EPA-650/2-74-058-Q

August 1975
    Environmental  Protection Technology Series
APPLYING  FABRIC  FILTRATION
                  TO  COAL FIRED
           INDUSTRIAL  BOILERS
             A PHOT SCALE INVESTIGATION
                   U.S    ;iiental Protection Agency
                    Office of R
                        Washington, 0. C. 20460

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                                   EPA-650/2-74-058-0
APPLYING  FABRIC  FILTRATION
           TO  COAL FIRED
       INDUSTRIAL BOILERS
         A PILOT SCALE  INVESTIGATION
                     by

 John D. McKenna, John C. Mycock, and William O. Lipscomb

          Enviro-Systems and Research, Inc.
                 P.O. Box 658
             Roanoke, Virginia 24004


              Contract No. 68-02-1093
               ROAP No. 21ADM-033
            Program Element No. 1AB012


         EPA Project Officer: James H. Turner

      Industrial Environmental Research Laboratory
        Office of Energy , Minerals, and Industry
      Research Triangle Park, North Carolina 27711


                  Prepared for

      U.S. ENVIRONMENTAL PROTECTION AGENCY
       OFFICE OF RESEARCH AND DEVELOPMENT
            WASHINGTON, D.C. 20460

                  August 1975

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                       EPA REVIEW NOTICE

This report has been reviewed by the National Environmental Research
Center - Research Triangle Park. Office of Research and Development,
EPA, and approved for publication.  Approval does not signify that the
contents necessarily reflect the views and policies of the Environmental
Protection Agency, nor does mention of trade names or commercial
products constitute endorsement or recommendation for use.
                   RESEARCH REPORTING SERIES

Research reports of the Office of Research and Development, U.S. Envii
mental Protection Agency, have been grouped into series.  These broad
categories were established to facilitate further development and applies
tion of environmental technology.  Elimination of traditional grouping w<
consciously planned to foster technology transfer and maximum interface
in related fields. These series are:

          1.  ENVIRONMENTAL HEALTH EFFECTS RESEARCH

          2.  ENVIRONMENTAL PROTECTION TECHNOLOGY

          3.  ECOLOGICAL RESEARCH

          4.  ENVIRONMENTAL MONITORING	

          5.  SOCIOECONOMIC ENVIRONMENTAL STUDIES

          6.  SCIENTIFIC AND TECHNICAL ASSESSMENT REPORTS

          9.  MISCELLANEOUS

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.
This document is available to the public for sale through the National
Technical Information Service, Springfield, Virginia 22161.

                Publicafidn No. EPA-650/2-74-058-a
                                u

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                                  CONTENTS
Abstract


List of Tables


List of Figures


Acknowledgements
                                   Page

                                      v


                                     vi


                                   vi ii


                                    xii
Sections

   I

  II

 III

  IV

   V

  VI

 VII
VIII
  IX
       Titles                      Page

Introduction                          1

Conclusions                           2

Recommendations                       3

Research Needs                        4

Glossary of Terms                     5

Background                            9

Program Description                  20

   Purpose & Scope                   20
   Kerr Industries                   21

Pilot Plant Description              22

   Design                            22
   Filter Media                      27
   Description of Kerr Boilers       27

Pilot Plant Operating Procedures     32

   Startup Procedure                 32
   Establishing A/C Ratio            32
   Normal Cleandown Mode             33
   System Monitoring                 33
   System Inspection                 33
   System Shutdown                   33
   Hopper Cleanout                   34
                                  m

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                               CONTENTS contd.


