United States
Environmental Protection
Agency
Industrial Environmental Research  -
Laboratory
Research Triangle Park NC 27711   "'fW x"
Research and Development
EPA-600/S9-81-019  Oct. 1981
Project Summary
Proceedings:  Symposium  on
Flue Gas  Desulfurization
Houston,  October  1980
Franklin A. Ayer
  These proceedings for the sympo-
sium on flue gas desulfurization FGD
constitute the final report submitted
to the Industrial  Environmental Re-
search Laboratory, U.S. Environmen-
tal Protection Agency, Research Tri-
angle Park, NC. The symposium was
conducted  in Houston, TX,  October
28-31, 1980.

  This symposium provided a forum
for  the exchange  of information,
including recent  technological  and
regulatory developments,  on  the
application of FGD to utility  and
industrial  boilers. The program in-
cluded a Keynote  Address on the
approaches for control of acid rain,
forecasts of energy and environmental
technologies and  economics for the
1980's, and sessions on the impact of
recent legislation and regulations,
research and development plans,
utility applications, by-product utiliza-
tion, dry scrubbing, and industrial
applications. Participants represented
electric  utilities,   equipment  and
process suppliers, state environmental
agencies, coal and petroleum sup-
pliers, EPA, and other Federal agencies.

  This Project Summary was devel-
oped by EPA's Industrial Environmen-
tal Research Laboratory, Research
Triangle Park. NC. to announce key
findings of the research project that is
fully documented in a separate report
of the same title (see Project Report
ordering information at back).
Proceedings: Symposium on
Flue Gas Desulfurization
Houston, October 1980

  This report summarizes the proceed-
ings of  the Symposium on Flue  Gas
Desulfurization (FGD), held on October
28-31,  1980, in  Houston, TX.  The
symposium brought together repre-
sentatives of the Federal government,
state and local governments, oil  and
chemical companies, electric  utilities,
architecture/engineering  companies,
process suppliers, equipment suppliers,
academia, research firms, and associa-
tions for the purpose of  providing a
forum for the exchange of information
including recent  technological  and
regulatory developments,  on  the ap-
plication of FGD to utility and industrial
boilers. The symposium was sponsored
by EPA's Industrial Environmental
Research Laboratory in Research Tri-
angle Park, NC (IERL-RTP).
  Michael A. Maxwell, Chief, Emis-
sions/Effluent Technology Branch,
EPA, IERL-RTP, welcomed the partici-
pants and outlined the purpose of the
meeting. The  keynote speaker  was
Stephen J. Gage,  Assistant Adminis-
trator for Research and Development,
EPA, Washington, DC, who  gave a
presentation on the approaches for
control of acid rain. Gage said that one
new control technology that shows
promise would simultaneously control
both of the major  components of  acid
rain—nitrogen oxides (NO,) and sulfur

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dioxide (SO2). This new control tech-
nology can be retrofitted to many
existing coal-fired boilers with only
minor modifications: the limestone
injection/multistage burner, or LIMB.
Frank T.  Princiotta,  Director  of EPA's
Energy Process Division, discussed the
nation's future with a focus on synthetic
fuels. Projections indicate that coal,
nuclear energy,  and oil shale will
become increasingly important as we
minimize oil  imports through adjust-
ments in static oil and gas production.
Gerald McGlamery,  Chief, Pilot Plant
Design and Construction,  Tennessee
Valley Authority  (TVA), discussed the
economics  of FGD  systems.  Jumpei
Ando, Chuo University of Japan, covered
S02 and NOX abatement for coal-fired
boilers in his country. FGD systems are
performing  reliably and effectively  in
improving the air quality in Japan.
  Walter C. Barber, Deputy Assistant
Administrator for Air Quality Planning
and Standards, EPA, chaired a panel on
the impact of recent legislation/regula-
tions under the Clean Air Act (CAA), the
Clean Water Act (CWA), and the
Resource Conservation and Recovery
Act (RCRA) on FGD systems. Other
panel members  included John Lum,
Senior Project Officer, Office of Water
Planning and Standards, EPA, and
Penelope Hansen, Program Manager of
the Minerals and Energy  Program,
Office of Solid Waste, EPA.

  FGD research and development plans
were discussed by three speakers: B.A.
Laseke,  Project Director, PEDCo Envi-
ronmental,  Inc.,  on recent  trends  in
utility flue gas desulfurization; Edward
Trexler, Program  Manager for  Demon-
stration, Department of Energy (DOE),
on DOE's FGD research and develop-
ment program;  and  Stuart  Dalton,
Program Manager, Desulfurization
Processes,  Electric Power  Research
Institute (EPRI), on  EPRI  research
results in FGD—1979-1980.
  Utility applications of FGD  systems
were  discussed  by  several speakers:
Dewey  Burbank, Project Manager,
Shawnee Program,  Bechtel  National,
Inc., test results on adipic-acid-enhanced
limestone scrubbing at the EPA Shawnee
Test  Facility; William Wells, TVA,
cocurrent scrubber and DOWA process
testing—Shawnee Test Facility; Dale
Hicks,  City Utilities, Springfield,  MO,
FGD experiences at Southwest Unit 1;
Thomas  Morasky, Project  Manager,
EPRI, results of the Chiyoda Thorough-
bred-121 prototype evaluation;  R.A.
Runyan, Project Manager, TVA, forced
oxidation of limestone scrubber sludge
at TVA's Widows Creek Unit 8 Steam
Plant; Richard Spring, Superintendent
Air  Quality Control, La Cygne Station,
Kansas City Power & Light Company, La
Cygne  Station  Unit  1  wet  scrubber
operating experience; Royce Hutcheson,
Plant Superintendent  of Environmental
Results, Alabama Electric Cooperative,
Inc., one-button operation: start-up and
operation  of  the  Alabama  Electric
Cooperative FGD System; Robert Hewitt,
Mechanical  Engineer, Texas Utilities,
operation and maintenance experience
of the world's largest spray tower S02
scrubbers; Robert Van Ness, Manager,
Environmental Affairs, Louisville Gas &
Electric  Company, operating and main-
tenance experience with the dual alkali
system  on Louisville  Gas & Electric
Company's Cane Run Unit No. 6; James
Van Meter, Director of  Power Produc-
tion and Procurement, Southern Indiana
Gas and Electric Company, operating
experience on the  FMC double alkali
system;  Earl  Mann, Executive Manager,
Electric  Production, Northern Indiana
Public Service Company, status report
on  the Wellman-Lord/Allied  Chemical
FGD plant at Northern Indiana Public
Service  Company's  Dean  H.  Mitchell
Station;  and Landon Fox, Staff Specialist,
TVA, magnesium FGD at TVA: pilot and
full scale.
  An overview of FGD  by-product
disposal and utilization was presented
by  session chairman Jerome Rossoff,
Director, Fossil Energy Technology, The
Aerospace Corporation. Other speakers
who followed  Rossoff were: Chakra
Santhanam,   Management Staff,  A.D.
Little, Inc., characterization and  envi-
ronmental  monitoring of full-scale
utility waste disposal sites—a status
report; Val Weaver, Program Manager
for  Waste Management, DOE, assess-
ment of the  economic impact of RCRA
on  the  electric utility  industry;  Dean
Golden,  Project Manager,  EPRI,  FGD
sludge disposal demonstration and site
monitoring  projects  at EPRI;  Gerald
Groenwold,  Geologist, North  Dakota
Geological Survey, potential effects on
ground  water of fly ash and FGD waste
disposal in lignite surface mine pits in
North Dakota; Iver Duedall, Professor,
Marine Sciences  Research Center,
State University of New York, at Stony
Brook, environmental compatibility, and
engineering  feasibility for utilization of
FGD waste  in artificial fishing reef
construction; and  Penelope Hansen,
Office of Solid Waste, EPA, government
procurement of cement and concrete
containing fly ash.
  At the symposium an evening session
was held on the subject of dry scrubbing.
Speakers and their topics were: Gerald
McGlamery, Chief, Pilot Plant Design
and Construction, TVA,  spray dryer
FGD:  technical  review and economic
assessment;  Marvin Drabkin, Senior
Systems Engineer, Mitre  Corporation,
spray dryer FGD capital and operating
cost estimates for a northeastern utility;
Mary E. Kelly, Chemical Engineer,
Radian Corporation, current  status of
dry FGD systems; Nicholas  Stevens,
Manager,  Chemical Process  Develop-
ment, Research-Cottrell, Inc.,  dry S02
scrubbing pilot test results;  Edward
Parsons, Engineering  Consultant  in
Product Design, Envirotech Corporation,
SO2 removal  by dry FGD;  and Thomas
Hurst, Babcock & Wilcox Company, dry
scrubber demonstration plant operating
results.


