EPA-600/2-76-037
February 1976
Environmental Protection Technology Series
CATALYTIC OXIDATION OF FUELS FOR
NOX CONTROL FROM AREA SOURCES
Industrial Environmental Research Laboratory
Office of Research and Development
U.S. Environmental Protection Agency
Research Triangle Park, North Carolina 27711
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RESEARCH REPORTING SERIES
Research reports of the Office of Research and Development, U.S. Environmental
Protection Agency, have been grouped into five series. These five broad
categories were established to facilitate further development and application of
environmental technology. Elimination of traditional grouping was consciously
planned to foster technology transfer and a maximum interface in related fields.
The five series are:
1. Environmental Health Effects Research
2. Environmental Protection Technology
3. Ecological Research
4. Environmental Monitoring
5. Socioeconomic Environmental Studies
This report has been assigned to the ENVIRONMENTAL PROTECTION
TECHNOLOGY series. This series describes research performed to develop and
demonstrate instrumentation, equipment, and methodology to repair or prevent
environmental degradation from point and non-point sources of pollution. This
work provides the new or improved technology required for the control and
treatment of pollution sources to meet environmental quality standards.
EPA REVIEW NOTICE
This report has been reviewed by the U.S. Environmental
Protection Agency, and approved for publication. Approval
does not signify that the contents necessarily reflect the
views and policy of the Agency, nor does mention of trade
names or commercial products constitute endorsement or
recommendation for use.
This document is available to the public through the National Technical Informa-
tion Service. Springfield, Virginia 22161.
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EPA-600/2-76-037
February 1976
CATALYTIC OXIDATION OF FUELS FOR
NOV CONTROL FROM AREA SOURCES
j\
by
J. P. Kesselring, R. A. Brown,
R. J. Schreiber, and C, B. Moyer
Aerotherm Division, Acurex Corporation
485 Clyde Avenue
Mountain View, California 94042
Contract No. 68-02-1318, Task 12
ROAP No. 21AUZ-019
Program Element No. 1AB015
EPA Project Officer: G. Blair Martin
Industrial Environmental Research Laboratory
Office of Energy, Minerals, and Industry
Research Triangle Park, NC 27711
Prepared for
U.S. ENVIRONMENTAL PROTECTION AGENCY
Office of Research and Development
Washington, DC 20460
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"...the. i.ncandeAce.nt botid muAt not fae c.om>£deAe.d a meJie. LdJLzn.
on. lookeA-on at the. cAowd ofa teaching mo£ecu£e*; actuary -it
gatva.nize.d -into tifie. the. downant a^-dvcttea, uiitk the. nzAuJLt
that the. &tateJLy minuet. o£ oldinasiy filame. comfaa6-tion gai/e place.
to the. (tiUA Intoxication o& the. 1/enaifaeAg."
from "Surface Combustion,"
Engineering, Vol. 93, May 10,
1912, p. 632.
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ACKNOWLEDGEMENTS
This document presents the results of a study to assess the feasibility of
catalytic oxidation of fuels for NO control and minimization of CO and UHC from
area sources. Aerotherm extends its appreciation for the valuable assistance pro-
vided by Dr. R. B. Rosenberg and J. C. Sharer of the Institute of Gas Technology,
Dr. R. V. Carrubba of Engelhard Industries, Lt. D. E. Walsh of AFAPL, T. S. Mroz,
Dr. D. N. Anderson and R. R. Tacina of NASA-Lewis, Dr. J. Houseman and Dr. G. Voecks
of JPL, and R. Bratko of the Bratko Corporation. In addition, the valuable contri-
butions of Dr. R. Levy and Dr. J. Cusumano of Catalytica Associates, Inc., are grate-
fully acknowledged.
This study was conducted for the Combustion Research Section of the Control
Systems Laboratory, U.S. Environmental Protection Agency. G. B. Martin was the
Task Officer. The Aerotherm Program Manager was Dr. L. W. Anderson, and A. J. Murphy
and P. T. Overly contributed to the final report.
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TABLE OF CONTENTS
Section Page
1 SUMMARY 1-1
1.1 Study Results 1-1
1.2 Conclusions 1-5
2 INTRODUCTION 2-1
3 CHARACTERIZATION OF STATIONARY COMBUSTION SOURCES 3-1
3.1 General Considerations 3-1
3.1.1 Residential Sector 3-2
3.1.2 Commercial Sector 3-2
3.1.3 Industrial Sector 3-6
3.2 Equipment and Operating Characteristics 3-9
3.2.1 Warm Air Furnaces 3-9
3.2.2 Boilers 3-26
3.3 Air Pollutant Emission Characteristics 3-44
3.3.1 Commercial and Residential Sector 3-44
3.3.2 Industrial Sector . 3-51
3.4 Conclusions 3-55
4 RECENT DEVELOPMENTS IN CATALYTIC FUELS OXIDATION CONCEPTS .... 4-1
4.1 General Considerations 4-1
4.1.1 Ignition Requirement 4-2
4.1.2 Flashback Potential 4-9
4.1.3 Lean and Rich Flammability Limits 4-9
4.1.4 Maximum Specific Heat Release' 4-9
4.1.5 Heat Removal Mechanisms 4-11
4.1.6 Combustion Efficiency 4-11
4.1.7 Pollutant Potential 4-11
4.2 Characteristics and Properties of Catalyst Materials .... 4-12
4.2.1 Support Material Types and Characteristics 4-12
4.2.2 Substrate Wash Coal Materials 4-24
4.2.3 Catalyst Coatings 4-29
4.2.4 Temperature Capability of Catalyst/Support System .... 4-36
4.2.5 Poisoning Effects 4-37
4.2.6 Characterization Techniques 4-38
4.3 Existing Applications of Catalytic Oxidation Concepts . . . 4-39
4.3.1 Nitric Acid Plant Tail Gas Cleanup 4-39
4.3.2 Industrial Odor Control 4-40
4.3.3 Low-Temperature Catalytic Heaters 4-40
4.3.4 Automotive Exhaust Catalysts 4-43
vn
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TABLE OF CONTENTS (Concluded)
Section Page
4.4 Current Research Programs in Catalytic Combustion 4-45
4.4.1 Air Force Aero Propulsion Laboratory 4-45
4.4.2 Bratko Corporation 4-49
4.4.3 Detroit Diesel Allison Division, General Motors
Corporation 4-49
4.4.4 Engelhard Industries 4-49
4.4.5 Institute of Gas Technology 4-51
4.4.6 Jet Propulsion Laboratory 4-52
4.4.7 NASA-Lewis Research Center 4-53
4.4.8 Oxy-Catalyst, Incorporated 4-53
4.4.9 Tokyo Gas Company, LTD 4-58
4.5 Conclusions 4-58
5 APPLICABILITY OF CATALYTIC FUELS OXIDATION CONCEPTS TO AREA
SOURCES 5-1
5.1 Potential Design Matrix 5-1
5.1.1 New Versus Retrofit 5-3
5.1.2 Applications 5-3
5.1.3 Catalysts 5-6
5.1.4 Catalyst Support Arrangement 5-7
5.1.5 Low NOX Techniques 5-7
5.1.6 Fuels 5-19
5.2 Other Design Considerations 5-22
5.3 Overall Conclusions 5-23
6 COMMERCIAL APPLICATION OF CATALYTIC CONCEPTS TO SELECTED
SYSTEMS 6-1
6.1 Home Heater Retrofit 6-1
6.2 Home Heater — New Designs 6-13
6.3 Commercial Boiler - Retrofit 6-20
6.4 Commercial Boiler — New Design 6-23
6.5 Industrial Boilers — Retrofit 6-23
6.6 Industrial Boilers — New Design 6-23
6.7 Conclusions 6-28
7 RECOMMENDATIONS 7-1
REFERENCES R-l
vm
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LIST OF FIGURES
Page
Residential heating equipment types 3-3
Commercial heating equipment types . 3-5
Industrial heating and process steam equipment — basic types
types 3-7
3-4 Industrial heating and process steam equipment — firetube boiler
types 3-8
3-5 Industrial heating and process steam equipment — packaged water-
tube boiler types 3-10
3-6 Industrial heating and process steam equipment — field erected
watertube boiler types 3-11
3-7 Forced warm air gas-fired furnace 3-12
3-8 Forced warm air oil-fired furnace — downflow 3-13
3-9 Forced warm air oil-fired — downflow, with compact heat
exchanger 3-14
3-10 Forced warm air gas-fired — upflow 3-16
3-11 Forced warm air oil-fired furnace — upflow 3-17
3-12 Forced warm air gas-fired furnace — horizontal 3-18
3-13 Forced warm air oil-fired furnace — horizontal 3-19
3-14 Temperature rise across a gas-fired warm air furnace during a
typical cycle 3-24
3-15 Temperature rise across an oil-fired warm air furnace during a
typical cycle 3-25
3-16 Gas-fired cast iron boiler 3-31
3-17 Oil-fired cast iron boiler 3-32
3-18 4-pass scotch firetube boiler 3-37
3-19 80 x 106 Btu/hr combination-fired packaged watertube,
D-type boiler 3-42
3-20 D-type bent tube configuration 3-43
3-21 Summary of 1972 stationary source NO emissions 3-45
3-22 General trend of smoke, gaseous emission, and efficiency versus
stoichiometric ration 3-47
3-23 Hydrocarbon and carbon monoxide trends during cycle 3-48
3-24 Particulate trends during cycle 3-49
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LIST OF FIGURES (Continued)
Figure Page
3-25 Nitric oxide trend during cycle 3-50
4-1 Conversion characteristics of base metal and noble metal
catalysts 4-4
4-2 Palladium catalyst performance 4-5
4-3 n-Heptane fume abatement effectiveness (115,000/hr space
velocity) 4-6
4-4 Lightoff characteristics — palladium catalyst 4-7
4-5 n-Heptane covnersion efficiency vs temperature and space velocity —
granular catalyst substrate 4-9
4-6 Example of flammability limit determination 4-10
4-7 Comparison of pressure drops for monolith and pellet bed
systems 4-14
4-8 Surface area for various pellet sizes 4-16
4-9 Examples of Thermacomb corrugated ceramics, produced by American
Lava Corporation 4-18
4-10 Structural types of Thermacomb corrugated ceramic monoliths .... 4-19
4-11 Examples of Celcor cordierite monoliths, produced by Corning Glass
Works 4-20
4-12 Examples of DuPont's TORVEX ceramic honeycomb 4-21
4-13 Examples of General Refractories Company's Versagrid ceramic
honeycomb 4-22
4-14 Norton Company's SPECTRAMIC honeycomb material 4-23
4-15 Johns-Mansvilie's Fibrechrome — a fiber pad 4-25
4-16 ICI United States' SAFFIL -an alumina fiber 4-26
4-17 Exmaples of Norton Company's catalyst carriers 4-28
4-18 The catalytic activity of oxides of the elements of the fourth
period in the homomolecular exchange of oxygen (1), oxidation of
hydrogen (2), oxidation of methane (3) and nitrogen oxide decom-
position (4) at 300°C 4-33
4-19 Activation energies of homomolecular oxygen exchange reaction (I),
methane oxidation (II), as a function of oxygen bond energy, for
oxides of elements of the fourth period 4-34
4-20 Catalytic activity of vanadium pentoxide promoted with sulfates of
various alkali metals. Curve 1 — reaction of exchange of molecular
oxygen; curve 2 — reaction of oxidation of sulfur dioxide 4-35
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LIST OF FIGURES (Continued)
Figure
4-21
4-22
4-23
4-24
4-25
4-26
4-27
4-28
4-29
4-30
4-31
4-32
5-1
6-1
6-2
6-3
6-4
6-5
6-6
6-7
6-8
6-9
6-10
6-11
6-12
6-13
6-14
Flow diagram of a typical catalytic incinerator using a
honeycomb catalyst
Schematic diagram — low temperature catalytic heater
Effect of catalyst composition on 1975 FTP emissions
AFAPL's catalytic combustor system assembly
CO and C H emission index variation with fuel air ratio
x y
Combustion efficiency variation with fuel -air ratio
JPL Small Scale Catalytic Combustor System
Exploded view of catalytic compact reactor containing cold-start
burner, air preheat heat exchanger, and catalyst bed containing
1.5 pounds of catalyst pellets
Oxy-catalyst's dual -catalytic bed oxidation apparatus
Schematic diagram — Tokyo Gas Company's two-stage combustion method
for NOX reduction
Variation in nitrogen compounds as a function of primary combustion
chamber equivalence ratio
Effect of various catalysts on the formation of nitrogen
compounds
Potential design matrix
Home heater retrofit design #1
Design number 2, cross flow ceramic heat exchanger
Home heater retrofit design
Catalytic pad oil burner
Home heater design #1
Scaled home heater design #1
Home heater design #2
Home heater design #3
Home heater design #4
Home heater design #5
Commercial boiler design #1 firetube boiler
Commercial boiler design #2 water wall configuration
Industrial boiler replacement catalyst burner
Luminous wall catalytic furnace
Page
4-41
4-42
4-44
4-46
4-47
4-48
4-54
4-55
4-57
4-59
4-60
4-61
5-2
6-3
6-5
6-7
6-12
6-14
6-17
6-18
6-19
6-21
6-22
6-24
6-25
6-26
6-27
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LIST OF TABLES
Table Page
3-1 Distribution of Residential Heating Systems from the 1970
U.S. Census 3-4
3-2 Design Point Characteristics of a Typical 10s Btu/hr Forced
Warm Air Gas-Fired Furnace 3-21
3-3 Design Point Characteristics of a Typical 10s Btu/hr Warm
Air Oil-Fired Furnace 3-23
3-4 Population Breakdown by Boiler Types (Percentage Basis) for All
Commercial-Industrial Boilers in Service in U.S. in Mid-1974 . . 3-27
3-5 Population Breakdown by Fuel Capability (Percentage Basis) for
All Commercial-Industrial Boilers in Service in Mid-1974 .... 3-28
3-6 Estimated Trends of Boiler Types (Percentage Basis) for All
Commercial-Industrial Boilers Installed in Years Noted 3-29
3-7 Characteristics of Typical 10s Btu/hr Gas- and Oil-Fired Cast
Iron Boilers 3-34
3-8 Characteristics of a Typical 4 x 10s Btu/hr (80 bhp) Packaged
Scotch Firetube Boiler 3-38
3-9 Summary of the Effect of Variations in Parameters and Operating
Conditions on NOX Emissions from Industrial Boilers 3-52
3-10 Average NOX Emissions from Industrial Boilers 3-54
4-1 Monolith Support Data 4-17
4-2 Fiber Pad Data 4-27
4-3 Metals of Catalytic Interest for Catalytic Combustion 4-30
4-4 Combustion Parameters for Catalyst C, Detroit Diesel Allison
Tests, 7.6 cm Length x 8.9 cm Diameter 4-50
4-5 Typical JPL Catalytic Generator Operating Conditions 4-56
5-1 Catalyst Bed Types from an Application Point of View 5-8
5-2 Potential Low NO Catalytic Concepts 5-10
A
5-3 Oil Vaporizer Designs 5-21
6-1 Data on Design #1 6-4
6-2 Data on Design #2 6-6
6-3 Data on Design #3 6-8
6-4 Data Summary Home Heater Design #1, 100,000 Btu/hr 6-16
xii
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SECTION 1
SUMMARY
The use of catalysts in place of conventional burners for promoting hydrocar-
bon oxidation reactions appears to have advantages in the control of emissions. The
operating conditions of these catalytic combustors are limited by the catalyst bed
temperature capability, and the temperature obtained through normal one-stage, low
excess air operation that is necessary for efficiency reasons is outside the current
temperature capability of catalyst systems. It is therefore necessary to consider
other system techniques such as bed cooling, exhaust gas recirculation, or staged
combustion to hold the bed temperature down. The purpose of this study is to update
the knowledge on catalytic combustion, and to assess the potential and problems of
catalytic combustors for stationary combustion systems. Earlier reviews examined the
use of catalytic combustors in point sources, such as utility boilers. This study
is concerned with stationary area sources, where emissions would be distributed
somewhat uniformly over a wide area. Based on a review of the state-of-the-art of
catalytic combustion concepts, an assessment has been made of their applicability to
gas- and oil-fired home heaters and commercial and industrial boilers. As used in
this study, "catalytic combustion" refers to devices which employ special additives
(usually precious metals) to enhance the heterogeneous activity of the surface. This
section gives a summary of the study results and the overall study conclusions.
1.1 STUDY RESULTS
The major results of the investigation are summarized below.
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Area Source Characterization
• The most popular means of heating homes and commercial buildings is
through the use of central, forced-warm-air, gas- or oil-fired furnaces.
Initial catalytic oxidation redesign and/or retrofit efforts for residen-
tial applications should be directed toward this type of equipment due to
the clean fuels used and the relative simplicity of the redesign effort.
t The design of warm-air furnaces is based largely on empiricism and proto-
type development, experience, and testing. No theoretical barriers appear
to exist to a catalytic redesign or retrofit program.
• The excess combustion air levels in a warm-air furnace are necessarily
high (20 — 50 percent for gas-fired furnaces, 25 — 100 percent for oil-
fired furnaces) in order to keep the heat exchanger metal temperature
below 900°F. A catalytic redesign or retrofit should be aimed at achiev-
ing sufficiently low combustion temperatures by means other than increas-
ing excess air, since flue losses increase as the mass of flue gas in-
creases, thereby lowering overall system thermal efficiency.
• The fuels supplied to residential and commercial heating equipment, in-
cluding warm air furnaces and cast iron boilers, are predominantly natural
gas and distillate oil. This will be an asset to new catalytic oxidation
concepts since they require clean fuels.
• Cyclic-based emissions from oil-fired warm-air furnaces can, in many
cases, account for most of the total CO, UHC, and smoke emissions. The
design of a substitute catalytic concept should be aimed at eliminating
these ignition peaks, as well as the reduction in efficiency caused by the
on-off mode of operation.
• Scotch firetube industrial boilers appear to offer some advantages to a
catalytic retrofit effort due to their unique internal, first pass fur-
nace volume.
Catalytic Combustion Review
• The overall success of a catalytic combustion system in reducing CO and UHC
to low levels is a function of both heterogeneous and gas-phase reactions;
surface reactions alone appear to be unable to achieve the desired low
levels.
• Newly developed high-temperature catalyst support materials that are ca-
pable of maintaining their structural and thermal integrity at tempera-
tures up to 3000°F are necessary for high system efficiency unless methods
for cooling the catalyst bed are used. However, current catalyst systems
1-2
-------
are limited by the catalyst coating to much lower temperatures than the
supports. An example is platinum, where the catalytic activity decreases
by 30 percent at a temperature of 1800°F, and by 75 percent at a tempera-
ture of 2200°F.
• The most promising catalyst materials are the noble metals, such as plat-
inum and palladium, because of their high activity and relatively low ac-
tivation temperature.
t Currently, there are no commercially available catalysts for application
to catalytic combustion.
• Metal oxides have activities which approach those of the noble metals,
but have significantly higher light-off temperatures, probably limiting
their use to spinel structures.
• The principal catalyst poisons for natural gas and light distillate oils
will probably be phosphorous, sulfur, and certain halides. Their effect
on a variety of catalysts is not known.
• The existing applications of catalytic oxidation concepts in industry,
such as in nitric acid plant tail gas cleanup, industrial odor control,
small catalytic heaters, and automotive oxidation catalyst systems, are
generally in the low-temperature range of applicability. The applicabil-
ity of this technology to high-temperature catalytic combustion is there-
fore quite limited, since the problems of catalyst sintering and thermal
degradation of the support are avoided at low temperatures (i.e., <1400°F).
• Research is presently being conducted in the area of high-temperature
catalytic combustion for application to gas turbine engines. This research
is done with extremely fuel-lean conditions, making it difficult to relate
directly to domestic, commercial, and industrial space heaters, where
near-stoichiometric conditions are desirable.
0 Operation of stationary heating and steam generating systems with low
overall excess air tends to optimize overall system thermal efficiency.
Two-stage combusion, wherein the first stage is run fuel-rich and secondary
air is added in a catalytic second stage to complete the combustion, has
been shown to be effective for utility and industrial boilers in control-
ling NO emissions. However, proper design is necessary to also minimize
J\
CO and UHC, and to keep the system fuel-air ratio near stoichiometric.
Staging should be examined carefully for application to catalytic combustor
technology.
1-3
-------
• Because of the necessity of avoiding local "hot spots" in the catalyst
bed, premixed fuel-air systems are needed for catalytic combustors. To
prevent blockage of the passages in a catalyst bed, liquid fuels must be
prevaporized. The problems associated with fuels introduction to the
catalyst bed are formidable ones that require careful attention.
• At the present time, it is assumed that the catalyst bed temperature must
be held below 2800°F to minimize the formation of NO . Further research
work should be undertaken to establish this maximum allowable temperature.
• Current research programs have all been conducted at catalyst bed tempera-
tures well below 2800°F (i.e., 2400°F), and have all demonstrated a suc-
cessful minimization of NO formation.
/\
• Because much of the research concerning catalytic oxidation is proprietary
information and therefore not available to the general research community,
an experimental program which examines catalyst-support performance and
addresses the application of these catalysts in various combustor-heat
exchanger systems is needed. Information on the proper methodology to
follow in selecting a catalyst is also unavailable from catalyst manufac-
turers, and needs to be addressed.
Application of Catalytic Combustion to Area Sources
t Flue gas recirculation with a single stage catalytic combustor appears to
be one of the most viable retrofit and/or redesign applications.
• Due to the limited furnace volume, low heat transfer coefficient, and
cyclic nature, gas-fired home furnaces exhibit several problems for retro-
fit of a catalytic combustor. These problems appear to be solvable, but
redesign appears to be a more viable solution.
0 The necessity for preheated air for some catalyst-fuel combinations to
activate the catalyst bed must be taken into consideration in any final
design.
• Oil-fired units present formidable problems for retrofit, including oil
vaporization, startup, and air preheating. Due to the complexity of these
problems, catalytic retrofit of oil-fired units is not recommended.
0 In order to keep system efficiency high, special control circuitry for on-
off operation may be required. This system would include a sequencing
control for air/fuel operations and a safety control.
1-4
-------
• Because of the many possible choices open to a designer for catalytic
combustor retrofit and/or redesign, preliminary conceptual designs for
gas- and oil-fired warm air furnaces and commercial and industrial boil-
ers have been made as a part of this study.
• Since the size of the catalytic combustor required for a given applica-
tion is unknown due to a basic lack of knowledge of the catalyst charac-
teristics, wash coat, support, and bed depth required for an oxidation
reaction to go to completion, any attempt at doing a cost analysis of a
retrofit or redesign catalytic combustor could lead to erroneous conclu-
sions regarding cost.
t The application of catalytic combustion may be more feasible for large-
size units because of the larger initial cost, generally more sophisti-
cated controls, better supervision of equipment, and less limitations on
heat transfer.
1.2 CONCLUSIONS
The results of this study indicate that the catalytic combustion concept is
feasible for gas- and oil-fired warm air furnaces, and commercial and industrial
boilers. At the present time, catalyst availability for systems of interest to
catalytic oxidation studies is unknown, however. Oil-fired units pose special pro-
blems in terms of fuel vaporization, startup, and air preheating.
It is recommended that a comprehensive testing program be undertaken to sup-
port the conclusions stated above. Because the bulk of the knowledge concerning
catalyst preparation and performance lies in the proprietary realm, and is thus un-
available generally, this information must be generated and disseminated in an open
manner before catalytic combustion can be successfully evaluated as a combustion
modification concept. Therefore, the following program is recommended:
• Screening tests of various catalyst-support combinations with a variety
of fuels, in order to determine activation energies and kinetic rate
constants.
0 Development of a mathematical model for combined homogeneous/heterogeneous
combustion, which will be capable of predicting the performance of a cata-
lytic bed. This model will make use of the data obtained in the screening
tests.
• Tests which demonstrate the feasibility of catalytic combustion in flue
gas recirculation, catalyst bed cooling, and two-stage combustion concepts.
Since the goal of low NO emissions is dependent on holding the bed temper-
J\
ature down, the mechanisms of active bed cooling must be studied in detail.
1-5
-------
• Prototype design and development of catalytic furnaces using flue gas re-
circulation, catalyst bed cooling, and/or two-stage combustion. Since
little data of any value presently exists to aid the designer in sizing
a catalytic combustor, this data must be obtained experimentally before
further prototype design is attempted.
1-6
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SECTION 2
INTRODUCTION
More than 150 years ago Davy discovered that platinum wires could promote
combustion reactions in flammable mixtures, and that the resulting reactions appeared
to take place on the surface of the wires, "without flame" and with the high radia-
tive fluxes associated with the solid surface emittance rather than the low emittance
of the combustion products (Reference 1). Subsequent study and investigation fol-
lowed a number of paths reviewed by Spa!ding in Reference 2. Of this work, a sub-
stantial fraction which might be termed "fundamental studies of heterogeneous catal-
ysis" has attempted to
• Identify specific heterogeneous reactions
• Quantify reaction kinetics for these reactions
• Define the mechanisms by which the solid surface promotes or accelerates
oxidation reactions and identify catalyst properties leading to high
activity.
A second fraction which can be labeled "computation" has dealt with theories and
analyses which mathematically
• Describe the diffusion of reactants to the promoting surface and the dif-
fusion of products away from it, in the bulk aerodynamic flow around the
surface
• Describe the diffusion of reactants and products in pores (if any) of
rough or permeable surfaces
• Link these descriptions to calculations of the catalytic reactions at
the promoting surface
• Predict, by appropriate numerical techniques, the combined heat and mass
transfer events in systems with convection, diffusion, and both homogene-
ous and heterogeneous chemical reactions.
A final third fraction can be termed "reduction to practice", which includes attempts
to construct and employ practical devices exploiting heterogeneous combustion. As is
frequently the case in combustion, work in this area has proceeded with very little
2-1
-------
reference to achievements in fundamentals and computation. Experiments throughout
the 1800's demonstrated that various materials promoted heterogeneous combustion re-
actions to various degrees, and that with increasing surface temperatures the number
of materials with the ability to promote reactions increased. Numerous investigators
attempted to make practical use of this knowledge. The earliest successful devices
exploited heterogeneous combustion to provide more efficient lamps. The best exam-
ple is the mantle lantern or Auer light, still sold in great numbers as a "camping
lantern", in which combustion takes place on the ash residue of a fiber bag mantle
surrounding the fuel/air orifice. This mantle ash contains oxides, including cerium
oxide and thorium oxide, which in addition to constraining radiation emission to
desirable lines in the visible spectrum, contribute to the catalytic activity of the
mantle (Reference 3). The outmoded theatrical chalk light employed a simpler and
less sophisticated surface combustion concept, but also achieved high radiance
levels.
Concepts close to the original experiments of Davy have been used as passive
ignition devices and as combustible detectors, particularly in the form of hydrogen
leak detectors. Related applications along this line include catalytic fume abate-
ment devices and automotive catalytic converters, both depending on precious metals
to oxidize low concentrations of combustibles in gas streams.
After extensive practical experimentation, Bone publicized various high tem-
perature applications of surface combustion, using for the most part conventional
ceramic materials (References 4, 5). He built and tested surface combustion furnaces,
boilers, and permeable panels. This line of investigation has not, however, proven
very fruitful, although some commercial equipment of this type is available (Refer-
ence 6). This is due primarily to the complexity and expense of the required air/
fuel mixing and distribution equipment, and the relative scarcity of industrial ap-
plications either requiring (or even able to accept) high radiative fluxes. Surface
combustion radiant panels are used as space heaters (although such panels require
careful engineering and often precious metal additives to function as true hetero-
geneous combustors). Catalytic tent heaters operating at quite low temperatures
constitute one familiar example in this class.
The range of commercial devices has recently led to some specialization of
terminology in a field where formerly several terms were used interchangeably. The
term "radiant burner" refers to burner types employing a refractory surface situated
within or near the flame so as to provide for radiant heat transfer from the flame
area. Heterogeneous combustion occurs in these devices to some degree, but generally
does not dominate the process and homogeneous combustion constitutes most of the
reaction mechanism. "Surface combustors" employ refractory in a similar manner but
use special provisions of air/fuel distribution to maximize the amount of heterogene-
ous combustion occurring. "Catalytic combustors" employ special additives (usually
precious metals) to enhance the heterogeneous activity of the surface.
