource areas. These include: land use; air
quality; hydrology; biological resources; utilities, energy, and
materials; wastes, byproducts, and hazardous materials; transportation;
aesthetics; socioeconomics; cultural resources; health and safety; and
environmental justice. DOE also considered potential impacts on these
resources from accidents and acts of sabotage. No wetlands would be
filled and no floodplains would be affected. The EIS also considered
cumulative impacts, that is, impacts from the Project combined with
those from other past, present, and reasonably foreseeable future
actions. The following sections discuss the potential impacts.
Land Use
Operation of the biorefinery would require approximately 880,000
dry short tons of lignocellulosic feedstock per year. Abengoa Bioenergy
anticipates that, at the start of operations, the primary feedstock
would be corn stover, with secondary feedstocks consisting of grain
sorghum stover, wheat straw, and mixed warm season grasses.
Approximately 20 percent of the total feedstock demand would consist of
corn stover for cellulosic ethanol production, with the remaining 80
percent consisting of any combination of feedstocks for bioenergy
production.
DOE conservatively estimates that the total annual demand for crop
residue by the biorefinery would equal about 60 percent of the targeted
crop residues that could be sustainably removed from the 50-mile region
surrounding the Biorefinery Project site. The demand for corn residue
for ethanol production would be about 20 percent of the amount that
could be sustainably removed from irrigated corn acreage. Thus,
production of targeted crop residues exceeds biorefinery demand and
Abengoa would have flexibility in feedstock procurement. DOE
anticipates the demand for crop residue by the biorefinery would have a
negligible impact on changes in land use type, including use of lands
in the Conservation Reserve Program, because there would be no
incentive to alter land use type for the purpose of meeting demand.
Over time, it is anticipated that mixed warm season grasses (such
as switchgrass) would replace corn residue as the primary feedstock for
producing ethanol resulting in (1) beneficial environmental impacts
where marginal cropland was converted, and (2) minimal environmental
changes where land use types such as nonharvested cropland, former
Conservation Reserve Program acreage, and pasture were converted. The
beneficial environmental impacts of converting marginal cropland to
mixed warm season grasses are related to establishment of a crop that
is resistant to many pests and plant diseases; uses relatively less
water, fertilizer, and pesticides; and establishes deep roots that
store carbon in the soil. Increased mixed warm season grasses
production would not be expected to result in an adverse impact to land
enrolled in the Conservation Reserve Program.
Contracts between Abengoa Bioenergy and producers of biomass would
include a requirement that crop residues would be harvested in
accordance with U.S. Department of Agriculture guidelines for
minimizing wind erosion. DOE concludes that, on a regional basis,
removing crop residue following these guidelines would have a
negligible adverse impact on soil organic matter content. On a field-
by-field basis, crop residue removal would have a negligible to minor
adverse impact on soil organic matter content. Any adverse impact to
soil organic matter content would be limited to land for which the
producer was compensated for residue removal.
Development of the biorefinery would result in the irreversible
conversion of 385 acres from agricultural to industrial use. The
Proposed Action is consistent with existing land use and zoning at the
[[Page 2100]]
Project site. The reduction in irrigated farmland associated with the
water rights Abengoa Bioenergy would transfer to industrial use at the
biorefinery would be a negligible change in regional irrigated
cropland.
Air Quality
Construction of the biorefinery would cause emissions from various
activities including use of heavy diesel-operated equipment,
disturbance of the soil, grading activities, material transport, and
material handling. These activities would be short term or intermittent
in nature and would only occur during the 18-month construction phase.
Best management practices would be employed to minimize these
emissions.
Concentrations of criteria pollutants estimated to be released
during operation of the biorefinery would be well below the National
Ambient Air Quality Standards. The estimated concentrations from the
biorefinery, combined with ambient background concentrations of
pollutants in the region, are about 67 percent of the National Ambient
Air Quality Standard for 24-hour PM10, 12 percent for
nitrogen dioxide, and less than 10 percent of the standard for other
pollutants. DOE concludes that air emissions would not harm human
health and the environment.
The biorefinery also would be a source of greenhouse gases, with
carbon dioxide the most abundant. The boilers would be the main source
of the greenhouse gases carbon dioxide, methane, and nitrous oxide.