  Industrial applications of FGD systems
were  discussed  by several speakers:
James Dickerman, Program Manager,
Radian Corporation, applicability of FGQ
systems to industrial  boilers; Charles
Sedman, Environmental Engineer-Air,
Office of Air Quality Planning and
Standards (OAQPS), EPA, SO2 emission
data and status of the new development
of  industrial  boiler new  source per-
formance standards; Avi Patkar, Project
Manager,  PEDCo  Environmental, Inc.
applicability of FGD systems to oilfielc
steamers and sodium waste  dispose
options; Theodore Brna, Manager
Abatement Engineering, EPA, perform
ance evaluation of an industrial spra^
dryer for SO2 control;  and Rober
Giammar, Associate Manager of Fuel;
and Combustion,  Battelle Columbus
Laboratories,  application of the coal/
limestone pellet process to stoker-coal
fired boilers.

  In closing,  Michael  Maxwell,  Chief
Emissions/Effluent Technology, EPA
indicated that the symposium provide)
the necessary foru m for the excha nge o
information, including  the recent tech
nological and regulatory development
on the application of FGD to utility am
industrial boilers.

  Summaries  or abstracts of thi
speakers' remarks follow:           I

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 Michael A. Maxwell, Chief,
 Emissions/Effluent
 Technology Branch, EPA,
 IERL-RTP
   Maxwell welcomed the participants
 and outlined the scope of the sympo-
 sium. He stressed the need for exchang-
 ing information on FGD technology
 developments, including the techno-
 logical and  regulatory aspects, on the
 application of FGD to utility and industrial
 boilers.

 Stephen J. Gage, Assistant
 Administrator for Research
 and Development,
 EPA - Washington
   Gage, in his keynote address, stressed
 the need to move away from our
 dependence  on foreign oil to greater
 reliance on coal where the U.S. has one
 of the greatest known reserves existing
 anywhere in the world. The President
 and the Congress have mandated this
 conversion to coal as part of the overall
 National  Energy  Plan.  The energy
 supply structure emphasizes the  con-
 servation  and use of domestic coal, oil
 shale, unconventional natural gas, and
 heavy oil (rather than the predominantly
 oil-based  structure).
   He explained that this means mining
 and burning "dirtier" fuels which could
 cause a growing air pollution problem.
 He pointed out that we must maintain
 air quality as the production of pollutants
 from burning fossil fuels rapidly expands.
   New source performance standards
 and those forthcoming are examples of
 recent environmental protection efforts
 to  continue  R & D  of environmental
 control technologies.
   Gage stated that FGD  systems are
 performing reliably and effectively both
 here and  abroad. The growing use of
 FGD means that the amount  of SOX
 emitted to the atmosphere is expected
 to remain constant or decrease slightly
 by the turn of the century.
   According  to Gage, EPA has  been
 aggressively pursuing an air emissions
 program  to control SOX, NOX and
 particulates—all released from the
 burning of coal and all contributors to
 the growing problem of acid  rain.
 Gage's concern  is  that acid rain may
 become  one  of the most significant
 environmental problems of the coming
 decade.   EPA must first  solve the
 perplexing mechanism by which acid
 rain is  formed in  order  to minimize
Lcostly investments  for  control.  In
addition to  EPA's efforts, many gov-
ernment agencies as well as private
industry are participating in  these
efforts.
  Besides generating information on
acid rain that can be used to develop air
quality control strategies and options.
Gage  said  that another fundamental
task was to communicate to Congress
and the public the effects of acid rain.
One  tool to  accomplish this is the
development  of  an  "acid deposition
document" that will attempt to quantify
and qualify the  entire  range  of pol-
lutants involved in acid rain creation.
  A new technology discussed by Gage
to control acid rain's major components,
SC>2 and NOX, which-shows promise and
which may be retrofitted to many coal-
fired boilers, was the limestone injec-
tion/multistage burners, or LIMB. LIMB
in the U.S.  is at the  bench/pilot scale
stage of development while Germany is
currently operating a 60-MW electric
boiler using the technology.
  Gage concluded by emphasizing the
need  for government and industry
working together to support the national
energy policy to expand the use of coal,
and he was sensitive to the fact that the
economy cannot regain its vital growth
without the aid of a vigorous industrial
base.

Frank T. Princiotta, Director,
Energy Processes Division.
EPA - Washington
  Projections indicate that coal, nuclear
energy, and  oil shale  will become
increasingly important as we adjust for
static  domestic oil and gas production
and minimization of  oil imports. Envi-
ronmental problems can be quite severe
for each of these fuel cycles. A massive
synthetic fuel industry based on coal, oil
shale, and  biomass  is emerging with
monumental potential for environmen-
tal damage. The Environmental Protec-
tion  Agency  (EPA)  has  designed  a
regulatory program aimed at mitigating
environmental damage while allowing
for birth and  nurturing  of this critical
industry.

Gerald G. McGlamery, Chief,
Pilot Plant  Design and
Construction  Branch, Energy,
Demonstration and
Technology Division,
Tennessee  Valley Authority
  This paper reviews  recent  results
from EPA-sponsored flue gas desulfuri-
zation  and byproduct/waste disposal
economic evaluations prepared by TVA.
Included are a summary of comparative
capital investments and annual revenue
requirements from a three-phase effort
to evaluate the leading FGD processes,
and similar results from three phases of
sludge disposal studies.  Data from a
1985  projection of  FGD  byproduct
sulfur/sulfuric acid marketing potential
are given.
  A new series of FGD process evalua-
tions is also previewed, including a set
of updated evaluation premises which
will be utilized  in the early 1980's.
Examples  of the  effects of the revised
premises on limestone scrubbing eco-
nomics are shown. Finally,  results are
provided from  a  recent evaluation of
limestone  scrubbing in a spray tower
using  adipic acid, forced oxidation, and
gypsum disposal by stacking.