2-2
-------
There are several reasons for the recent upsurge of interest in catalytic com-
bustion. Use of the diffusion flame for combustion appears to place a limit on the
lower level of control that can be achieved economically for clean fuels (approximately
25 — 30 ppm of NO for small sources), and catalytic combustion appears to be able
3\
to reach lower levels of NO control (perhaps <10 ppm). In addition, catalytic com-
bustion is soot-free, and the potential of high combustion efficiency for the over-
all system is present if the excess air can be limited in some way such as two-stage
combustion, flue gas recirculation, or cooling of the catalyst bed.
A recent study by the Control Systems Laboratory of the EPA reported the re-
sults of tests conducted on commercially available catalytic heaters, to determine
the potential of catalytic combustion for pollution-free domestic heating applica-
tions based on camper heaters (Rerference 56). This study found that while NO emis-
sions were very low from nearly all the heaters, UHC emissions were higher than those
of conventional domestic heating units and CO emission levels were extremely high in
some cases. It was concluded that more research was necessary before catalytic heat-
ing could be considered a viable domestic heating alternative.
The EPA has classified pollutant sources as "area" sources (relatively few
emissions from a large number of sources distributed over a wide area, e.g., home
furnaces), "line" sources (e.g., highways), or "point" sources (a large amount of
emissions emanating from a single source, e.g., utility boilers). The Aerospace
Corporation, under an EPA contract, reviewed the state-of-the-art of surface and
catalytic combustion concepts in 1973, and assessed the applicability of these con-
cepts to large utility boilers and stationary gas turbines (Reference 7). It was
concluded that catalytic combustors might be applicable to both existing and new
stationary gas turbines, but it was unlikely that catalytic combustors could be eco-
nomically installed in utility boilers.
This study, then, was undertaken to assess the present state-of-the-art in
catalysis and in catalytic combustion, to assess the feasibility of catalytic com-
bustion for the control of NOV emissions from stationary sources, and to define the
}\
problems that would be encountered in the redesign and/or retrofit of catalytic com-
bustors for stationary sources. Recommendations of the most promising applications
for area source combustors as presented, based on cost and technical factors.
2-3
-------
SECTION 3
CHARACTERIZATION OF STATIONARY COMBUSTION SOURCES
This section has four subsections as follows:
• General considerations, in which the nature of the residential, commer-
cial, and industrial area source sectors are described, current cost and
sophistication restraints are discussed, and the various types of equip-
ment are introduced
• A description of the design and operating characteristics of warm air
furnaces and boilers
• Air pollutant emission characteristics
• Conclusions
This discussion provides the background information required for a future catalytic
combustion redesign or retrofit effort.
3.1 GENERAL CONSIDERATIONS
Emissions of nitrogen oxides from fuel combustion account for over 98 percent
of the nation's total of 20 million tons per year. This contribution is almost
evenly divided between mobile sources and stationary sources. Reducing emissions
from the latter is the thrust of the present study.
The options available for controlling these NO emissions include fuel modi-
A
fication, flue gas treatment, modification of operating conditions, or use of alter-
nate processes. The first three of these methods have, in the recent past, been
vigorously investigated and one of them, combustion modification, has proven largely
successful for the more prolific NO emitters. In order to extend the reduction
A
capability of such sources as well as to bring those sources which do not respond to
the simpler reduction options into compliance with future emission regulations, al-
ternate processes must be explored. One of these, catalytic combustion, is the fo-
cus of this report.
The catalytic approach may offer significant NO , CO, and unburned hydrocar-
A
bon emission reduction potential due to a possible low operating temperature as
well as a concurrent promotion of oxidation reactions. An assessment of the appli-
cability of catalytic concepts to gas turbines and utility boilers was performed by
3-1
-------
the Aerospace Corporation in 1973 (Reference 7). This report concluded that cataly-
tic oxidation might be applicable to gas turbines, but that application to a utility
boiler might require a new system design. The report also indicated that only gase-
ous fuels and light, sulfur-free hydrocarbons could be used in catalytic systems due
to system requirements and catalyst poisoning difficulties. Since these fuels are
used predominantly in area sources, which may also be more amenable to redesign, it
is necessary to extend consideration to these sources.
This section of the present study will begin the task of assessing the applic-
ability of catalytic combustion to area sources by discussing their design, operating
and emission characteristics and by noting which of these factors may be critical for
catalytic concepts. The area sources of concern include residential and commercial
comfort heating equipment and industrial boilers.
3.1.1 Residential Sector
Figure 3-1 gives a breakdown of the major types of residential heating equip-
ment. The prevalent designs are the warm air furnace and hydronic systems, as shown
in Table 3-1. According to data obtained from the Gas Applicance Manufacturers Asso-
ciation (GAMA), the trend in the last 10 years has been toward gas-fired forced warm
air systems. The 1970 U.S. Census data substantiates this by indicating that for
houses built prior to 1939 almost 30 percent of the warm air furnaces are oil-fired
compared to approximately 15 percent for houses built during the period 1960-1970.
This overall trend toward the use of gas-fired equipment is favorable to programs
involving the use of catalytic oxidation processes since they have been identified
as requiring clean fuels.
Equipment characterization and system concept evaluation will, therefore, con-
centrate on gas-fired central furnaces and steam or hot water units, the latter over-
lapping to some extent on the commercial heating sector (that is, cast iron boilers
are used for both residential and commercial heating applications).
3.1.2 Commercial Sector
The two major categories of commercial comfort heating equipment are warm air
furnaces and boilers, as illustrated in Figure 3-2. The warm air furnace design con-
cept resembles that used for residential heating purposes except that the larger-
scale equipment dictates that the unit usually be mounted on the roof of the building.
Boilers include water tube, fire tube, and cast iron types, all of which usually em-
ploy only one burner.
The distribution of equipment types for heating commercial buildings varies
around the country. On the West Coast, or in other moderate climates, about 85 per-
cent of the heating units are warm air furnaces. If comfort heating is the only
3-2
-------
Residential
Heating
Equipment
Steam or
r Hot Water
Units
Warm Air
Furnaces
(central
Floor, wall
or pi pel ess
- Other
Upflow or "Highboy"
Horizontal or "Lowboy"
Downf1ow
Floor
Wall
Pi pel ess
Other (hybrid)
Stoves
Fireplaces
Portable Heaters
Figure 3-1. Residential heating equipment types.
3-3
-------
TABLE 3-1. DISTRIBUTION OF RESIDENTIAL HEATING SYSTEMS FROM
THE 1970 U.S. CENSUS
Equipment Type and Fuel
Rank
Warm Air Furnace
Gas
Fuel Oil
Coal or Coke
Wood
Electricity
Bottled, Tank, or LP Gas
Other Fuel
Steam or Hot Water
Gas
Fuel Oil
Coal or Coke
Wood
Electricity
Bottled, Tank, or LP Gas
Other Fuel
Floor, Wall, or Pipeless
Gas
Fuel Oil
Coal
Wood
Electricity
Bottled, Tank, or LP Gas
Other Fuel
Other Heating Equipment
Gas
Fuel Oil
Coal
Wood
Electricity
Bottled, Tank, or LP Gas
Other Fuel
Percent of
National
Total
31.56
10.37
1.00
Negligible
Negligible
2 04
0.08
8.78
12.29
1.02
Negligible
Negligible
0.28
0.36
7.79
0.98
0.10
Negligible
Negligible
0.65
0.01
12.06
4.67
1.00
1.36
Negligible
3.57
0.01
Rank
1
4
9
5
2
6
3
7
10
8
TOTAL 99.98
3-4
-------
Commercial
Heating
Equipment
Warm Air
Furnaces
L Boilers
Packaged
Watertube —
(wall-fired)
Firetube
(wall-fired)
rCoil
- Firebox
Scotch
Horizontal Return Tube
Firebox
Vertical
Locomotive
L Cast Iron
Figure 3-2. Commercial heating equipment types.
3-5
-------
requirement and if mildly fluctuating delivered air temperatures can be tolerated,
warm air furnaces are chosen over boilers. In addition, a warm air furnace has a
lower initial cost than that of a boiler, and the latter requires a more elaborate
piping system. Highrise buildings, however, almost always require boilers due to a
demand for different kinds of heated fluids.
The predominant fuels burned in warm air furnaces are distillate fuel oil and
natural gas. As for residential heating equipment of this type, it appears that ex-
cellent opportunities exist for the application of retrofit or new-design catalytic
concepts to commercial warm air furnaces. The best approach would be to choose a
typical commercially-available furnace for intensive analysis. Of the myriad manu-
facturers, Lennox appears to produce moderately-priced and popular equipment of rep-
resentative design, and would be suitable for this purpose.
Fuels burned in boilers used for heating commercial buildings include distil-
late and residual fuel oil, natural gas, and, to a small degree, process gas. Na-
tural gas and distillate oil dominate. The type of boiler chosen for a given commer-
cial heating application depends mostly on the size of boiler required or its function.
Generally speaking, cast iron sectional boilers are used for supplying most low pres-
sure steam or hot water in a small to medium size application. Fire tube boilers,
all of which are packaged, are available in sizes up to 25 x 106 Btu/hr, while pack-
aged water tube boilers range in capacity between 10 x 106 and 250 x 10s Btu/hr.
Most fire tube or water tube boilers are offered with dual fuel burners (gas and oil).
3.1.3 Industrial Sector
The types of heating equipment utilized in the industrial source sector are
divided, as with commercial heating equipment, between warm air furnaces and boilers.
Figure 3-3 depicts the relationship between these basic types. In industrial build-
ings where there is no requirement for hot water or steam, about 90 percent of the
heating sources are warm air furnaces or radiant heaters. These furnaces are iden-
tical to those used in commercial heating applications. In most industrial build-
ings, however, the processes in operation on the premises demand the availability of
hot water and/or steam. A variety of boiler types are used for these purposes.
Firetube boilers, as shown in Figure 3-4, comprise the first category. These
packaged units are essentially the same as the commercial heating units described
previously, but include additional, very rare, types of stoker-fired HRT and firebox
boilers. These are, of course, coal-fired, and may not be germane in the context of
a catalytic retrofit program. Distillate oil and natural gas are the most common
fuels delivered to the remaining types of boilers.
3-6
-------
_ Warm Air Furnaces
(comfort heating only)
Industrial Heating
and Process Steam
Equipment
Boilers
Field Erected
Watertube
Packaged Watertube
1- Packaged Firetube
Figure 3-3. Industrial heating and process steam
equipment — basic types.
3-7
-------
Firetube Boilers
r Scotch
Horizontal Return
Tube (HRT)
Fi rebox
- Vertical
L Locomotive
Wall-Fired
r Wall-Fired
u Stoker-Fired
-Wall-Fired
- Stoker-Fired
Wall-Fired
Wall-Fired
Figure 3-4. Industrial heating and process steam
equipment - firetube boiler types.
3-8
-------
Watertube boilers comprise the remaining types of industrial boilers, and
are available in packaged or field-erected form. A breakdown of the former type is
shown in Figure 3-5, while Figure 3-6 illustrates the variety of field-erected
boilers. Both types are commonly one-or two-burner, multi-fuel (including residual
oil) facilities. Most packaged watertube boilers range in capacity from 10 x 106
to 250 x 106 Btu/hr, while field-erected units are available in sizes above 100 x
106 Btu/hr and designs that are similar to full-scale utility boilers at very large
capacitites.
The remainder of this section is devoted to a more detailed discussion of the
combustion equipment types comprising the source sectors described above, and is
divided into separate discussions on warm air furnaces and boilers (steam and hydronic)
3.2 EQUIPMENT AND OPERATING CHARACTERISTICS
3.2.1 Warm Air Furnaces
A warm air furnace is a self-enclosed appliance used for heating air for a
house or building. It discharges hot air directly into the space being heated or
more commonly through ducts which transport the warm air to the area to be heated.
Some furnaces operate by gravity (buoyancy forces), but the majority are forced air
systems, using a pressure blower to move the air through the ducts and back to the
furnace (References 8, 9, 10).
The furnace consists of a burner with related piping and controls, a heat ex-
changer, and a blower for forced air systems. The furnace package is enclosed in a
rectangular steel casing. The heat exchanger compartment is insulated to improve
efficiency and to limit the outer casing temperature for personnel safety. The com-
bustion takes place in the primary combustion space of the metal-walled heat exchan-
ger. The combustion products pass through secondary flue gas passageways of the heat
exchanger and exit through a flue to the atmosphere. The air to be heated circulates
over the outside of the heat exchanger to the warm air discharge. The air discharged
is heated to 100°F to 150°F. Furnaces are fired by natural gas and distillate oil
and (rarely) by coal.
Domestic or residential warm air furnaces are usually defined as furnaces
whose capacities are under 300 x 103 Btu/hr and are generally classified into four
types:
• Downflow, in which the blower is mounted above the heat exchanger, the
flue gas discharges at the side or top and the warm air discharges from
the bottom of the unit (counter-flow). Figure 3-7 shows a typical gas-
fired downflow unit, while Figures 3-8 and 3-9 show counterpart oil-fired
furnaces utilizing two different heat exchanger designs.
• Upflow or "high-boy", which is similar to downflow except that the blower
is mounted below the heat exchanger and both the warm air and flue gas
3-9
-------
i- Wall-Fired
Packaged Watertube Boilers
(single and multi-burner)
— Bent Tube
Stoker-Fired
(coal only)
r Wall-Fired
L Straight Tube
Stoker-fired
(coal only)
Figure 3-5. Industrial heating and process steam
equipment - packaged watertube boiler
types.
3-10
-------
Field Erected Watertube
Boilers
Large Utility Type
(>108 Btu/hr)
Small
(<108 Btu/hr)
Stoker-Fired
(coal only)
r- Tangentially-Fired
- Single Wall-Fired
Opposed Wall-Fired
Vertically-Fired
Cyclone-Fired
Single Wall-Fired
Figure 3-6. Industrial heating and process steam equipment
field erected watertube boiler types.
3-11
-------
Direct
Drive
Blower
Heat
Exchanger
Burners-
Air
In
Air Out
Flue
Gas
Supply
Solenoid
Figure 3-7. Forced warm air gas-fired furnace - downflow (note:
Figures 3-7 through 3-13 courtesy of the Lennox Co.).
3-12
-------
Air In
Direct
Drive
Blower
Burner
Heat Exchanger
Figure 3-8. Forced warm air oil-fired furnace - downflow.
3-13
-------
Blower
Heat Exhanger
Flue
Figure 3-9. Forced warm air oil-fired -downflow, with compact
heat exchanger.
3-14
-------
discharge from the top of the unit (co-flow). Gas-fired furnaces of this
type mounted with direct and belt-driven blowers are shown in Figure 3-10.
Figure 3-11 illustrates the same furnace design fired by oil.
• Horizontal, in which the blower is mounted next to the heat exchanger,
the flue gas discharging at the top and the warm air at the end of the
unit (Figures 3-12 and 3-13).
• Basement or "low-boy", which is very similar to the horizontal unit ex-
cept that the flue gas discharges at the side and the warm air from the
top. In addition, the heat exchanger may be higher and narrower than for
a horizontal furnace.
All of these units are available in a wide range of capacities. The choice of
the appropriate type is based most often on available installation space. For exam-
ple, horizontal units are intended for use in situations where headroom is limited,
such as in attics or crawl spaces.
Sub-types of warm air furnaces include space heaters and unit heaters. A
warm air furnace is known as a space heater or unit heater when it discharges dir-
ectly into the space being heated and has no ducts. By definition of the American
Gas Association, a unit heater is non-residential (larger than domestic). While
domestic heaters may be used in commercial installations, commercial or industrial
size heaters are seldom used in domestic applications.
Space heaters are designed as room heaters, wall furnaces and floor furnaces.
A room heater is a self-contained, free standing, gas-fired air heater installed in
the space being heated. It may employ gravity or forced air circulation and be
vented or unvented. Wall furnaces are similar but are designed to be mounted in a
wall and are vented. A floor furnace is mounted under a floor with a grill at floor
level. Unit heaters may be free-standing floor units or may be designed for suspen-
sion from the ceiling.
The heat exchanger in a warm air furnace can have a single combustion chamber,
usually cylindrical, or a series of individual sections. The single combustion cham-
ber is used with a single port oil-fired burner, as shown in Figure 3-8. It is usu-
ally lined with insulating refractory or felt insulation but can be fabricated from
a temperature resistant alloy steel. The sectional type is used with multiple gas-
fired burners which are cross-connected to use a single port. This type is illus-
trated in Figure 3-7. The exchanger sections are connected at the bottom and at the
top to a common flue gas breeching. Construction may be of alloy steel, stainless
steel or sometimes aluminized steel.
Two types of blowers are found on modern forced warm air furnaces: direct
drive and belt drive. Direct drive blowers are of the multiple speed type and usually
3-15
-------
Belt drive blower
Direct drive blower
Figure 3-10. Forced warm air gas-fired furnace — upflow.
3-16
-------
Belt drive blower
Flue
Burner l!_Lif
Heat
Exchanger
Blower
Direct drive blower
Figure 3-11. Forced warm air oil-fired furnace — upflow.
3-17
-------
Flue
Gas
Supply
Solenoid
Heat
Exchanger
Burner
Figure 3-12. Forced warm air gas-fired furnace -horizontal.
3-18
-------
Air In
Heat Exchanger
Flue
Burner
Figure 3-13. Forced warm air oil-fired furnace —horizontal
3-19
-------
are found on combination heating and cooling furnaces. However, they are also used
on heating furnaces only. When properly connected electrically, the blower will run
at slower speeds in the winter months and at a faster speed during the summer months.
Belt drive blowers operate at one speed, which is dependent on the adjustment
of the pulley system. This speed is set by the servicemen during furnace installa-
tion, and can have a major impact on efficiency if done improperly.
The gas burners on residential-size warm air furnaces are naturally aspirated
types consisting of three to four Venturis, with distribution pipes consisting of
rows of small orifices (Figure 3-7). The primary air is drawn into the venturi by
the gas pressure and premixes with the gas prior to ignition. The primary air/fuel
ratio can be controlled by small shutters at the end of each venturi. Secondary air
from the furnace room enters around the burners to reduce the overall flame tempera-
ture and allow complete combustion. Units always utilize draft diverters which di-
lute the flue gas stream and prevent downdrafts from blowing out the pilot.
Typical operating conditions of a domestic-size warm air furnace (100,000
Btu/hr) are given in Table 3-2. The wide range in excess air levels is due to vari-
ations in installations and meteorological conditions. The combustion chamber pres-
sures are quite low due to the naturally aspirated burners. Consequently, the heat
transfer open area on the flue gas side is quite large to prevent excessive pressure
drop. This results in the fairly low heat transfer coefficients on the hot side,
as shown in Table 3-2, which necessitates fairly large surface areas. An overall
heat transfer coefficient of 2.7 Btu/hr-ft2-°F is recommended by ASHRAE.
Gas-fired furnaces rely on the stack to create sufficient draft to draw the
secondary air through the furnace. Manufacturers frequently claim that reducing the
stack temperature below 300°F will result in insufficient draft for the burners and
cause condensation in the stack.
In all, the design procedure of gas-fired forced warm air furnaces is largely
empirical and relies on testing and modifications of experimental units to meet AGA/
ANSI standards.
Oil-fired forced warm air furnaces look very similar to the gas-fired units
from the outside and are now being made with overall volumes not much greater than
the gas-fired versions. There are considerable differences internally, however.
The heat is supplied by a gun type oil burner of the type pictured in Figure 3-8.
These burners consist of a combustion air blower, motor, damper, fuel pump, spark
ignition system, main air tube and swirlers, and fuel nozzle. The fuel flow rate is
determined by the oil nozzle orifice size, and the total air flow rate by the blower
and damper. The proper air/fuel ratio is adjusted using the damper until the opti-
mum CO and smoke levels are achieved.
3-20
-------
TABLE 3-2. DESIGN POINT CHARACTERISTICS OF A TYPICAL 10s BTU/HR
FORCED WARM AIR GAS-FIRED FURNACE*
Excess Combustion Air: 20% to 50%
Flue Exit Diameter: 3-1/2" to 5"
Heat Exchange Area: - 30 to 35 ft2
Overall Heat Transfer Coefficient: 2 to 3 Btu/hr-ft2-°F
Exit Flue Gas Temperature (Before Draft Diverter): 450°F to 650°F
Draft Diverter Dilution Air Flow Percent of Flue: 20% to 50%
Combustion Chamber Pressure: ± 0.2" W.G.
Recirculating Air Flowrate (scfm): 800 to 1200 scfm
Temperature Rise on Air Side: 70°F to 75°F
Maximum Gas Side Heat Exchanger Metal Temperature: 900°F
Overall Steady State Efficiency: 75% to 80%
Common Operating Mode: on/off
Ignition System: Pilot flame
Draft System: Natural
*
Data is compiled from discussion with manufacturers and from Refer-
ences 10, 11, 12, 13, 14.
3-21
-------
The burner is mounted in a refractory or refractory-felt lined combustion
chamber which is cooled by air circulating through the house. From the combustion
chamber the flue gas passes through a heat exchanger, as discussed previously, and
finally out the stack. The absence of a pilot flame and the use of a forced draft
system precludes the need for a draft diverter in the flue. The burner blower may
supply the full pressure to exhaust the gas from the stack or it may rely partially
on the buoyancy forces downstream of the stack. Table 3-3 lists typical operating
conditions for this type of furnace.
As for gas-fired furnaces, the design procedure is quite empirical and relies
on prototype development, experience, and testing. Standards for construction and
thermal efficiency are set by Underwriters Laboratory and ANSI.
One of the most important attributes of a conventional warm air furnace is
the cyclical operating mode. This often contributes to an overall thermal effi-
ciency of significantly less than the AGA standard 80 percent. A 1970 study by
Strieker (Reference 15) attempted to measure the efficiencies of gas- and oil-fired
warm air furnaces in the "as-found" condition in the field over a 6-month period.
Figures 3-14 and 3-15 from this study show the typical temperature rise on the air
side during a cycle. The fire is extinguished at the maximum temperature rise, and
it is at this point that the peak, or certified, efficiency is probably achieved.
For the remainder of the cycle the air blower remains on but the flue gas tempera-
tures and flow rates have dropped. Perhaps what is more important and not shown
on this curve is that the burner has been firing for several seconds prior to cooling
air blower start-up. Again, this means that there is a significant period of time
when there is very little flow on the air side, implying inefficient heat exchange.
Of course, some of this heat is stored as heat capacitance in the furnace structure
to be recovered eventually, but much of it escapes out the stack under inefficient
conditions.
One type of warm air furnace that bears further discussion is the roof-mounted
commercial-size unit. The designs of these units vary considerably among manufactur-
ers, relative to the domestic sector. The apparent standardization of the latter is
due mainly to the large sales volume as well as an extremely competitive market place.
These conditions differ sufficiently in the commercial heating sector to allow some
design innovations, especially in gas-fired units.
The burners in these units tend to be inherently more versatile. One such
unit, used in rooftop furnaces manufactured by The Trane Company, consists of a
"Series NP Maxon Burner" with a 25 to 1 turndown capability.
Novel heat exchangers are also more common in these units, such as the "Muti-
loy" type found on General Electric products. This heat exchanger is composed of a
bundle of parallel stainless steel fire tubes with numerous small cooling fins welded
to the outside.
3-22
-------
TABLE 3-3. DESIGN POINT CHARACTERISTICS OF TYPICAL
10s BTU/HR WARM AIR OIL-FIRED FURNACE
Excess Combustion Air: 25% to 100%
Flue Exit Diameter: 5" to 7" (round)
Heat Exchange Area: 20 ft2 to 30 ft2
Overall Heat Transfer Coefficient: 2 to 3 Btu/hr-ft2-°F
Exit Flue Gas Temperature: 500°F to 900°F (older units)
Combustion Chamber Pressure: 0.05" W.G. to 0.2" W.G.
Recirculating Air Flow: 800 to 1300 scfm
Temperature Rise on Air Side: 75°F to 80°F
Maximum Gas Side Heat Exchanger Metal Temperature: 900°F
Overall Steady State Efficiency: 70% to 80%
Common Operating Mode: on/off
Ignition System: Spark
Draft System: Forced
3-23
-------
100
80
F1re Stops
CO
i
PC
u
ro
VI
(/I
u
f
0)
in
a)
QJ
a.
OJ
01
n)
(.
a>
60 -
Area Under Curve
Represents 6.51 KWH
40
20
Area Represents
0.103 KWH
Blower Stops
Extrapolated to
Zero Temp. Rise
6 9 12 15
Blower on Time 1n Minutes
18
21
-------
CO
ro
en
Area Under Curve
Represents 2.42 KWH
Area Represents
0.145 KWH
Blower Starts
Blower Stops
Extrapolated to
Zero Temp. Rise
3.5
10.5 14.0 17.5
Blower on Time in Minutes
21.0
24.5
Figure 3-15. Temperature rise across an oil-fired warm air furnace during
a typical cycle.
-------
Higher quality materials of construction and larger interior volumes are
other factors that distinguish commercial-size from domestic-size furnaces.
3.2.2 Boilers
A boiler is a device designed to generate steam or hot water by transmitting
heat from an external combustion source to water in a container (References 9, 16,
17). Heat for the production of steam or hot water is obtained from the combustion
of a fuel by a burner in a furnace or fire box. The energy released by combustion
is absorbed by the water and its vapor which are contained in the boiler. The boiler
heat transfer surfaces usually consist of steel tubes that are exposed to, or carry,
the hot combustion gases. Boilers designed to produce steam utilize a uniquely-
designed pressure vessel in which saturated steam is separated from the steam-water
mixture.
Most of today's boilers are internally fired, that is, the furnace volume is
an integral part of the unit and is often surrounded by water-cooled surfaces.
Boilers that have additional water-cooled surfaces, such as superheaters, air heaters
and economizers, are steam generators. However, the term "boiler" is applied to
both steam and hydronic, or hot water, units.
Boilers are marketed as packaged, shop-assembled or field-erected units.
Packaged boilers are equipped and shipped complete with fuel-burning equipment,
mechanical draft equipment, automatic controls and accessories. They were introduced
in the early 1940's and have since gained wide acceptance. Both firetube and smaller
watertube units are available in packaged form. Firetube units range in size from
below 107 Btu/hr to 25 x 106 Btu/hr. Ratings of industrial watertube units overlap
those of the firetube boilers, with nearly all of the units less than 500 x 106 Btu/
hr. Generally, above 250 x 106 Btu/hr, watertube boilers are field erected.
The principal types of industrial and commercial boilers in use today are
the cast iron, firetube and watertube boilers. Table 3-4 gives a breakdown of in-
dustrial boiler types by percentage of the entire boiler population. This informa-
tion is a "best estimate" of the number of watertube and firetube boilers in service
based on the total capacity of the type in operation about 1972. Table 3-5 shows a
breakdown by fuel capability. Table 3-6 presents estimated installation trends be-
tween 1930 and 1990. The major points to be noted from these tables are:
• A higher portion of packaged boilers in the smaller sizes and field-
erected boilers in the larger sizes
• More firetube and cast iron boilers in the smaller sizes and watertube
boilers in the larger sizes
3-26
-------
TABLE 3-4. POPULATION BREAKDOWN BY BOILER TYPES (PERCENTAGE BASIS) FOR
ALL COMMERCIAL-INDUSTRIAL BOILERS IN SERVICE IN U.S. IN MID-1974
(Reference 18)
10e Btu/hr or
103 Ib itm/hr
RATED
CAPACITY.
SIZE RANGE
CO
I
ro
WATER TUBE
Industrial Type > 104 # Steam/hr
Packaged
Field erected
Commercial Typo < 104 # Steam/hr
Coil
Firebox
Other
FIRE TUBE
Packaged Scotch
Firebox
Vertical
Horizontal Return Tubular (HRT)
Misc. (Locomotive typo, etc.)
CAST IRON
MISC. (Tubelen. etc.)