Secti ons                       Titles                     Page

   X                   Test Methods                         35

                          Velocity                          35
                          Static Pressure                   35
                          Temperature                       36
                          S02-S03                           36
                          Parti dilates                      36
                          Permeability                      39

  XI                   Data Obtained                        41

                          Inlet Conditions                  41
                          Teflon Felt, Style 2663           52
                          Gore-Tex/Notnex                    61
                          Oral on T Felt                     70
                          Nomex Felt                        78

 XII                   Economics                            97

                          Capital Costs                     97
                          Annual Operating Costs            102
                          Annualized Costs                  106

XIII                   Discussion                           121

 XIV                   References                           126

  XV                   Bibliography                         127

 XVI                   Appendix                             130
                                   IV

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                                ABSTRACT

     A pilot scale investigation was conducted to determine the techno-
economic feasibility of applying a fabric filter dust collector to coal
fired industrial  boilers.  This report extends and confirms earlier work
reported in July of 1974, EPA Publication 650/2-74-058.   The pilot
facility, installed on a slip stream of a 60,000 lb./hr.  boiler, was
sized to handle 11,000 acfm when operating at an air-to-cloth ratio of
6/1.  Filter media evaluated were Nomex^felt, Teflon^felt (2 styles),
Gore-Te@, and Dralo@-T.
     Fractional efficiency was determined using an Andersen inertial
impactor for the four filter media at three A/C levels.   The effect of
reverse air volume on outlet loading and pressure drop across the bags
was evaluated for Nomex felt.
     Nomex felt achieved the lowest outlet dust concentrations while
Teflon felt operated at the lowest pressure drop.  All media tested
achieved outlet loadings well within allowable limits.  When Nomex felt
was employed, higher collection efficiencies were achieved by discon-
tinuing the reverse air cleaning.  Varying the volume of reverse air
from 1400 to 4000 ACFM had little effect on removal efficiency.
Increasing the amount of air used for cleaning does reduce the pres-
sure drop across the bags.
     Installed costs, annual operating costs and total annualized costs
for a fabric filter and an electrostatic precipitator, capable of
handling 70,000 ACFM of flue gas from a coal fired boiler, are presented,
     A full scale demonstration program is anticipated.   The purpose of
this program is the acquisition of bag life data and evaluation of the
relationship between overall performance and on-stream time.
     This report was submitted by Enviro-Systerns & Research, Inc.,
Roanoke, Virginia, in fulfillment of Contract No. 68-02-1093 under the
joint sponsorship of Enviro-Systerns & Research, Inc., Kerr Industries
and the Environmental Protection Agency.

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                            List of Tables

Table
Number                          Title                          Page
  1           Capacity Range for Industrial  Boilers              10
  2           Industrial  and Utility Use of Fossil  Fuels         11
  3           Population  Breakdown by Fuel Capability           13
  4           Population  Breakdown by Burner Type               13
  5           Estimated Trends by Fuel Capability               14
  6           Estimated Trends by Burner Type                   15
  7           Baghouse Installations on Coal Fired  Boilers      16
  8           Filter Media Characteristics                      28
  9           Coal Analysis                                     30
 10           Particulate Concentration Data                    42
 11           Inlet Concentration by Particle Size               43
 12           Inlet Concentrations                              46
 13           Effects of Gas Volumes on Baghouse Temperatures   47
 14           Effects of Inlet Conditions on Outlet Emissions   48
 15           Permeabilities of Clean Bags                      49
 16           Filter Media Permeability                         51
 17           Outlet Concentration, Cumulative %, and
                Penetration - Teflon, 2663                      56
 18           Outlet Concentration, Cumulative %, and
                Penetration - Gore-Tex                          64
 19           Outlet Concentration, Cumulative %, and
                Penetration - Oralon T                          73
 20           Outlet Concentration, Cumulative %, and
                Penetration - Nomex                             81
                                 VI