Jumpei Ando, Professor,
Science and Engineering,
Chuo University
  The total capacity of coal-fired utility
boilers in Japan, which was only 4,300
MW (3.7% of total utility power) in 1979,
is expected to increase to 10,000 MW
(5.6%) in  1985,  and to  22,000 MW
(10.0%) in  1990. Most of the boilers will
apply  FGD by the wet  limestone-
gypsum process because of its reliability
and relatively low cost. To save energy
and water, FGD  systems with  a  low
pressure  drop  and small water con-
sumption are preferred. Tests on FGD by
a dry carbon process are underway.
  NOX concentrations in flue gases from
existing coal-fired boilers  have been
lowered to 200-350 ppm by combustion
modification including staged combus-
tion and the use of Iow-N0x burners. For
further abatement, selective catalytic
reduction  (SCR) has started  to  be
applied to several coal-fired boilers. The
first full-scale  combination system of
SCR and FGD was put into operation in
April 1980. The plant cost  for SCR is
about  one-third that for  FGD. A new
combustion technology has also been
developed  in  attempts to  lower NOX
below 100 ppm.

B.A.  Laseke. Jr.. Project
Director, PEDCo
Environmental, Inc.
  PEDCo  Environmental, Inc.,  under
contract to the Industrial Environmental
Research Laboratory-RTP and the Divi-
sion of Stationary Source Enforcement
of the U.S. Environmental Protection

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Agency, has been monitoring the status
of utility flue gas desulfurization (FGD)
technology since 1974. Information for
this  program  is obtained by visits to
plants having operational FGD systems
and  through  periodic contacts with
representatives of utility companies,
FGD system and equipment suppliers,
system  designers, research organiza-
tions, and regulatory agencies.
  This paper summarizes the status of
utility FGD technology as of the end of
August 1980 and indicates recent
trends in both the design and perform-
ance of the FGD systems. The discussion
of current status includes the number of
capacity of operational  and planned
FGD systems, as well as identification of
the systems according to process type,
emission  control  strategy, S02 inlet
concentration  levels, and removal ef-
ficiencies. Process design developments
and  trends are summarized  for the
major components  and  subsystems
associated with commercial FGD sys-
tems. In discussing  FGD  system per-
formance, composite graphs  are in-
cluded  presenting annual system
availability data (through June 1980}for
low-, medium-, and high-sulfur  coal
FGD installations. A statistical analysis
of the data for the years 1978 and 1980
indicates overall trends in FGD system
dependability.  Finally,  capital  and
annual  cost  data (both  reported and
adjusted) are  included for the opera-
tional FGD systems and cost model
comparisons are made.
  The current data indicate that 203
FGD systems are either  operational,
under construction, or planned (as of
August  1980),  representing  a total
controlled capacity  of about  97,000
MW. Of the 203 systems,  73 are
operational, representing  27,155 MW
of controlled capacity. The dependability
analysis indicates  that  the  overall
median availability for these operational
systems has  increased 1.5%, 16.5%,
and 50.6% for low-, medium-, and high-
sulfur coal FGD  installations,  respec-
tively, between the years  1978 and
1980.

Edward C.  Trexler, Program
Manager for Demonstration,
Office of Coal Utilization,
U.S. Department of Energy
  The Department of Energy's flue gas
desulfurization (FGD) research and
development activities are conducted as
part of  the Advanced Environmental
Control  Technology Program (AECT)
which is managed within the organiza-
tion of the Assistant Secretary for Fossil
Energy. This new AECT program was
initiated in FY  1979 with a  goal to
identify, research, develop, refine, and
demonstrate equipment that will clean
flue gas for compliance with existing
and anticipated environmental pollution
regulations, and equipment that  will
remove the undesirable components
from coal-derived gas streams to ensure
reasonable life for utilization equipment
such as gas turbines and fuel cells. The
flue gas cleanup portion of the AECT
program budget amounted to $2.7
million in FY 1979 and $20.1 million in
FY 1980.
  The FGD project  is divided into two
parallel efforts identified by the scheduled
completion dates as very near-term (end
1983) and  near-term (end 1986). The
very near-term effort aims at improving
the S02 removal efficiency and reducing
the waste disposal problems of conven-
tional lime/limestone scrubbers. This is
being  done in coordination with EPRI
and EPA scrubber  improvement pro-
grams, through private sector scrubber
instrumentation and analysis, by tests
at TVA and other utility prototype and
full-scale  scrubber facilities,  and by
transfer of process improvement  in-
formation. The near-term effort is aimed
at supporting newer technology  S02
removal processes  that include non-
regenerable (throwaway) and regen-
erable systems that produce potentially
marketable by-products such as sulfur
and sulfuric acid. These technologies
are, or will, be under experimental test
at Fossil  Energy Technology Centers,
under prototype testing by  DOE  and
EPRI at TVA and other sites, and under
initial  commercial  use evaluation by
DOE at  power stations and industrial
plants. As these technologies  mature,
private industry will be encouraged to
cost-share development with the Gov-
ernment. Information on progress will
be disseminated via reports, symposia,
plant visitations, demonstrations, and
workshops.

Stuart M. Dalton, Program
Manager, Desulfurization
Processes, Electric Power
Research Institute
  EPRI has a  research  effort of about
$10 million/year in flue gas desulfuri-
zation covering engineering evaluations,
field testing, bench testing, pilot plants,
prototypes, and  demonstrations. This
paper reports  selected results from
projects  on FGD water  integration,
gypsum crystallization,  limestone dis-
solution,  wet stack operation, sulfur
production via RESOX, absorption/steam
stripping, cyclic  reheat,  and integrated
emission control.  A brief review  of
current demonstration plans  and pro-
gram emphasis is also included.