TOTAL
COMMERCIAL-INDUSTRIAL
BOILERS
-------
TABLE 3-5. POPULATION BREAKDOWN BY FUEL CAPABILITY (PERCENTAGE BASIS)
FOR ALL COMMERCIAL-INDUSTRIAL BOILERS IN SERVICE IN MID-1974
(Reference 18)
RATED
CAPACITY.
SIZE RANGE
FUELS
Oil Only
Gai Only
Coal Only
106 Btu/hr or
10? lb stm/hr
Boiler Horsepower
Oil & Gas and Gas & Oil
Oil & Coal and Coal & OH
Gas & Coal and Coal & Gas
Misc. Fuels
(alone or with alternate fuels)
OIL
Total
Distillate. No. 2
Resld
No. 4 and
Heavy No.
•
Light No. 5 (No preheat)
5 ind No. 6 (Preheated)
Total Oil
_ « . .
10-50
42
50
2
1
100%
95
(5)
4.5
O.S
100%
5MOO
42
50
1
1
100%
85
(15)
14
1
100%
101-300
40
50
1
1
100%
50
.(SO)
30
20
100%
• 1 . • 1
10-16
301-500
35
45
3
1
100%
10
(90)
20
70
100%
17-100
35
35
10
2
100%
2
(98)
2
96
100%
101-250
30
22
18
26
0.5
0.5
3
100%
2
(98)
nil
98
100%
251-500
22
22
22
23
3
3
5
100%
2
(98)
nil
98
100%
GO
I
ro
CO
-------
TABLE 3-6. ESTIMATED TRENDS OF BOILER TYPES (PERCENTAGE BASIS)
FOR ALL COMMERCIAL-INDUSTRIAL BOILERS INSTALLED IN YEARS
NOTED (Reference 18)
• Commercial •
Indurtrial-
RATED
CAPACITY.
SIZE RANGE
10s Btu/hr or
103 Ib stm/hr
Boiler Horsepower
10-50
51-100
10-16
101-300
301-500
17-100
101-250
251-500
30 '60 70 '90
30 '50 70 '00
30 '50 70 '90
WATER TUBE
Industrial Type > 104 # Steam/Hr
Packaged
Field erected
Commercial Type <104 # Steam/Hr
Coil
Firebox
Other
FIRE-TUBE ' .
Packaged -Scotch
Firebox
Vertical
Horizontal Return Tubular (HRT)
Misc. (Locomotive type, etc.)
CAST IRON
MISC (TUBELESS. ETC)
TOTAL
COMMERCIAL-INDUSTRIAL
BOILERS
nil 10 11. 10
6 11 18 20
5666
5 1 nil nil
8532
60 50 45 40
3211
100 100 100 100
X
1 14 22 26
20 15 17 23
3532
5 2 nil nil
5111
50 45 40 36
3 2 1 nil
100 100 100 100
30 '50 70 '90
(25)(17)(19)(20)
0 2 18 20
25 15 1 0
'30 '50 70 '90
(94) (97) (94) (90)
0 8 80 89
94 89 14 1
'30 '50 70 '90
100) (100) (100)000)
0 0 80 90
100 100 20 10
'30 '60 70 '90
aooaoo) (ioo) aoo
0 0 1 20
100 100 99 80
2 21 41 40
20 30 35 30
5 2 nil nil
60 25 1 nil
8 5 2 nil
nil 5 10 15
111
100 100 100 100
nil 35 40
20 40 40
50 5 'nil nil
53 1 nil
5 4 nil nil
nil nil nil nil
-------
• The expanding role of packaged Scotch firetube boilers for commercial and
small industrial applications.
The characteristics of these boilers are described individually below.
3.2.2.1 Cast Iron Boilers - Capacities up to 13.5 x 106 Btu/hr (References 8, 9)
One class of domestic and small commercial boilers sold today have heat ex-
changers that are constructed of cast iron. They are designed for supplying low
pressure steam (15 psig maximum) or hot water (40 psig maximum) and are used pri-
marily for air or water heating systems.
These boilers usually consist of an assembly of vertical cast iron sections.
Water enters at the bottom of the sections and hot water or steam exits at the top.
The products of combustion are conducted through labyrinth passages cast into the
sections. The capacity of a sectional boiler may be varied by the addition or de-
letion of sections.
Cast iron boilers tend to be more expensive than steel firetube boilers, but
they are more reliable, longer lived, and require less maintenance. One disadvantage
of cast iron boilers is that the sections tend to deform and take a permanent set
due to thermal expansion which can lead to flue gas leaks at the joints and around
the doors.
Figure 3-16 shows a typical gas-fired cast iron boiler. New units are usu-
ally considerably more expensive than forced air systems and are, therefore, now
being made only in the larger size ranges of 130,000 Btu/hr and higher. However.
old units are still prevalent in the Northeastern and Northcentral regions of the
country. The natural gas supply systems on the newly-designed units are quite simi-
lar to the warm air furnace, utilizing naturally aspirated burners.
Heat transfer area is governed by the gas side transfer coefficient which is
once again limited by the pressure drop requirements of the burners.
Figure 3-17 shows an oil-fired cast iron boiler. Again, although quite com-
mon in older homes in the Northcentral and Northeast states, these units are now
quite costly and are- limited to the larger size ranges. These boilers are similar
in some respects to oil-fired warm air furnaces in that they employ a refractory-
lined combustion chamber followed by the heat exchange surface. No draft diverter
is required.
It has been reported that poor matching of burner and combustion chamber re-
quirements frequently occurs between the burner manufacturer and furnace manufacturer
3-30
-------
Flue
Water
Pump
Burners
Figure 3-16.
Gas-fired cast iron boiler (courtesy of Slant-Fin
Corporation).
3-31
-------
Flue
Burner
Heat
Exchanger
Figure 3-17.
Oil-fired cast iron boiler (courtesy of the Utica Radia-
tion Company).
3-32
-------
(Reference 19). Typically, considerable leakage of secondary air into the firebox
is allowed, which serves to lower the flame temperature. In many cases this is
necessary to prevent damage to the combustion chamber, but leakage probably results
in overall lower furnace efficiency. Typical operating conditions and design factors
for both oil- and gas-fired systems are given in Table 3-7.
Cast iron boilers are rated by The Hydronics Institute (IBR ratings). They
must be designed and constructed in accordance with the ASME Code, Section IV,
Heating Boilers. The IBR Testing and Rating Code specifies the test conditions
and such things as minimum efficiency, percentage of carbon dioxide in the flue gas,
flue gas temperature and smoke reading. The ratings cover a range of 48 x 103 Btu/
hr to 13.5 x 106 Btu/hr.
3.2.2.2 Firetube Boilers -Capacities up to 25 x 106 Btu/hr (References 9, 16, 17,
20, 21)
In a firetube boiler the products of combustion are directed through the tubes
which are submerged in water. The tubes are normally straight and may be horizontal,
inclined, or vertical with one or more passes. They are held in place inside the
boiler shell by tubesheets at either end of the bundle. Except for small domestic
units, many of which are vertical, most units have horizontal tubes. Firetubes have
large water storage capacity which effectively dampens wide fluctuations in steam
demand. Firetube boilers are more efficient than simple shell boilers because heat
is absorbed by the tubes as well as the shell.
All units must be designed in accordance with the ASME, Section I, Power
Boiler Code, or Section IV, Heating Boiler Code. Firetube boilers are rated by the
Steel Boiler Institute Division of The Hydronics Institute. The ratings are based
on tests, the results of which are reviewed by the Institute. There are three gen-
eral classifications:
Schedule 1: Residential and Commercial
• Natural draft up to 1.8 x 106 Btu/hr
• Mechanical draft from 1.8 x 106 to 23 x 106 Btu/hr
Schedule 2: Commercial and Industrial
• Natural draft up to 18 x 106 Btu/hr
• Mechanical draft from 800 x 103 to 22 x 106 Btu/hr
Schedule 3: Commercial and Industrial
• Mechanical draft up to 23 x 106 Btu/hr
(All ratings given are SBI gross output.)
3-33
-------
TABLE 3-7. CHARACTERISTICS OF TYPICAL 10s BTU/HR GAS- AND OIL-FIRED
CAST IRON BOILERS
Recirculating Water Flows (gpm):
Excess Air (percent):
Flue Exit Diameter (inches):
Exit Flue Gas Temp (Upstream Draft Diverter)(°F):
Exit Flue Gas Temp (Downstream Draft Diverter)(°F):
Combustion Chamber Pressure (" W.G.):
Temperature Rise on Water Side (°F):
Overall Steady State Efficiency (percent):
Gas
3 15
30 - 500
3-1/2 - 5
500 - 600
300 400
0.05 2
10 40
75 - 80
Oil
3 15
30 100
3-1/2 5
400 - 600
--
0.2
10 - 40
70 - 75
3-34
-------
Firetube boilers are used where steam demands are relatively small. The prin-
cipal uses of firetube boilers are for heating systems, for industrial process steam,
or as portable boilers. The heating boilers are restricted to 15 psig steam pressure
or 30 psig hot water pressure. The power boilers are limited to about 250 psig steam
pressure.
Most firetube boilers are now constructed with an internal furnace. The in-
ternal furnace is substantially surrounded by water-cooled surfaces. The internal
furnace in a firebox firetube boiler, described below, is surrounded by water-cooled
surfaces except at the bottom.
There are many firetube boilers in operation which have been constructed with
an external furnace, usually of brick construction. The brickset type is not very
suitable if water scale or silt is to be expected. The water leg design, normally
incorporated into the internal furnace concept, is much better for poor boiler water
conditions. Water circulation is enhanced, and suspended solids can be conveniently
drained off and the system purged.
The types of firetube boilers are:
• Horizontal Return Tubular (capacities up to 22 x 106 Btu/hr)
The horizontal return tubular (HRT) is a two-pass (one under shell, and one
through the tubes) power boiler. It was formerly the most popular type of firetube
boiler. At present, approximately 10 percent of all commercial-size boilers are HRT.
It has the advantage of low installed cost due to its simple setting (brickset).
Water circulation, however, tends to be sluggish, contributing to a boiler efficiency
of about 70 percent.
• Locomotive (capacities up to 20 x 106 Btu/hr)
This is a single pass firetube firebox boiler. It has an internal water
jacketed furnace and is used primarily as a portable power source. It requires un-
usually long firetubes to prevent excessive exit gas temperatures. Water circula-
tion is better than with an HRT boiler, but it is still poor. Boiler efficiencies
of slightly less than 70 percent are normal.
• Firebox (capacities up to 20 x 106 Btu/hr)
The two major types of firebox boilers are the short and the compact, the for-
mer employing two passes and the latter three. These units are constructed with an
internal, steel encased, water-jacketed firebox. This design makes for very good
circulation and the boiler attains efficiencies of about 80 percent. Since the
furnace size is limited, properly matching burner flame length and combustion volume
is a critical factor. The greatest advantage of this type of boiler is its efficiency
and the minimum floor space required for installation.
3-35
-------
• Vertical (capacities up to 3.5 x TO6 Btu/hr)
Vertical boilers are normally single-pass boilers and are used for power boiler
applications and as residential hot water and steam boilers. As a power boiler, its
most important use is as a portable steam source for construction work. Boiler ef-
ficiencies are about 70 percent. Power boilers are designed for up to 3.5 x 10s
Btu/hr, and high head room is required for these units. They have a limited steam
release surface and since the upper ends of the tubes are steam-cooled, a slow start-
up is essential to prevent tube damage by overheating.
• Scotch (capacities up to 25 x 106 Btu/hr)
This type of boiler was developed 30 years ago based on the Scotch marine
boiler and has since become one of the most popular firetube boilers, as indicated
previously in Table 3-4. In addition, Table 3-6 shows an increasing trend toward
the use of this boiler type.
Figure 3-18 shows a typical oil-fired Scotch boiler. Its design emphasizes
compactness and limited head room requirements, and attains efficiencies of about
80 percent. It is capable of gas, oil, or combination firing. Inside shell diame-
ters are normally limited to about 95 inches and operating pressures to 250 psig,
although some units are designed for 600 psig.
Characteristics of a typical Scotch boiler are given in Table 3-8. They can
have either two, three, or four passes. The burner flame is contained in an elong-
ated, water-cooled combustion chamber which also acts as the first pass. This char-
acteristic is unique to this type of boiler. The rear wall of the furnace is either
refractory-lined ("dry-back") or water-cooled ("wet-back") in the larger versions.
Due to the relatively small diameter firetubes and concomitant large pressure drop,
they require provision for mechanical draft.
Most Scotch boilers are designed with a minimum amount of heating surface.
In most cases, five square feet of heating surfaces are required to produce one
boiler horsepower. Improved heat transfer is attained by:
• Keeping the flue gas velocity high throughout the boiler by routing the
gas through a steadily diminishing number of constant-diameter firetubes
per pass
• The installation of "turbulators" in the firetubes
• Improving water side circulation by internal baffling and other means.
Due to their compact design and multiple tube passes, the packaged Scotch
boiler is more difficult to clean than other firetube boilers.
3-36
-------
Flue
Firetubes, showing flue gas
directions ——
Blower
Figure 3-18. 4-pass scotch firetube boiler, (courtesy of the Cleaver
Brooks Company).
3-37
-------
TABLE 3-8. CHARACTERISTICS OF A TYPICAL 4 x 10s BTU/HR
(80 BMP) PACKAGED SCOTCH FIRETUBE BOILER
Excess Air: 5% to 20%
Heat Exchange Area: 400 ft2
Combustion Chamber Dimensions: D = 1 to 2 ft, L = 10 to 12 ft
Firetube Diameter: 1 to 2 inches
Common Operating Mode: on/off and partial load
Ignition System: Spark
Draft System: Forced
Maximum Gas Side Heat Exchanger Temperature: 900°F
Overall Steady State Efficiency: 80%
Exit Flue Gas Temperature: 450°F to 650°F
Natural Gas Fuel Consumption: 3350 ft3/hr
Light Fuel Oil Consumption: 24 gal/hr
3-38
-------
3.2.2.3 Water-tube Boilers -Capacities to 500 x 106 Btu/hr (References 9, 16, 21)
Above a capacity of 16 x 106 Btu/hr. industrial boilers are almost exclusively
of the watertube type. They also dominate the market where design pressure exceeds
150 psig.
Watertube boilers can be either field-erected or packaged. Common sizes for
the former type fall between 50 x 106 and 500 x 106 Btu/hr, while 107 to 250 x 106
is the capacity range for the latter. Larger packaged boilers, above 450 x 106 Btu/
hr, are currently being designed but are not yet common.
Since the industrial-sized watertube packaged boiler was first introduced in
the early 1940's, they have become very popular. In the period of 1930-1950, almost
95 percent of the 107 to 100 x 106 Btu/hr units were field-erected. However, it is
anticipated that by 1990 about 99 percent of this class will be packaged. Similarly,
until 1950 all of the watertube boilers in the range of 100 x 106 to 500 x 106 Btu/hr
were field-erected. Forecasts, such as Table 3-6, indicate that by 1990 about 90
percent of the sizes up to 250 x 106 Btu/hr will be packaged.
As the name implies, watertube boilers are designed to flow water through the
heat transfer tubes, instead of combustion products as in the firetube design. Be-
cause of the smaller diameter pressurized components and the advantage using tubes
gives in accommodating expansion, they are better able to contain the pressure and
afford an inherently safer design.
Field-erected boilers are usually balanced draft and therefore require both
forced draft and induced draft fans. Field-erected boilers are commonly fired with
coal, gas and/or oil. Many such boilers exist today but very few new applications
have capacities lower than 200 x 106 Btu/hr, except for pulverized or stoker coal-
fired units. This is because of the packaged boiler's domination of the oil- and
gas-fired boiler market, which is in turn due to their low capital cost in the sizes
between 12 x 10s and 200 x 106 Btu/hr.
Packaged watertube boilers are used for gas and oil firing applications. They
are not used for coal firing because they have much smaller furnace volumes than are
permissible. They are designed to be rail-shipped as a complete, single package with
minimum fieldwork. The furnaces are also designed to operate under positive pressure
versus the balanced or slightly negative pressure found in coal-fired boilers.
Boiler efficiencies attained in watertube boilers are about 80 percent without
heat recovery. Watertube boilers are designed in accordance with the ASME Code and
must conform with state and local ordinances.
The two general types of watertube boilers are horizontal-straight and bent
tube boilers.
3-39
-------
Straight tube boilers are no longer manufactured, having been completely sup-
planted by firetube boilers in the smaller sizes and bent tube boilers in the inter-
mediate sizes. There are, however, a large number of straight tube boilers still in
operation.
The straight tube boiler owed its early popularity to its low draft loss,
good tube visibility for inspection and cleaning, ease of tube replacement and low
headroom requirements. It is often subject to leaks around the handholes; consider-
able labor is required to open a sectional header type for inspection; and it has
poor water distribution and low circulation rates.
These boilers are normally baffled to create two or three flue gas passes
across the water tubes. The tubes are grouped into sections and expanded at the
ends into headers. The headers are connected to the drum by downcomers for supply-
ing water to the tubes and by risers for discharging water and steam from the tubes.
In some models steel saddles connect the header to the drum. The "horizontal" tubes
are inclined at an angle of 5 to 15 degrees for natural circulation of the water.
The flue gas is normally moved by a forced circulation fan.
Horizontal straight tube boilers can be subdivided as follows:
• Type of Header
Box Header
This is a box-like uptake or downcomer which forms a tube sheet and hand-
hole plate. It is normally braced with staybolts and gives better circu-
lation than a sectional header.
Sectional Header
This is formed from many individual forged steel headers. Each header
has a riser and a downcomer which connect to the steam drum. The lowest
header is known as the mud drum. It acts as a collecting chamber for the
sediment, solids or mud, in the boiler water.
• Type of Drum
Long Drum
The long drum is located longitudinally and parallel to the horizontal
tubes. Since the riser and downcomer (one or many depending on the header
type) must be connected to the long drum circumferentially, there is a
limit to the number of headers or tubes that can be connected to a single
drum. Multiple drums can be used if required. The long drum design is
used for units rated from 5 x 106 to 80 x 10s Btu/hr at pressures of 160
to 325 psig.
3-40
-------
Cross Drum
The cross drum is mounted at right angles to the tubes. The drum is lo-
cated above the downcomer with the steam and water risers connected to
the drum in longitudinal rows. It provides better steam distribution in
the drum than the long drum design and presents no problems in increasing
capacity by increasing the unit width. It is used for capacities of 5 x
106 to 500 x 106 Btu/hr and pressures up to 1450 psig.
• Portable Firebox Boiler
This is a straight watertube boiler built with a steel encased, brick!ined
firebox with water cooled walls. The water and steam are contained in an
enclosure above the crownsheet. It is designed for 1 x 106 to 18 x 106
Btu/hr and 15 psig to 250 psig pressure.
Horizontal bent tube boilers, the other major type of watertube boiler, are
classified by the number of drums, headroom, and tube configuration, the latter of
which is the most important distinguishing factor. The most common tube configura-
tions are:
• 0-type with two drums, one upper and one lower, centrally located
t D-type, a modification of the 0-type, with the two drums located to the
side (top and bottom) of the tube bundle (Figures 3-19 and 3-20)
• A-type which has three drums, two lower drums and an upper, centrally
located drum for steam-water separation.
In the bent tube boiler each tube is connected to the steam drum and to at
least one lower drum or header. The tubes enter a drum radially and are designed to
allow for the anticipated expansion. The furnace is of the waterwall type backed up
with refractory. The tubes, which form the furnace waterwall, are an integral part
of the boiler. The steam drum contains internals, such as separators and cyclones,
to facilitate steam-water separation. Bent tube boilers have the advantage of great
design flexibility making them readily adaptable to space limitations by either ex-
tending their length or, more practically, the width. They provide good accessibil-
ity for inspection and cleaning, which normally entails mechanical cleaning from in-
side the steam drum.
Most packaged units are oil-, gas- or combination-fired, although there are
some coal-fired packaged units. The furnace wall cooling tubes are usually oriented
vertically. Vertical furnace tubes are particularly desirable on coal-firing since
they are less susceptible to slag adherence.
Heat recovery from the flue gas is practical and often desirable with bent
tube boilers, particularly in the intermediate and large sizes. This may consist of
3-41
-------
Figure 3-19. 80 x 106 Btu/hr combination-fired packaged watertube,
D-type boiler (courtesy of the Cleaver-Brooks Co.).
3-42
-------
Figure 3-20.
D-type bent tube configuration (courtesy of
the Cleaver Brooks Co.).
3-43
-------
an economizer, which preheats feedwater, an air preheater, to heat combustion air,
or both. These may be internally mounted in the boiler, but are more commonly ex-
ternal to the boiler.
The larger industrial-size, field-erected watertube boilers (> 250 x 106 Btu/
hr) are identical to utility boilers used for generating electrical power. These
multi-burner facilities are available in the tangentially-fired design as well as
the wall-fired type found in the smaller units.
3.3 AIR POLLUTANT EMISSION CHARACTERISTICS
The preceding subsections of Section 3 described the equipment and operating
characteristics of-residential, commercial, and industrial combustion-generated air
pollution sources. Warm air furnaces and boilers were included in this category.
The following discussion will center on a characterization of the pollutant emissions
from these sources as well as the conventional means by which such emissions have
been reduced.
3.3.1 Commercial and Residential Sector
As shown previously in Table 3-1, natural gas and distillate oil-fired heating
equipment account for about 80 percent of the residential heating units in the U.S.
The actual contribution from fuel combustion in this equipment to the total national
air pollutant loading (summation of mass of particulate, SO , NO , CO, and unburned
A A
hydrocarbons) is unclear. One investigator estimated that air pollution from the
combination of residential and commercial heating sources constitutes about 10 per-
cent of the national total (Reference 22). This figure, however, may be outdated;
the source paper was published in 1964. Fuel usage and emission factors were the
basis for this estimate.
Another data dource, the National Emission Data System (NEDS), does not com-
pile information for sources that emit less than 25 tons/year of any pollutant.
This limitation causes the exclusion of residential heating from consideration.
From all indications, however, this contribution to the nation's total emissions
probably falls in the 1 to 10 percent range.
The emissions from commercial and residential space heating for one pollutant
species, oxides of nitrogen, have been fairly well established by recent studies.
The 1972 data shown in Figure 3-21 gives an estimate of 826,800 tons/year (7.1 per-
cent of total) as the contribution from commercial and residential heating (Refer-
ence 23).
The impact of these emissions is greater than a simple weight percent would
indicate, however, since the emissions occur in regions of high population density,
they are emitted at essentially ground level, and they are seasonal in nature so
that there is a concentration of emissions within a 3- to 5-month time span. For
these reasons the U.S. Environmental Protection Agency has instigated an emission
reduction R&D program.
3-44
-------
i— Incineration 0.4%
Noncombustion 1.32
Gas Turbine 2.5%
Industrial Process
Heating 3.3%
Commercial/
Residential
Space
Heatin
7.1%
Industrial
Boi1ers
18.1%
Utility Boilers
48.6%
Reciprocating
1C Engines
18.8%
Estimated NOX Emissions
Tons/Year
5,670,000
2,189,000
2,108,000
826,800
390,200
291.000
149,000
41.000
11,665,000
Source
Utility Boilers
Reciprocating 1C Engines
Industrial Boilers
Commercial/Residential Heating
Industrial Process Heating
Gas Turbines
Noncombustion
Incineration
TOTAL
Figure 3-21. Sumnary of 1972 stationary source NOX emissions.
3-45
-------
To aid in the effort of reducing emissions from this sector, the EPA is con-
ducting research on the reduction of air pollution from various types of residential
heaters. Early work was performed on an experimental furnace to determine the basic
reduction parameters. Later, commercially available equipment was investigated.
The most recent published work from this project appeared in 1974 (Reference 24).
This study, which concentrated on an oil-fired warm air furnace, showed that
residence time, flame retention devices, maintenance, and excess air are major fac-
tors in the control of emissions, the latter being the dominant one. Emissions of
CO, UHC, smoke, and particulates pass through a minimum as excess air is increased
from stoichiometric, as shown in Figure 3-22. It is observed that both thermal ef-
ficiency and NO emissions behave in the opposite manner: as excess air is increased,
they pass through maximum points.
At stoichiometric ratios ranging from 1.2 to 1.5, the NO, HC, and CO emissions
from various types of gas-fired burners averaged 0.104, 0.0032, and 0.051 g/106 cal
input, respectively. Emissions of the same species from equivalent size oil burners
were comparable to these levels, with particulates being a problem only from this
fuel. Compared to other sources of air pollution, the levels of UHC and CO from
properly adjusted furnaces are very low.
Combustion chamber material was found to affect all emissions. Furnaces with
steel-lined chambers required higher excess air levels to reach optimum emission
levels, thus reducing efficiency. The shape of the combustion chamber had little
effect on pollutant generation.
As mentioned in Section 3.2.1 of this report, the on/off mode is the outstand-
ing operating characteristic of warm air furnaces, and is the major efficiency re-
ducing factor. The aforementioned EPA study has since identified the importance of
cyclic-based emissions. Work on a model residential heating system indicated that
the sizeable peak emissions measured during ignition and shutdown can account for
most of the total emissions.
CO and UHC emissions peak at ignition and shutoff as shown qualitatively in
Figure 3-23. HC concentration drops to insignificant levels between the peaks,
while CO emissions tend to flatten out at a measurable level. Figure 3-24 shows
that particulate matter continuously tapers off after the ignition-induced peak.
Figure 3-25 shows that, after an initial peak, the NO emission level continues to
rise. The operating time of most domestic burners seemingly is not long enough for
NO to reach equilibrium levels.
The transient emissions are caused mainly be variations in the combustion
chamber temperature. At ignition, a cold refractory will not support complete com-
bustion, producing peaks of CO, UHC, and smoke. These peaks could be eliminated by
3-46
-------
2.00
1.50
0)
cn
. 1.00
o
0.50
0.00
Smoke
(10th
min.)
Optimum setting for minimum
emissions and maximum
efficiency
I-
10
8
c
0)
o
0)
ex
o
X
7 s
o
0)
C7»
J*
en
0.8 1.0 1.2 1.4 1.6 1.8 2.0 2.2 2.4 2.6
Stoichiometric ratio
Figure 3-22. General trend of smoke, gaseous emissions, and effi-
ciency versus stoichiometric ratio.
3-47
-------
Burner
on
s-
4J
OJ
o
e
o
O
o
s_
Burner
off
Time
Figure 3-23. Hydrocarbon and carbon monoxide trends during cycle.
3-48
-------
I
c
o
c:
O)
o
c
o
o
T3
ZJ
(J
I.
(O
a.
Burner
on
*
Time
Figure 3-24. Particulate trends during cycle,
3-49
-------
Burner
off
I
Burner
on
c
o
c
(U
(J
c
o
(J
Time
Figure 3-25. Nitric oxide trend during cycle.
3-50
-------
keeping the refractory warm during the off-time by a pilot or modulating burner. NO
emissions show a continuous increase due to the steadily rising temperature of the
combustion chamber walls.
It is important to recognize that cyclic-based emissions mainly affect emis-
sions of CO and UHC, both of which are very low for oil burners in any case. It is
hoped that particulate emissions can be reduced by new burner designs.
3.3.2 Industrial Sector
Combustion sources of air pollution in this sector include mainly firetube
and watertube boilers in the range of 107 to 500 x 106 Btu/hr capacity. These
boilers contribute the largest portion of air pollution from this sector since, as
indicated in Table 3-5, they are fueled mainly by residual oil and coal.
Information on the total pollutant mass emissions from industrial boilers is
scarce. As in the case of residential and commercial heating, however, total NO
emissions have been fairly well documented for this type of equipment and are shown
in Figure 3-21. Industrial boilers accounted for 2,108,000 tons/year, or 18.1 per-
cent of the total, of NO in 1972.