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                              List of Tables
Table
Number                             Title                      Page
  21          Outlet Concentration, Cumulative  %,  and
                Penetration for 3 Levels of Reverse  Air,
                A/C 3.4, - Nomex                               84
  22          Outlet Concentration, Cumulative  %,  and
                Penetration for 3 Levels of Reverse  Air,
                A/C 6.4, - Nomex                               85
  23          Outlet Concentration, Cumulative  %,  and
                Penetration for 3 Levels of Reverse  Air,
                A/C 8.9, - Nomex                               86
  24          Analysis of Nomex Felt Properties                95
  25          Fabric Filter Unit Size vs. A/C. Ratio             98
  26          Bag Costs as Percent of Installed Costs          101
  27          Pressure Drop for Five Bag Materials at
                4 A/C Ratios                                  105
  28          Fabric Filter Cost Data                         115
  29          Electrostatic Precipitator Cost                 116
  30          Annualized Costs Based on Accelerated
                Depreciation                                  117
  31          Comparison of Particle Size Efficiencies
                for Various Bag Materials                     125
 A-l          Outlet Concentration, Cumulative % and
                Penetration - Teflon, 2063                    139
 A-2          Pilot Plant Flow Data                           146
 A-3          Particle Size Distribution for Andersen  Tests   154
 A-4          Fractional Loading for Andersen Tests            157
 A-5          Tabulation of Data for Statistical Analysis     186
 A-6          Analysis of Variance Table                      189
                                  VII

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                                  Figures
Figure
Number                            Title                  Page
   1          Fabric Filter Pilot Plant Installed
                at Kerr                                   23
   2          Pilot Plant Temperature Profile             24
   3          General Arrangement Drawing                 25
   4          Baghouse Pictorial Showing Gas  Flow         26
   5          Schematic Showing Slip Stream Duct
                Installation                              31
   6          Particulate Sampling Train                  37
   7          Inlet Particle Size Distribution            44
   8          Permeabilities of Clean Bags                50
   9          Positioning of Teflon Felt Bags             53
  10          Outlet Particle Size Distribution -
                Teflon Felt                               54
  11          Outlet Concentration by Particle Size -
                Teflon Felt                               57
  12          Penetration vs. Particle Diameter -
                Teflon Felt                               58
  13          Pressure Drop Across Bags vs. A/C
                Ratio - Teflon Felt                       59
  14          Typical Cleaning Cycles - Teflon Felt       60
  15          Positioning of Gore-Tex Bags                62
  16          Outlet Particle Size Distribution -
                Gore-Tex                                  63
  17          Outlet Concentration by Particle Size -
                Gore-Tex                                  65
  18          Penetration vs. Particle Diameter -
                Gore-Tex                                  66
  19          Pressure Drop Across Bags vs. A/C
                Ratio - Gore-Tex                          68
                             vm

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                                  Figures
Figure
Number                            Title                   Page
  20          Typical  Cleaning Cycles  -  Gore-Tex           69
  21          Positioning of Dralon T  Bags                 71
  22          Outlet Particle Size Distributions  -
                Dralon T                                  72
  23          Outlet Concentrations by Particle
                Size - Dralon T                           74
  24          Penetration vs. Particle Diameter -
                Dralon T                                  75
  25          Pressure Drop Across Bags vs. A/C
                Ratio - Dralon T                          76
  26          Typical Cleandown Cycles - Dralon T         77
  27          Positioning of Nomex Felt Bags              78
  28          Outlet Particle Size Distributions -
                Nomex                                     79
  29          Outlet Concentration by Particle Size
                vs. A/C Ratio - Nomex   ..                  82
  30          Penetration vs. Particle Diameter -
                Nomex                                     83
  31          Outlet Concentration vs. A/C Ratio for
                Different Levels  of Reverse Air -
                Nomex                                     87
  32          Outlet Concentration  (Dp  .36 Microns)
                vs. A/C  Ratio for Different Levels
                of  Reverse  Air  -  Nomex                    89
  33          Outlet Concentration  (Dp 2.73 Microns)
                vs. A/C  Ratio for Different Levels
                of  Reverse  Air  -  Nomex                    90
  34          Outlet Concentration  (Dp 5.89 Microns)
                vs. A/C  Ratio for Different Levels
                of  Reverse  Air  -  Nomex                    91
                                  IX