Biomass fermentation and distillation processes also would emit carbon
dioxide. The total emissions of carbon dioxide equivalents (used to
represent the contribution of all gases) from operation would be 3.61
million tons per year. According to the DOE Energy Information
Administration, the total U.S. greenhouse gas emissions in 2008 was
7,775 million tons of carbon dioxide equivalents, with 6,409 million
tons of the total from energy-related carbon dioxide. The projected
greenhouse gas emissions from the biorefinery would be 0.046 percent of
the total U.S. carbon dioxide equivalent value.
Although the biorefinery would be a source of greenhouse gas
emissions, operation of the biorefinery would provide a net reduction
in greenhouse gas emissions when considering the emissions produced
during the lifecycle of ethanol production and use relative to the
lifecycle of gasoline production and use. To determine the level of
greenhouse gas reduction from the Proposed Action, DOE used the
Greenhouse gases, Regulated Emissions, and Energy use in Transportation
(GREET) Model, developed by DOE's Argonne National Laboratory. The
GREET Model examines ``well-to-wheel'' fuel lifecycles by considering
factors such as producing raw materials for fuels, refining the raw
materials into fuels, and using the fuel in vehicles.
The Abengoa Biorefinery Project would reduce greenhouse gas
emissions not only by producing a fuel that displaces gasoline, but
also by producing power that displaces electricity from other
electricity generating sources. The GREET Model combines these
reductions and other factors into a single metric to express the net
effect on lifecycle greenhouse gas emissions relative to a baseline
scenario in which the biorefinery is not built. Because the majority of
the electricity the biorefinery would produce would be exported rather
than used for biorefinery operations, the greenhouse gases displaced by
the biorefinery would be larger than the greenhouse gases emitted by
biorefinery operations, thus causing a decrease in greenhouse gas
emissions that exceeds 100 percent. As a comparison, if only enough
electricity was produced to run the biorefinery (none would be sold to
the grid), the percent reduction under the Proposed Action would be 69
percent as compared with the baseline where the biorefinery is not
built and passenger vehicles use 100 percent conventional or
reformulated gasoline.
Hydrology
Wastewater, petroleum products, and hazardous chemicals would be
generated by the biorefinery. Planned releases of wastewater would be
limited to the non-contact wastewater that would be used for irrigation
of the buffer area. Petroleum products and hazardous chemicals used
during construction and operations would be managed within secondary
containment on the site, and there are no surface waters in the nearby
area that would be affected by accidental releases.
Disturbed and built-up land areas would result in increased runoff;
this runoff would be directed to natural low areas within the
biorefinery parcel. Changes in infiltration would be minor and likely
would be limited to small changes in the exact locations where
infiltration would occur. Alterations to surface water drainage would
be limited to minor changes within the 385-acre parcel and possibly
within the buffer area. Natural low areas where runoff accumulates
would not be altered. The Department concludes the potential for
adverse impacts to surface waters from the Proposed Action is
negligible.
Construction of the biorefinery would require approximately 220
acre-feet of water, and operations would require about 2,900 acre-feet
of water per year. DOE estimates that an additional 46 acre-feet of
groundwater would be withdrawn per year by the city of Hugoton to meet
the domestic needs of biorefinery workers, bringing the total annual
estimated demand to support the biorefinery to approximately 2,950
acre-feet per year.
Abengoa Bioenergy has optioned existing irrigation water rights
from eight wells to meet the water demand for construction and
operation of the biorefinery under the Proposed Action. The maximum
permitted withdrawal associated with those water rights is about 7,240
acre-feet per year, and the total volume discharged from those wells in
2008 was about 4,380 acre-feet. Thus, use of those water rights for
operation of the biorefinery would result in a reduction of more than
4,290 acre-feet compared with the permitted annual volume, and a
reduction of more than 1,430 acre-feet compared with withdrawals during
2008. DOE concludes that operation of the biorefinery would result in a
beneficial decrease in groundwater withdrawals from the High Plains
aquifer.