A
The most thorough investigation of emissions from industrial boilers was con-
ducted recently by Cato, et al., in 1974 (Reference 25). From tests of a sample of
50 industrial boilers ranging in capacity between 18 x 106 and 500 x 106 Btu/hr, a
wide variation in pollutant concentration was discovered. In the "as found" condi-
tion, CO varied from 0 to 1000 ppm, UHC from negligible to about 600 ppm, SO from
negligible to 1800 ppm, and solid particulates from 0.001 (gas) to 2.8 lb/106 Btu
fired (coal).
The major objectives of the study were to characterize NO emissions from
these boilers, as well as to identify the effective reduction methods. Table 3-9
summarizes the effects of various parameters on these NO emissions. In general, it
A
was found that typical, existing industrial boilers have limited flexibility to allow
combustion modifications for reducing NOX-
Table 3-10 gives the average NO emissions from all the boilers measured un-
A
der both baseline and low NO conditions. The largest degree of success was achieved
A
on natural gas-fired units. For all fuels, however, the most effective techniques
were off-stoichiometric combustion, excess air reduction, and burner adjustment.
The reduction of other pollutants from industrial boilers can be achieved
by other methods. Fuel switching is an effective means for reducing particulates
and SO , new burner design for particulates (and NO ) and burner adjustment and fur-
X A
nace maintenance for reduction of CO and UHC concentrations.
3-51
-------
TABLE 3-9. SUMMARY OF THE EFFECT OF VARIATKNS IN PARAMETERS AND OPERATING CONDITIONS
ON NOX EMISSIONS FROM INDUSTRIAL BOILERS
Burner Heat
Release Rate
(Btu/hr/burner)
Excess Oxygen
Natural Gas Fuel
i NOX emissions increase with
increasing burner loading
• The relationship between NOX
and burner loading depends
on combustion air tempera-
ture; the higher the air
temperature the more impor-
tant the burner loading
• NOX emissions not affected
by 02 level for ambient
temperature combustion air
• NOX emission decrease with
decreasing 02 level for pre-
heated combustion air
Oil Fuel
• NOX emissions increase with
increasing burner loading
• NOx emissions decrease with
increasing 02 level
• Number 2 oils not as sensi-
tive to 02 level as No. 5 and
6 oils
• Combustion air temperature
does not affect NOx-vs.-O?
relationship as found with
natural gas
Coal Fuel
NOX emissions increase with
increasing burner loading
t NOX emissions decrease with
decreasing 02 level and are I
more sensitive than for
either oil or natural gas
fuel
• Combustion air temperature
does not affect NO-VS.-02
relationship as found with
natural gas
Furnace Heat
Release Volume
(ft3/Btu/hr)
• Not an important considera-
tion for natural gas fired
boilers
• NOX emissions decrease as
furnace heat release volume
increases
• Relationship does not appear
to be dependent upon oil
grade
• NOX emissions decrease as
furnace volume increases
t The furnace volume required
for carbon burnout depends
on the design of the coal
burning equipment which may
also influence the N0x-vs.-
volume relationship
Combustion Air
Temperature
• NOX emission increase with
increasing combustion air
temperature
• Burner loading influences
the relationship between
NOX emissions and air tem-
perature
t NOX emissions for the lar-
ger burners increases at a
greater rate with increas-
ing air temperature than for
the smaller burners
• Not an important considera-
tion for oil fired boilers
• Not an important considera-
tion for coal fired boilers
Fuel Nitrogen
Content
Does not apply (except in
some waste fuel streams)
• NOX emissions increase with
increasing fuel nitrogen
content
t The average conversion ratio
was 46% (590 ppm/U fuel N)
and the average thermal NOX
was 105 ppm
t Fuel nitrogen content of
the coals did not vary
significantly and no corre-
lation could be made of
nitrogen content with NOX
emissions
Fuel Firing
Method
• Nearly all natural gas-
fired boilers tested had
multiple ring burners
• The design of the ring
burner is believed to affect
NOX emissions but data are
not available from this pro-
gram to support this thesis
t Data from other programs
show that air-rich operation
of gas spud burners tend to
produce higher NOX emissions
than do ring burners
• When properly atomized, the
type of oil atomizer did not
affect NOX emissions (air,
steam or mechanical)
• The operating conditions for
a particular atomizer such
as fuel oil temperature,
atomizer air pressure, etc.,
at the burner did affect NOX
emissions
Underfed stokers had the
lowest NOX emissions, a
cyclone combustor had the
largest NOX emissions, and
spreader stoker and pulver-
ized coal burners had simi-
lar intermediate NOX emis-
sions
3-52
-------
TABLE 3-9, CONCLUDED
Natural Gas Fuel
011 Fuel
Coal Fuel
Off-Sto1chiometr1c
Operation
• NOy emissions were success-
fully reduced by burners out
of service and air flow ad-
justments which effect bur-
ner stolchlometry
•Air register and damper
tuning was necessary to
avoid excessive CO and hy-
drocarbons emissions
• Successful application of
this technique requires
sufficient test time to em-
pirically determine boiler
adjustments to allow opera-
tion at low overall excess
Q£ with a burner out of
service. The time available
in Phase I was insufficient
to arrive at optimum adjust-
ments
• NOv emissions were success-
fully reduced by burners
out of service and air flow
adjustments which effect
burner stolchlometry
• Air register tuning was
necessary to reduce smoking
which limited excess 02
levels and NOX emission
reductions
• Successful application of
this technique requires
sufficient test time to em-
pirically determine boiler
adjustments to allow opera-
tion at low overall excess
02 with a burner out of
service. The time available
in Phase I was insufficient
to arrive at optimum adjust-
ments
t Conversion of fuel nitrogen
to NOX is also reduced by
0/S operation. Other studies
show reductions 1n conversion
from the normal 40 to 502 to
20 to 30%
i NOv emissions were success-
fully reduced by burners
out of service and air flow
adjustments which effect
burner stoichiometry
• Air register tuning was
necessary to reduce smoking
which limited excess 02
levels and NOx emission
reductions
• Successful application of
this technique require
sufficient test time to em-
pirically determine boiler
adjustments to allow opera-
tion at low overall excess
02 with a burner out of
service. The time avail-
able in Phase I was insuf-
ficient to arrive at opti-
mum adjustments
• Conversion of fuel nitrogen
to NOX is also reduced by
0/S operation. Other
studies show reductions in
conversion from the normal
40 to BOX to 20 to 30*
3-53
-------
TABLE 3-10. AVERAGE N0¥ EMISSIONS FROM INDUSTRIAL BOILERS
A
Fuel
Coal
#2 Oil
#5 Oil
#6 Oil
Natural Gas
Baseline
Operation
NOX
(ppm)
442
126
295
275
131
()5
9.0
5.7
5.8
6.0
5.0
Low NOX
Operation
NOX
(ppm)
385
115
254
230
105
09
(%)
6.3
2.8
4.9
5.4
5.3
Average %
NOX Reduction
15
10
15
20
25
3-54
-------
3.4 CONCLUSIONS
The following discussion gives the principal conclusions drawn from the pre-
ceding characterization of area sources and the impact these conclusions will have
on a catalytic combustion redesign or retrofit effort:
• The most popular means of heating homes and commercial buildings is through
the use of central, forced warm air, gas- or oil-fired furnaces. Initial
catalytic oxidation retrofit or redesign efforts should be directed toward
this type of equipment.
• There is very little variation in the design and cost (for the same capa-
city) among manufacturers of gas- or oil-fired domestic-size warm air
furnaces. This is due mainly to the extremely competitive nature of the
furnace market.
• The cooling coils for air conditioning installed on many warm air furnaces
apparently will not impact retrofit possibilities.
• Commercial-size, roof-mounted furnaces appear to offer advantages to a
redesign or retrofit program due to their larger interior volume as well
as higher-quality materials of construction.
• The design of these warm air furnaces is based mainly on empiricism and
prototype development, experience, and testing. No theoretical barriers
appear to exist to a catalytic redesign or retrofit program.
• The excess air levels in a warm air furnace are necessarily greater than
20 percent in order to keep the heat exchanger temperature below 900°F.
A catalytic redesign or retrofit should be aimed at achieving sufficiently
low combustion temperatures by means other than increasing excess air.
• The fuels supplied to residential and commercial heating equipment, in-
cluding warm air furnaces and cast iron boilers, are predominantly natural
gas and distillate oil. This will be an asset to new catalytic oxidation
concepts since they require clean fuels.
• Emissions of CO, UHC, and NO are observed from gas-fired residential
heating units, all of which can be eliminated by a properly designed cat-
alytic combustor. Particulates and SO are normally not present in the
3\
effluent from these sources.
• Cyclic-based emissions from oil-fired warm air furnaces can, in many cases,
account for most of the CO, UHC, and smoke emissions. In contrast, emis-
sions of NOX increase steadily during the on-cycle. The design of a sub-
stitute catalytic concept should be aimed at eliminating these ignition
and shutdown peaks, as well as the reduction in efficiency caused by the
on/off mode of operation.
3-55
-------
• Scotch firetube industrial boilers appear to offer some advantages to
a catalytic retrofit effort due to their unique internal, first pass
furnace volume. Strategies for retrofitting or redesigning watertube
boilers are less obvious.
• Although the initial attempt to characterize area sources during the pre-
sent study was successful, further effort should be directed toward com-
piling more detailed design and operating information on typical units,
including industrial process furnaces, before initiating a catalytic re-
design or retrofit program.
3-56
-------
SECTION 4
RECENT DEVELOPMENTS IN CATALYTIC FUELS OXIDATION CONCEPTS
In this section, the recent developments in catalytic fuels oxidation con-
cepts are discussed in the following order:
• General considerations, where the catalytic combustion process and some
of the important system characteristics are described
• Characteristics and properties of catalyst materials, where a review of
the support, wash coat, and catalyst materials presently available for
use in catalytic combustion is presented
• Existing applications of catalytic combustion, where proven catalytic com-
bustion applications are described
t Research programs in catalytic combustion, wherein current on-going re-
search programs are described
• Conclusions
This discussion provides the background information to assess the state-of-the-art
in catalytic combustion.
4.1 GENERAL CONSIDERATIONS
During steady operation, the catalytic combustion process can be described as
follows:
• The premixed gases are introduced at a velocity in excess of the flame
speed associated with the equivalence ratio and preheat of the mixture
(to avoid flashback).
0 These gases diffuse to the surface - and presuming the catalyst surface
is at sufficient temperature (related to self-ignition temperature) -
will react on the active sites at and within this surface.
• Heat will be generated and conducted, radiated or convected away. A
portion will serve to heat the bulk gases in the main flow.
4-1
-------
• The bulk gases will commence to react in the gas phase as initially
sustained by the heat input from the catalyst surface. This combustion
is related to the observed light-off in some systems.
• As the combustible gases are consumed, radiative and conductive heat re-
moval will reduce the surface and gas phase temperatures and reactions
will slow. Under some conditions this can result in extinction.
The overall success of a catalytic system in reducing hydrocarbons and CO to
low levels depends, somewhat ironically, on gas phase reactions. A reduction of
unburned hydrocarbons, for example, to low ppm levels probably cannot be achieved by
purely surface reactions, even under the assumption of perfect catalytic reaction
rates. Under such conditions, the reaction rates are limited not by chemical kinet-
ics but by the rate of mass transfer of the reactants from the bulk gas to the cata-
lyst surface (Reference 26). This rate is fairly low. Idealized analysis identifies
a requirement of 2.3 "transfer units" for each order of magnitude reduction of a gas
phase combutible by surface contact, and a required length of approximately 100 hy-
draulic radii for each transfer unit. This would imply far too lengthy a system for
most purposes.
Therefore, system design must ensure that gas-phase reactions occur to reduce
combustibles to low levels. For most conjectured applications, the temperatures and
concentrations in the bulk gas are within the range where gas-phase reactions occur
at significant rates. For example, in automative catalytic converters at certain.
operating conditions, gas-phase oxidation of hydrocarbons in the bulk stream can
produce a net increase in CO (additional flow length is required to provide for fur-
ther gas-phase and surface reactions to eliminate the CO).
An evaluation of a catalytic combustion system involves a determination of
the important operating characteristics of the system. These characteristics include:
• Ignition requirement
• Flashback potential
• Lean and rich flammability limits
• Maximum specific heat release
• Heat removal mechanisms
• Combustion efficiency
• Pollutant potential
These characteristics are discussed in greater detail below.
4.1.1 Ignition Requirement
An important factor for evaluating catalyst performance is the ability of the
fuel-air mixture to ignite in the presence of a catalyst. The ignition temperature
can be determined by comparing the temperatures of the air-fuel mixture both upstream
4-2
-------
of and in the catalyst bed, and beginning with an air temperature well below the seIt-
ignition limit. As the air temperature is raised, an increase in the catalyst bed
temperature over that upstream of the bed will indicate the onset of ignition.
The "light-off" temperature is determined by interpreting the unburned hydro-
carbon measurements. At the beginning of a test the amount of unburned hydrocarbons
will be at a maximum (100 percent). At some point as the inlet air temperature is
increased ignition will occur and the amount of unburned hydrocarbons will decrease.
The "light-off" temperature can be defined as that inlet temperature at which the
catalyst has appreciable activity with regard to oxidizing the reactants. "Appreciable
activity" is typically defined as either 50 or 90 percent conversion of hydrocarbons
to oxidized species.
Ignition and light-off temperatures are functions of:
• Catalyst (material, area, substrate composition)
• Catalyst bed geometry
• Fuel type
• Space velocity
• Air/fuel ratio
0 Pressure
• Dilution
An example of the effect that the catalyst material can have on the ignition
temperature of a fuel is shown in Figure 4-1. For this automotive application (Re-
ference 27) a noble metal catalyst exhibits a higher ignition temperature than a
base metal catalyst. Light-off temperatures, though, are much lower with the noble
metal catalyst when defined at rates of conversion of 60 percent or greater. An ex-
ample of possible effects due to variations in catalyst content, chemical composition
of the substrate, and substrate surface area is shown in Figure 4-2. This figure is
from Reference 28 which studied variations of catalysts and substrates on the oxida-
tion of n-heptane. In this case, minimal effect on light-off temperature was found.
Typical catalyst bed geometry effects on light-off temperature are shown in
Figure 4-3. This study of n-heptane fume abatement (Reference 29) illustrates that
a catalyst on a crossflow ceramic honeycomb substrate has a lower "light-off" tem-
perature than the same catalyst on spherical pellets. Ignition temperature appears
to be about the same.
The type of fuel combusted will also affect the catalyst ignition and light-
off requirements. Figure 4-4 shows the effect of various fuels on the ignition and
light-off temperatures of a palladium catalyst on an alumina substrate. Notice that
methane, which is a low-carbon number molecule, has the highest light-off tempera-
tures. It has been concluded that light-off temperature varies inversely with the
carbon number of the fuel used.
4-3
-------
-P.
A HC
O CO
NOBLE METAL
BASE METAL
300
400
500
TEMPERATURE, °F
700
Figure 4-1. Conversion characteristics of base metal and noble metal
catalysts (General Motors Bench Test Evaluation)
(Reference 27).
-------
100
T
80
i
en
u
m
y
iZ
u.
UJ
<
U
60
40
20
100
A
O
a
N-HEPTANE OXIDATION AT 10% LELa IN AIR
AND 80,OOOSVb ON Pd/CARRIER/B-HONEYCOMB
0.5% Pd ON CARBON (8130 m2/g)
0.3% Pd ON V-ALUMINA (215 m2/g)
0.33% Pd ON V- ALUMINA (140m2/g
0.15% Pd ON A MIXTURE OF OXIDES
(Cr, Mn, NI, Co, Si)
0.05% Pd ON Co3O4 (89 m2/g)
I
200 300
CATALYST BED INLET TEMPERATURE, °C
400
lean explosive limit
'space velocity
Figure 4-2. Palladium catalyst performance (Reference 28).
-------
100
8 80
01
CL.
01
4->
C
o 60
O
to
o
o
•r~
•M
V>
40
20
1/4" Cell
Cross-Flow
-Ceramic
Honeycomb
lotal Combustion Curves
Direct Flame
Pre-Heater
100
200
300
Reactor Inlet Temp, °C
400
500
Figure 4-3. n-Heptane fume abatement effectiveness
(115,000/hr space velocity) (Reference 29).
-------
100
80
8.
u 60
u
u
u.
L.
U
s
<
40
20
200
I ' I ' I
HYDROCARBON OXIDATION ON Pd/AU03/B-HONEYCOMB
AT 10% LELa IN AIR AND 80,000 S\T
O N-HEPTANE
A PROPANE
D METHANE
• METHANE ON
Pd/NIO(109mVg)
B^HONEYCOMB
300 400 500
CATALYST BED INLET TEMPERATURE. °C
lean explosive limit
* space velocity
600
Figure 4-4 . Lightoff characteristics—palladium catalyst (Reference 28).
-------
Typical variations in light-off temperature due to space velocity are shown
in Figure 4-5 (Reference 29). This shows light-off temperature increasing with
space velocity for n-heptane combustion in a pellet bed catalyst.
4.1.2 Flashback Potential
Flashback refers to the propagation of a flame back to the fuel-air mixing
chamber, with the resulting possibility of explosion and equipment damage. Flash-
back can be avoided by
• Keeping the temperature of the surfaces enclosing the mixing chamber
below the ignition temperature
• Keeping the velocity of the mixture through the injection port higher
than the normal flame velocity for that mixture
• Operating outside the flammability limits for the mixture.
The tendency of a catalyst/fuel combination to exhibit flashback can be evaluated
by operating the catalyst at the maximum space velocity. From this point the fuel
mixture supply can be decreased until either flashback or extinction occurs. If
extinction does not occur, it is expected that flashback will occur when the flow
velocity becomes smaller than the flame propagation velocity.
4.1.3 Lean and Rich Flammability Limits
A fuel-air mixture will fail to ignite when a large excess of either fuel or
air prevents the temperature from rising to the ignition point in spite of the pre-
combustion reactions that occur. One technique for the determination of the flam-
mability limits for a particular catalyst-fuel combination in air is as follows: a
lean equivalence ratio, ^, is selected and the fuel/air throughput increased until
a rapid increase in unburned hydrocarbon emissions is noted. A second equivalence
ratio, (j>2> and two rich equivalence ratios, 3 and 4> are then tested in the same
fashion. From this data the flammability limits as a function of space velocity for
a given catalyst-fuel combination can be determined. The data would appear as shown
in Figure 4-6.
4.1.4 Maximum Specific Heat Release
The maximum specific heat release from the catalyst bed can be determined from
*
systempsystem Tuel
where HR is the heat release rate in Btu/hr-ft3atm, mfue] is the mass flow rate of
fuel in Ibm/hr, HHVfuel is the higher heating value of the fuel in Btu/lbm, v
is the combustor volume in ft3, Psystem is the inlet pressure in atm, and rjf ^
4-8
-------
c
O
100
80
60
40
20
30,000 SV
70,000
100,000
122,500
Reactor Inlet Temp, °C
Figure 4-5. n-Heptane conversion efficiency vs temperature and space velocity
granular catalyst substrate (Reference 29).
-------
-pa
—I
O
•M
tO
ro
er
Rich limit
r-
O
Lean limit
Space velocity
Figure 4-6. Example of flammability limit determination
-------
the conversion efficiency of the fuel. The maximum specific heat release will be
obtained when the fuel mass flow rate is at its maximum value, the fuel conversion
efficiency is nearly 100 percent (i.e., complete combustion), and stoichiometric
fuel/air ratios are used. Since this would normally result in bed temperatures be-
yond the thermal stability limits of the bed, the maximum bed temperature is deter-
mined by varying the equivalence ratio and dilution, and the maximum specific heat
release determined at that condition.
4.1.5 Heat Removal Mechanisms
Heat may be removed from the catalyst bed through conductive, convective, or
radiative heat transfer. Depending on the bed geometry and overall system design,
one of these mechanisms will usually be dominant. Section 5 discusses various bed
heat removal techniques in detail as related to system concepts.
4.1.6 Combustion Efficiency
The combustion efficiency is another variable necessary to evaluate system
performance. It can be calculated by the following formula
nc-l
combustibles in emissions
combustibles in inlet gas
where h enthalpy
m mass flow rate
i species index
The energy of the combustibles (fr'h.m.) in the inlet gas is computed from the fuel
flow rate measurements and the heat of combustion of the fuel. The energy of the
combustibles in the emissions can be computed by knowing the total flow rate and the
mass fractions of all combustible species (which includes CO) in the exhaust. These
species concentrations are obtained by FIR, NDIR, and gas chromatograph instrumenta-
tion.
4.1.7 Pollutant Potential
Catalyst system performance can be evaluated in terms of unburned hydrocarbons,
NO , particulates, and carbon monoxide. It must be recognized that pollutants once
formed (or already present) in the bulk flow can be reduced by factors of approximately
100 by surface interactions but not by factors of 10" or greater. This comes about
from the idealized requirement for 2.3 transfer units for each order of magnitude re-
duction of a gas phase pollutant by surface contact. For typical compact heat exchangers,
4-11
-------
operating near optimum, each transfer unit involves a length of approximately 100
hydraulic radii. Typical optimum compact heat exchangers utilize about two trans-
fer units (Reference 30). Thus, the occurrence of significant gas phase reactions
is mandatory for reduction of UHC to ppm levels.
4.2 CHARACTERISTICS AND PROPERTIES OF CATALYST MATERIALS
A review of catalyst materials which are suitable for the oxidation of hydro-
carbon and other fuels was conducted to obtain information on their characteristics
and availability. The review included
• Support types and characteristics
• Substrate wash coat materials
• Catalyst coatings
0 Temperature capability of the catalyst/support system
t Poisoning effects
• Characterization techniques
These items are discussed in detail below.
4.2.1 Support Material Types and Characteristics
The catalytic support serves three important functions in a catalyst system:
0 It increases surface area of the active metal or metal oxide by providing
a matrix that stabilizes the formation of very small particles.
•
• It increases thermal stability of these very small particles, thus pre-
venting agglomeration and sintering with consequent loss of active sur-
face.
• In certain cases, it provides catalytic activity due to special properties
of the support.
These functions have found increasing use in catalytic applications, in particular
in the petroleum and petrochemical areas. Most common support materials are A190_
£ j
and SiO?, and they are prepared as pellets in a variety of shapes and sizes. In
some cases, they are formulated in such a way that their surface has inherent cata-
lytic activity without the addition of a transition metal or metal oxide. This is
the case for a combination of Si02 and AUO, to give highly acidic surfaces active
for hydrocarbon cracking reactions via the formation of carbonium ion intermediates.
More commonly, however, they are impregnated with an active catalyst and special
techniques have been developed to obtain uniform distribution of finely dispersed
particles. These techniques are particularly important for the expensive noble
4-12
-------
metals such as platinum. Dispersions of 100 percent (all the noble metal atoms are
exposed to the surface) are often obtained, leading to complete utilization of the
expensive active component of the catalyst system.
The application of these supports in catalytic combustion presents a number
of problems that have to be considered:
• The large space velocities used in a catalytic combustion unit will re-
sult in severe pressure drops if the catalyst beds are packed with con-
ventional pellets like those used in the petroleum and petrochemical in-
dustry.
• The high reaction rates of complete combustion usually present severe
pore diffusion limitations for the effective operation of the system.
• The high temperatures and heat fluxes place special constraints on the
thermal properties of the system.
Over the last decade, a number of new materials and new preparative techniques have
been developed to overcome this problem. They are:
0 Monolithic Supports
• Fibers and Fiber Pads
• Surface Impregnated Pellets
4.2.1.1 Monolithic Supports
Monolithic supports are composed of small parallel channels of a variety of
shapes and diameters. These structures may be in the form of honeycombed ceramics
extruded in one piece, oxidized aluminum alloys in rigid cellular configurations,
or multilayered ceramic corrugations. The channel in honeycomb-like structures
have tubular diameters of 1 to 3 mm. The overall diameter of the monolithic support
may vary from 1 inch to 2 feet, and is limited, in the case of extrusion processes,
by availability and operation of the metal die. Materials of fabrication are usually
low surface area ceramics such as mullite (3A1203 • 2Si02) or cordierite (2MgO •
5Si02 • 2AO,). The refractory monolith is produced with macro-pores (ly lOy)
and may be coated with thin layers of catalytic materials, 5-20 wt% coatings being
common.
The two major advantages of monolith supports for catalytic operations are:
• High superficial or geometrical surface area
t Low pressure drops during operation
A comparison of the properties of a monolith with a bed of spherical pellets shows
these advantages dramatically. From Figure 4-7 it is clear that the pressure drop
4-13
-------
0.1
CORRECTED TO
928 cm2 AREA
X 30.5 cm LONG
I I
I III
103
10" 10s
SPACE VELOCITY (SCF/CF • HR)
Figure 4-7. Comparison o^ pressure drops for monolith and pellet bed systems (Reference 31).
e « open area fraction.
4-14
-------
is decreased by over one order of magnitude. This is achieved without loss in geo-
metric surface area, as shown in Figure 4-8. In order to achieve comparable catal-
ytic (total) surface areas, on the other hand, coating a material on the monolith is
required. The nature of this coating will be discussed later.
Manufacturers of monolith supports include American Lava Corporation, Corning
Glass Works, E. I. Dupont de Nemours & Company, General Refractories Company, and
Norton Company. A variety of materials and configurations are available, and Table
4-1 presents some of the significant characteristics of the various monolith supports.
American Lava's Thermacomb corrugated ceramics are available in two ceramic
compositions (alpha-alumina and cordierite), and in two structure types (honeycomb
and split cell). Figure 4-9 shows examples of Thermacomb corrugated products, while
Figure 4-10 shows the structural types available. The cross-flow, split cell struc-
ture shows potential for a cross-flow ceramic heat exchanger.
Corning Glass Works produces Celcor, a porous cordierite ceramic, in a honey-
comb structure with square or triangular cells. Examples of Celcor monoliths are
shown in Figure 4-11. Celcor has been used extensively as a catalyst support for
controlling automobile emissions.
Dupont produces TORVEX ceramic honeycomb in two ceramic compositions, alumina
and mullite. Three geometric configurations (straight honeycomb, slant cell honey-
comb, and cross-flow honeycomb) are available, and examples of these configurations
are shown in Figure 4-12.
Versagrid ceramic honeycomb is produced by the General Refractories Company.
Versagrid is available in four cell shapes (round, square, triangular, and rectangu-
lar) and two compositions (cordierite and mullite). The maximum operating temperature
of Versagrid is among the highest of the monolith supports listed in Table 4-1, and
samples of Versagrid honeycomb are shown in Figure 4-13.
Norton Company produces SPECTRAMIC Honeycomb products in three compositions
(silicon carbide, silicon nitride, and silicon oxynitride) and in either rectangular
or circular cell shapes. The products can be supplied with the cell axis at any
specified bias angle, and have very high maximum use temperatures. An example of
SPECTRAMIC Honeycomb is shown in Figure 4-14.
4.2.1.2 Fibers and Fiber Pads
Fibrous substrates are used primarily in low-temperature combustors for domes-
tic, agricultural, and industrial heaters (Reference 7). Recent U.S. patents, how-
ever, have proposed the use of fiber pads in high temperature combustors (References
32-24). In Reference 32, a pre-mixed combination of fuel and air is passed through a
refractory fiber of alumina and silica such as Cerafelt, produced by Johns-Manville.
4-1.5
-------
300
GEOMETRICAL SURFACE
AREA OF SQUARE CELL
MONOLITHS OF,
2.5 5.0 7.5
SPHERICAL PELLET DIAMETER, irni
10.0
Figure 4-8. Surface area for various pellet sizes.
e = open area fraction.
4-16
-------
TABLE 4-1. MONOLITH SUPPORT DATA
Manufacturer
American Lava
Corporation
Corning
Glass Works
E. I. DuPont
de Nemours
& Company
General
Refractories
Company
Norton
Company
Product
Thermacomb
AlSiMag 614
Thermacomb
AlSiMag 776
Thermacomb
AlSiMag 795
Celcor 9475(EX-20)
TORVEX
Versagrid
SPECTRAMIC
honeycomb
Description
Dense 96%
alpha-alumina
Porous 96%
alpha-alumina
Cordierite
Cordierite
Alumina
Mullite
Cordierite
Mullite
Sil icon carbide
RX387
Silicon nitride
RX384
Silicon
oxynitride
RX385
Temperature
Limit (°F)
2800
2192
2192
2200
2732
2462
2550
3000
3000
2800
2800
Specific Heat
(Btu/lb-°F)
@ 1000°F
0.21
0.21
0.19
0.27
N/A
N/A
N/A
N/A
0.15
0.15
0.22
Density
lb/ft?