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                                  Figures
Figure
Number                            Title                  Page
  35          Outlet Concentration (Dp > 9.31 Microns)
                vs. A/C Ratio for Different Levels
                of Reverse Air - Nomex                    92
  36          Pressure Drop vs. A/C for 3 Levels
                of Reverse Air - Nomex                    93
  37          Comparison of Bag Cleaning at 3 Clean-
                ing Durations - Nomex                     94
  38          Installed Costs vs. A/C Ratio              100
  39          Installed Cost vs. Efficiency - ESP        103
  40          Annual Operating Costs vs. A/C Ratio       104
  41          Annual Operating Costs vs. A/C Ratio
                for Different Bag Life Assumptions-
                Dralon T                                 107
  42          Annual Operating Costs vs. A/C ratio
                for Different Bag life Assumptons -
                Teflon                                   108
  43          Annual Operating Cost vs. % Bag
                Replacement Per Year at Different
                A/C Ratios - Oral on T                    109
  44          Annual Operating Cost vs. % Bag
                Replacement Per Year at Different
                A/C Ratios - Teflon                      110
  45          Operating Costs vs. Efficiency - ESP       111
  46          Annualized Costs vs. A/C Ratio             112
  47          Annualized Costs vs. Efficiency - ESP      114
  48          Annualized Cost Comparison                 118
  49          Outlet Loading vs. Annualized Costs        119
  50          Outlet Concentration vs. A/C Ratio  for
                Various Bag Materials                    122

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                                Figures
Figure
Number                           Title                            Page
  51-         Penetration vs.  A/C Ratio for Different  Bag
               Materials                                            123
  52         Comparison of Operating Pressures  for Various
               Bag Materials                                         124
 A-l         Positioning of Teflon Felt Bags -  Style  2063           137
 A-2         Outlet Particle Size Distribution  - Teflon,  2063        138
 A-3         Outlet Concentration by Particle Size vs.  A/C
               Ratio - Teflon, 2063                                 140
 A-4         Penetration vs.  Particle Diameter - Teflon,  2063        141
 A-5         Pressure Drop vs. A/C Ratio - Teflon, 2063             142
 A-6         Typical Cleaning Cycles - Teflon,  2063                 143

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                            ACKNOWLEDGEMENTS

     This program was sponsored by the Federal Environmental  Protection
Agency with participation by Kerr Industries and Enviro-Systems &
Research, Inc.

     Gore-Tex bags were donated to the program by W.  L. Gore &
Associates.  Teflon felt was donated by E. I. duPont.

     Statistical analysis was designed and reviewed by Dr. Ray Meyers
of Virginia Polytechnic Institute.

     The authors wish to express their deep appreciation for all of the
foregoing contributions and in particular thank the following people for
their assistance:  Mr. Robert P. Perrin and Mr. Sidney Perry of Kerr
Industries, Concord, North Carolina, Dr. James Turner and Mr. Bruce
Harris of EPA, Research Triangle Park, North Carolina, Mr. Edward de
Garbolewski of W. L. Gore & Associates, Elkton, Maryland, Mr. Joseph A.
Genereux and Dr. H. H. Forsten of E. I. duPont de Nemours & Company,
Wilmington, Delaware.
                                  XII

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                              INTRODUCTION

     This  report extends  and confirms  the work initiated  under Contract
No.  68-02-1093 and reported in July of 1974 publication  EPA 650/2-74-058.
The  purpose  of this study was to evaluate the application of fabric
filter dust  collection to industrial size coal fired boilers.   The
techno-economic evaluation conducted was based primarily upon  data
obtained from a pilot plant installed on a  slip stream of a stoker
boiler stack.

     The earlier studies  indicated the critical parameters influencing
pressure drop and outlet  loadings.  The prior studies were mainly
conducted on Nomex^felt.  The work cited in this report expands   and
confirms  the earlier studies on Nomex and  extends  them to include
Teflon^ felt, Gore-Te@and Dralon^T felt.

     The performance data, obtained in the  screening of the various
filter media, was  employed in the development of capital and operating
costs.  Various bag life  assumptions were employed in developing  these
costs, since no bag life  data was  obtained in this program.
  Registered Trade Mark as follows:  Nomex^ and Te£lnrt-/registered trade
  mark of E. I.  duPont de Nemours & Company,  Dcalon-'registered trade
  mark of Farbenfabriekn Bayer AG, and Gore-Te*-'registered trade mark
  of W. L. Gore  and Associates.

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                              CONCLUSIONS

     The four (4) filter media studied had different performance
characteristics.