Changes in cropping practices as a result of the Proposed Action
are not expected to occur. Further, increases in water withdrawals for
agricultural purposes in Kansas are limited by State water
appropriation regulations, although increases in Oklahoma and Colorado
may be allowed. Thus, DOE concludes that changes in water use in the
region resulting from changes in land use to meet the demand of the
biorefinery for biomass are not expected to occur.
Any spills of hazardous materials would be handled in accordance
with a spill prevention, control, and countermeasures plan, which would
minimize or eliminate potential impacts to the groundwater quality from
construction and operation of the biorefinery.
Biological Resources
There are no Federal- or state-endangered and/or threatened
species, candidate species, or state species in need of conservation
present or within 1 mile of the Biorefinery Project site. DOE concludes
that construction and operation of the biorefinery would have no
impacts on threatened or endangered species or their designated
critical habitat.
[[Page 2101]]
To construct the biorefinery, the biorefinery parcel, which is
currently used for dry-land farming, would be converted to industrial
use. There would be some minor, short-term adverse impacts to
biological resources from the construction and some minor, long-term
adverse impacts from the operation of the biorefinery, but these
impacts would affect only common species on or within 1 mile of the
Biorefinery Project site. The analysis of potential changes in land use
resulting from the Proposed Action indicated that conversion of
Conservation Reserve Program lands to tilled cropland from the Proposed
Action is not expected, and other changes in land use would be minimal.
Thus, DOE does not expect the Proposed Action to impact biological
resources within the region surrounding the Project site.
Utilities, Energy, and Materials
Biorefinery workers and their families would rely on the city of
Hugoton water system, the city of Hugoton sewage system, and the
Stevens County landfill. The Hugoton water system also would supply
potable water for the biorefinery facilities. Anticipated demands are
well below the excess capacity of the City water system. The sewage
collection system in Hugoton has sufficient capacity to accommodate use
of the system by construction and operations workers and their
families. In addition, the Stevens County landfill has enough capacity
to handle the increase in solid waste during construction and
operations due to the influx of workers and their families living in
Hugoton.
The biorefinery would require no electric power from the regional
grid during operations. Rather, the biorefinery would supply 75
megawatts of electricity to the grid during normal operations, which
equals 5.8 percent of the production capacity in the western-central
region of Kansas, but only about 0.2 percent of current summer demand
in the Southwest Power Pool. The amount of natural gas and diesel fuel
required for normal operation of the biorefinery is approximately 0.1
and 0.05 percent, respectively, of the amounts of these fuels used in
Kansas and would not adversely impact their supply and distribution in
the region.
The Proposed Action would involve a commitment of building
materials. With the possible exception of stainless steel, these
materials would be available and their procurement would not decrease
availability to other users in regional markets. Components used in
stainless steel production (such as chromium and nickel) are in high
demand and, at times, affect availability of stainless steel. However,
the amount of stainless steel required for construction of the
biorefinery is a very small portion of the amount that moves through
the U.S. market annually.
Wastes, Byproducts, and Hazardous Materials
The wastes and byproducts the biorefinery would produce include
construction wastes, wastewater, solid biomass boiler ash, distiller's
residual biomass solids (stillage cake), stillage syrup, wastewater
treatment facility sludge, lignin, genetically modified organisms, dirt
and fines resulting from biomass processing, municipal solid waste, and
hazardous waste.
Solid biomass boiler ash and lignin are byproducts that could be
sold to consumers within the 50-mile region of influence. Abengoa
Bioenergy would burn stillage cake, dirt and fines from biomass
processing, and genetically modified organisms in the solid biomass
boilers as part of the Proposed Action. Domestic and process wastewater
would be treated in the onsite wastewater treatment facilities, and
treated process wastewater would be recycled in the ethanol production
process. Wastewater treatment facility sludge would be used in the
boiler fly ash pelletization process or burned in the solid biomass
boilers. Abengoa would use non-contact wastewater for crop irrigation
on the buffer area, and would treat, recycle, and/or dispose of boiler
bottom ash, municipal solid waste, hazardous waste, and construction
debris at permitted facilities within the region of influence.