N/A
N/A
16-40
94.9 - 99.9
10 - 34
20 - 35
35 - 40
45 - 50
25 - 31
25 - 37
19-25
Thermal
Conductivity
(Btu-in/ft2-°F-hr)
-------
a. 8x enlargment
b. Rolled structures
c. Rolled and stacked structures
Figure 4-9. Examples of Thermacomb corrugated ceramics, produced by
American Lava Corporation.
4-18
-------
HC HONEYCOMB
B ) SC SPLIT CELL (Note Separator)
XFSC
CROSS-FLOW,
SPLIT CELL
Note separators
and corrugations
at 90°
XXSC
CRISS-CROSS,
SPLIT CELL
Note separators
and corrugations
at 45°
XXHC
CRISS-CROSS,
HONEYCOMB
with corrugations
at 45°
Note there is no
separator.
Figure 4-10, Structural types of Thermacomb
corrugated ceramic monoliths.
4-19
-------
Figure 4-11, Examples of Celcor cordierite monoliths,
produced by Corning Glass Works.
4-20
-------
a. Straight honeycomb
b. Slant cell honeycomb c. Crossflow honeycomb
Figure 4-12. Examples of DuPont's TORVEX ceramic honeycomb.
4-21
-------
••••••••••••••••••••••••••••••••••••••••I
••••••••••••••••••••••••••••••••••••••••I
••••••••••••••••••••••••••••••••••••••••I
••••••••••••••••••••••••••••••••••••••••I
••••••••••••••••••••••••••••••••••••••••I
••••••*••••••••••«•••••••••••••••••••••»'
••••••••••••••••••••••IB
Figure 4-13. Examples of General Refractories Company's
Versagrid ceramic honeycomb.
4-22
-------
Figure 4-14. Norton Company's SPECTRAMIC honeycomb material
4-23
-------
Upon ignition, the Cerafelt supports the combustion on the surface, but has no tendency
to flash back. Porous heat-insulating fibers such as asbestos, silica, or basaltic fi-
ber are proposed for use in catalytic heaters in Reference 33, and Reference 34 describes
the use of Johns-Manville's Fibrechrome refractory felt as a burner face material.
While asbestos is suitable for low-temperature applications, high-temperature
requirements call for fibers of silica or alumina. For example, Johns-Manville's
Fibrechrome is formed from an alumina-silica-chromia composition and has a maximum
use temperature of 2700°F. This material is shown in Figure 4-15. Imperial Chemi-
cal Industries United States Incorporated markets both alumina and zirconia fiber
materials, under the trade name SAFFIL, with Figure 4-16 showing their alumina fiber.
Table 4-2 lists some important properties of these fiber materials; one advantage of
all fiber pads is their low thermal conductivity, thus preventing flashback since
the plenum side of the pad remains well below ignition temperature.
4.2.1.3 Surface Impregnated Pellets
One advantage of monolithic supports is the presence of a large geometric
surface area and the possibility of depositing the catalytic materials on this sur-
face. This increases the availability of the active catalyst to the main stream of
the combustion mixture, a property that increases performance in these fast reaction
systems. The presence of the catalyst as close to the geometric surface of the sup-
port as possible is important to minimize diffusion limitations of the reactants into
pores. This property can be achieved with highly porous pelleted catalysts as well.
It requires the application of a special technique of catalyst preparation called
surface impregnation. The pellets, or catalyst carriers, come in a variety of mate-
rial composition, including alumina and silica. Formed by a variety of methods, such
as extrusion, the catalyst carriers come in different shapes and forms. Both Norton,
Chemical Process Products Division and Houdry Division, Air Products and Chemicals
offer catalyst carriers that have a wide range of surface areas and pore size dis-
tributions. Typical shapes and forms of Norton catalyst carriers are shown in
Figure 4-17.
4.2.2 Substrate Wash Coat Materials
As mentioned earlier, the low surface area of the monolith structure requires
the application of a thin coat of oxide such as Al^O,. This wash coat, which strongly
adheres to the ceramic or refractory support, provides a uniform high surface area
while still insuring that the catalytic material which is subsequently impregnated on
the wash coat is close to the main flow of reactants. The thickness of the wash coat
is usually between 10 x 10~6 and 20 x 10"6 m (10-20 microns).
4-24
-------
! i
I
:- ,
CJ1
Figure4-15. Johns-Manvilie's Fibrechrome - a fiber pad.
-------
ro
CPi
Figure 4-16. ICI United States' SAFFIL -an alumnia fiber.
-------
TABLE 4-2. FIBER PAD DATA
Manufacturer
ICI United
States Inc.
Johns-Manville
Product
SAFFIL
(Standard
Alumina)
SAFFIL
(High Temperature
Alumina)
SAFFIL
(Standard Zirconia)
SAFFIL
(High Temperature
Zirconia)
Cerafelt
Fibrechrome
Description
Inorganic alumina
fiber
Inorganic alumina
fiber
Inorganic zirconia
fiber
Inorganic zirconia
fiber
Silica-alumina
fiber
Silica-alumina-
chromia fiber
Temperature
Limit (°F)
1850
2750
2000
2900
2300
2700
Specific Heat
(Btu/lb-°F)
1000°F
0.95
N/A
0.90
N/A
0.7a
0.75a
4=-
ro
Density 10 lb/ft:
-------
4»
oo
*Z£^
***.. .».^4.-ii-^:.»v.. if -•- '. - • ' • . — •».• S
Stars
Fluidizable
-20 mesh)
Aggregate
( + 20 mesh)
Spheres
Saddles
Figure 4-17. Examples of Norton Company's catalyst
carriers.
-------
Many different materials can be used as wash coats. ZrCL. for example, has
been used in test runs for the catalytic combustion of hydrocarbons in automotive
exhaust. Variation in the type of wash coat can have important consequences in the
stability and life of the catalyst system.
4.2.3 Catalyst Coatings
Although the field of catalysis has progressed substantially over the past
decade, its theoretical aspects are not yet at the degree of sophistication which
would enable one, a priori, to choose or design an active oxidation catalyst with a
given set of catalytic properties. However, a vast amount of data exists which per-
mits the development of correlations useful for choosing promising candidates based
on excellent catalytic activity and catalyst stability. Over the last decade there
has been a rapid development of the art, science and technology necessary to synthe-
size, test and manufacture ultrastable oxidation catalysts for the abatement of auto-
motive emissions. These catalysts operate under the most stringent conditions, and
sometimes at temperatures close to 2000°F. The expertise developed in this area will
be useful in the development of a stable catalytic combustion system.
Two broad classes of catalytic coating materials are available: metals and
oxides. These are discussed separately in the following sections.
4.2.3.1 Metals
The metals of catalytic interest, which are readily synthesized in the zero
valent state at reasonable conditions, are listed in Table 4-3. Of these metals,
the only ones which have a possibility of remaining in the metallic state in a high-
temperature, oxidizing environment are the noble metals. The others readily form
oxides, and will be discussed in Section 4.2.3.2. Of the noble metals, a large vol-
ume of data and correlations are available for Pt and Pd because of their use as
automotive oxidation catalysts. They are among the most active catalysts for the
oxidation of a number of fuels, e.g., methane (Reference 35), methanol (Reference
36) and hydrogen (Reference 37). The high activity of these metals is related to
their ability to activate H^, O^, and carbon-hydrogen and oxygen-hydrogen bonds.
Palladium and platinum are readily prepared in a highly dispersed form on a number
of support materials. Because of the high activity of these metals per unit area of
metal surface (specific activity) and the ability to attain high dispersions, only
small amounts are necessary for catalytic combustion (0.1 - 0.5 wt%). Ruthenium
metal is another possible candidate for catalytic combustion; however, under oxidi-
zing conditions it forms a volatile oxide (RuO.), which is rapidly removed from con-
ventional catalyst supports. This problem has been recently solved by researchers
interested in the NO reduction properties of Ru. One approach has been to anchor
A
Ru to a support by forming a relatively stable perovskite structure with certain
4-29
-------
TABLE 4-3. METALS OF CATALYTIC INTEREST FOR CATALYTIC COMBUSTION
GROUP
Fe Co
Ru Rh
Os Ir
VIII* GROUP IB*
Ni
Pd
Pt
Cu
Ag
Au
Enclosed metals are considered noble.
4-30
-------
oxides such as La_0- (Reference 38). Osmium is even more volatile and poisonous
than ruthenium in an oxidizing environment. Also, as with iridium and rhodium, it
is very costly, and available in limited supply. The use of the latter two metals,
if at all, would be restricted to small quantities in multimetallic systems. Silver,
while quite active at low temperatures for the activation of (L, melts at low temper-
atures and therefore sinters to a significant degree at the high temperatures of
catalytic combustion. However, it could find use as an additive in a multimetallic
catalyst. Gold is very inactive for oxidation, and would therefore only be consid-
ered as a structural or electronic modifier for multimetallic catalysts.
Based on the above considerations, those metals which show the greatest pro-
mise for use in a single-active-element catalyst system are:
• Pt
• Pd
• Ru (stabilized)
Highly active and stable catalyst systems can be produced through the use of multi-
metallic systems and the addition of structural and electronic promoters. For exam-
ple, Pd/Pt bimetallic clusters, which have been extensively studied as automotive
oxidation catalysts, combine the high catalytic activity of platinum with the rela-
tively low cost of palladium. Similarly, extensive studies with metals have shown
that the rate of catalytic oxidation of hydrocarbons parallels the catalytic activity
for CL isotope exchange:
0216 + 0218 -»• 2018016
Thus, exchange is thought to be sensitive to the electronic properties of the metal.
These properties are readily changed by alloying or forming supported multimetallic
clusters. Therefore, Groups VIII and VIII-IB combinations appear promising. Bime-
tallic combinations can have high structural and thermal stability, especially if
one of the metals is high melting.
4.2.3.2 Metal Oxides
The catalytic properties of metal oxides have been extensively studies by a
number of research groups (Reference 39). Some of the simple oxides, e.g., Co-0.,
have oxidation activity comparable to the very active noble metals like Pt and Pd.
A primary difference between these metals and the oxides'is the so-called "light-
off" temperature. This relates the ability of a catalyst to reach a significant
conversion level at low temperatures and in short periods of time. This is more of
a problem for automotive oxidation systems where a significant amount of emissions
occurs after a cold start. Therefore, it is imperative that the oxidation catalyst
4-31
-------
bed reach operation temperature as quickly as possible. This could also be a prob-
lem for catalytic combustion installations, although for some units a precombustor
might be built into the system for startup. Other alternatives include doping a
high light-off temperature catalyst with small amounts of noble metals to initiate
low temperature combustion, or using a multi-bed catalyst where the first small bed
is a noble metal catalyst.
There has been a significant amount of work with oxides in the area of cataly-
tic oxidation. The specific catalytic activity, i.e., per unit surface area, can be
varied over very wide limits. It has been found, as for the case of metals, that
the activity for hydrocarbon oxidation parallels the ability of the catalyst to cata-
lyze the homomolecular exchange of oxygen. Figure 4-18 illustrates the extensive
range of activities one can achieve for this exchange reaction. It also shows the
parallel behavior of various oxidation reactions. One will note that the oxides of
transition metals containing ions with partially filled d-orbitals have the greatest
activity. It also has been found that the rate of hetero-exchange,
0018 + O16 - -»• 018016 + O18 .
2 surf surf
over oxides which contain an equilibrium amount of oxygen in the surface layer is
equal to that for homomolecular exchange (Reference 40). The coincidence of rates
of homomolecular and hetero-exchange suggests that on oxides with an equilibrium
oxygen content, simple isotopic exchange of molecular oxygen takes place with parti-
cipation of oxidic lattice oxygen. Since this exchange parallels oxidation rate
(Figure 4-18) one can deduce that the strength of the oxygen bond in the oxide plays
a significant role in determining activity. This point is further amplified by the
data of Figure 4-19, which shows the correlation between activation energies for
methane oxidation and oxygen bond strength for a number of oxide catalysts. An anal-
ysis of these data suggests that the rate limiting step for methane oxidation invol-
ves the breaking of an oxygen-catalyst bond (Reference 40). The oxygen lattice en-
ergy in many cases can be controlled by the addition of certain dopants. Thus,
Figure 4-20 shows that one can control this parameter and therefore the rate of ex-
change and the catalyst's oxidation activity.
The above considerations have indicated that the most active simple oxides
are:
Co304, Mn02, NiO, CuO, Co^, Fe^, V^.
Other simple oxides such as Ti02 and ZnO have very low activity, and would therefore
be of interest only in the consideration of complex oxides and multicomponent systems.
4-32
-------
C7>
O
10
TiO
ZnO
Figure 4-18 , The catalytic activity of oxides of the elements
of the fourth period in the homomolecular exchange
of oxygen (1), oxidation of hydrogen (2), oxida-
tion of methane (3) and nitrogen oxide decomposi-
tion (4) at 300°C.
4-33
-------
Co304
NiO
I
Fe2°3
V2°5
I
I
10
20
30 40
q, kcal/mole
ZnO TiO,
I
50
60
Figure 4-19. Activation energies of homomolecular oxygen exchange
reaction (I), methane oxidation (II), as a function
of oxygen bond energy, for oxides of elements of the
fourth period (Reference 40).
4-34
-------
Logy
K2S04
Rb2S04
Cs2S04
Figure 4-20. Catalytic activity of vanadium pentoxide promoted with sulfates
of various alkali metals. Curve 1 - reaction of exchange of
molecular oxygen; curve 2 - reaction of oxidation of sulfur
dioxide (Reference 40)
4-35
-------
As with the metal, multi-component catalysts may provide increased activity
and stability. Materials of interest include stable spinel structures such as Co304/
CuO, Cr203/CuO and La20/Co304- These materials are likely to be very active and show
good thermal stability. Doping, using alkali, alkaline-earth metals and rare-earth
metals, may also show increased activity and thermal stabilization.
4.2.4 Temperature Capability of Catalyst/Support System
The choice of an optimum catalyst/support combination requires a consideration
of the temperature capability of a given combination. The low temperature limit is
dictated by the so-called "light-off" temperature. This limitation has been discus-
sed in Section 4.2.3.2. Solutions to this problem are not complex for most catalytic
combustion systems, and some of the possible solutions have been discussed in that
section. The major thermal limitation for catalytic combustion is the high tempera-
ture of operation. The phenomena which lead to catalyst deactivation at high temper-
atures are:
• Sintering of the catalytic species
t Changes in catalyst stoichiometry
• Sintering of the wash coat
t Thermal degradation of the ceramic support material
0 Mechanical failures
Sintering of the catalytic species will lead to a concomitant loss in surface
area and therefore a loss in catalyst activity per unit mass of catalyst. The tem-
perature at which sintering occurs is a function of the catalytic material. Thus,
Ag will sinter at much lower temperatues than Pt or Rh. In an oversimplified man-
ner this sintering or crystallite growth is a function of the melting point for
metals. Thus, Ag melts at much lower temperatures than Pt or Rh, and therefore Ag
atoms will have greater mobility at a given temperature than Pt or Rh atoms. Such
mobility is required for crystallite growth. A number of techniques have been de-
veloped to minimize or prevent sintering. For example, multimetallic systems can be
prepared which are more stable than the constituent metals. A number of structural
promoters are known. For example, A1203 is used to stabilize high surface area Fe,
which is active for NH3 synthesis, and Th02 is similarly used to stabilize Fe for
Fischer-Tropsch syntheses.
Stoichiometry changes for oxides can lead to a catalyst with dramatically dif-
ferent catalytic properties. As previously discussed, loss of lattice oxygen can
cause an increase in the energy required to activate 02 and thereby decrease combus-
tion activity. As indicated in Section 4.2.3.2, one method for overcoming this
4-36
-------
problem is to dope the lattice with a material which causes a decrease in the energy
necessary to activate oxygen and also stabilizes the stoichiometry of the lattice.
A third mechanism of thermal deactivation is wash coat sintering. At temper-
atures above 1650°F high surface area n- or Y-Al^O., undergoes a phase change to a-
A^O-j with concomitant sintering. The change may be from a surface area of 300 m2/g
to about 5 m2/g. This sintering results in pore closure and a "burying" of active
catalytic sites in the Al_0,. To minimize this problem, it is possible to work with
catalysts for which the catalytic phase has been deposited on a presintered AUO.,.
Alternatively, other materials which are thermally more resistant may be investiga-
ted as wash coats. These might include ZHL, Th02 and UOp.
At very high temperatures, the ceramic support, be it spheres or monolithic
honeycomb structures, begins to degrade. Typical substrate fail temperatures have
been given in Tables 4-1 and 4-2. Although catalytic combustion units are not ex-
pected to operate continuously at the temperatures listed, the possibility of local
hot spots occurring due to uneven air/fuel mixing and local catalyst bed nonuniform-
ities must be considered.
Thermal expansion and contraction may also occur at high temperatures. Both
pellet and monolithic substrates have thermal expansion coefficients different than
their mounting hardware. Considerable catalyst mechanical attrition can occur if
the catalyst becomes loose, thus causing a decrease in catalytic performance.
4.2.5 Poisoning Effects
Two types of adsorptive poisoning can be distinguished; (a) homogeneous ad-
sorption of the poisoning molecule, and (b) selective adsorption. In homogeneous
adsorption, the poison is uniformly distributed over the catalyst surface and through-
out the pores. This usually occurs when the poison is weakly adsorbed on the surface
and usually with a strength comparable to that of the reactants. An example of this
type of poisoning is the effect of small amounts of sulfur in a dehydrogenation re-
action over a Pt catalyst. In this case the sulfur will be removed in the presence
of hydrogen at reaction conditions and activity can be recovered. Selective poison-
ing occurs when the poison is so strongly adsorbed that the pore mouth in the cata-
lyst becomes almost completely poisoned before the pore interior is affected. For
this type of poisoning, one can measure the progressive poisoning across the cross-
section of the catalyst pellet, provided the concentration of poison is low in the
reactant stream. This type of poisoning is usually irreversible and leads to a
stoichiometric reaction with the catalytic phase. A typical example is the sulfur
poisoning of a nickel catalyst, where the interaction results in a compound forma-
tion of nickel sulfide.
4-37
-------
Participate poisoning is also possible and occurs when the catalyst bed acts
as a filter and removes participate material such as carbonaceous particles from the
combustion products. This coats the catalyst surface and acts as a physical barrier
to the diffusion of reactant species to the catalyst. Deposits of poisons such as
lead and inorganic materials are very harmful, as shown by previous work with auto-
motive catalysts.
In general, lead, sulfur and phosphorous are considered strong poisons for
metal catalysts because of the possibility of particulate poisoning (lead) or selec-
tive adsorption (sulfur and phosphorous). This is confirmed by studies performed in
the automotive industry. Other potential poisons are zinc, barium, halides and other
trace elements. Restricting consideration to natural gas and light distillate oils,
many of these poisons are not expected. Possibly phosphorous, sulfur and certain
halides would be the major poisons encountered.
4.2.6 Characterization Techniques
A common basis of comparison is crucial for the effective evaluation of a
series of different catalysts. Since catalytic action occurs on the surface of the
solid, surface area is the basis that has to be used. Therefore, the only meaning-
ful activity comparison for catalysts is to express the rate on a surface area basis,
e.g., moles/sec/cm2. If this is not done, a catalyst coating of normally very high
activity may appear to be less active than one which is normally of lower activity
because the former is poorly dispersed and the latter is highly dispersed. A know-
ledge of the surface characterization of the catalyst is needed to determine the
light-off characteristics of the catalyst and the area available for the diffusion
of reactant species to active catalyst sites. Ideally, only the surface area of the
active catalyst component should be included on this basis. By selective adsorption
of either H2 or CO, one can determine the amount of catalyst exposed at the surface.
The titration technique pioneered by Benson and Boudart (Reference 41) can be used to
determine the surface area of the noble metal catalysts. No such technique is avail-
able for oxides. Total surface area, e.g., by the BET technique (which includes the
support), is used for the evaluation of these catalysts.
The correlation of catalytic behavior with the physical properties of a cata-
lyst is crucial in understanding the reasons for catalyst performance. Measurement
of the physical properties before and after reaction is particularly important in
assessing the thermal stability of a catalyst. Sintering of the catalyst will lead
to a loss in surface area and thus a loss in catalyst activity per unit mass of cata-
lyst. Wash coat sintering results in pore closure and the burying of active catalyst
sites, again leading to a loss in surface area and a lessening of catalyst activity.
The properties that should be determined for the catalysts tested would be:
t Total surface area by the Brunauer, Emmett, Teller method (BET)
• Selective surface area of metallic catalysts by titration, H2 or CO ad-
sorpti on
4-38
-------
t Pore volume and pore size distribution by physical adsorption or Hg
porosimetry
• Structure and particle size by x-ray crystallography
• Metal or oxide distribution within the catalyst pellets by scanning micro-
probe analysis.
In cases where catalyst agglomeration cannot be measured by selective chemi-
sorption, x-ray diffraction can be used to determine an average particle size. This
technique, however, is limited to particles greater than 40 A in size and crystal-
line in structure. In the case of oxides, x-ray crystallography is also helpful to
determine the phase of the oxide and any changes in stoichiometry that may occur due
to the high temperatures of the reaction.
4.3 EXISTING APPLICATIONS OF CATALYTIC OXIDATION CONCEPTS*
The existing applications of catalytic oxidation concepts in industry are
largely in the low-temperature area at this time. Several current research programs
are concerned with high-temperature catalytic combustion applications, and these
will be discussed in Section 4.4. In this section the use of catalytic combustion
for the following applications will be discussed:
• Nitric acid plant tail gas cleanup
• Industrial odor control
• Small catalytic heaters
• Automotive oxidation catalyst systems.
4.3.1 Nitric Acid Plant Tail Gas Cleanup
Nitric acid is produced commercially by reacting ammonia with air to produce
nitrogen oxides, which are then absorbed in water to yield nitric acid. The basic
steps in the production of nitric acid from ammonia are:
• Reaction of ammonia with air over a catalyst at high temperature to pro-
duce nitric oxide
• Oxidation of the nitric oxide by oxygen remaining in the gas stream to
produce nitrogen dioxide
0 Absorption of the nitrogen dioxide in water to produce nitric acid, with
additional nitric oxide being released which must be reoxidized.
This discussion will deal only with catalytic combustion, as defined in Section 2,
rather than with high-temperature refractory surface combustion; Reference 7 re-
viewed applications in this second category in detail.
4-39
-------
Large amounts of unabsorbed nitrogen oxides in the tail gas from the absorption
tower pose a pollution problem, which has been solved in some cases by the catalytic
processing of this tail gas over platinum-group metals to yield useful energy in the
form of steam and/or power (References 42-26). The basic reactions for the cataly-
tic treatment of nitric acid tail gas over platinum, palladium, or rhodium for me-
thane reducing fuel are:
• CH4 + 4N02 -»• 4NO + C02 + 2H20 (decolorization)
• CH4 + 02 -»• C02 + 2H20 (combustion)
• CH4 + 4NO -»• C02 + 2H20 + 2N2 (abatement)
The tail gas reactor outlet temperature is usually between 1250°F and 1380°F. Sup-
port materials for the catalyst have included nichrome wire, alumina pellets, and
alumina honeycomb materials
4.3.2 Industrial Odor Control
The elimination of organic fumes is desirable from both air pollution and
fire safety points of view. The platinum metals have been used for several years as
catalysts for the oxidation of carbon monoxide and a wide range of organic molecules
in the presence of air or oxygen. Most odors are caused by the emission of low con-
centrations of organic molecules to the air, with these organic molecules always con-
taining carbon and hydrogen and generally sulphur, nitrogen, and oxygen as well.
Since most industrial odor problems are caused by organic compound concentrations
well below the level required for spontaneous combustion in air, it is necessary to
raise the contaminated air stream temperature to a level at which combustion can oc-
cur The use of catalysts lowers the temperature needed to achieve odor removal,
and also lowers the necessary residence time at the combustion temperature. A typi-
cal catalytic incinerator using a platinized ceramic honeycomb catalyst is shown in
Figure 4-21.
Various catalyst systems presently in use for industrial odor control are dis-
cussed in References 48-54. In Reference 49, heat removal from the catalyst bed is
achieved through the use of pipe coils embedded in the catalyst layers. This tech-
nique is very effective in limiting the catalyst temperatures.
4.3.3 Low-Temperature Catalytic Heaters
Low-temperature catalytic heaters are characterized by the small portable
radiant heaters that operate at temperatures below 800°F. Operating characteristics
include heat release rates of approximately 75 Btu/in2 and lifetimes of several
thousand hours. A typical low-temperature catalytic heater is shown in Figure 4-22.
Gaseous fuel enters the metal disk through an orifice. The disk is designed to
4-40
-------
Catalytic combustion unit
Process
sir inlet
Clean air
outlet
*f
3 5
2 o "S
•SaT»
•5 2-2.
inised
Figure 4-21. Flow diagram of a typical catalytic incinerator
using a honeycomb catalyst (Reference 11).
4-41
-------
Metal dish
Orifice
Catalytic pad
Protective screen
Figure 4-22. Schematic diagram - low temperature catalytic heater.
4-42
-------
evenly distribute the gas to all parts of the catalytic pad, and combustion takes
place on the surface of the fibers of the pad. A metal screen protects the front
face of the pad. A variety of applications for low temperature catalytic heaters
is given in Reference 55.
The Control Systems Laboratory of the EPA has conducted an extensive emissions
testing program on a number of catalytic heaters, as reported in Reference 56. No
correlation between emissions and specific heat release rates was found, and CO and
UHC levels were generally quite high.
4.3.4 Automotive Exhaust Catalysts
Since platinum metal catalysts were selected for emission control on conven-
tional automotive internal combustion engines for the 1975 model year, a great deal
of development work went into these emission control systems. In general, NO emis-
sions are controlled by a reduction mechanism, and CO and UHC emissions are removed
by catalytic oxidation with secondary air added to the exhaust stream to ensure com-
plete oxidation.
A reactor for catalytic exhaust emission control has three essential design
features:
• A ceramic support on which the catalyst is deposited in a manner that
prevents attrition
• Rapid warm-up of the catalyst unit, and hence rapid light-off
• Nearly complete conversion efficiency.
The essential features of a satisfactory CO/UHC oxidation catalyst for auto-
motive emission control are (Reference 57):
• A light-off temperature in the region of 250°C
• Conversion efficiencies in excess of 90 percent for both CO and UHC at
space velocities up to 150,000/hr
• High temperature stability of the support and platinic crystallite system
at temperatures to 950°C
• Poison resistance to compounds containing lead, phosphorous, and sulfur.
Platinum-palladium catalysts have been extensively tested in full-scale vehi-
cle tests (Reference 58). Two different locations were tested: at the exhaust mani-
fold outlet flange (up-front), and at the exhaust system "Y", where the exhaust
streams merge. Figure 4-23 shows the effect of catalyst composition on CO and UHC
emissions. As seen here, the differences between Pt and Pd catalyst performances
were quite small.
4-43
-------
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Figure 4-23. Effect of catalyst composition on 1975 FTP emis-
sions (Reference 58).
4-44
-------
Reference 59 discusses possible substitute catalysts for platinum in automo-
bile emission control. In this study it was concluded that base metal catalysts
generally are not as effective as platinum/palladium catalysts for automobile emis-
sion control, especially for hydrocarbon and carbon monoxide oxidation. For NO
/\
reduction, certain base metal catalysts initially are more active and selective
than are noble metal catalysts; however, most suffer from rapid deactivation.
4.4 CURRENT RESEARCH PROGRAMS IN CATALYTIC COMBUSTION
Since catalytic combustors have excellent potential for low NO emissions, a
A
number of research programs investigating their use in automotive, gas turbine, do-
mestic appliance, and home furnace applications are currently going on. Much of
this work is being conducted under proprietary secrecy agreements, making it impos-
sible to gather information on the catalyst material and method of preparation.