Dewey A. Burbank. Project
Manager, Shawnee Program,
Bechtel National, Inc.
  Adipic acid has been demonstrated as
a powerful  scrubbing additive for en-
hancing SOa removal in lime and lime-
stone wet scrubbing tests both at the
EPA/IERL  pilot plant at Research
Triangle  Park, NC,  and at the EPA-
sponsored Shawnee Test Facility  near
Paducah,  KY.  Improved  limestone
utilization and operating reliability have
also been demonstrated.
  Earlier test results using  adipic  acid,
July  1978 -  October 1979,  were
reported at the Fifth Symposium on Flue
Gas Desulfurization in Las Vegas, NV,
March 5-8, 1979,  and  at EPA's  Fifth
Industry Briefing in  Raleigh, NC,
December  5, 1979. This  is  the  third
report  on the recent adipic  acid test
results at the Shawnee Test Facility i
from October 1979 through May 1980. '
  The recent tests with adipic acid were
conducted  only  on  the venturi/spray
tower system. All tests were made with
limestone slurry, including: (1) partial
factorial tests to characterize the effects
of pH, adipic acid  concentration, and
other operating parameters on S02
removal;  (2) single-loop (one-tank) tests
without forced oxidation at low pH and
high (4000  ppm) adipic acid concentra-
tion; (3)  tests with a venturi only  to
determine the limits of SO2 removal;  (4)
single-loop  forced oxidation tests, with
both one and two tanks; and (5) bleed
stream oxidation tests  at low pH and
high (4000  ppm) adipic acid concentra-
tion.
  Major efforts during the recent  tests
were  directed toward investigation  of
the effect of pH on the  degradation of
adipic acid.  Adipic acid degradation was
found to  be minimized  when the
scrubber is operated at low (below 5.0-
5.1) inlet pH. Forced oxidation and poor
limestone utilization tend to increase
the degradation.
William L Wells, Program
Manager, Tennessee Valley
Authority
  Prototype cocurrent limestone scrubbei

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tests were performed at the Shawnee
Test Facility. The  initial cocurrent
prototype tests consistently achieved
greater  than  90% S02 removal while
operating  with inlet  flue gas SO2
concentrations ranging from 1500 ppm
to 3000 ppm. Although the prototype
scrubber tower was  reliable, total
system  reliability was not achieved
during the initial tests at  27 ft/sec
superficial  scrubber gas velocity,  pri-
marily because of solids deposits in the
mist eliminator and the inline, indirect
steam reheater. At a 20 ft/sec super-
ficial gas velocity and with low fly ash
loading  in the inlet flue gas, there were
no significant solids deposits in the mist
eliminator or  reheater.  Mist eliminator
operation was reliable during operation
with high  fly  ash loadings and a 20
ft/sec superficial gas velocity, but the
inline reheater continued to plug with
slurry solids.  Forced-oxidation tests,
with a  single  scrubber hold tank  and
multiple hold tanks, identified operating
conditions which consistently removed
greater  than 90% of the S02 and
oxidized  greater than 95%  of  the
calcium sulfite in the scrubber slurry to
gypsum.

William L. Wells, Program
Manager, Tennessee Valley
 Authority
  Dowa dual-alkali process tests at the
 nawnee  Test  Facility  were the first
application of the Dowa process with
flue gas from  a coal-fired boiler. The
operating conditions were based on
operating experience at Dowa facilities
at smelter  plants, sulfuric acid plants,
and oil-fired steam generator plants in
Japan.
  The initial tests utilized the existing
Turbulent Contact Absorber (TCA) in the
Shawnee train 200. The maximum SCb
removal efficiency by the TCA was 85%
to 90%. During this TCA testing, prob-
lems with gas flow  distribution in the
absorber were observed. Subsequently,
the mobile sphere packing in the TCA
was replaced with rigid packing to
improve gas  flow  distribution and
gas/liquor  contact. A factorial absorp-
tion test series using the rigid packing
identified  operating  conditions which
will consistently achieve greater than
90% S02 removal efficiency.
  The neutralization and gypsum  de-
watering process steps were generally
satisfactory during the absorption tests.
  Extensive reliability  tests were  not
conducted; however,  no  significant
reliability problems were identified
during the factorial absorption tests.

N. Dale Hicks, Superintendent,
Southwest Power Station,
Springfield City Utilities
  City Utilities  of Springfield,  MO,
began commercial operation of this FGD
system  in  September  1977.  Two
turbulent contact absorber modules are
arranged in parallel  and  utilize  a
pulverized  limestone slurry for S02
removal. The scrubbers serve a 195 MW
unit with a Riley Stoker boiler burning
3.5% sulfur coal. Station design was by
Burns & McDonnell, with  the Air
Correction  Division  of  UOP, Inc., re-
sponsible for the FGD system on this
new facility.
  The absorber  modules and various
support  systems have  experienced  a
variety of problems since initial start-up.
The more severe problems encountered
have been: absorber  and demister
pluggage; failure of absorber spheres;
pipe breakage; control and instrumenta-
tion  malfunctions; and expansion  joint,
damper,  and duct corrosion. Past and
planned efforts to  rectify these dif-
ficulties, and to improve  FGD system
reliability, are discussed in detail.
  A  related problem area has been the
continuous monitoring systems for flue
gas opacity and SO2 emissions. Original
equipment  has  proven  unsuccessful
and the investigation toward a solution,
with  the aid of a  consulting firm, is
described.
  The station is to be the hostfacilityfor
an EPA-sponsored full-scale demon-
stration of adipic acid as an additive to
wet limestone FGD systems. Anticipated
results are  enhanced efficiency and
improved operation  of  the pollution
control facility.  Also involved in the
project are the Radian Corporation and
UOP, Inc.

Thomas M. Morasky, Project
Manager,  Electric Power
Research  Institute
  A 10-month evaluation of the Chiyoda
Thoroughbred 121  Prototype  Process
(CT-121) was conducted at the Scholz
Electric  Generating  Station of  Gulf
Power Company. The 23-MW CT-121
prototype was  modified from existing
CT-101 process equipment at Scholz by
Chiyoda  International Corporation, a
subsidiary of Chiyoda Chemical  Engi-
neering  and Construction Company,
Ltd. Chiyoda operated the prototype, and
the Electric Power Research Institute and
Southern Company sponsored technical
evaluations of the  prototype  process
performance.  This paper summarizes
the findings of  these  evaluations.
Detailed results of the gypsum stacking
evaluation are  presented with the
Chiyoda Thoroughbred  121 presenta-
tion.

R.A. Puny an. Project Manager,
Environmental Control
Assessment Branch, Tennessee
Valley Authority
  Tests on one module (140 MW) have
been  carried  out to demonstrate the
feasibility of forced  oxidation of lime-
stone scrubber sludge to gypsum as a
viable technique for ultimate disposal of
these waste materials. Both one- and
two-tank oxidation experiments were
studied with  data indicating that the
two-tank runs more closely met test
objectives. Equations to  predict oxida-
tion were developed and expressed as a
function of mass transfer and chemical
kinetics. Air stoichiometries of between
1.75 and 2.0 Ib atoms 0/lb mole S02
absorbed will consistently produce
oxidation of —95%.
  As a result of the Forced Oxidation
Test Program, this method is being
given  consideration as one of the
alternative methods of scrubber sludge
disposal for Widows Creek Units  7 and
8. Additionally, Paradise Steam  Plant
Units 1 and 2 scrubber trains are being
designed with a forced oxidation option
to produce a sulfate waste product.

Richard A. Spring,
Superintendent, Air Quality
Control, La Cygne Station,
Kansas City Power  & Light
Company
  In the late 1960's, Kansas City Power
& Light Company and Kansas Gas &
Electric Company entered  into a joint
venture to construct an 800-MW coal-
fired generating  unit. An east central
Kansas location  was selected for its
ample coal reserves and  adequate
water supply.
  The coal reserves proved to be a low
grade with an average of 5.25 percent
sulfur and 24 percent ash. To make this
coal an acceptable boiler fuel a large
scale  air quality  control system was
required.  After considerable pilot test-
ing on a smaller generating unit burning
similar coal, a venturi-absorber scrubber
using limestone as the scrubbing  agent
was selected. Construction  of the La

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Cygne Station Unit 1 started in April
1969; commercial operation began in
June 1973.
  This  paper reviews the operating
experiences, operation and maintenance
(O & M)  cost trends,  availabilities,
modifications, manpower,  and other
supportive data relating to this limestone
scrubber system.