The Stevens County landfill would not have adequate capacity to
receive the construction wastes generated and maintain its small arid
landfill exempt permit status (limited to 20 tons per day); revising
that permit would be expensive. The non-recycled construction waste
streams would be split among other permitted landfills and transfer
stations within 35 miles of the biorefinery without significantly
affecting their capacity. Less than 1 ton per day of municipal solid
waste would be generated during the expected 30-year operating life of
the biorefinery and would be sent to the Stevens County landfill. This
waste stream would be about a 3 percent increase to the landfill's
current waste stream and would reduce the life of the landfill by less
than 1 year.
The onsite wastewater treatment facility would treat all process
wastewater generated at the Biorefinery Project site and would not
discharge any to the Hugoton wastewater system. Wastewater treated
onsite would be reused in the ethanol production process. Wastewater
that would not be recycled and reused in the production process or
treated onsite (non-contact wastewater) would be produced at a rate of
370 gallons per minute and would be used to irrigate biomass crops on
the buffer area. This water would be conveyed to two 11.5-acre storage
ponds prior to application to the buffer area. Wastewater treatment
facility sludge would be used in the boiler fly ash pelletization
process or burned in the solid biomass boilers. Based on an agronomy
study, the chemical composition of the wastewater and the anticipated
stipulations of a required discharge permit, DOE does not anticipate
adverse impacts from the land application of wastewater, including odor
or aesthetic impacts. Abengoa Bioenergy would have to modify the
facility water balance and wastewater treatment facility design if
lignin was extracted from the stillage cake, thereby generating
additional wastewater.
Chemicals required for operation of the biorefinery would be
received by truck or rail and off-loaded and transferred by an enclosed
chemical delivery system to storage tanks, silos, or other chemical
storage facilities. Chemicals would have to be obtained from outside
the region. The demand for chemicals for the biorefinery would be an
insignificant percentage of the production in the United States.
The Project would generate 2,000 pounds per year of hazardous waste
(for example, spent solvents, waste ethanol, and caustics). Those
wastes would be collected and treated/disposed of by licensed hazardous
waste facilities. DOE does not anticipate adverse impacts from the
handling and disposal of hazardous wastes generated at the biorefinery
because Abengoa Bioenergy's proposed hazardous waste management
practices will be implemented.
Genetically modified organisms used in the enzymatic hydrolysis
process would be killed by a heat sterilization process and would be
contained in the beer column bottoms. The bottoms stream would be
dewatered and the residual solids sent to the solid biomass boiler for
burning.
The solid biomass boilers would generate up to 16 tons of bottom
ash per day. The bottom ash would be sent to the Seward County
landfill. Disposal of the bottom ash at this landfill over the life of
the biorefinery would reduce the life of permitted landfill space by
about 2.2 years. In addition, the solid biomass boilers would generate
up to 350 tons of fly ash per day. Abengoa Bioenergy plans to sell the
fly ash as a nutrient
[[Page 2102]]
replacement co-product to biomass producers in the region. If the ash
could not be sold or otherwise used in a beneficial manner, it would
require disposal at permitted solid waste disposal facilities. The
Stevens County landfill does not have adequate capacity to receive this
amount of ash without a permit modification, so this waste stream would
be split among permitted landfills and transfer stations within 35
miles of the biorefinery. However, impacts on existing permitted solid
waste disposal facilities could be problematic if a significant
percentage of the boiler fly ash was not marketable as a soil amendment
byproduct. The loss of land used for landfill disposal of solid wastes
generated during construction and operation of the biorefinery would be
an irreversible and irretrievable loss of resources.
Transportation
There would be approximately 32,000 truck shipments of materials
during construction, and about 80,000 to 116,000 truck and 1,300 to
6,600 rail shipments per year during the 30-year operating period of
the biorefinery. DOE estimates there would be 35 to 41 traffic
fatalities during the 30-year operations period due to these shipments
and the commuting of workers, the majority (32 to 38) of which would be
due to shipments of biomass, chemicals, denatured ethanol product, and
waste. For perspective, over the 30-year operations period, there would
be an estimated 13,400 traffic fatalities in Kansas and 820 traffic
fatalities in the nine counties surrounding the Project site.