    Nomex felt achieved the lowest outlet dust concentrations.

    Studies employing Nomex felt indicated that higher collection
efficiencies are possible when no cleaning is employed.

    Increasing the duration of cleaning time from 7 seconds to  25
seconds does not improve the cleaning of Nomex felt.

    Teflon felt operated at the lowest pressure drop.

    The dust release properties of Teflon felt and Gore-Tex appeared
better than those of Nomex felt and Oral on felt.

    An increase in filtering velocity (air-to-cloth ratio) results in
an increase in outlet loading.

    Varying the volume of cleaning air from 1400 to 4000 ACFM has little
effect on overall dust removal efficiency.

    An increase in the amount of air used for cleaning reduces  the
pressure drop across the bags.

    For the industrial boiler size studied, if two (2) year bag life
can be achieved, fabric filter dust collectors appear economically
attractive when compared to electrostatic precipitators operating at
95% efficiency or better.

    A PTFE laminate on a woven backing can yield dust removal effi-
ciencies similar to that of felt media.

    In view of the different performance characteristics obtained on the
four (4) filter media types tested, careful filter media selection appears
important for both particulate removal efficiency and pressure  drop
requirements.
                                   -  2 -

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                            RECOMMENDATIONS

     The pilot scale study has  indicated that it is possible  to  operate
the fabric filter dust collector at high filtering velocities (6 fpm  or
greater) and to achieve both high dust removal  efficiencies  and  econom-
ically tolerable pressure drops.   The limitation of this program has
been the fact that it does not  provide life data on the filter media.

     It is recommended that a full  scale unit be built and tested over
a year or more duration.  Such  a program would provide bag life  data
necessary for the evaluation of annualized^costs.  It is also recom-
mended that such a demonstration program include periodic performance
evaluation in order to determine whether or not performance changes
occur with increasing on-stream time.

     The data obtained in this  program is only valid for stoker  boiler
applications.  If the same high velocity filter approach to pulverized
coal boilers is desirable, it is recommended that a similar pilot plant
program first be conducted.

     In order to provide better correlation of dust removal  efficiency
and filtering velocity it is recommended that a bench scale program be
undertaken.  The laboratory program is recommended over the pilot plant
for this purpose because of the better control of inlet conditions
achievable on the bench.
                                    - 3 -

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                             RESEARCH NEEDS

     In studying outlet particulate loadings at the various filtering
velocities or air-to-cloth ratios, it was determined that as the velocity
increased the overall outlet loading also increased.  In studying the
different size fractions, however, there were indications that while the
largest particle penetration increased, the finer size fractions did not
correlate in the same manner (e.g. See Figure 32).

     It is generally recognized that the finest size fractions are
controlled by a different mechanism (diffusion) than control the larger
fractions (controlled by inertial impaction and interception).  The
results obtained appear, on the surface at least, to be contrary to
the collection - velocity relationships dictated by these simple single
mechanism formulae.  There does not exist at present a correlation
which accommodates the results obtained.

     In order to refine the type of data obtained and perhaps gain some
insight into the combination of mechanisms at work it will be necessary
to conduct experiments under much more controlled and well defined
conditions than are possible via a pilot plant.  It is therefore recom-
mended that a bench scale experimental effort be undertaken for the
purpose of developing correlations between penetration and filtration
velocity, as a function of particle size.  Such basic information would
be of significance in developing the technical underpinnings of any
future fine particulate codes.

     Two other research areas of interest, but lesser immediate signif-
icance, are further studies of laminate (e.g. Gore-Tex) filtration
mechanisms and also bench exploration of the impact reverse air volumes
and durations on pressure drop and penetration.
                                 -  4  -

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                              GLOSSARY  OF TERMS
ACID DEW-POINT - The temperature at which  the  condensation of the acid
    vapors initiates for a given state  of  humidity  and pressure.

AIR-TO-CLOTH RATIO - The volumetric rate of  capacity of  a fabric filter;
    the volume of air (gasX cubic feet  per minute,  per square foot of
    filter media (fabric).*

BAG - The customary form of filter element.  Also known  as tube, stocking,
    etc.  Can be unsupported (dust on inside)  or used on the outside of
    a grid support (dust on the outside).