Royce Hutcheson, Plant
Supervisor, Environmental
Results,  Tombigbee Power
Plant, Alabama Electric
Cooperative, Inc.
  Alabama  Electric Cooperative's
Tombigbee Power Station is on  the
Tombigbee River  about 70 miles north
of Mobile,  AL. The most recent expan-
sion at this site was the addition of Units
2 and 3. Each unit has a rated capacity of
255  MW  and is designed  to burn
Alabama  and Kentucky coals with a
maximum  sulfur  content of 1.8%. To
meet the emission standard of 1.2 Ib
S02  per million  Btu, flue gas desul-
furization was required. In September
1975 Peabody Process systems was
awarded a contract to furnish a lime-
stone FGD System for both units.

Robert A.  Hewitt, Mechanical
Engineer,  Texas Utilities
Services, Inc.
  The 750-MW Monticello boiler 3 of
Texas Utilities  Services,  firing lignite
coal, is equipped with three large spray
towers, designed  by Chemico Air Pollu-
tion  Control Corporation. Each spray
tower is sized to  handle over 1 million
ftVmin of flue  gas.  This flue  gas
desulfurization system uses pulverized
limestone slurry for scrubbing  and
includes a  flue gas bypass as well as an
external steam flue gas reheat system.
The FGD system went into operation in
mid-1978  and  has since consistently
logged very high  availability as well as
high  S02 removal efficiency. The extreme
simplicity of the spray tower system has
resulted in only a modest increase in the
power  plant's operating and mainte-
nance staff. A recent inspection of the
system revealed no major problem with
the tower  and duct liners or the tower
internals.  A  few  isolated spots on the
internal slurry pipes showed wear due
to close proximity to the sprays. Failure
of the rubber lining on the side-mounted
agitators and slurry recycle  pumps has
been the  primary source of problems
with the system. The experience with
this system in general has been very
satisfactory  and Texas Utilities  has
purchased two essentially duplicate
systems for  the Twin  Oak  Power
Station.

Robert P.  Van Ness, Manager,
Environmental Affairs,
Louisville Gas & Electric
Company
  This pa per discusses the results of the
recently performed acceptance test on
the dual alkali system serving Louisville
Gas and Electric Company's Cane Run
Unit 6 boiler. The acceptance test was
conducted to measure  the system
performance with respect to the guar-
antees  offered  Louisville Gas and
Electric by Combustion  Equipment
Associates. The results of the testing
were:
  • SOa removal averaged 94%  and
    143 ppm outlet concentration.
  • Soda  ash consumption averaged
    0.042 mole soda ash per mole S02
    removed.
  • Lime consumption averaged 1.04
    mole CaO per mole SOa removed.
  • Power consumption averaged
    1.05% of generation.
  • Filter cake solids averaged 52.2 wt
    %  insoluble solids.
  • There was  no net particulate
    addition.
Various problems attributable to  the
boiler, the  FGD system, and the quality
and quantity of the carbide lime supplied
to the system delayed the acceptance
testing  until July 1980. The year-long
demonstration  period  started officially
in May  1980. The nature of the prob-
lems experienced and their solutions
are discussed.

James A. Van Meter, Director
of Power Production and
Procurement, Southern
Indiana Gas and Electric
Company
  This  paper  reviews the design  and
initial operating  experience with  the
flue  gas desulfurization system at
Southern  Indiana  Gas and  Electric
Company's (SIGECO's)  A.B.  Brown
Station Unit 1, a 265-MW steam electric
station  burning up to 4.5% sulfur coal in
a pressurized, pulverized coal boiler.
  After initial checkout in the spring and
summer of 1979, the FGD system began
routine  continuous operation.  Overall
operating results are presented for SO?
collection, chemical  consumption,
availability, maintenance requirements,
and operating costs. The problem areas
that contributed significantly to main-
tenance requirements or nonavailability
of the system are discussed in detail.
Not counting the scheduled outage, the
system has enjoyed a 96% availability
overall in its first year of operation on a
high sulfur coal application. SOa removal
of over 90% has been routinely demon-
strated. Overall operating costs on  an
annual revenue requirements basis are
close to the original projections.

Earl L.  Mann,  Executive
Manager, Electric Production,
Northern Indiana Public
Service Company
  The Northern Indiana  Public  Service
Company and the U.S. Environmental
Protection Agency entered into a cost-
shared contract in June  1972 for the
design, construction, and operation of a
regenerable flue gas desulfurization
(FGD) demonstration plant. The system
selected for the project was a combina-
tion of the Wellman-Lord SOa Recovery
Process  and the  Allied Chemical SOa
Reduction Process. The FGD plant was
to be retrofitted to NIPSCO's 115-MW
pulvenzed-coal-fired Unit 11  at  the
Dean  H.  Mitchell Station in Gary,  IN. j
NIPSCO entered into contracts with.
Davy Powergas, Inc., for the design an4(
construction of the FGD plant, and
Allied Chemical Corporation for opera-
tion of the piant.
  The FGD plant acceptance test was
successfully  completed on September
14, 1977. The plant completed a 2-year
demonstration test period during which
information was collected and reported
regarding pollution control performance,
secondary effects,  economics, and
reliability of the system. TRW, Inc. was
the independent evaluator for the EPA
through  October  1979. A follow-on
EPA/NIPSCO contract of  7-V2  months
has recently been completed. Operation
of the plant continues.

Landon D. Fox, Staff
Specialist, Tennessee Valley
Authority
  This paper discusses pilot and full-
scale  magnesium flue gas desulfuriza-
tion (FGD) designs by TVA.
  The full-scale (600-MW equivalent)
magnesium FGD design is for operation
at high and low load factors for a high
sulfur coal. After a process and system
chemistry (magnesium sulf ite/bisulf ite)
description, the  paper describes  th

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FGD equipment and system operation
which includes an onsite acid plant. The
second  part of the paper discusses
information on  a  test program and
schedule of a pilot plant being  con-
sidered by TVA to verify the magnesium
FGD design.

Chakra J. Santhanam,
Management Staff, Arthur
D.  Little, Inc.
  This paper presents a status report on
the EPA project, "Characterization and
Environmental Monitoring of Full-Scale
Utility  Waste Disposal Sites" (EPA
Contract 68-02-3167). Arthur D. Little,
Inc.  is the  prime  contractor  on this
project which  involves the character-
ization, environmental monitoring, and
engineering/economic  assessment of
coal ash and FGD waste disposal at 12
full-scale waste disposal sites. The
project is designed to obtain technical
background  data and information so
that EPA can determine the degree to
which disposal of these wastes (from
coal-fired  power plants) needs to be
managed  in order to protect  human
health and the environment. This effort
will fulfill some of EPA's responsibilities
under RCRA.
  To date,  major accomplishments of
the project include:
  • Evaluation of available data on
     coal-fired power plants in the U.S.
     to develop a list of candidate and
     backup sites.
  • Preparation of procedures manuals.
  • Progress in securing utility involve-
     ment and cooperation.