DOE estimates that 1,075 rail carloads of denatured ethanol and
waste and 211 to 5,554 rail carloads of biomass and chemicals would be
shipped to and from the biorefinery per year of operation, which is
equivalent to about 49 to 241 additional trains per year. This would
result in an increase in the approximately 600 trains per year that
travel on the Cimarron Valley Railroad, but is less than the capacity
of 40 to 60 trains per day on that line. Thus, the additional rail
traffic for the Proposed Action would not adversely affect the
operations of the Cimarron Valley Railroad.
Increased truck traffic would result in increased pavement
deterioration. For biomass, chemical, and waste shipments associated
with the Proposed Action, DOE estimated the annual cost of this
pavement damage to range from $580,000 to $840,000.
Aesthetics
DOE considered the potential impacts of the Abengoa Biorefinery
Project on views in the area surrounding the Biorefinery Project site
and evaluated how noise and odor from the biorefinery could affect
residents in the area.
Visual Resources--The tallest structure at the biorefinery
considered under the Proposed Action would be approximately 115 feet,
but many of the other structures would be 40 feet tall or less. The
biorefinery would be visually similar to the grain storage silos and
elevators, chemical tanks, and other structures located adjacent to the
Biorefinery Project site and would be visible from surrounding vantage
points, such as the city of Hugoton and the Forewinds Golf Course. The
Proposed Action would require a new 1.5-mile-long transmission line
that would be visible from Road P and Road 11 near the Biorefinery
Project site, but would result in minimal visual impacts to viewers
from a distance.
The biorefinery would operate 24 hours a day, 350 days a year, and
thus would be a source of night lighting.
Noise--Workers would be exposed to noise during construction from
construction equipment and trucks traveling to and from the biorefinery
construction site. Workers would also be exposed to noise from
equipment and biorefinery processes during operations. Best management
practices would be employed to limit noise, and a hearing conservation
program would be implemented; therefore, permissible noise exposure
levels are not expected to be exceeded.
The nearest residence to the Biorefinery Project site,
approximately 0.6 mile away, may experience some annoyance from
construction noise. The noise level at that distance would be
approximately 56 decibels which is approximately the same noise level
as a normal conversation.
In addition to being temporary, EPA states that this noise level
should not interfere with daily activities such as conversation,
working, or recreation. As such, the impact would be small. At 0.6
mile, noise from wood hog operations could be distinguishable from
other background sources of noise. Noise from biorefinery operations
would attenuate to below background levels beyond 0.6 mile. Therefore,
except for the residence at the northwest property boundary, DOE does
not anticipate impacts to members of the public from construction or
operation of the biorefinery due to noise.
During construction, there would be about 70 truck shipments to the
biorefinery site per day, or about one truck arriving every 12 minutes
(assuming all traffic occurs from 7 a.m. to 9 p.m.). During operations,
202 trucks per day are expected (one truck every 4 minutes). The routes
taken by those trucks through and around Hugoton would vary, but it is
anticipated that at least 50 percent of the traffic (one truck every 8
minutes during operations) would use the truck bypass and affect two
residences along Road Q. Along a route that passes the Stevens County
Hospital, several schools, and places of worship, trucks are
anticipated to pass at a rate of one every 21 minutes during
operations. Noise from these passing trucks would frequently interfere
with outdoor conversations and cause annoyance indoors. Rail traffic
would increase by about 255 trains per year. Most of the rail shipments
would carry wood waste and are expected to occur on weekdays during
normal working daylight hours.
Odor--Odors may result from emissions of volatile organic
compounds, including ethanol, and hazardous air pollutants, and from
nitrogen dioxide and sulfur dioxide. Engineered controls implemented to
minimize these emissions would reduce odors from the biorefinery. Air
dispersion modeling indicates that no odorous compounds would be
detected at the biorefinery parcel fence line or offsite locations
where the public would commonly be located. Therefore, DOE anticipates
no impacts to the public from the release of odorous compounds.
Socioeconomics
DOE evaluated the potential impacts of construction and operation
of the biorefinery on socioeconomic variables, including population and
housing, employment and income, taxes, and public services, in Stevens
County and the three surrounding counties; that is, Morton and Seward
counties in Kansas and Texas County in Oklahoma.