BLINDING (BLINDED) - The loading, or  accumulation,  of filter cake to the
    point where capacity rate is diminished.   Also  termed "plugged".

CLOTH - In general, a pliant fabric;  -  woven,  knitted, felted,  or other-
    wise formed of any textile fiber, wire,  or other suitable material.

CLOTH WEIGHT - Is usually expressed in  ounces  per square yard or ounces
    per square foot.  However, cotton sateen is often specified at a
    certain number of linear yards per pound of designated width.  For
    example, a 54" - 1.05 sateen weighs 1.05 linear yards per pound in
    a 54" width.

DAMPER - An adjustable plate installed in a duct for  the purpose of reg-
    ulating air flow,

DIMENSIONAL STABILITY - Ability of the fabric to retain  finished length
    and width, under stress, in hot or moist atmosphere.

DUST LOADING - The weight of solid particulate suspended in  an  air  (gas)
    stream, usually expressed in terms of grains per cubic  foot, grams
    per cubic meter or pounds per thousand pounds  of gas.
    *A1though it is EPA's policy to use the metric system for quantative
     descriptions, the British system is used in this report because not
     to do so would tend to confuse some readers from industry.   Readers
     who are more accustomed to metric units may use the table of con-
     versions in the appendix to facilitate the translation.
                                  -  5  -

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                              GLOSSARY  OF TERMS
FABRIC - A planar structure produced by interlacing yarns, fibers or
    filaments.

    KNITTED fabrics  are produced by  interlooping strands of yarn, etc.

    WOVEN fabrics are produced by interlacing  strands  at more or less
    right angles.

    BONDED fabrics are a web of fibers  held together with a cementing
    medium which does not form a continuous sheet  of adhesive material.

    FELTED fabrics are structures built up  by  the  interlocking action
    of the fibers themselves, without spinning, weaving or knitting.

FILTER MEDIA -  The substrate support for the filter cake; the fabric
    upon which  the filter cake 1s built.

FILTER VELOCITY - The velocity, feet per minute, at which the air (gas)
    passes through the filter media, or rather the velocity of approach
    to the media. The filter capacity  rate.

FILTRATION RATE - The volume of air  (gas),  cubic feet  per minute, pass-
    ing through one  square foot of filter media.

FRACTIONAL EFFICIENCY - The determination of collection efficiency  for
    any specific size or size range  of  particles.

GRAIN - 1/7000 pound or approximately 65 milligrams.

INCH OF WATER - A unit of pressure equal to the pressure exerted by a
    column of liquid water one inch  high at a  standard temperature.
    The standard temperature is ordinarily  taken as 70°F.  One inch of
    water at 70°F. = 5.196 1b per sq. ft.

MASS MEAN PARTICLE DIAMETER - Refers to the point  of a curve plotting
    particle diameter versus cumulative mass percent that shows 50%
    of the material  is less than and 50% of the material is greater
    than the Indicated particle diameter.

MICRON (urn) - A unit of length, the  thousandth part of 1 mm or the
    millionth of a meter, (approximately 1/25,000  of an inch).

MULLEN BURST - The pressure necessary to rupture a secured fabric speci-
    men, usually expressed 1n pounds per square inch.

NEEDLED FELT - A felt made by the placement of loose fiber in a systematic
    alignment, with  barbed needles moving up and down, pushing and  pulling
    the fibers to form an interlocking  of adjacent fibers.
                                  - 6 -

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                              GLOSSARY  OF  TERMS
NON-WOVEN FELT - A felt made either by needling, matting  of fibers or
    compressing with a bonding agent for permanency.

NYLON - A manufactured fiber in which the fiber forming substance is
    any long-chain synthetic polyamide having recurring amide groups.

PEARLING - Refers to a condition of the dust cake  on  the  fabric which
    appears as nodular structures of agglomerated  dust.