Val E.  Weaver, Program
Manager for Waste
Management, U.S. Department
of Energy
  This paper presents "interim" findings
of  a continuing evaluation  of  the
impacts on coal-fired electric generating
facilities  in the utility sector deriving
from Proposed Rules issued by EPA for
implementing Sections 3001, 3002,
and 3004 of RCRA Subtitle C (December
18,  1978)  and Proposed Guidelines
under Section 4004 (February 6, 1979)
and Section 1008  (March  26,  1979).
Cost analyses were made  on direct
costs only and presented in  1979
dollars.
  The primary purpose for undertaking
this study  was to assess RCRA's
impacts  on coal-fired utilities as a
means to understanding the implica-
tions of RCRA regulations  on  the
National Energy Plan (NEP), the Power-
plant  and Industrial  Fuel  Use  Act of
1978 (PIFUA), which gives DOE authority
to enforce coal conversion actions, and
on utilities. Ultimately, this information
can be used to understand and deter-
mine  RCRA's  implications on  DOE's
Fossil  Energy mission  objectives of
developing programs and supporting
advanced technologies which  will
promote greater utilization of coal in an
environmentally acceptable manner.
  Cost and other impact considerations
were  developed through a survey of
available information from 29 significant
coal producing and/or using states and
by in-depth  case studies of operating
conditions and engineering and design
requirements for RCRA compliance at 6
operating and 16 theoretical base-case
coal-fired power generating plants. The
six plants were selected to encompass a
broad cross-section of  industry operating
factors. Solid waste disposal costs were
developed for three scenarios structured
to bracket the probable cost impacts of
the proposed RCRA regulations on the
utility sector. Cost  curves and mathe-
matical models of capital and operation
and  maintenance (O&M)  costs  asso-
ciated with each disposal scenario were
developed as  a function of  waste
generation rates. In  all  instances  the
"least cost of compliance" rather than
"worst case" data were employed.
  Preliminary national costs for waste
disposal, based on direct costs alone,
reflected an increase in disposal costs of
over "4 times" for nonhazardous and
over "13 times" for hazardous disposal.
This results  in a cost increase of from
 1.09  to 3.2 mills  per  kWh  of power
generated (in terms of 1979 dollars).

Dean M. Golden, Project
Manager,  Electric Power
Research  Institute
  The increasingly stringent air quality
requirements on power plants necessi-
tated  the cleanup of flue gas stack
emissions, resulting in ever-increasing
quantities of  solid wastes from  the
combustion of coal. Presently, the most
used  type of FGD scrubber is the wet
scrubber. This kind of scrubber is
expected to dominate the industry into
the 1990's. The waste produced by wet
scrubbing is a sludge composed of the
scrubbing liquor, calcium sulfite/sulfate
solids, and varying quantities of fly ash.
EPRI has a number of research projects
recently completed or  underway explor-
ing new options for disposal of the FGD
sludges. This  paper summarizes the
results of two  projects, one evaluating
the stacking method for gypsum  dis-
posal, and the other a site monitoring
investigation to assess the acceptability
of sludge/ash  fixation.
  The  results of  the FGD gypsum
stacking demonstration indicate that
this oxidized FGD sludge has settling,
dewatering, and structured character-
istics  similar  to and, in some cases,
superior to phosphate gypsum, making
this a viable option for disposal.
  The results of the site monitoring of
the first full-scale fixed sludge disposal
system are still inconclusive. Well
monitoring indicates some impact on
groundwater quality in the vicinity of the
disposal facilities. Field permeabilities
of the fixed sludge samples were found
to be higher than laboratory test results.


Gerald H. Groenewold,
Geologist, North Dakota
Geological Survey
  Increased reliance on coal-burning
power plants is resulting in the genera-
tion  of large  quantities of waste
products. Fly  ash and FGD waste
constitute the two major by-products of
coal-burning power plants in the U.S. At
mine-mouth power stations a common
method of disposal of these wastes is by
emplacement in surface mine pits.
  In this study, initially funded by EPA
and presently  by DOE, the  potential
impacts of surface mine pit disposal of
fly ash and FGD waste at the Center
Mine  near  Center, ND,  are being
evaluated. The FGD waste at Center is
generated by using the highly alkaline
fly ash as the SO2 sorbent. The research
involves field studies, laboratory studies,
and computational geochemical studies
to determine  the  potential  for FGD
waste and fly ash to affect groundwater
quality.

   FGD waste from North Dakota lignite,
when placed in contact with water in
various types of laboratory experiments,
produces leach fluids with high  SO*,
Mg, and Na  concentrations  and pH
values in the range of 7.0 to 8.5. Toxic
metal and nonmetal concentrations are
generally not significantly in excess of
drinking water standards. The concen-
trations of S04 and Ca are limited by the
solubility of gypsum in conjunction with
the degree of ion pairing between the
major cations and sulfate. Highest total
dissolved solids occur when Na and Mg
are present as soluble sulfate salts.

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Iver W. Duedall, Professor,
Marine Sciences Research
Center, State University of
New York at Stony Brook
  A multidisciplinary team at the State
University of New York at Stony Brook,
in collaboration  with  ID Conversion
Systems, Inc. (Horsham, PA), is assessing
the feasibility of using  blocks of waste
materials from coal-fired power plants
for underwater construction of artificial
fishing  reefs. Experiments conducted
over the past  3 years in the laboratory
and in the sea have suggested that coal
waste  blocks are  environmentally
acceptable in the ocean.
  On September 12, 1980, a 500 ton
reef was constructed  in the  Atlantic,
south of Long Island, from 18,000 solid
blocks 8 in. x 8 in. x 16 in. of stabilized fly
ash and FGD sludge obtained from coal
burning  power plants in Ohio and
Indiana. The reef blocks were fabricated
at a commercial concrete block plant in
Pennsylvania using automatic block
making equipment. The ratio (dry
weight)  of fly ash to FGD sludge was
1.5:1 and 3:1.
  In preparation for fabrication of the
500 tons of  reef blocks, a combination of
different coal waste mixes, stabilization
additives, and curing procedures were
screened to  develop  candidate  mix
designs. Experiments were made at the
research facilities of the Besser Com-
pany in Alpena, Ml, to develop methods
by which coal wastes could successfully
be formed into blocks by block making
machines.
  The demonstration disposal reef will
be monitored for 3 to 4 years to assess
environmental impacts  which may
occur and to measure the development
of the biological communities which will
be associated with the  reef.