This section describes on-going research programs in catalytic combustion.
It cannot provide an all-inclusive compilation of catalytic combustion research,
due to the proprietary nature of the subject.
4.4.1 Air Force Aero Propulsion Laboratory
The AFAPL has conducted an in-house program to study the feasibility of using
solid catalytic beds in the reaction zone of aircraft gas turbine combustors, and
reported this work in Reference 60. The catalytic unit used in this program was
supplied by Engelhard Industries at no charge under a secrecy agreement as to the
nature of the combustor. The bed was of the monolith type, with pressure drops of
approximately 1 percent at 40 fps inlet velocity and 4 percent at 80 fps inlet ve-
locity. No igniter was needed as preheated air at 800°F was used to get the bed
to operating temperature.
All tests were run at low equivalence ratios (fuel-lean operation) on JP-4
fuel. Flashback and pre-ignition were observed during the tests, causing the Air
Force to do considerable work in developing an acceptable fuels introduction system.
At all operating conditions tested, NO concentration was below 2 ppm. Vir-
A
tually 100 percent combustion efficiency was obtained at combustor inlet temperatures
above 700°F and fuel-air ratios above 0.02, and specific heat release rates of 3.5 x
106 Btu/atm-hr-ft3 were achieved. A diagram of the AFAPL catalytic combustor system
assembly is shown in Figure 4-24, with CO and hydrocarbon emission data shown in
Figure 4-25, and combustion efficiency in Figure 4-26. Figure 4-25 indicates that
emissions were sharply reduced when the fuel-air ratio was above 0.0212. These data
were then translated into the combustion efficiency curve of Figure 4-26, where com-
bustion efficiencies of nearly 100 percent are noted for fuel-air ratios above 0.0195.
4-45
-------
-p»
en
DMT
sown* ourr/f DUCT
W7AUT77C UHlT OUTOJ DUCT
Figure 4-24. AFAPL's catalytic combustor system assembly.
-------
CALCULATED EXHAUST TEMPERATURE (°F)
1800
2000
2200
Ul
en
en
x
UJ
o
I—•
to
o
cz
o
o
1000
600
400
200
100
60
40
20
10
6
i
4
1.0
.6
.4
.2
COMBUSTOR INLET
TEMPERATURE
COMBUSTOR PRESSURE - 7 atm
INLET VELOCITY - 44 Ft/Se<
= 710°F
.015
.0175 .02 .0225
FUEL-AIR RATIO
.025
Figure 4-25. CO and C H emission index variation with fuel air
ratio (Reference 60).
4-47
-------
TOO
90
CJ
£ 80
u.
UJ
CO
CO
i
70 J
60
1800
CALCULATED EXHAUST TEMPERATURE (°F)
2000 2200
2400
INLET TEMPERATURE = 710°F
PRESSURE = 7 atm
REFERENCE VELOCITY = 44 Ft/Sec
.015
,020
.025
.030
FUEL-AIR RATIO
Figure 4-26. Combustion efficiency variation with fuel-air ratio (Reference 60)
-------
The combustor tested in this program was designed for high-power application,
and the AFAPL is presently involved in selecting a contractor to begin work on a low-
power catalytic combustor. Work on the low-power phase should begin by June 1, 1976.
4.4.2 Bratko Corporation
Rudolph Bratko, owner of the Bratko Corporation, is engaged in industrial pro-
cess heating work, and is also active in the use of fiber pads as combustors in
radiant-furnace applications. Mr. Bratko holds patents for the application of Johns-
Manville fiber pads to surface or catalytic combustion applications (References 32,
34), and is presently working on a home furnace concept in which the fiber pad is
built in the shape of a top hat. Using natural gas or propane as the fuel, Bratko
passes a premixed air-fuel stream through the fiber pad and ignites the mixture on
the pad surface. The extremely low thermal conductivity of the pad prevents flash-
back, and Bratko claims 100,000 Btu/ft2 heat release, with combustor surface temper-
atures of approximately 1700°F. The top hat combustor has been placed in a conven-
tional home furnace by Bratko, with excellent results.
4.4.3 Detroit Diesel Allison Division, General Motors Corporation
Detroit Diesel Allison has conducted a test program in which three different
catalysts, consisting of Pt-catalyst coated ceramic monoliths having different cata-
lyst surface concentrations, were used to investigate the combustion of propane-air
mixtures at inlet temperatures of 700°K as a function of fuel-air ratio. No details
are available on the composition of the catalysts. These tests, reported in Refer-
ence '61, are intended as screening tests for gas turbine applications. A typical set
of data for one of the catalysts is shown in Table 4-4, and shows that at a fuel-air
ratio of 0.0152, excellent NO , HC, and CO emission levels are attained.
/\
4.4.4 Engelhard Industries
Engelhard has done a great deal of work on gas turbine catalytic combustors,
both in-house and in liaison arrangements with other investigators. Because of
Engelhard's proprietary concerns, however, they are able to make very little of
their information public. Their efforts in catalytic combustion include the
following areas:
• Catalyst screening
t Catalyst evaluation/performance studies (fuel-air ratio, inlet tempera-
ture, etc.)
• Liaison area-working with others (AFAPL, NASA-Lewis, industries)
• Interfacing of catalyst with product.
4-49
-------
TABLE 4-4. COMBUSTION PARAMETERS FOR CATALYST C, DETROIT DIESEL ALLISON TESTS,
7.6 CM LENGTH x 8.9 CM DIAMETER9
en
o
Run
No.
B.C.
1
2
3
4
5
6
Air
(kg/hr)
41.8
41.8
41.8
41.8
41.8
41.8
41.8
(Mass/Mass)
C3H8/A1r
0
0.00586
0.00895
0.0106
0.0121
0.0143
0.0152
°K
Inlet
708
711
711
714
714
719
719
Outlet
653
686
739
789
869
1000
1144
% C02
0.08
0.30
0.70
1.17
1.77
2.83
4.95
9/kg C3H8
NOX
--
0
0
0
0.013
0.022
0.042
HC
--
712
542
465
376
244
0
- CO
—
0.164
1.08
1.91
54.2
82.3
0.222
«%
0
26.3761
41.6383
53.8397
65.2915
78.9164
99.9998
B.G. denotes background readings obtained prior to run.
-------
From data generated internally on small test rigs, Engelhard's present operating
range for the catalyst bed is:
• Inlet temperature: 400°F 1000°F
• Operating temperature: 2000°F 2600°F
0 Pressure: 1-10 atm
0 Heat release rate: 100,000 20,000,000 Btu/hr-ft3atm
0 Fuel —Gaseous, lead-free distillate (almost all fuels have been tested)
0 Combustion efficiency: 99.99 percent
0 NO emissions: 1 ppm.
Engelhard has done some studies on catalyst life, and found good performance
after 1000 hours of operation for some combinations. They have also tested both pel-
let bed and honeycomb monoliths, but prefer the honeycomb because of its low pres-
sure drop.
Engelhard is now actively engaged in conducting full-scale tests of catalytic
combustors for gas turbine application. Some of their test results to date include:
0 Size: 5- to 7-inch diameter, 0.5- to 2-foot length
0 Fuels: Gasoline, JP-4, diesel, propane
0 Operating range: Catalyst inlet temperature 600°F 1000°F
Catalyst exit temperature: 2000°F 2800°F
Pressure: 3-10 atm
0 Emissions: HC = 0.01 g/kg fuel
CO = 0.1 g/kg fuel
NOV 0.1 g/kg fuel.
A
The goal now is to interface the catalyst with the engine and develop a burner that
is not simply a laboratory device. Their in-house work is actively pursuing this
goal.
4.4.5 Institute of Gas Technology
IGT has been involved in the development of catalytic combustors since the
early 1950's. Their main investigations have involved the use of methane and pro-
pane for fuels in catalytic combustion devices. Currently, IGT has three programs
going on in the catalytic combustion area:
0 Subcontractor to Engelhard on an EPA contract on cracked ammonia
0 Contractor on a Southern California Gas Company contract for vent!ess
home appliances
0 Contractor on a joint EPA-SCG range-top burner development for hydrogen
catalytic combustion
4-51
-------
• Contractor on methane and propane catalytic combustion units for various
commercial sponsors.
Since there are different temperature requirements for various appliances, IGT
feels that more than one burner design will be necessary for the variety of home ap-
pliances. They have investigated the complete combustion and emissions aspects of
ventless home appliances, using reformed natural gas as the fuel. The gas produced
by steam reforming of methane is approximately 80 percent hydrogen, 20 percent carbon
dioxide, and a trace of carbon monoxide. Using this fuel, a variety of appliances
have been developed (Reference 62). These burners use a noble metal catalyst placed
on a permeable support plate, and are self-igniting at room temperature (Reference
63). Emissions data have been reported for these ventless appliances (Reference 64),
and show very small amounts of NO and CO (typical values are 1.1 x 10~" lb/106 Btu
for NOV, 4 x 10~2 lb/106 Btu for CO).
A
In summary, IGT's work on ventless home appliances shows the following advan-
tages and disadvantages:
t Advantages
Produce minimal quantities of pollutants
- Ventless appliances reduce building construction costs
Can humidify homes concurrently with heating
High efficiency from catalytic combustion
Lower operating temperatures reduce fire hazard
Self-igniting catalytic appliances eliminate pilots or ignition systems
t Disadvantages
Hydrogen not currently available as fuel
Catalyst life may be limited
Odorant required for safety which must not poison catalyst
Safety hazard from extreme combustibility of hydrogen
Excessive humidification of homes may result
4.4.6 Jet Propulsion Laboratory
JPL has been conducting tests over the past 18 months on a compact onboard
hydrogen generator for use with a hydrogen-enriched gasoline internal combustion en-
gine. This modified fuel system, called partial hydrogen injection, substantially
lowers NOX emissions and also increases engine efficiency considerably. Details of
the system are discussed in References 65 and 66.
4-52
-------
The hydrogen generator uses gasoline and air in a partial oxidation reactor
to produce a gaseous product consisting of hydrogen, carbon monoxide, minor amounts
of methane, carbon dioxide and water, and nitrogen. It was found that a nickel
catalyst speeds up the partial oxidation reaction, and commercially available nickel
catalysts known as steam reforming catalysts were used. A sketch of JPL's catalytic
reactor is shown in Figure 4-27, and an exploded view of the reactor is seen in Fig-
ure 4-28. Alumina pellets have usually been used as the support, but monolith struc-
tures are also being tested.
Typical catalytic generator operating conditions and output are given in
Table 4-5. Air preheat of 450°F is utilized to prevent any condensation of the
vaporized gasoline. The air-fuel ratio of 5.15 is the theoretical optimum operating
point, where a hydrogen/fuel mass ratio of 0.136 can be obtained under soot-free con-
ditions. Note that the hydrogen/fuel mass ratio actually obtained in this test was
0.12.
4.4.7 NASA-Lewis Research Center
The NASA-Lewis program in gas turbine catalytic combustor development began
when Engelhard provided a test unit to Lewis on a no-cost basis and under a secrecy
agreement. This unit had very low CO, UHC, and NO emissions, and encouraged Lewis
A
to continue working with Engelhard on catalytic combustor development for gas tur-
bines.
In addition to contractual work with Engelhard, NASA-Lewis is currently pur-
suing two in-house programs on catalytic combustion. Both programs are just being
initiated at this time. One program will consider the screening of a large number
of catalyst-support combinations, determining such parameters as ignition temperature,
maximum temperature, and poisons. The goal is to select several good candidate
catalyst-support combinations for further development work.
The second in-house program is concerned with the fuel-air preparation sys-
tems for introduction of the premixed fluid to the catalyst bed. Fuel distribution
and start-up properties of the catalyst system will be studied, with an effective
carburetion system as the goal.
4.4.8 Oxy-Catalyst, Incorporated
Oxy-Catalyst, long active in fume abatement by catalytic oxidation, has been
assigned a patent on a dual-catalytic bed device for the oxidation of internal com-
bustion engine exhaust gases (Reference 67). In this device, shown in Figure 4-29,
a catalytic hot resistance element of small mass and surface area is placed upstream
of a catalyst bed of large mass and surface area. The hot resistance element quickly
reaches catalytically effective temperature, and its heat plus the heat of catalytic
4-53
-------
.Air InUt
Fuel Preheat Co))
Pressure tap
Friitur* Tap
-P»
i
en
•Ph
C**aust*.
:. i • II'III:: ii .;•.; / / / /'-: -Jt! :..'..''/.'/.._;. //
(Us SanpHng Tap
Catalyst Bed
Air Preheat &
Catalyst Bed-
Cooling Channel
Needle Valve
Fuel Line
Figure 4-27. JPL Small Scale Catalytic Combustor System.
-------
in
un
Figure 4-28. Exploded view of catalytic compact reactor containing cold-start burner, air
pre-heat heat exchanger, and catalyst bed containing 1.5 pounds of catalyst
pellets.
-------
TABLE 4-5. TYPICAL JPL CATALYTIC GENERATOR OPERATING CONDITIONS
Input Condition
Airflow rate, Ib/h
Fuel flow, Ib/h
A/F
Equivalence ratio
Generator pressure, psig
Catalyst temperature, °F
Mole
Output Condition Fraction
H2 0.2160
CO 0.2360
CH4 0.0103
C2H4 0.0009
C0£ 0.0123
H20 0.0120
N2 0.5125
1.0000
Mean molecular weight
H2/ hydrocarbon mass ratio
H/C atomic ratio
Exit pressure, psig
Exit temperature, °F
Generator efficiency
Value
45.6
8.9
5.15
2.83
1.4
1774
Mass Mass
Fraction Output, Ib/h
0.0194 1.06
0.296 16.19
0.0074 0.404
0.0011 0.062
0.024 1.326
0.0097 0.529
0.6420 35.15
1.000 54.72
22.33
0.12
1.925
1.0
1527.0
0.785
4-56
-------
•f*
U1
Catalytic
Hot
Resistance
Element
Large
Catalytic
Bed
Figure 4-29. Oxy-catalyst's dual-catalytic bed oxidation apparatus (Reference 67)
-------
oxidation serve to accelerate the heating of the second, large catalyst bed. The
device thus serves as an aid in overcoming the problems of cold starting, wherein
the catalytic bed is ineffective until considerable time has passed.
4.4.9 Tokyo Gas Company. LTD
In order to reduce NO emissions, the Tokyo Gas Company has developed a
A
technique for two-stage combustion wherein partial combustion at high fuel-air ratios
is carried out in the first stage, secondary air is added, and the combustion is com-
pleted in the second stage. Nitrogen compounds such as HCN, NH3 and NO are formed in
the first stage and are converted to NO in the second stage. These nitrogen com-
A
pounds can be reduced by carrying out the primary combustion with the aid of a cata-
lytic bed. Reference 68 discusses the work done in detail; a schematic diagram of
the experimental facility is shown in Figure 4-30.
The amount of nitrogen compounds NO, HCN, and NH, formed in the fuel-rich
conditions of the first stage is closely related to the type of primary combustion.
Figure 4-31 shows the variation in nitrogen compounds as a function of primary com-
bustion chamber equivalence ratio. The use of catalysts to promote the partial com-
bustion and thus suppress the formation of these nitrogen compounds is shown in Fig-
ure 4-32. As the nitrogen compounds decrease in the primary combustion, NO in the
J\
exhaust gas is also reduced.
4.5 CONCLUSIONS
Based upon the review of the catalytic combustion process, the available
catalyst materials and their properties, the existing applications of catalytic
combustion, and the current research programs in catalytic combustion, the following
conclusions have been made:
• The overall success of a catalytic combustion system in reducing CO and
UHC to low levels is a function of both heterogeneous and gas-phase re-
actions; surface reactions alone cannot achieve the desired low values.
• New high-temperature catalyst support materials that are capable of main-
taining their structural and thermal integrity at temperatures up to
3000°F are necessary for high system efficiency unless methods for cooling
the catalyst bed are used. These materials come in pellet, monolith, and
fiber pad geometries. However, the catalyst coating is limited to much
lower temperatures (i.e., 1800°F) than the support.
• The most promising catalyst materials are the noble metals, such as plat-
num and palladium, because of their high activity and relatively low ac-
tivation temperature.
4-58
-------
Primary combusion chamber
en
vo
Cooling water Sampling
outlet probe
Cooling water inlet
Secondary combustion chamber
Figure 4-30. Schematic diagram —Tokyo Gas Company's two-stage combustion method for NO reduction (Reference 68),
-------
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c
3
o
Q.
o
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-------
40
30
o.
a.
•o
c
o
a.
o
o
C71
o
20
10
NO in the exhaust gas
HCN at the exit of the primary
combustion chamber
NO
Nothing
Catalyst
Figure 4-32. Effect of various catalysts on the formation of nitrogen compounds
(Reference 68).
4-61
-------
Metal oxides have activities which approach those of the noble metals,
but have significantly higher light-off temperatures, probably limiting
their use to spinel structures.
The principal catalyst poisons for natural gas and light distillate oils
will probably be phosphorous, sulfur, and certain halides. Their effect
on a variety of catalysts is not known.
The existing applications of catalytic oxidation concepts in industry,
such as in nitric acid plant tail gas cleanup, industrial odor control,
small catalytic heaters, and automotive oxidation catalyst systems, are
generally in the low-temperature range of applicability. The applicabil-
ity of this technology to high-temperature catalytic combustion is there-
fore quite limited, since the problems of catalyst sintering and thermal
degradation of the support are avoided at low temperatures (i.e., <1400°F).
Research is presently being conducted in the area of high-temperature
catalytic combustion for application to gas turbine engines. This re-
search is done with extremely fuel-lean conditions, making it difficult
to relate directly to domestic, commercial, and industrial space heaters,
where near stoichiometric conditions are desirable.
Two-stage combustion, wherein the first stage is run fuel-rich and secon-
dary air is added in a catalytic second stage to complete the combustion,
is effective in controlling emissions of NO . CO and UHC emissions can
A
be controlled at the same time by proper design, keeping the system fuel-
air ratio near stoichiometric. Staging should be examined carefully for
application to catalytic combustor technology.
Because of the necessity of avoiding local "hot spots" in the catalyst
bed, premixed fuel-air systems are needed for catalytic combustors. To
prevent blockage of the passages in a catalyst bed, liquid fuels must be
pre-vaporized. The problems associated with fuels introduction to the
catalyst bed are formidable ones that require careful attention.
At the present time, it is assumed the catalyst bed temperature must be
held below 2800°F to minimize the formation of NO . Further research
/\
work should be undertaken to determine this temperature.
The current research programs have all been conducted at catalyst bed
temperatures well below 2800°F (i.e., 2400°F), and have all demonstrated
a successful minimization of NO formation.
Because much of the research concerning catalytic oxidation is proprietary
information and therefore not available to the general research community,
an experimental program which examines catalyst-support performance and
addresses the application of these catalysts in various combustor-heat ex-
changer systems is needed. Information on the proper methodology to fol-
low in selecting a catalyst is also unavailable from catalyst manufacturers.
4-62
-------
SECTION 5
APPLICABILITY OF CATALYTIC FUELS OXIDATION
CONCEPTS TO AREA SOURCES
The usefulness of the information presented in the previous sections will be
proven through the development of a complete combustion system. This study has been
limited to assessing the applicability of the information generated to three area
sources: home heating systems, commercial boilers and industrial boilers. The fol-
lowing section includes a discussion of the options and problems associated with the
applicability of catalytic combustion to these areas. The ultimate test of the con-
cept through actual hardware development must await a further study.
This section attempts to discuss the factors which must be considered when
assessing the applicability of catalytic combustion to this equipment. Following
this, some conceptual designs are presented and the advantages and disadvantages
discussed.
This section begins with a discussion on the potential matrix of possibilities
that confronts the designer.
5.1 POTENTIAL DESIGN MATRIX
The potential design matrix may be considered by reference to the "design
tree" illustrated in Figure 5-1. Six levels of design choices, consisting of New/
Retrofit, Applications, Catalyst Support Arrangement, Cooling, Staging, and Flue Gas
Recirculation (FGR), are shown on the tree. The complete tree, of course, is not
shown. Whenever there is a branch ending with "same" and an arrow pointing to the
next level, this indicates that the identical set of branches is below each of those
boxes. Even this extensive tree does not represent the full choice of options avail-
able to the designer, since within the catalyst support structure category there are
different monolith styles (materials, open area, shape, wall thickness), packed beds
(shape, size, material), or fiber pads that could be considered. The objective is
to prune this tree; to either eliminate whole application areas (if only because
another area appears more promising) or to narrow the choices for a given area. It
5-1
-------
CXjn.icA.Te
01
IM
[ COAMBRCIAI- UNITS
[ml (Vfruit cetA»oTT. An |
Figure 5-1. Potential design matrix.
-------
may be necessary to make some arbitrary choices when there is no rational reason
for one option over another, but clearly these options must be reduced in some logi-
cal manner to limit the choices to a practical number. A brief review and discus-
sion of each of these areas is given below.
5.1.1 New Versus Retrofit
A new design requires a totally different design approach than a retrofit de-
sign. In a new design one can arrange the heat transfer area as required to take
advantage of the unique characteristics of catalytic combustion particularly where
radiation is required. The design will also not necessarily be restricted to design
for minimum pressure drop. It also may be easier in a new design to reduce the over-
all volume and thus cost using catalytic combustion. Finally, in a new design there
are many more options available to the designer. This is good in the sense that he
is not as restricted but unfortunately it makes it more difficult to select the best
approach.
In a retrofit design there will always be certain dimensional as well as pro-
cess constraints. Pressure drop and particularly heat transfer problems have to be
overcome using existing equipment. But, perhaps most importantly, cost will be a
much more significant factor in a retrofit design.
At this point it seems possible to come up with designs for both the new and
retrofit application areas.
5.1.2, Applications
Section 3 discussed the important features of the potential application
areas in some detail, and indicated that the design requirements for each of the
three application areas vary considerably. Here the relationship of each of the ap-
plications to the other design variables as shown in Figure 5-1 is discussed.
5.1.2.1 Residential Furnaces
As can be seen in Figure 5-1 there are basically two furnace types that are
of interest: warm air furnaces and hot water boilers (either gas or oil fired).
Gas fired warm air furnaces will be discussed first, followed by oil fired warm air
furnaces, gas fired hot water and oil fired hot water boilers.
Warm air furnaces, under present design practices, are quite pressure-drop
limited on both the flue gas and process side (when the process fluid is air). There
is no inherent reason, however, other than cost of blowers and perhaps noise, why the
pressure drop should be so limited in new designs. To retrofit, however, care must
be given to these pressure levels and if higher pressure drops are required it may
5-3
-------
necessitate replacing or adding a combustion air blower or induced draft fan. In
addition, higher velocities may be required on the process side to increase heat
transfer rates. Whatever is done that might influence cost, it should be remembered
that home owners and developers operate on a lowest first cost basis rather than
total operating cost; this will significantly influence the maximum permissible sys-
tem cost. In addition, no flue gases may be allowed to leak to the process side and
the ratio of process stream/flue gas is on the order of 100 to 1. Home furnaces have
a heat release rate of 10,000 to 300,000 Btu/hr and operate at nominally atmospheric
pressure.
Also of prime concern for the home heating application is the cyclic nature
of the equipment as discussed in Section 3.2. Where thermal masses may be signifi-
cantly higher in a catalytic system it may be advisable to try to modulate the firing
rate to match the load. Either way presents problems with flame stability and off-
design heat transfer and special problems for liquid fuels, as will be discussed in
a later section. Also of importance here is the ratio of warm-up time to cycle-on
time because most any catalytic system will require a thermal combustion warm-up
period. If the thermal mass of the unit can be kept low then the period of higher
pollutant formation will be kept low.
For the gas fired warm air furnace, then, the felt pad may be a good choice
for a catalyst support material. However, both the monolith and packed bed approach
are also feasible. The monolith is a better choice from a pressure drop view
point. Gas fired units typically operate with uncontrolled secondary air. Thus,
some form of closure will be required if the fuel/air ratio is to be controlled.
Staging, cooling and flue gas recirculation will be discussed in a later section.
Most any of the design options look feasible for new designs, although with
warm air furnaces an auxiliary fluid may be required to achieve significant radia-
tion heat transfer from a bed.
The oil fired warm air furnace typically uses a relatively large refractory
or refractory felt-lined combustion chamber with a separate heat exchanger. This
volume should allow sufficient room to incorporate most any design configuration
which involves staging, internal bed cooling, various catalyst supports and an
oil vaporizer. One drawback is that little heat transfer surface or local heat sink
will be available to assist in cooling the bed. Problems associated with all oil
systems will be discussed in a section on fuels.
The oil fired hot water furnace (or cast iron boiler) also utilizes a similar
large combustion volume. One advantage in this case is that oftentimes the combustion
5-4
-------
volume is backed by a flooded water surface. This surface may be able to be utilized
as a heat sink to aid in cooling the bed.
Gas fired hot water furnaces come in a variety of designs. Some look almost
identical to the oil fired cast iron boilers except the combustion volume is fore-
shortened. Usually the same "gas logs" are used as with the warm air furnace and
the combustion volume is open for secondary air addition. Therefore, the same com-
ments apply as with the warm air furnace except that the combustion volume is con-
siderably larger which may allow greater latitude in design concepts.
5.1.2.2 Commercial Units
Commercial heating systems can be broken down into basically three categories -
warm air roof top, cast iron boilers and firetube boilers. Any of these may be gas
fired, oil fired and dual fuel fired. The gas fired warm air system utilizes a for-
ced combustion system with a Maxon type burner even though the heat release rates
are not much different than residential furnaces. Considerable excess air is still
used, however, to keep the hot flue gas temperature down. Units employ a variety of
flue gas to air heat exchange surfaces but most have higher heat transfer rates than
the home furnace. This may allow sufficient radiation cooling of the catalyst bed.
The cast iron commercial boilers are not unlike the residential units and offer con-
siderable combustion volume to work with. Dual fuel units present the problem of
trying to design a complete oil fired system with all the associated ramifications
and cost penalties as well. Firetube designs also offer considerable volume to work
with and have the added advantage of a water wall for heat transfer purposes.
With regard to a preference for any of the design parameters at this time no
one design branch seems to have an advantage over another. These systems may allow
greater pressure drop and a more sophisticated design due to greater capital cost of
this size of equipment. This may allow use of the packed bed approach with its
greater pressure drop. Since most commercial heating systems utilize water it
will easily be available as a heat transfer medium. If two stage catalytic combus-
tion is eventually shown to be one of the optimum routes to pursue there surely will
be ample volume to incorporate that approach. It may even be possible to introduce
the second stage air at the first return manifold in a multipass firetube configura-
tion and to use the smaller tubes as a catalyst holder in the second stage.
Cycling will also be a factor but will not be as severe as in the residential
application. Many manufacturers are now advertising using several small units
to achieve modulation by bringing them on line only as needed. The same approach
could be taken using catalytic combustion.
5-5
-------
5.1.2.3 Industrial Boilers
In the lower heat release range the units are predominately firetube whereas
in the larger sizes they are almost exclusively watertube, either package or field
erected. Essentially the same comments apply with the firetube boilers in the indus-
trial size range as with the commerical boilers. The only additional criteria gov-
erning the design will be that again greater capital costs will be involved and the
loads will be more uniform.
Watertube boilers are generally of the water-wall design with single or multi-
ple burners in front wall, horizontally opposed or tangentially fired configurations.
Although there certainly will be sufficient volume to accommodate most any catalytic
replacement burner design by extending into the combustion volume it may be rather
difficult to accomplish for a retrofit design. The water walls will usually provide
only a minimum opening or access for the burner into the combustion space. If the
catalytic burner cannot be accommodated into this open area it will either require
extending the burner into the firebox or to the backside. If it extends into
the firebox this will present many materials and structural problems. If it extends
to the backside some auxiliary internal cooling will be required. Again at this
point any of the catalyst support materials are candidates as well as any of the
other NO control schemes. Flue gas recirculation may be a strong candidate due to
A
the simplicity, especially for the retrofit application. Testing will be required
to determine the performance of catalytic combustion with FGR. New designs for in-
dustrial boilers will probably arrange to facilitate radiation heat transfer from
the bed. To do this in the very large heat release rates of large industrial boilers
may require a very different design approach. For example, the burner may become a
large radiative slab in the center of the boiler. Water walls could be incorporated
into the structure of this burner to help support it and perhaps provide some inter-
nal bed cooling as well.