PERMEABILITY, FABRIC - Measured on Frazier porosity meter, or Gurley
    permeometer, etc.  Not to be confused with dust permeability.  The
    ability of air (gas) to pass through the fabric,  expressed in cubic
    feet of air per minute per square foot of fabric  with &  0.5" H20
    pressure differential.

PITOT TUBE - A means of measuring velocity pressure.   A device consisting
    of two tubes - one serving to measure the total or impact pressure
    existing in an air stream, the other to measure the static pressure
    only.  When both tubes are connected across a  differential pressure
    measuring device, the static pressure is compensated  automatically
    and the velocity pressure only is registered.

POROSITY, FABRIC - Term often used interchangeably with permeability.
    Actually percentage of voids per unit volume  - therefore, the term
    is improperly used where permeability is intended.

PRESSURE, STATIC - The potential pressure exerted  in  all  directions  by
    a fluid at rest.  For a fluid in motion, it is measured  in a dir-
    ection normal to the direction of flow.  Usually  expressed in inches
    water gage, when dealing with air.

PRESSURE, TOTAL - The algebraic sum of the velocity pressure  and the
    static pressure (with due regard to sign).  In gas-handling systems
    these pressures are usually expressed in inches water gage.  The
    sum of the static pressure and the velocity pressure.

TEMPERATURE, DEW-POINT - The temperature at which  the condensation  of
    water vapor in a space begins for a given state of humidity and
    pressure as the temperature of the vapor is reduced.  The temperature
    corresponding to saturation (100 per cent relative humidity) for
    a given absolute humidity at constant pressure.

TWILL WEAVE - Warp yarns floating over or under at least  two  consecutive
    picks from lower left to upper right, with the point  of intersection
    moving one yam outward and upward or downward on succeeding picks,
    causing diagonal lines in the cloth.
                                 - 7 -

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                              GLOSSARY OF TERMS
VELOCITY HEAD - Same as velocity pressure.   (See Pressure,  Velocity).

VELOCITY OF APPROACH - The velocity of air (gas), feet per  minute,  normal
    to the face of the filter media.

VELOCITY TRAVERSE - A method of determining the average air velocity  in
    a duct.  A duct, round or rectangular,  is divided into  numerous
    sections of equal area.  The velocity is determined in  each  area
    and the mean is taken of the sum.
                                  - 8 -

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                              BACKGROUND

     Fabric filters (baghouses) have historically been one of the major
types of control for participate emissions employed by industry.   Bag-
houses have been used to control industrial dusts since the early
nineteenth century.  They have been used with good success in industries
such as carbon black, aluminum, asbestos, steel, ferroalloy, cement,
rock products and others.  Baghouses are typically noted for high effi-
ciencies and have proven  to be one of the better control methods for
fine particulates.  It has been, however, only in the last decade that
baghouses have been used for large combustion sources.  The combustion
of coal , 400 million tons per year, by utility and industrial boilers
is a major source of particulate emissions, some 5.7 million tons of
fly ash annually.  Industrial boilers account for 100 million tons per
year and generate 2.6 million tons of particulate emissions per year.

     The capacity range typically designated for industrial boilers is
from 10 million to 500 million BTU/Hour output (10 thousand to 500
thousand pounds of steam per hour).  Commercial boilers are smaller
and utility boilers are larger, even though some industrial boilers
are used for electrical generation by utilities.  The Battelle study^
characterizes the current field population of industrial boilers.

     Table 1  shows the capacity range for  industrial boilers in approx-
imately equivalent units of output and fuel inpat.

     The significance of industrial steam  generation can be seen in
Table 2, which shows the usage of fossil fuels for major industrial
applications in comparison to the total usage and to the utility
sector.

     Steam generation is the predominant industrial use and is almost
as large in fuel consumption as the utility sector.  In the base year,
                                - 9  -

-------
                             Table 1

       Capacity Range for Industrial  Boilers in Approximately
                          Equivalent Units
                                       Minimum           Maximum
      Capacity Rating                  Capacity          Capacity
Boiler Output Units


   BTU/Hr.  Output                     10,000,000       500,000,000

   Pounds Steaw/Hr. Output, PPH(a>        10,000           500,000

   Boiler Horsepower(b>                      300


Fuel  Input Units(c)
Oil Input Gallons/Hr.
Barrels/Day
Gas Input, Cubic Feet/Hr.
Coal Input, Lb./Hr.
Tons/Day
83
48
12,000
1,000
12
4,200
2,400
620,000
50,000
600
         on equivalent output of saturated steam.