Penelope Hansen, Program
Manager  of the Minerals and
Energy Program, Office of
Solid Waste, EPA-Washington
  The  Resource  Conservation and
Recovery Act (RCRA)  has two major
goals: 1) the protection of human health
and  the environment,  and 2) the
conservation  of valuable material and
energy  resources.  EPA's  efforts have
been concentrated on the first goal. This
paper,  however, concentrates  on  re-
source  recovery and reuse of waste
materials  as outlined under RCRA
Section 6002.
  Federal procuring agencies are man-
dated to purchase items containing the
maximum practical amount of recovered
materials.  Recycled products are dis-
cussed from reasonable equivalents in
technical performance, price, levels of
competition, and product availability.
Criteria  developed to aid in the pro-
curement process are discussed. The
scenario used  is the application of
Federal  procurement to either cement
or concrete which contains fly ash and
the guidelines proposed  for  their
procurement.
Gerald G. McGlamery, Chief,
Pilot Plant Design and
Construction Branch,
Tennessee Valley Authority
  This paper summarizes the results of
an EPA-funded  study of dry scrubbing
technology and economics. The relative
economics of a generic lime spray dryer
process and a limestone scrubbing
process were compared for three coal
applications: a low-sulfur western, and
low- and high-sulfur eastern coals. The
cost estimates  are based on recently
updated TVA design and economic
premises and include all of the process-
ing required  to meet the  1979  new
source performance standards (NSPS)
for both paniculate matter and S02 and
to dispose of the resulting FGD waste in
an environmentally acceptable manner.
  The resulting  preliminary economics
are included  for all three  coal appli-
cations for both the generic lime spray
dryer process and the limestone scrub-
bing process. Sensitivity of the resulting
annual  revenue requirements  to the
delivered raw material cost and the raw
material stoichiometry are also included.


Marvin Drabkin, Senior
Systems Engineer, The
Mitre Corporation
  This paper responds to a request  by
the EPA Office of Environmental Engi-
neering and Technology (OEET)  to
develop investment and operating costs
for a spray dryer flue gas desulf urization
(FGD)  system  retrofitted  on  several
boilers  in two power  stations  of a
northeastern  utility. These  power
stations are among  23  power plants
involved in DOE-proposed coal conver-
sion actions under the Fuel Use Act of
1978.  Based on budget estimates
received from a number of FGD system
vendors,  total  installed cost of this
system (which would control SOX and
paniculate  emissions to present un-
controlled levels produced by firing No.
6 oil, would range from  $153.9 million
($89/kW) to $204.0 million ($118/kW)
for  a  generalized  northeast location,
with a  significantly higher  cost  of
$295.8 million ($171/kW) for a highly
urbanized location typified by the northern
New Jersey or southern New York area.
Based on projected oil costs, coal costs,
plant renovation costs, and annualized
operating costs of the emission controls,
potential  savings  by coal  conversion
would  be $187  million  annually (19
mills/kWh).  Problems of FGD waste
disposal as well as site-specific problems
are also considered in this paper.

Mary E. Kelly, Chemical
Engineer, Radian Corporation
  Radian Corporation  is currently
conducting  a survey of the commercial
and developmental status of dry  FGD
systems in  the U.S. for the EPA.  This
paper discusses the current commercial
status of these systems, the focus  of
current research and development activ-
ities, the potential advantages of dry
scrubbing over conventional wet scrub-
bing, and possible technical and  eco-
nomic limitations of dry FGD.
  For this study, dry FGD is defined  as
any  FGD process producing a dry
product for  disposal. Dry FGD systems
are grouped according to system type:
(1) spray dryer based systems with ESP
or fabric filter collectors; (2) dry injection
systems, primarily  with baghouse
collectors; and (3) other systems, in-
cluding those where alkaline material is
added  directly to the  fuel prior  to
combustion.

  Of the  three types, only spray dryer
systems  have been commercially ap-
plied.  Ten utility (low sulfur coal)
systems had been sold as of May 1980.
Two industrial spray dryer based systems
have been sold. Higher sulfur coal (2 to 3
percent) is  fired at the industrial sites.
The dry injection/baghouse collection
systems have been the  subject  of
numerous past and ongoing bench and
pilot scale studies, but no commercial
systems have been sold to date. Tech-
nologies involving combustion  of a
coal/alkaline fuel mixture are still in the
early stages of  development.  Two
processes are currently under study:
combustion of coal/limestone pellets
and firing of a pulverized coal/limestone
fuel mixture in a low-NO* burner.     4

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*  Nicholas J. Stevens, Manager
  Chemical Process
  Development, Research-
  Cottrell, Inc.
    Dry SC>2 scrubbing has emerged as an
  attractive technology for  flue  gas
  desulfunzation  to meet NSPS. Pilot
  testing by Research-Cottrell and others
  indicates that a spray dryer followed by
  a particulate collection device is a viable
  alternative to wet scrubbing for  low
  sulfur coals.
    Research-Cottrell and its spray dryer
  supplier, Komline-Sanderson, have
  conducted several investigations in
  Texas and Colorado employing spray
  dryer/fabric filter technology. This
  paper describes  some of the results of
  the  Research-Cottrell/Komline-
  Sanderson pilot test work performed for
  its commercial interests as well as for
  an EPA-funded  program. Key process
  parameters that affect SOa removal,
  including stoichiometry, flue gas tem-
  perature, inlet SOa concentration, and
  recycle  are  discussed. Other  related
  variables and the limits of dry  S02
  scrubbing are also considered.

 , Edward L. Parsons, Jr.,
  Engineering Consultant in
  Product Design, Envirotech
  Corporation
    This  paper describes the removal of
  SO2 from boiler flue gases using two dry
  FGD technologies: spray absorption and
  dry injection.  These two  dry FGD
  methods were investigated in an EPA-
  sponsored pilot test  program,  in co-
  operation with  the City of Colorado
  Springs at its Martin Drake Station. Flue
  gas from an 85-MW pulverized-coal-
  fired boiler at rates up to 34,000 m3/hr
  (20,000 acfm) could be handled by the
  spray absorber;  up to 10,000  mVhr
  (6,000  acfm) was available to the dry
  injection system.
    A comprehensive series of parametric
  optimization  tests, just completed by
  Envirotech and Anhydro A/S, investi-
  gated  many aspects of the  spray
  absorption equipment/process inter-
  face,  including  the   spray  absorber,
  sorbent preparation and delivery system,
  fabric filter, controls, and  instrumenta-
  tion.  Process feasibility/demonstration
  tests were conducted using slaked lime
  and trona as primary sorbents. Recycled
  process off-product,  consisting of fly
  ash and  reaction products, and lime-
 L stone with adipic acid additive were
 jested as supplementary alkalis for the
reduction of primary sorbent consump-
tion. Absorber inlet temperature and
SOa concentration, reactant stoichi-
ometry, and approach to saturation at
the absorber outlet were varied as
process parameters. Test results, with
SOa removal rates of up to 94 percent,
are discussed in relation to published
analytical models.
  The use of dry injection of pulverized
sodium compounds as a means of SOa
removal in  conjunction with  a  fabric
filter was evaluated in a separate test
program. The reactants used  were:
nahcolite, a naturally occurring sodium
bicarbonate; crude  lake bed trona ore;
and trona upgraded by mining methods
to 70  percent  sodium bicarbonate
content. SOa removal by reaction with
the dry pulverized sorbents was eval-
uated as a function of reactant stoichi-
ometry, baghouse  inlet temperature,
and air-to-cloth  ratio.  Removal per-
formance as a function of stoichiometry
is compared to spray absorption results.
Only nahcolite produced performance
comparable to spray absorption, with
SOa removals of up to 90 percent.