A very large packed bed with internal cooling may be an alternate approach
for the industrial boiler. The bed itself would provide the initial heating of the
water-steam circuit. The bed would be followed by conventional convective sections.
Perhaps the chief problem with this approach is accessibility for maintenance to the
water or steam tubes buried within the bed. The dual fuel capability must also be
built into this equipment.
5.1.3 Catalysts
Section 4.2 indicates many possible candidate catalysts. Taking the above
applications into account as well as start-up problems, catalyst support, cooling,
staging, and fuel, different catalysts may be appropriate for different applications.
From an applications viewpoint, cost will also be a significant factor.
5-6
-------
5.1.4 Catalyst Support Arrangement
The choice of the catalyst support arrangement will be a strong function of
the proposed design. Different supports can be formed into a variety of shapes to
give different pressure drop characteristics and activity area per unit volume.
Table 5-1 lists some of the characteristics of the various support arrangements from
an application point of view, along with the respective advantages and disadvantages.
As we shall see later in this section, a significant feature of the monolith (honey-
comb) structure is the ability for this material to be fabricated into a crossflow
heat exchanger (either metal or ceramic). From an applications standpoint, at this
time we feel the monolith, pellet bed, and felt pad to be the primary catalyst sup-
port materials. A wire mesh is limited by temperature but is suitable for lower tem-
perature application. The fluidized bed will probably suffer from attrition of the
catalyst surface although this problem should be further explored. Combinations of
various support arrangements may also be feasible. For example, monolith slabs may
be used to containerize a packed bed.
5.1.5 Low NO Techniques
A
There are a great variety of potential arrangements involving catalytic com-
bustion which could be used to aid in lowering N0x emissions, while maintaining load
and keeping CO and UHC emissions low. These possibilities include:
• Catalytic combustion with cooling
• Staged combustion
• Flue gas recirculation
• Catalytic combustion with variable catalyst loading to control heat
release
0 Combinations of any or all of the above.
Table 5-2 delineates the unique features of each of these schemes, together
with the advantages and disadvantages. Table 5-2 also shows the various combinations
within each NO reduction scheme. For example, nine different techniques of cooling
the different types of beds are illustrated. An attempt has been made to rank these
schemes from an applications point of view. Further analysis and testing will be re-
quired to verify this ranking. Some addition general comments appropriate to these
various low NO techniques are in order.
A
5.1.5.1 Cooling Schemes
Some form of cooling the bed will be required either through active cooling,
by staging with intercooling or by flue gas recirculation, to keep the catalytic
bed within the materials structural temperature limits and to keep the thermal N0x
levels low.
5-7
-------
TABLE 5-1. CATALYST BED TYPES FROM AN APPLICATION POINT OF VIEW
Bed Types
Description
Advantages
Disadvantages
A. Monolith
• Honeycomb ceramic
• Square or round
• Can be made into cross flow
heat exchanger
t Most any size, thickness,
and pore size
Can be formed in cross flow
heat exchanger
Not as subject to abrasion
as others
High temperature capability
(2200°F - 2800°F)
• Subject to cracking and
breakage; thermal shock
t Heat exchanger configura-
tion may be expensive to
manifold
B. Packed Bed
tn
oo
t Any size or shape
0 Particle size any size or
shape
0 Must containerize incom-
patible material
0 Coated pellets, solid cata-
lyst, sintered balls
0 Can be "filled" to any size
and shape
0 High temperature capability
0 Can imbed cooling coils in
any position or orientation
0 Easy Replacement
0 Subject to abrasion
0 Must containerize (tem-
perature considerations)
C. Coated Tubes
0 Coat the inside surfaces of
conventional firetube
boiler
0 No special "catalyst bas-
ket" required
0 Low surface area
0 Low temperature capability
D. Felt Pad of Catalyst
Fibers
0 Felt blanket material de-
rived from insulating
material
0 May be all catalytic fibers
or impregnated with a few
fibers
• Can be surface combustion
or reactor bed provided
temperature low enough
0 Simple to form in most any
size or shape
0 Cheap
0 Life unknown
0 Limited to 2600°F
0 Unsupported life questionable
-------
TABLE 5-1. CONCLUDED
Bed Types
Description
Advantages
Disadvantages
E. Wire Mesh
0 Stainless, high alloy steel
or other metal coated with
catalyst or mesh made of
catalytic material
• Can be formed into almost
any size or shape
• Temperature limited
• May be difficult to coat
surfaces with catalyst
F. Fluidized Bed
CJI
-------
TABLE 5-2. POTENTIAL LOW NOX CATALYTIC CONCEPTS
(a) Thermal Combustion/Catalytic Afterburning
Combustor Concept
Description
Advantages
Disadvantages
Air
— To load
t High temperature thermal
combustion followed by re-
duction of NOX by high tem-
perature catalysis
Fuel
• Can achieve good flame
stability by firing with
minimum of excess air
• Good cyclic operation
• Does not require prevapor-
ized fuels
• May not work
• High temperature catalysis
support materials required
in
o
(b) Thermal Combustion With Cooling Followed by Catalytic Afterburning
Combustor Concept
Description
Advantages
Disadvantages
Air
To load
• Lower temperature thermal
combustion followed by
catalytic oxidation of CO
and H/C.
Fuel
• Lower catalyst bed tempera-
tures
• Achieve low NO
» Possibly good cyclic opera-
tion
• Does not require prevapor-
ized fuels
• May have flame stability
problems if cooled too much
-------
TABLE 5-2. CONTINUED
(c) Catalytic Combustion With Cooling
Combustor Concept
Description
Advantages
Disadvantages
1. Monolith Sandwich
JL L
—
- —
• Monolith could be heat
exchanger
• Sandwich material could be
same support structure as
catalytic surface or other
• Cooling could be in tubes
- Process fluid; gas or
liquid
— Combustion air
- Flue gas
- Intermediary fluid
• Compact
• Amenable to many design
configurations
• Any cooling medium may be
utilized
• Cooling rates have to be
carefully controlled
• May not be practical to use
water cooling
• Manifolding cold side may
not be simple
• Thermal stress problems
2. Packed Bed-Cooling Coil
• Cooling coil imbedded in
bed
• Cooling fluid
— Process fluid gas or
liquid
— Combustion air
- Flue gas
- Intermediary fluid
• Cooling can be distributed
anywhere in bed
• Cooling can be crossflowi
counterflow, or parallel
flow
• Must watch temperature of
metal cooling tubes
• Cooling uniformly across the
bed could be difficult
3. Fluidized Bed-Cooling Coil
• Same as above
• Same as above
• Excellent heat transfer
characteristics
• Metal cooling coils tempera-
ture limited
t »t
4. Fluidized Bed-Moving Bed
Cold
• Fluidized catalytic bed is
continuously or on a batch
basis moved from the hot bed
to a cold bed where it ex-
changes heat
• Bed will achieve some steady
state lower temperature than
otherwise
• Can replenish catalyst
• Can clean catalyst
• Good heat transfer character-
istics
• May be solution to poison
(S)
t Probably expensive
t Carryover of residues and
other unburned hydrocarbons,
etc., to cold side
• Transfer of catalyst back to
hot bed not simple
-------
TABLE 5-2. CONTINUED
(c) (Continued)
Combustor Concept
5. Rotary Bed
hot
^
cold
in
ro
Hot
7. Heat Pipe Immersed in Bed
*
8. Radiation to Cold Surface
ICOL D
Description
• Monolith, packed bed, wire
mesh, tube bundle or other
can make up the bed
• Alternately exchanges heat
with cold fluid in transient
mode
• Hot and cold streams alter-
nately flow through two beds
by appropriately valving
• Bed may be of any type de-
scribed in Table 2-11
• Beds always operate in the
transient mode
• Multiple heat pipes immersed
in bed or between monolith
sandwich and transferring
heat to a cold stream
• Any type catalytic bed
transferring heat prin-
cipally by radiation (IR)
Advantages
• Uniform average temperature
of catalyst
• No metal cooling tubes to
worry about
• Thermal stress and high
temperature material prob-
lems minimized
May be attractive from a
construction standpoint for
same designs
Manifolding and sealing prob
lems between hot and cold
streams may be minimized
Some thermal stress problems
may be minimized
Amenable to many design
configurations
May be combined with convec-
tive cooling schemes (sand-
wich concept above #1)
Can achieve large ratios of
hot to cold side heat flux
Disadvantages
Carryover of exhaust gases
and even unburned hydrocar-
bons
Heat transfer fluid must be
combustion air
Sealing problems
May be expensive to drive
the wheel
Carryover of partial products
of combustion
Thermal cycling could cause
problems
Valving may cause pulsations
in combustion
Cold fluid must be combustion
air
• Nonuniform bed and sandwich
cooling
• Heat pipe compatible with
temperature may be excessive
(liquid Na)
t Bed design must be compatible
with heat pipe configuration;
i.e., the vapor "end" is
relatively short
• Bed must be kept relatively
thin
t If cooling fluid is air,
metal temperatures must be
carefully designed
-------
TABLE 5-2. CONTINUED
(c) (Concluded)
Combustor Concept
Description
Advantages
Disadvantages
9. Direct Injection of Water
• Introduce water in the
middle of a packed bed
• Could be "slow leak" in
combustion with cooling
t Becomes steam/methane
reformer
• Thermal shock
• Generation of steam
• Consumes water
-------
TABLE 5-2. CONTINUED
(d) Staged Combustion
in
i
Combustor Concept
1 . 1st Stage:
2nd Stage:
isr
A(f\ ^
T
FUEL
2. 1st Stage:
2nd Stage:
i"
Fuel rich/
catalytic
Remaining excess
air/conventional
combustion
, 0 «<>
— i x'
)- *-
~- l
I
Fuel rich/
catalytic
Remainder excess
air/catalytic
combustion
2nd
Fue L
3. 1st Stage:
2nd Stage:
F
/"" •> r
'| li
1
ft/£t
4. 1st Stage:
2nd Stage:
/1/Rv =
T i
1
FUEL
Fuel lean/
catalytic
Remainder fuel/
conventional
ii .n.
-1
Fuel lean/
catalytic
Remainder fuel/
catalytic
1
il i
A
— i
i
— 1
Description
• First stage could be pre-
mixed or mixed in the
chamber rapidly or slowly
t Any of the catalyst con-
figurations
• Second stage air mixed
rapidly or slowly
• Air preheat or not
• Same as above
• First stage could be pre-
mixed or mixed in the
chamber
• Any of the catalyst con-
figurations could be used
• Additional fuel in second
stage mixed rapidly or
slowly
• Air preheated or not
• Same as (3)
Advantages
• Relatively simple to design
such a concept for many of
the applications
• Controlled heat release
between stages
• Same as (1)
• Same as ( 1 )
• Same as (1)
Disadvantages
• Depending on fuel (e.g., HL)
even first stage may produce
excessive peak temperatures
• Flame stability problems
(this may be helped by cata-
lyst)
• Second stage temperatures
may become too high with-
out intercooling
• Same as (1)
• Flame stability problems
(this may be helped by
catalyst)
• Second stage temperatures
may become too high without
intercooling
• Same as (3)
-------
TABLE 5-2. CONTINUED
(d) (Concluded)
in
I
Combustor Concept
5. 1st Stage: Thermal; fuel
lean or rich
2nd Stage: Catalytic, re-
mainder fuel or
r-, Pir
r^jpr
fue.L
6. Multiple Stage/All
Catalytic/Air
Fu'tL
7. Multiple Stage/All
Catalytic/Fuel
AIR
Description
• Normal thermal combustion
operated in fuel lean or
rich to achieve low NOX
• Remaining air or fuel
added assisted by catalytic
oxidation of unburned H/C
and CO.
• Catalytic bed could be mono-
lith sandwich or packed bed
• Air injection in controlled
fashion (perhaps transpira-
tion type surface)
• Air injection could be
coolant as well
• Catalytic bed could be mono-
lith sandwich or packed bed
• Fuel injection in controlled
fashion (perhaps transpira-
tion type surface)
• Fuel injection could be
coolant as well
Advantages
• Good cyclic operation
• Possible retrofit
• Controlled rate of reaction
and hopefully temperature
• Controlled rate of reaction
and hopefully temperature
• May be good way to vaporize
oil or other liquid fuel
Disadvantages
t Possible flame stability and
light-off problem in first
stage
t Second stage temperatures
may become too high without
interceding
• Lots of manifolds and meter-
ing
• Lots of experimenting to
achieve proper configuration
• Manifolding and metering
• Design to avoid hot spots and
injection tube failure
-------
TABLE 5-2. CONTINUED
(e) Flue Gas Recirculation
01
I
Combustor Concept
1. Single Stage Catalytic
s ^
1
't
-~—
=
2. Two Stage/Catalytic
full
3. Multiple Stage Catalytic
AIR
Description
• FGR introduction into
— combustion air
— combustion chamber prior
to catalyst
- the catalyst bed
— gaseous fuel
FGR introduction into
— combustion air
— combustion chamber prior
to catalyst
- second stage air
- second stage combustion
chamber
- either catalyst bed
— gaseous fuels
• FGR introduction into
- combustion air
- gaseous fuel
— bed at any location
Advantages
• Applicable to many systems
• Easy method to lower tem-
perature
Same as (1)
• Same as (1)
Disadvantages
• May require auxiliary high
temperature blower although
natural draft feasible in
some systems
• Care must be taken to avoid
condensation of 1^0 in flue
gas
• Same as above
• Same as (1)
-------
TABLE 5-2. CONCLUDED
(f) Catalytic Combustion with Variable Catalyst Loading to Control Heat Release
Combustor Concept
Description
Advantages
Disadvantages
Variable Catalyst Loading
t Would probably require
multiple thin beds
t Simple system
• May not work; after a minimum
threshold of catalyst you
may get full activity
(g) Combinations-of A, B, C, D, E, and F
Combustor Concept
Description
Advantages
Disadvantages
For example, see C-3
A unique combination of any
of the above allowing cool-
ing of the bed, staged com-
bustion and flue gas recir-
culation may prove useful
-------
The choice of a cooling fluid is dictated by the type of catalyst support.
For example, water cooling should not be considered using a monolith heat exchanger
due to the high thermal stress that could occur. Conversely, if metal cooling tubes
are buried in a packed bed, air cooling may not be sufficient to keep the tubes cool.
It will probably be difficult to cool the felt pad arrangement except by radiation.
Retrofit designs must carefully consider if there is sufficient cooling to accommo-
date a radiation cooled catalyst bed. Very likely those heat transfer surfaces that
are air cooled will have insufficient heat transfer coefficients. Water backed units
can probably accommodate the load.
5.1.5.2 Staging
Staging is an alternate method of maintaining low thermal NO emissions. As
A
previously shown in Figure 5-1, the first stage can be either lean or rich. Some
interceding between stages will always be required to keep the peak flame tempera-
ture low in the second stage. Either stage could be catalytic or thermal. A thermal
first stage has the advantage with oil that the fuel would not require vaporization
in the first stage. However, a stable fuel rich condition might be difficult to
achieve without sooting and possibly plugging the catalyst. Thus the first stage
using oil (if the first stage is thermal) would most likely be fuel lean with a pre-
vaporized fuel oil addition in the second stage. At this time the consideration of
other fuels or two catalytic stages gives no evidence of a preferred first stage sto-
ichiometry. In fact, for gaseous fuels there is no preference for which stages should
be catalytic or thermal. In a retrofit application one might want to operate with the
existing first thermal stage and add a catalytic second stage. Some retrofit appli-
cations might not lend themselves to staging. For example, it would probably be
difficult to incorporate a staged concept into the existing gas fired home heating
furnace. However, there is more than enough room for such a concept in the cast iron
and firetube boilers. In particular, the turning point in the tube of a Scotch ma-
rine boiler is an excellent point to inject secondary air for a two-stage catalytic
system.
At this point, too, it is difficult to judge whether a staged approach with
internal cooling may offer some advantage. Some interstage cooling will certainly be
required.
The choice of a catalyst support will not be influenced greatly if staging is
used, although the packed bed may offer an advantage if the first stage is sooty.
It seems likely that the monolith would plug more easily under those conditions and
be more unlikely to cure itself.
5.1.5.3 Flue Gas Recirculation
Flue gas recirculation is another known method for NO reduction which might
be very effective in lowering the peak flame temperature in a catalytic combustion
5-18
-------
process. It would most likely be applied in a single stage system by introducing
it with the combustion air. However, it can be applied in a two-stage concept as
well. There are other locations where the flue gas might be introduced other than
the combustion air to achieve different types of mixing, depending on the final
physical configuration of the system. Combustion instabilities can be caused in
conventional combustion systems by introducing the flue gas into the combustion
air. However, with a premixed catalytic system this is not anticipated to be a pro-
blem. In fact, it may be desirable to use the combustion air blower to draw in flue
gases as well. This can be done by appropriately sizing the ducts and/or orifices.
This requires that the fan be able to take the higher exhaust gas temperatures and
that the combined temperature of the combustion air and flue gas not be below the
dew point of the mixture. Alternatively a separate fan could be employed. In the
case of oil fired units the flue gas could be introduced upstream or downstream of
the preheated air, again as along as condensation is avoided. From an applications
point of view flue gas recirculation could be applied to any of the proposed appli-
cations; either new design or retrofit. The primary problem will be economic; can
flue gas recirculation (fans, valves, ducting) be accomplished less expensively than
other options.
Initially flue gas recirculation coupled with a single stage catalytic combus-
tion system looks like one of the most promising schemes. The simple ducting coupled
with a premixed arrangement may result in one of the least expensive systems, provided
that significant benefits result. This is especially true for a retrofit applica-
tion. However, flue gas recirculation may not work as well for fuel oil applications
where fuel nitrogen could contribute to the total NO picture.
In the final analysis, the highest ranking scheme will probably be a combina-
tion of several of these schemes. For example, two-stage combustion combined with
cooling the bed may prove to be the most promising technique. Of course, it should
be kept in mind that what may be an optimum scheme for a new design may not be suit-
able for a retrofit application.
5.1.6 Fuels
The fuel to be considered can greatly influence the potential design, particu-
larly if it is a liquid fuel. Several factors which must be kept in mind are noted
below:
• Lightoff characteristics
• Flame speed
0 Flammability limits
t Adiabatic flame temperature as a function of equivalence ratio
5-19
-------
t Sooting characteristics
• Vaporization characteristics
• Sulfur content
• Nitrogen content
Most of the parameters were discussed in Section 4.2. From an applications
point of view they can influence size, shape, equivalence ratio of a stage, residence
times, degree of cooling, and startup procedures.
Problems associated with liquid fuels (No. 2 fuel oil) as applied to home
heating can be significant. Conventional designs operate in a highly cyclic fashion
to meet the load. Strieker (Reference 15) reported typical cyclic firing times on
the order of 5 to 6 minutes (see Figure 3-15 of Section 3.2). (This will vary de-
pending on the load and heater size per unit floor area.) Typical firing times in
some West Coast furnace installations indicate a much shorter firing time, on the
order of 2 to 3 minutes. Off cycles between firings can be on the order of 10 min-
utes to an hour depending on the load.
Typical catalyst warmup periods have recently been reduced to about 1 minute
in an automotive application (Reference 65). However, until the bed is hot the com-
bustor will require thermal combustion which will probably be a higher polluting
regime. Thus, it can be seen that this polluting regime may be a significant frac-
tion of the firing cycle. In addition, the cooldown cycles can be sufficiently long
to allow the bed to cool, requiring a warmup period each time the furnace is cycled.
This problem is most severe with No. 2 oil which requires either fuel atomization or
an electric prevaporizer during warmup. (It is assumed that the liquid fuel will re-
quire vaporization during normal running in catalytic combustion.) An important task
in designing an oil fired catalytic furnace will therefore be the development of a
fast response oil vaporizer. Factors which must be considered in the vaporizer de-
sign are:
• Coking and cracking of the oil
t Flow instabilities due to boiling and two-phase flow (particularly during
initial startup and shutdown)
• Turndown
• Start-up and shutdown.
The problem is to volatilize a liquid which has a range of boiling points from 325°F
to 750°F and contains some ash and residue. Several approaches are listed in Table
5-3 with their advantages and disadvantages.
5-20
-------
TABLE 5-3. OIL VAPORIZER DESIGNS
en
ro
Approach
1. Use heat of combustion
2. Clamshell electric
heater-tube with
small quartz balls
V.'S.'.'S* t.V.V. «.•> J.
• ?• .•„•••»» "v» •l_f-;
3—
3. Hot pot of Dowtherm G
with oil coil
Advantages
• Does not require auxil-
iary heat source
t Can be built into the
apparatus
• Smoothes out two phase
flow problem
0 Good heat transfer
• Can electrically main-
tain precise tempera-
ture control
• Good capacitance
• Good capacitance
• Good temperature control
Disadvantages
Must start up on alter-
nate method
Must be carefully
designed to avoid coking
Shut down/soak down
may be a problem
• High pressure drop
• May clog up with time
• Requires auxiliary
power
• Flow instabilities es-
pecially on start up may
still be there. (May
want to fill oil tube
with quartz balls)
• Requires auxiliary
power
-------
Cycling problems can be reduced if the furnace is modulated to meet the load.
Modulation will probably require a turndown ratio of at least 10 to 1 and will also
necessitate a corresponding turndown on the process side. Under the low fire condi-
tion care would have to be taken that the temperature in the catalyst bed did not
fall below a critical level. It may be that the lowest firing level to sustain this
critical level would be too high for sound energy conservation practices. That is,
even though an energy saving (as well as emissions) could be realized by using a mod-
ulated approach, the required "pilot" for a catalytic combustor could negate those
positive savings. It should also be noted that the combustion air will require pre-
heating as well to avoid any condensation of the oil vapor. Thus, at this point,
and without detailed analysis, there is no clear direction on which approach to take
when designing an oil fired catalytic system. Perhaps the best approach would be to
go with a two-stage approach, the first stage thermal followed by a catalytic second
stage to overcome these startup problems. Other possibilities include dual catalyst
systems involving noble metal startup or pilot catalysts (lower ignition temperature),
and metal oxide operating catalysts (slower deactivation rate at high temperature).
5.2 OTHER DESIGN CONSIDERATIONS
As we have seen in the previous sections a great number of parameters must
be considered when formulating a new design. There are in addition some practical
design problems which are discussed briefly below:
• Flashback — Flashback to a stable thermal combustion zone as well as
flashback in an unstable manner must be prevented for safety, for equip-
ment lifetime, and to minimize pollutant emissions. This can be accom-
plished through quenching, maintaining velocities of a premixed mixture
above the flame speed or remaining outside the flammability limits.
• Partial Plugging — This may be a serious problem. If for some reason
local combustion produces soot and plugs the catalyst pores, the reac-
tivity will fall off, the temperature will drop, thus producing a local
instability.
• Nonuniformities Across the Bed — Likewise, nonuniform cooling might pro-
duce similar results. Local conduction will offset both the above prob-
lems and help maintain a uniform bed temperature.
• Mixing of Staged Air -As in any combustion process, proper mixing is a
must to prevent bypassing of CO and UHC.
• Cooling the Bed - Methods of cooling the bed were discussed at some length
in Section 5.1.4. However, the bed must not be cooled too much or the re-
actions will not be sustained.
5-22
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t Sulfur Content of Liquid Fuels —The sulfur content is of concern for
two reasons: (1) Sf^ and S0.j emissions and (2) poisoning of the catalyst.
It may be possible to combine catalytic combustion with a sulfate removal
process such as insertion of a bed of ZnO to collect the S as ZnS.
• Pressure Drop Available — This will always be coupled to the overall cost
allowed and also possibly to noise.
• Intermediary Cooling Fluid - Required heat absorption rates for cooling
the catalyst bed by radiation may exceed the capability or pressure drop
limitations using air. Consequently, an intermediary fluid could be used
to remove the heat and then transport it to the process fluid.
• Thermal Shock — Thermal shock to refractory materials must be evaluated
and avoided if possible.
• Thermal Stresses and Low Cycle Fatigue — One of the most serious problems
in conventional furnace design is thermal fatigue of the heat exchanger.
In any heat exchanger design great care must be taken to avoid severe
thermal stresses.
t Size — Overall size is always a factor. It is conceivable that a new
catalytic combustion system would be made more compact than conventional
designs.
• Cost -Overall cost of the system will probably be the single most impor-
tant factor. Unfortunately, most customers look only at the capital cost
of the equipment as opposed to the overall operating cost.
• Maintenance — Ease of maintenance, and periods between maintenance must
be considered.
• Retrofit Compatibility - Designs for retrofit should be considered as well
as new designs.
5.3 OVERALL CONCLUSIONS
In general, it has been shown that the matrix of possible design choices for
each of the application areas is quite large. The initial survey to this point does
not indicate a clear direction to follow, except for a few isolated examples, either
for a retrofit or new design application. Flue gas recirculation with a single stage
catalytic combustor may be one of the better and least expensive variations for many
of the applications. Gas fired home furnaces present special problems for retrofit
due to limited volume, low existing heat transfer coefficient and their cyclic nature.
Any oil fired unit also presents special problems including oil vaporization, startup
and air preheating.
5-23
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Section 6 following will examine several specific design problems and present
suggested solutions for the following cases:
• Home heater - retrofit
t Home heater - new design
• Commercial boiler - retrofit
• Commercial boiler — new design
• Industrial boiler — retrofit
• Industrial boiler — new design.
5-24
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SECTION 6
COMMERCIAL APPLICATION OF CATALYTIC CONCEPTS
TO SELECTED SYSTEMS
This section presents a number of possible design concepts for several of the
application areas. For three of these concepts detailed sizing calculations have
been made. It should be emphasized that the concepts presented here are by no means
the optimum for any candidate application, but only represent a possible design.
Which of the many possible designs has the greatest potential for success will
ultimately depend on the cost of the hardware. Many possible good design options
(branches) could not be considered within the scope of this program.
Application areas where designs have been developed include
§ Residential heating — retrofit
• Residential heating — new design
• Commercial boiler — retrofit
• Commercial boiler - new design
• Industrial boiler — retrofit
• Industrial boiler — new design
Summaries of the work performed on each of these areas is presented below.
6.1 HOME HEATER RETROFIT
Due to Aerotherm's prior experience with home heater design studies, a pro-
bably disproportionate number of design possibilities come to mind. However, it is
also felt that this may be one of the most feasible applications for catalytic com-
bustion. Also, although some of the concepts offered here are biased towards a home
heater application, many of the same principles or concepts could be applied to the
other areas. They must be evaluated in light of the system limitations (cost, pres-
sure drop, etc.) of alternate applications.
There are basically four retrofit home heating applications which must be
considered. These include
• Gas fired - warm air
6-1
-------
• Gas fired — hot water
• Oil fired — warm air
• Oil fired — hot water
Although it is conceivable to design a room or floor heater using catalytic
combustion, these do not significantly contribute to the population of furnaces,
especially for new units being sold. Thus only the units listed above will be dis-
cussed in the following text.
As was shown in Section 3.2, nearly all gas fired burners, whether in a warm
air or hot water application, consist of the typical naturally aspirated "stick" or
"log" type burner. These burners are generally of the premixed type and rely on am-
ple quantities of secondary excess air to keep the "combustion chamber" cool. In
reality, there usually is not a combustion chamber as such; firing is direct to the
heat exchange surface. The units have no control over the secondary air opening.
Thus, in a retrofit application, if the overall excess air is to be controlled, the
combustion chamber or volume will require modification to seal it around the burner.
Furthermore, there will usually be little volume to work with and radiation heat
transfer and maximum metal temperature must be considered in the design. There is
generally no refractory lined or refractory fiber lined combustion chamber with gas
fired units.