The Proposed Action would require 256 workers at the peak of
construction. About 190 of those positions likely would be filled by
people who would migrate into the four-county region, which would
result in a temporary increase in the population in the region of less
than 1 percent and would have little impact on the availability or cost
of housing or on public services. In addition to the jobs directly
associated with the construction of the biorefinery, 88 indirect jobs
are expected to be created during the peak period of construction. DOE
estimates that during construction, there would be about 110 additional
students enrolled in local school districts. This represents a 1.0
[[Page 2103]]
percent increase in enrollment in the region. During the 12-month
period of the most-intense construction activity, the region could
experience an approximately $17-million infusion of earnings, which
equals about 1 percent of the 2006 per capita income in the region.
The anticipated life of the biorefinery is 30 years, during which
it would employ 43 people. This would result in a regional increase in
the local population of less than 0.1 percent, and would have little or
no impact on housing, public services, or educational services. During
operations, the region would experience an annual $4.4 million infusion
in earnings. In addition, 23 indirect jobs are expected to be created
during the operations phase.
Cultural Resources
No properties listed on the National Register of Historic Places
are within or on properties adjoining the Biorefinery Project site.
Based on DOE review of published information, coordination with the
State Historic Preservation Officer, and the results of a Phase I/II
investigation of a 160-acre portion (areas investigated were
coordinated with the State Historic Preservation Officer) of the
Project site, construction and operation of the biorefinery would not
result in adverse impacts to State-preserved or National Historic
Register sites, sites of prehistoric or early historic occupation, or
historic resources of local significance. When selected, offsite
biomass storage locations will be evaluated for cultural resources in
coordination with the Kansas State Historical Preservation Office to
ensure no adverse impacts.
Health and Safety
DOE estimated health and safety impacts to workers from industrial
hazards using incidence rates for 2007 for both nonfatal occupational
injuries and occupational fatalities from the U.S. Department of Labor,
Bureau of Labor Statistics. Members of the public would not be located
within the Biorefinery Project site and would not be affected by
industrial hazards at the biorefinery.
The potential for adverse impacts to health and safety from the
Proposed Action would be very minor. During construction, the
industrial health and safety impacts to workers are estimated to be 14
total recordable cases (that is, work-related deaths, illnesses, or
injuries that result in the loss of consciousness, days away from work
restricted work activity or job transfer, or required medical treatment
beyond first aid), 7 days away from work, and 0.026 fatality. During
operations, the total annual industrial health and safety impacts to
workers from all operations at the biorefinery (such as, ethanol
manufacturing, milling and grinding operations, and electric power
generation) are estimated to be 2.7 total recordable cases, 0.94 day
away from work, and 0.0014 fatality. Based on these results, DOE
concludes that a fatality would be unlikely. No adverse health impacts
to members of the public from air emissions under normal operations are
anticipated.
Facility Accidents and Sabotage
Based on the operational history of existing ethanol plants, DOE
concludes that the hazards of ethanol production to members of the
public are minor, and that accidents during biorefinery operations are
not likely to result in permanent health effects to offsite members of
the public. In some accident scenarios, such as the failure of an
ethanol or gasoline storage tank, workers could be injured or killed
depending on the location of the worker at the time of the event.
DOE considered the most hazardous intentional destructive act to be
the deliberate destruction of a toxic chemical storage tank. The
consequences of such an act would be similar to the accidental failure
of a toxic chemical tank and would be limited to injury and, in
unlikely circumstances, death to nearby workers.
Environmental Justice
No impacts to communities with high percentages of minority or low-
income populations were identified that would exceed those identified
for the general population. In addition, during the scoping process,
DOE identified no unique exposure pathways, sensitivities, or cultural
practices that would result in different impacts on minority or low-
income populations. Disproportionately high and adverse impacts would
be unlikely as a result of the Proposed Action.
Potential Impacts of the Action Alternative
Under the Action Alternative, the environmental impacts would be
similar to those of the Proposed Action. For most resource and subject
areas, there are no or minor differences between those alternatives.
Differences exist between the alternatives for the following resource
and subject areas.
Air Quality--The Proposed Action would result in a greater
reduction in greenhouse gas emissions (340 percent) than the Action
Alternative (39 percent) by producing more fuel with biomass-derived
ethanol and producing more electricity from biomass.