Thomas B.  Hurst, Manager,
Technology & Product
Development, Babcock &
Wilcox Co.
  As part of a continuing development
program for dry scrubbing of SOa from
stack gases, Babcock & Wilcox designed
and constructed a 20 MW demonstration
unit at Pacific Power and  Light
Company's  Jim  Bridger Station. The
objective in building this facility was to
demonstrate the  operating capabilities
and  performance of a dry scrubbing
system in large scale. Initial operation of
the dry scrubbing research (DSR) unit
commenced in late 1979 and is con-
tinuing. This paper deals with the
operating results learned to date from
this  installation  and from  supporting
research activities.

James C. Dickerman, Program
Manager, Radian Corporation
  The  CAA Amendments of  1977
require EPA to coordinate and lead the
development and  implementation of
regulations on  air pollution.  These
include standards  of performance for
new and modified sources of pollution.
Specifically mentioned as a prioritized
pollution source in the August 21,1979,
Federal Register are industrial  fossil-
fuel-fired steam generators. Accord-
ingly, the EPA has undertaken a series
of studies  of  industrial boilers  and
pollution control systems with the
intent to  promulgate  standards of
performance based on the study results.
  This paper presents the results of an
evaluation of the application  of FGD
controls for  industrial boilers. Factors
considered included development status,
environmental impacts, energy impacts,
and capital and operating costs of the
various  FGD processes.  The focus of
this  paper  is  on the results of the
environmental, energy, and cost impact
analysis; it considers only those processes
that have been commercially applied.

Charles B. Sedman,
Environmental Engineer,
EPA-RTP
  To support development of standards
of performance for new  industrial
boilers, EPA initiated a test program on
industrial FGD applications to develop a
data base for  SOa emissions  control.
The   program   included  continuous
monitoring of SOa, oxygen, and moisture
at both scrubber inlet and outlet.
Systems selected included sodium
scrubbing  on oil  and pulverized-coal
boilers, dual alkali systems on spreader-
stoker boilers,  and  a lime/limestone
application  on spreader-stoker boilers.
All boilers fired relatively high (2.5 to 4.0
percent) sulfur fuels.
  Performance of the industrial FGD
systems was generally superior to that
previously examined  in the utility
sector, with respect to  reliability and
mean SOa  removal. Variability of
emissions from industrial FGD systems
was somewhat  less than for utility
systems.


A vi N. Patkar, Project Manager,
PEDCo Environmental, Inc.
  This paper summarizes the evaluation
of 12 commercial FGD  processes for
their applicability to steam generators at
thermally enhanced oil recovery (TEOR)
sites in California. All the FGD processes
were  compared on a' common design
basis with  the  sodium-throwaway
process  currently  used  at  the TEOR
sites. PEDCo concluded that the ammo-
nia, lime, limestone, double alkali, and
Chiyoda T-121 processes  are very
competitive with the sodium-throwaway
process. The Department  of  Energy
(DOE) sponsored the study to assist the
oil companies in FGD process selection,
and  DOE  in planning  future R&D
projects. The paper also presents the

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status of existing FGD systems in the
oilfields.
  The primary concerns about the
sodium-throwaway process are the cost
of the alkali and waste disposal. The
paper reviews the current practices of
sodium-based waste disposal in indus-
trial applications which include disposal
to holding pond for evaporation, and
wastewater treatment and discharge to
city sewer, tailing pond, or waste wells.
The paper discusses two major options
for bleed stream treatment:  oxidation
(oxidation/crystallization, or oxidation/
partial quenching of the flue gas) and
central regeneration (chemical  or
thermal). The marketability of Na2S04,
gypsum, or sulfuric acid will determine
the applicability for a specific site.

Theodore  G. Brna. Project
Manager Dry FGD,
EPA-RTP
  Using  methods specified by EPA for
compliance testing, the performance of
a dry S02 control system was evaluated.
The system tested treated flue gas from
the coal-fired boiler  located  at the
Amcelle Plant  of the Celanese Fibers
Company in Cumberland,  MD. This
system and its operation are described
briefly.
  Results, based on 25  days of data
obtained over a 33-day period, showed
the mean S02 removal to be 69 percent,
with a range of 60 to 80 percent, except
for upsets, over the test period when the
sulfur content of the coal averaged 2
percent. Operating experience with the
spray-dryer/baghouse  system is sum-
marized for the 5-month period ending
with the completion of testing  on
September 30, 1980.

Robert D.  Giammar, Associate
Manager Fuels and Combustion
Section, Battelle Columbus
Laboratories
  This paper presents the results of a
three-phase  program to evaluate emis-
sions and control technology for indus-
trial stoker boilers. The paper focuses on
the third phase "Limestone/Coal Pellet
Development,"  while  summaries  are
given of the first two phases, "Alternate
Fuels Evaluation" and "Control Tech-
nology  Evaluation." Because SO2
appears to  be the  most  troublesome
emission to control  for stokers, a
limestone/high-sulfur-coal pellet was
developed and evaluated as a SO2.
control  technique.  Initially, this pellet
with a  Ca/S  molar ratio  of  7  was
successfully fired in an 8-MW industrial
spreader-stoker boiler with S02 emis-
sions reduced by 75 percent. However,
from both an  economical and  opera-
tional standpoint, the amount of lime-
stone required  had to be reduced  to
correspond to a Ca/S molar ratio of 3 to
4. Furthermore, the mechanical proper-
ties of this pellet were inadequate to
withstand the  severe stresses of an
industrial fuel-handling system. Ac-
cordingly, a research and development
effort was undertaken to refine the
pellet. A refined pellet, with a Ca/S
molar ratio of  3.5 ,  with appropriate
binders was produced that had  similar
or  improved physical characteristics of
raw coals. Additionally, economic
analysis indicates that this pellet can be
produced for approximately $15/ton
above the cost  of high sulfur coal. This
refined pellet was fired in a 200-kW
laboratory spreader-stoker boiler,
achieving sulfur captures as high as 70
percent. However, when fired in the 8-
MW (25,000-lb steam/hr) stoker boiler,
sulfur  captures on the order of 50
percent were achieved.
   Franklin A. Ayer, compiler, is with Research Triangle Institute, Research Triangle
    Park, NC 27709.
   Julian W. Jones is the EPA Project Officer (see below).
   The complete report, entitled "Proceedings: Symposium on Flue Gas Desulfu-
    rization—Houston, October 1980."
       Volume 1.  (Order No.  PB 81-243  156; Cost: $36.50, subject to change)
       Volume 2.  (Order No.  PB 81-243  164; Cost: $38.00, subject to change)
    will be available only from:
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
          Telephone:  703-487-4650
   The EPA Project Officer can be contacted at:
          Industrial Environmental Research Laboratory
          U.S. Environmental Protection Agency
          Research Triangle Park, NC 27711
                                 10
                                                            . S. GOVERNMENT PRINTING OFFICE: I98I/559-092/3323

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