Figures 6-1 to 6-3 show several potential designs. All these units replace
the conventional log burners. In the first case (Figure 6-1) heat is transferred from
a monolithic or felt pad bed by radiation only. Preliminary calculations show that
heat transfer rates are sufficient to keep the bed below 2800°F without exceeding a
maximum metal temperature of 900°F. A summary of the calculations for Figure 6-1 is
shown in Table 6-1. These calculations are based on some rather optimistic assump-
tions. For example, radiation heat transfer is calculated on the basis of a slab
radiating to two perpendicular walls. The convective heat transfer from the metal
heat exchange surface and the thermal entry length heat transfer relationships were
used in combination with free convection coefficients. This combined coefficient is
three to four times higher than the usual average heat transfer coefficient given
for warm air furnaces. Thus it may be necessary to increase the heat transfer coef-
ficient on the warm air side. This can be accomplished by increasing the local ve-
locity around the heat exchanger, inducing turbulence, or adding heat exchange area
by the use of fins. The first two options will increase pressure drop and may re-
quire a change in the air circulation fan. Testing of the concept will be required
to verify these calculations. Figures 6-2 and 6-3 show convective cooling schemes.
A summary data sheet on each design is included as Tables 6-2 and 6-3. The first
scheme utilizes a monolith structure in the form of a crossflow heat exchanger.
This ceramic heat exchanger, discussed in Section 4.2.1.1, is cooled using air
6-2
-------
Premixed
air-fuel
Catalyst bed
Figure 6-1. Home heater retrofit design #1
6-3
-------
TABLE 6-1. DATA ON DESIGN #1
Length: 15 inches
Width: 2 inches
Height: 0.5 inch
Volume: 15 in3
Surface Area per Unit Volume: 50 ft2/ft3
Height Required to be Coated with Catalyst: 0.25 inch
Heat Release in Bed: 25,000 Btu/hr
Heat Transferred by Radiation: 11,400 Btu/hr
Heat Transfer Coefficient on Air Side: 8.9 But/hr-ft2-°F
Pressure Drop through Bed: < 0.25"H20
Bed Temperature: 2200°F
Wall Temperature: 900°F
Type Bed: Celcor Honeycomb Monolith
Number of Units: 4
6-4
-------
Coolant
out
Purified
fuel air
Coolant
in
Figure 6-2. Design #2 cross flow ceramic heat exchanger.
6-5
-------
TABLE 6-2. DATA ON DESIGN #2
Length: 15.00 inches
Width: 1.0 inch
Height: 0.50 inch
Heat Released in Bed: 25,000 Btu/hr
Heat Transferred by Radiation: 4612 Btu/hr
Heat Transferred by Convection: 6788 Btu/hr
Cooling Air Temperature Rise: 621°F
Cooling Air Flow Rate: 105 scfm
Cooling Air Pressure Drop Across Bed: ~ 3.0"H2
Effectiveness of Heat Exchanger: 0.46
Number of Transfer Units (NTU): 0.825
Surface Area Per Unit Volume: 600 ft2/ft3
6-6
-------
en
Coolant Out
Cooling Tubes
Insulating Pad
1 Conventional Heat
Exchanger Surface
Cooling Air
Premixed Fuel
and Air
Figure 6-3. Home heater retrofit design
-------
TABLE 6-3. DATA ON DESIGN #3
Width: 2 inches
Length: 15 inches
Height: 1.0 inch
Heat Release Per Burner: 25,000 Btu/hr
Total Number of Burners: 4
Number of Cooling U-Tubes: 6
OD of Cooling Tubes: 1/16"
Heat Transferred from Bed by Radiation: 4612 Btu/hr
Heat Absorbed by Tubes: 6788 Btu/hr
Coolant Flow Rate Per Burner: 21.5 gal/hr
Exit Gas Temperature: 2200°F
Coolant Inlet Temperature: 70°F
Coolant Exit Temperature: 120°F
Pressure Drop through Cooling Tubes: 11.16 ft H20
6-8
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(water would cause excessive thermal shock). The cooling air is supplied using a
separate small fan and the inlet and exit manifold are at the same end of the burner.
The heat exchanger manifolding represents one of the most difficult technological
problems. Representatives of the American Lava Corporation claim they have solved
this problem, although the design is proprietary at this point and has only been
tried on an experimental basis. In addition, in its present configuration the cera-
mic material from which the exchanger is made is permeable and will allow some leak-
age depending on the pressure differential. This situation cannot be tolerated if
the leakage is to the coolant side (and perhaps even to the hot side). American
Lava is developing a nonpermeable material which will soon be available in this
cross flow heat exchanger form. In that case, this cooling air can then be fed back
to the main cooling air or routed to a separate room or basement. Radiation heat
transfer in this case was calculated using the assumption that the convective coef-
ficient from the heat exchanger was the more conventional 2.7 Btu/hr-ft2-°F. The
heat exchanger surface is an American Lava Thermocomb material with approximately
8 corrugations per inch.
The last design, shown in Figure 6-3 (followed by a data sheet in Table 6-3),
shows a pebble bed approach for the retrofit application to a gas fired furnace uti-
lizing small U-tubes of cooling water.
The heat absorbed by the cooling water is then transferred to the circulating
air just prior to entering the furnace. This arrangement requires an auxiliary pump
and finned tube heat exchanger. The water cooling circuit is arranged to come on
after the catalytic bed has reached a specified temperature. It may also be possi-
ble to run cooling coils between a sandwiched monolithic bed or just above the bed.
In the latter case the cooling water must be flowing during the initial light-off,
where thermal combustion will occur. The entire transient problem must be studied
in detail in any of these designs to insure that an unsafe condition does not occur
For example, in conventional furnaces the burner comes on for a minute prior to the
circulating air fan. Depending on the length of time required for the water system
to heat, it may be necessary that the circulating air fan come on sooner than current
practice to insure that heat is extracted from the water and boiling does not occur.
Similarly, in the pebble bed case (Figure 6-3) timing of the cooling water flow and
recirculating air flow must be carefully controlled.
The three designs just discussed cover the gas fired warm air and hot water
retrofit applications. There remain the oil fired applications.
Oil fired warm air heaters utilize a refractory or refractory felt combustion
chamber connected to a heat exchanger of varying design (unlike the gas fired units
which are all very similar in design). All the heat exchanger designs are low pres-
sure drop devices, resulting in low velocities, low heat transfer coefficients, and
thus large heat transfer areas. Generally a relatively small fraction of the heat is
6-9
-------
transferred from the combustion chamber. This fact presents a difficult design
problem for a cooled retrofit catalytic combustor. However, it may lend itself to
a multistage configuration where a larger volume may be required.
There are a number of problems that will be common to any potential design
using oil. These are:
• The oil will require prevaporization when operating in the catalytic
mode
• The combustion air must be preheated above 600°F to avoid condensation
of vaporized oil
• The oil may be vaporized using the heat of combustion or electrically
0 Sooting of a thermal combustion phase must be avoided
• Light-off and heat-up of the catalyst system will either require a thermal
combustion phase or air electrical preheating scheme
0 Thermal combustion of the vaporized fuel must be avoided prior to the
catalyst bed during the normal operating mode.
The designs previously discussed and shown in Figures 6-1 through 6-3 could be applied
to oil combustion by adding an air preheater and oil vaporizer. However, it may be
more appropriate to develop a design more suited to the combustion volume of the oil
fired furnace.
A design that initially seems ideally suited to this volume is the concept
developed by JPL and shown in Figure 4-27 of Section 4.4.6. This design would fit
into the combustion volume and solves the six common problems mentioned earlier.
The heat up period for this design has been reduced to about 1 minute, which may be
acceptable in a home heater application. It is important to note that the JPL de-
sign operates only in the fuel-rich mode at this time. One drawback is that little
heat is extracted from the bed. As with the gas fired design, in order to achieve
low NOX the maximum combustion temperature must be reduced. This can be achieved
by cooling the bed or going to a two-stage or flue gas recirculation concept. Cool-
ing the bed is easily adaptable to the JPL design. Water cooling coils can be embed-
ded in the packed bed. This heated water then exchanges heat with the incoming
house red railating air using a finned tube heat exchanger. Alternatively, a ceramic
heat exchanger (monolith) using a separate cooling air supply can be incorporated.
The principal problem is in ducting and manifolding the air. Flue gas recirculation
in conjunction with the JPL approach is also feasible.
Another potential problem with the JPL design is assuring that sooting does
not occur with the relatively cold combustion chamber walls when firing #2 fuel oil.
JPL has achieved a no-sooting condition on kerosene, and it is conceivable that the
design would work on #2 oil.
6-10
-------
It would be convenient to utilize an existing burner in a retrofit applica-
tion to provide combustion air as well as to provide the light-off and heat-up capa-
bility. Several factors discourage this approach:
• During normal catalytic running, the combustion air must be preheated;
this would necessitate diverting the flow downstream of the burner blower
a difficult task.
• Conventional burners soot or smoke during light off when the walls are
still cool.
0 The blowers are pressure drop limited.
• The burners are not built to handle preheated air.
Another approach, shown in Figure 6-4, utilizes a catalyst impregnated felt pad.
The chief design questions with this approach for a retrofit oil system are as
follows:
• Lightoff — What type of lightoff system should be used with this design?
Unless the combustion air and all structural parts are above the boiling
point of the oil it is likely that condensation of the oil will occur
and perhaps plug the pad.
In order to achieve preheating either a thermal combustion system or elec-
trical preheating of both the combustion air and oil vaporizer may be em-
ployed. Electric preheating offers the advantage of simplicity. Since
electrical power will be required in any case to operate fans, etc., it
seems to be the preferred method with this design.
• Heat Transfer
- In a cylindrical or conical arrangement, as shown in Figure 6-4,
there has to be sufficient heat transfer by radiation alone to get
the flame temperature below the acceptable limit for low NO ; espec-
ially when minimum excess air is used. Heat must be transferred to
three places: (1) to the combustion air, (2) to the room recircula-
ting air, and (3) to the oil to be vaporized. In the first case
this heat transfer does not aid in lowering the combustion tempera-
ture since the air is part of the combustion process. In the second
case current heat transfer coefficients on the heat exchanger may not
be sufficiently high to achieve low enough combustion temperatures.
Therefore, it may require some auxiliary heat transfer surface, pos-
sibly water cooled.
t Oil Vaporization -The best arrangement in this case would be to wrap
coils around the combustor in the proper temperature regime. Care must
be taken to avoid overheating.
6-11
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Combustion air
Cooling Air
Heat exchanger
Electric air preheater
Oil vaporization tube
Cooling Fluid
Catalytic Impregnated
pad
Cooling air
Combustion products
Figure 6-4. Catalytic pad oil burner.
6-12
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• Shutdown and Standby
Since the nature of a home heating system is currently a cyclic one, it
may be desirable to keep the oil vaporizer hot during standby periods.
This is accomplished through auxiliary electrical heating or burying the
tubes in a high heat capacitance material. (This requires a longer ini-
tial warm up period.)
Although this design is feasible it requires considerable modification and new hard-
ware. It may be more appropriate to consider it for a new design concept.
In summary, it appears that the most reasonable approach for an oil fired re-
trofit application is a single catalytic system using a thermal lightoff and warm
up. The oil would be vaporized during the normal running and the catalyst bed would
be actively water or air cooled.
6.2 HOME HEATER - NEW DESIGNS
The freedom of a completely new design presents fewer constraints on physical
size and heat transfer arrangement. There will still be an overall size limit (simi-
lar to current practice) but that is easily met. Two other basic criteria which
will not be as easy to meet are cost and noise, the latter because of the higher
pressure fans that may be required to achieve higher heat transfer rates. Within
these limits literally thousands of arrangements are potential candidates, as seen
in Section 5.1. Gas and oil fired warm air and hot water heating systems are con-
sidered. For oil fired units the requirements of preheated combustion air and va-
porized oil still exist. For either fuel it is necessary to take into consideration
either cyclic operation or modulation to match the variation in load. Coupled with
those aspects is the transient response of the furnace. At this point it appears
quite feasible to design a gas warm air or hot water furnace. Oil fired units pre-
sent considerably more problems, none of which are insolvable. Following are des-
criptions of several designs which warrant further study.
Home Heater Design #1
This design, pictured in Figure 6-5, involves radiant cooling of the catalyst
bed, lean catalytic first stage, addition of fuel before the second stage, and cata-
lytic combustion of the second stage. The unit is compact, involving a concentric
cylinder arrangement of the catalyst bed, fuel addition units, and outer shell. The
outer shell can either be water or air cooled, with additional fins placed in the
outer shell if it were air cooled. The catalyst bed could either be a packed bed,
a fiber mat, or possibly a monolith bed. Fuels for this application would most
likely be the gaseous fuels, but a prevaporized oil could also be used. Thermal or
electrical start up similar to the retrofit design would be required for oil to
6-13
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Flue Out
Connective Section
.Premixed Fuel Lean
1st Stage
Coolant Out
2nd Stage Catalyst Bed
1st Stage Catalyst Bed
Coolant In
Figure 6-5. Home heater design #1.
6-14
-------
vaporize the fuel and preheat the combustion air. Oil vaporizing tubes would be
placed between the cold shell and the catalytic surface. Preliminary calculations
have been made on this design to size the first and second stage catalyst beds and
the heat transfer area. Table 6-4 summarizes the important design parameters cal-
culated. Figure 6-6 shows this design to scale. This unit is air-cooled and could
utilize an existing house air recirculation fan; it could also be designed as a water-
cooled unit. Note that the overall dimensions are well within current practices,
although the room air fan, combustion blower, and fuel controls must be packaged in-
to the unit as well.
It must also be noted that sufficient heat must be extracted from the first
stage to achieve two goals:
• To insure the maximum flame temperature in the second stage does not
exceed 2200°F ->- 2500°F to achieve low N0x and be within the limits of
the catalyst
0 To lower the temperature sufficiently to prevent thermal combustion prior
to the second stage catalyst bed after introduction of the second stage
fuel.
The latter criterion can be circumvented if the velocities are greater than the
flame speed. This can certainly be achieved by appropriately sizing the passages.
The catalyst volume calculation was based on ~ 11,000 Btu/hr-ft2 of catalyst
surface area, based on experimental JPL criteria. Within this constraint, the sizes
shown in Figure 6-6 and Table 6-4 depend on radiative and convective heat transfer
calculations.
Home Heater Design #2
Figure 6-7 shows a variation of design #1. Premixed fuel and air (fuel lean
or rich) passes through a cylindrical catalytic bed which transfers heat by radia-
tion and convection to water cooled tubes connected with sintered copper balls. The
exhaust products are passed through a second stage with fuel or air addition and
finally out through additional heat exchange area. In this case the first stage is
catalytic, whereas the second stage is thermal. The heat transfer surface could be
tailored to achieve the proper temperature distribution or be designed with more sur-
face on the process side if air cooling were incorporated. No detailed calculations
were performed on this design.
Home Heater Design #3
This concept, shown in Figure 6-8, is patterned after the Bratko furnace de-
sign with some improvements. A conical fibrous catalyst surface radiates to an outer
6-15
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TABLE 6-4. DATA SUMMARY HOME HEATER DESIGN #1, 100,000 BTU/HR
1st Stage 2nd Stage
Heat Release (Btu/hr) 68,750 31,250
Stoichiometry 1.60 1.10
Gas Inlet Temperature (°F) 70 HOI
Gas Exit Temperature (°F) 2200 2591
Catalytic Surface Requirement (ft2) 6.12 2.78
Surface Area/Unit Volume (ft2/ft3) 200 200
OD (inches) 2.86 2.43
ID (inches) 2.00 2.00
L (inches) 4 4
Pressure Drop ("H20) -0.04 > 0.1
Heat Transfer Area Downstream: 12.26 ft2
Average Overall U = ~ 5 Btu/hr-ft2-°F
Exit Gas Temperature: 400°F
Use 28 Fins 1.3 inches long on either side
Cooling Air Flowrate: 1000 scfm
Pressure Drop Air Side: 0.122"H20
6-16
-------
Catalytic surface
2nd stage
Room air
Catalytic surface
1st stage
12 x 8
Room air
Fuel plus combustion
air
Additional fuel
Figure 6-6. Scaled home heater design #1.
6-17
-------
Flue Out
Coolant Out
Cooling Tubes and
Porous Fins
Thermal 2nd Stage
1st Stage
Catalyst Bed
Coolant In
Premixed 1st Stage
Fuel and Air
Premixed 2nd Stage
Fuel and Air
Figure 6-7. Home heater design #2.
6-18
-------
Flue Out
Coolant Out
Fibrous Catalytic
Mat
Convective
Heat Exchange
Section
Radiant Section
Cooling
Fluid
Premixed Fuel and Air
Figure 6-8. Home heater design #3.
6-19
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air or water cooled shell. A premixed mixture of air and fuel would be routed behind
the felt pad and ignited at the outer surface. After exchanging heat radiatively with
the outer shell the flue gases are passed through the tubes of a convective section.
The process stream is passed through in a multipass crossflow arrangement outside the
tubes. This design is single stage, operating with minimum excess air but relying on
radiation cooling to keep the catalyst surface cool. It could be designed to operate
on oil.
Home Heater Design #4
Figure 6-9 shows a concept utilizing heat pipes between sections of catalysts.
The heat is picked up by the room air stream flowing adjacent to either side of the
combustion chamber. This design could easily use oil or gaseous fuel. The first
combustion chamber would be modified to utilize a startup oil spray nozzle firing
thermally and later switched to vaporized oil. The oil vaporization tubes could also
be located between catalyst beds. The remaining heat is finally extracted through a
convective section at the right hand side of the figure.
Home Heater Design #5a, b, c
Figure 6-10 shows three variations of a common design. This unit could be
built as a single test rig and modified for the alternate approaches. The concepts
include staged combustion, first-stage thermal or catalytic, second-stage thermal or
catalytic, integrally cooled catalyst bed or radiatively cooled catalyst bed. This
concept is probably the most versatile as far as testing numerous concepts. Flue
gas recirculation could be added to any of these schemes.
6.3 COMMERCIAL BOILER - RETROFIT
As indicated in Section 3.3, the principal existing commercial boiler styles
in use are the cast iron and firetube designs. Within the firetube design, packaged
scotch and firebox are prevalent. All of these designs have relatively large initial
combustion volumes, whether gas or oil fired. The firebox designs, including some of
the cast iron boilers, employ a refractory or refractory felt-lined combustion cham-
ber. The others (packaged scotch) utilize a large water backed volume for the ini-
tial combustion chamber. The on-off cycles again are highly dependent on the indi-
vidual load and can conceivably be as short as the home heater application.
The principal difficulty is to extract sufficient heat from the bed to achieve
low N0x. All the problems associated with oil fired home heater applications also
apply in this instance. The most significant difference is that the capital cost of
these units is an order of magnitude higher than the home heating systems. This
will allow considerably more latitude in potential designs.
6-20
-------
at
ro
Catalyst Beds —i
Premixed Fuel v
and Air V,
Convective Heat
Exchange Section
Fuel Out
Out
Heat Pipes
Figure 6-9. Home heater design #4.
-------
Coolant In
Flue Out
Convective
Heat Exchanger
Catalyst Bed
Catalyst Bed
Prenrixed
Fuel & A1r
Coolant Out
2nd Stage Fuel
or Air
(0
Heat Exchanger Coolant In
Connectlve
Heat Exchanger
-j— Catalyst Bed
„ T *—Catalyst
Premixed Be()
Fuel & Air
2nd Stage Fuel or Air
(b)
Catalyst Bed Heat Exchanger
Flue Out
Convective
Heat Exchanger
•- Coolant In
Premlxed
Fuel S Air
2nd Stage
Fuel or Air
(a)
Figure 6-10, Home heater design #5.
6-22
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First consider a design with a refractory lined firebox. In this case a lar-
ger version of the home heater retrofit design shown in Figure 6-3 could equally
well be applied. In the case of internal cooling of the catalyst bed a portion of
the feed water or circulating water could be used as the coolant. If it is desir-
able to use air as the internal catalyst coolant, as with a monolith heat exchanger,
it should not be the combustion air but rather an auxiliary air supply which would
than transfer heat to the recirculating water. This does not seem to be a very logi-
cal approach and therefore a monolithic heat exchange catalyst would not be chosen
for this application.
The felt pad in a conical or cylindrical arrangement is also a possibility for
a retrofit combustor. Much commercial equipment, being oil fired, presents the prob-
lem of incorporating oil firing with the felt pad mentioned in previous sections.
6.4 COMMERCIAL BOILER - NEW DESIGN
Figure 6-11 shows a potential new design concept for a firetube boiler. The
firetubes are filled with pellets of catalyst or coated with a catalytic material.
A combustion chamber is added of any desired length for first-stage thermal combus-
tion, if required. In addition, a second-stage can be added as desired, followed by
additional cooling. FGR can be added to this design as well.
A catalytic water wall design is shown in Figure 6-12. Actually, this is very
similar to the Home Heater Design #1 in that it employs a cylindrical catalytic com-
bustor radiating to the water wall. This radiant section is followed by a convective
section. This design is a single stage and relies on the high radiant cooling.
6.5 INDUSTRIAL BOILERS - RETROFIT
The retrofit designs for the firetube commercial boilers could equally well apply
to the small industrial boiler. The problems associated with a watertube design were
briefly discussed in Section 5. Figure 6-13 shows one approach, incorporating a sin-
gle stage catalyst and flue gas recirculation. This unit would be built as a replace-
ment combustor and would be required to fit into an existing burner port. For oil
firing preheated air and an oil vaporizer are required.
6.6 INDUSTRIAL BOILERS - NEW DESIGN
As mentioned in Section 5, it may be advantageous to incorporate radiation
cooling of the catalyst bed into a new design for an industrial waterwall boiler.
This approach is shown in Figure 6-12 under new commercial boiler designs. Figure
6-14 shows slight modification of that approach. This design looks more like the
luminous wall furnace as built by Hoi den (Reference 69).
6-23
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.Conventional
Burner
Catalyst Plug
Fuel
ro
Air
Water Cooled
Shells
2nd Pass Heat
Exchanger
Optional Staging Injection Section
Figure 6-11. Commercial boiler design II Firetube boiler.
-------
Coolant Out
Coolant In
Air
Convective Section
Connective Cooling Tubes
Radiant Section
Catalytic Bed
t
Fuel
Figure 6-12. Comnercial boiler design #2 water wall configuration.
6-25
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Burner mounting flange-
A1r
Fuel
FGR
Refractory lined
burner throat
Water wall of boiler
A-IOS77
Figure 6-13. Industrial boiler replacement catalyst burner.
-------
Luminous wall
catalytic combustion
Water wal1
Premixed air/fuel mixture
Figure 6-14. Luminous wall catalytic furnace.
6-27
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6.7 CONCLUSIONS
Data which would be useful to the design for sizing the catalyst bed and cal-
culating heat release rates are almost nonexistent. Nevertheless, several possible
designs have been generated.
• Gas fired warm air and hot water retrofit designs appear to be feasible,
and although problems exist, are the easiest retrofit methods to accom-
plish.
t Oil fired warm air and hot water retrofit designs present special prob-
lems concerning oil vaporization prior to combustion, and oil preheating
without thermal combustion occurring.
• The necessity for preheated air for some catalyst-fuel combinations to
activate the catalyst bed must be taken into consideration in any final
design.
t New designs based on oil- or gas-fired warm air and hot water furnaces
offer fewer constraints than retrofit designs. Based on limited exist-
ing information, these designs appear feasible.
• Designs of both retrofit and redesign systems for commercial and indus-
trial boilers have been made. These new designs stress radiative heat
transfer, while retrofit designs stress catalyst bed cooling and flue
gas recirculation. All appear feasible.
• At the present time it is not possible to make a reasonable cost esti-
mate of catalytic combustors, due to a general lack of knowledge con-
cerning bed depth required. This information must be obtained to allow
cost analyses to be made.
6-28
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SECTION 7
RECOMMENDATIONS
Based upon extensive reviews of stationary combustion source characterizations
and existing catalytic combustion knowledge, a complete design matrix has been de-
fined, and several conceptual designs from this matrix have been completed. Because
of the proprietary nature of most of the existing data on catalytic oxidation, the
designer is severely hampered in his ability to do realistic calculations. It is
therefore recommended that a comprehensive testing program on high-temperature cata-
lytic oxidation be conducted, in order to provide the designer with firm data for use
in sizing calculations. This program should include:
• Screening tests of various catalyst-support combinations with a variety of
fuels, in order to determine activation energies and kinetic rate constants,
and to study heat release limits, catalyst life, poisoning effects, ignition
and light-off for various air/fuel ratios, preheat temperatures, and surface
temperatures.
• Development of a mathematical model for combined homogeneous/heterogeneous
combustion which will be capable of predicting the performance of a cata-
lytic bed. This model will make use of the data obtained in the screening
tests.
• Tests which demonstrate the feasibility of catalytic combustion in flue
gas recirculation, catalyst bed cooling, and two-stage combustion concepts.
Since the goal of low NO emissions is dependent on holding the bed tern-
A
perature down, the mechanisms of active bed cooling must be studied in
detail.
• Prototype design and development of catalytic furnaces using flue gas re-
circulation, catalyst bed cooling, and/or two-stage combustion. Since
little data of any value presently exists to aid the designer in sizing
a catalytic combustor, this data must be obtained experimentally before
further prototype design is attempted.
The results of such a test and analysis program would provide a base of design
information, currently lacking, sufficient to allow an accurate assessment of the
prospects for NO reduction by catalytic combustion concepts and of the commercial
A
prospects of catalytic combustion in area-source applications.
7-1
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TECHNICAL REPORT DATA
(Please read ImLnictiuns on the reverse before completing)
1. REPORT NO.
EPA-600/2-76-037
2.
3. RECIPIENT'S ACCESSION-NO.
4. TITLE ANDSUBTITLE
Catalytic Oxidation of Fuels for NOx Control from
Area Sources
5. REPORT DATE
February 1976
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
J. P.Kesselring, R. A. Brown,
R. J.Schreiber, and C. B. Moyer
8. PERFORMING ORGANIZATION REPORT NO
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Aerotherm Division, Acurex Corporation
485 Clyde Avenue
Mountain View, California 94040
10. PROGRAM ELEMENT NO.
1AB015: ROAP 21AUZ-019
11. CONTRACT/GRANT NO.
68-02-1318, Task 12
12. SPONSORING AGENCY NAME AND ADDRESS
EPA, Office of Research and Development
Industrial Environmental Research Laboratory
Research Triangle Park, NC 27711
13. TYPE OF REPORT AND PERIOD COVERED
Task Final: 10/74-4/75
14. SPONSORING AGENCY CODE
EPA-ORD
15. SUPPLEMENTARY NOTES
EPA Project Officer for this report is B.Martin, 919/549-8411, Ext 2235.
16. ABSTRACT Tne repOrt gives results of a review of the state-of-the-art of catalytic
combustion concepts, and of an assessment of the applicability of catalytic com-
bustion to gas- and oil-fired home heaters and commercial and industrial boilers.
Newly developed high-temperature support materials will greatly enhance the field
of high-temperature catalytic combustion, but current catalyst systems are limited
by the calatyst coating to much lower temperatures than the supports. To keep
combustor temperatures below those that would cause catalyst degradation, to
achieve high system efficiency, and to prevent NOx formation, combustion system
concepts such as two-stage combustion, flue gas re circulation, and bed heat
removal appear necessary. Application of these concepts to home furnaces appears
feasible, but their application to larger size units may be more attractive because
of their greater initial cost, generally more sophisticated controls, better super-
vision of equipment, and heat transfer characteristics.
7.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.lDENTIFIERS/OPEN ENDED TERMS
c. COSATI Field/Group
Air Pollution
Combustion
Nitrogen Oxides
Catalysis
Oxidation
Fuels
Hydrocarbons
Air Pollution Control
Stationary Sources
Area Sources
Staged Combustion
Flue Gas Recirculation
Bed Heat Removal
13 B
21B
07B
07D
07C
21D
Z. DISTRIBUTION STATEMENT
Unlimited
19. SECURITY CLASS (This Report)
Unclassified
21. NO. OF PAGES
194
20. SECURITY CLASS (Thispage)
Unclassified
22. PRICE
EPA Form 2220-1 (9-73)
F-l
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