Utilities--The Proposed Action would produce and sell electricity
in excess of that required to operate the biorefinery equal to about 5
percent of the production capacity in west-central Kansas. The Action
Alternative would produce less electricity and would require electrical
power from the regional grid to operate the biorefinery equal to about
1 percent of the combined production capacity of two suppliers in the
region.
Transportation--The Proposed Action would require substantially
more truck shipments than the Action Alternative during operations;
thus, the number of traffic accidents and amount of road damage would
be proportionally greater under the Proposed Action.
Noise--For operations, because there would be more truck shipments
for the Proposed Action, local residents would experience noise from
truck shipments more frequently under the Proposed Action than under
the Action Alternative.
Socioeconomics--Approximately 10 percent more workers would be
employed at the biorefinery under the Proposed Action, and more
earnings would be infused in the local economy.
Under the Action Alternative, the biorefinery would produce 33
percent less ethanol [12 million gallons (45 million liters)] and 80
percent less biopower (20 megawatts) than under the Proposed Action. In
addition, less salable byproducts, such as lignin and lignin-rich
stillage cake, would be produced under the Action Alternative.
Potential Impacts of the No-Action Alternative
Under the No-Action Alternative, none of the adverse impacts
identified above for the two action alternatives (for example,
emissions of air pollutants, use of land for disposal of solid wastes,
increase in truck traffic, and associated increase in accidents and
noise) or beneficial impacts (for example, increased employment,
decrease in groundwater use, and increase in the electrical production
capacity for the region) would occur. Further, the benefits that would
be gained from the development, demonstration, and commercial operation
of an integrated biorefinery that uses lignocellulosic feedstocks would
not be realized. In addition, no benefits would be realized from the
development of a renewable energy system that would reduce air
pollutants and sequester emissions of greenhouse gases. For example,
the reductions in greenhouse gas emissions estimated to occur if the
Proposed
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Action were implemented would not be realized with the continued use of
gasoline instead of biofuel and no generation of biopower.
Environmentally Preferred Alternative
The Proposed Action and Action Alternative would result in both
beneficial and adverse potential environmental impacts (summarized
above and in Table 2-2 of the EIS). Potential beneficial impacts
include those associated with reductions in greenhouse gas emissions
and a decrease in water withdrawals; adverse impacts include those
associated with a substantial increase in transportation activity and
minor impacts from air emissions. On balance, DOE regards the No-Action
Alternative, which would result in no change in existing environmental
conditions, as the environmentally preferred alternative.
Decision
DOE has decided to implement the Proposed Action to provide Federal
funding of up to $71 million (2009 dollars), subject to annual
appropriations, to Abengoa Bioenergy Biomass of Kansas, LLC (Abengoa
Bioenergy) to support the design, construction, and startup of the
Abengoa Biorefinery Project. DOE has also decided to adopt the
mitigation measures discussed in the Final Abengoa Biorefinery EIS and
summarized below under ``Mitigation''.
Basis of Decision
DOE's decision is based on the importance of achieving the
objectives of the EPAct 2005 and careful review of the potential
environmental impacts presented in the Final Biorefinery EIS. This
Project will support advanced biofuel production pursuant to the
Renewable Fuel Standard established by EISA 2007, which requires EPA to
ensure that transportation fuel sold or introduced into commerce in the
United States contain at least 36 billion gallons per year of biofuels
by 2022. It provides an opportunity to demonstrate that commercial-
scale integrated biorefineries that use a wide variety of
lignocellulosic (second-generation) feedstocks to produce biofuels and
biopower can operate without direct Federal subsidy after construction
costs are paid, and that these biorefineries can be easily replicated.
The Project would reduce greenhouse gas emissions not only by
producing a fuel that displaces gasoline, but also by producing power
that displaces electricity from other electricity generating sources.
In addition, this Project would have economic benefits in the region.
The Project would require 256 workers at the peak of construction and
during the 12-month period of the most-intense construction activity,
the region could experience an approximately $17-million infusion of
earnings. Over the anticipated life of the biorefinery of 30 years, it
would employ 43 people and the region would experience an annual $4.4
million infusion in earnings.
To meet the mandates of the EPAct 2005 and other governing
policies, it is in the best interest of DOE to select and fund the most
technologically and economically viable alternative. Production of more
ethanol and production of biopower would make the Proposed Action a
more economically viable alternative than the Action Alternative. The
Proposed Action, therefore, better meets the direction of Section
932(d)(2) of EPAct 2005, which directs the Secretary of Energy to
select only proposals that ``demonstrate that the project will be able
to operate profitably without direct Federal subsidy after initial
construction costs are paid.'' In addition, the Proposed Action more
fully supports the intent of the Section 932(d)(1) of EPAct 2005 to
encourage the commercial application of biomass technologies for a
variety of uses, including high-value bio-based chemicals and energy in
the form of electricity and useful heat. For these reasons, DOE
determined the Proposed Action more fully meets its purpose and need,
and has decided to implement the Proposed Action.
This decision incorporates all practicable means to avoid or
minimize environmental impacts. DOE plans to review annual monitoring
reports to assess the environmental impacts predicted in the EIS and
the implementation of appropriate avoidance and mitigation measures.
Mitigation
DOE's decision incorporates best management practices and
additional measures to avoid or minimize adverse environmental impacts
during the design, construction, and operation of the Project. DOE will
require Abengoa Biorefinery to implement the best management practices
outlined in Chapter 6, Section 6.1, of the Final Biorefinery EIS, for
the following resource areas: land use; air quality; geology and soils;
surface water; groundwater; biological resources; utilities, energy,
and materials; wastes and hazardous materials; visual resources; noise;
odor; cultural resources; and health and safety.
DOE regards mitigation measures as activities or actions that would
be above and beyond (in addition to) best management practices. DOE
requires that the participants comply with all applicable Federal,
state, and local environmental laws, orders, and regulations.
Mitigation measures beyond those specified in permit conditions will be
addressed in a mitigation action plan (MAP) that DOE will prepare
pursuant to 10 CFR 1021.331. The MAP will explain how the mitigation
measures will be planned, implemented, and monitored and is an adaptive
management tool. Mitigation conditions in it will be removed if
equivalent conditions are otherwise established by permit, license, or
law, as compliance with permit, license or regulatory requirements are
not considered mitigation activities subject to DOE control and are
therefore not included in MAPs.
DOE will ensure that commitments in the ROD are incorporated into
DOE's Cooperative Agreement with Abengoa Bioenergy. The MAP and annual
monitoring reports will be available on the DOE NEPA Web site (https://www.nepa.energy.gov) and the DOE Golden Field Office Web site (https://www.eere.energy.gov/golden/Reading_Room.aspx). DOE will make copies of
the MAP available for inspection in appropriate locations (e.g., local
library or DOE reading rooms) for a reasonable time. The Department
also will provide copies of the MAP and annual reports upon request.
In the Final EIS, DOE stated that mitigation measures for the
following resource areas were being considered: air quality, biological
resources, visual resources, odor, socioeconomics, wastes and hazardous
materials, and transportation. Upon consideration of the findings
presented in the Final EIS, DOE has determined that no mitigation is
required for air quality, odor, or socioeconomic impacts. The required
implementation of air quality best management practices presented in
Section 6.1 will adequately minimize impacts and therefore no
additional mitigation is required. While the EIS concludes that odor
may result from emissions of volatile organic compounds, it also
concludes, based on air dispersion modeling, that there are no
anticipated impacts to the public from the release of odorous compounds
and therefore no mitigation is required. The EIS concludes that the
impacts to community services would be temporary and not likely to
place an undue demand on community services, and therefore no
mitigation is required.
Biological Resources Mitigation. While the EIS concludes that DOE
does not expect the Proposed Action to
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impact biological resources (including threatened and endangered
species) within the region or the Project site, DOE acknowledges that
the new transmission line should be designed to minimize impacts to
raptors and migratory birds. At this time it is uncertain whether
Abengoa or Pioneer Electric Cooperative, Inc. (Pioneer Electric) will
be responsible for the design and construction of the new transmission
line, or if an existing transmission line will be upgraded by Pioneer
Electric to serv