( 'One boiler horsepower is equivalent to approximately 33,500 BTU/Hr.
   output.   Boiler horsepower ratings are commonly used for firetube
   boilers, which are generally available only in  sizes up to about
   900 boiler horsepower.

^'Assuming full-load operation at 80 percent boiler efficiency and
   fuel  heating value 150,000 BTU/Gal. for residual  oil, 1,000 BTU/
   cubic foot for natural  gas, and 12,500 BTU/Lb.  for coal.
Source for Above Table:  D. W. Locklin, et al, "Design Trends and
Operating Problems in Combustion Modification of Industrial  Boilers",
April - 1974, NTIS PB-235-712.
                                - 10 -

-------
                                Table 2

              Industrial and Utility Use of Fossil Fuels
Trillions of BTU's
for Base Year 1968
TOTAL - ALL SECTORS
UTILITY SECTOR TOTAL
INDUSTRIAL SECTOR TOTAL
All
Fossil
Fuels
59,639
11,556
19,348
Coal
13,326
7,130
5,616
Oil
26,749
1,181
4,474
Gas
19,564
3,245
9,258
  Fuel-Fired in Boilers for
    Steam Generation

    Process & Space Heating       10,132     2,349     1,986     5,797

    Electricity Generated
      On-Site                        410        95        80       235

  Fuel Used for Direct Heat
    Applications (Not
    including purchased
electrical energy.)
Fuel Used as Feedstocks
6,604
2,202
3,025
147
808
1,600
2,771
455
Source for Above Table:  D. W. Locklin, et al, "Design Trends and
Operating Problems in Combustion Modification of Industrial Boilers",
April - 1974, NTIS PB-235-712.
                                  - 11 -

-------
gas accounted for 57 percent of the fuel input to boilers for industrial
steam generation, with coal and oil accounting for 23 and 20 percent,
respectively.  The coal share has declined steadily in the past few
decades, due primarily to the low cost of gas and low capital and
operating costs of gas-fired package boilers.  Coal-fired steam plants
must include coal storage and handling, air pollution control and ash
disposal.  Emission requirements have also increased the number of
conversions of coal fired plants to gas or to low sulfur oil, adding
to the demand for these clean fuels.  However, as these clean fuels
become less available, it appears probable that the industrial sector
will be forced to rely Increasingly upon coal.

     Tables 3 and 4 give the population breakdown by fuel capability
for all industrial boilers now in service in the U.S. and by burner
type for coal fired facilities.  The estimated trends for these two
categories thru 1990 are given in Tables 5 and  6.  The national
population of industrial boilers is approximately 36,000 of which only
23% are greater than 100,000 pounds of steam per hour.  This places
the bulk of industrial units (approximately 28,000) in the less than
100,000 pounds of steam per hour size range.

     Traditionally, the method of emission control for coal fired boilers
has been electrostatic precipitation (ESP), often in conjunction with
mechanical collection, generally of the cyclone type dust collector.  This
is particularly true of utility boilers.  There are an estimated 1200-1500
ESP's on coal fired boilers.  The need to minimize SO^ emissions by using
low sulfur coal, however, has caused problems of reduced ESP efficiency.
Also the control of fine particulates requires a more costly design  .

     In contrast, the number of baghouses installed on coal fired boilers
is very limited, most of these installations are summarized in Table 7.
Although fabric filters are highly efficient there are problems associated
with their use on large combustion sources.  Some of these are large size
                                - 12 -

-------
                              Table 3
       Population Breakdown by Fuel  Capability (Percentage Basis)
               for All Industrial  Boilers Now In  Service
Rated Capacity
Size Range
                                TO6 BTU/Hr.  or IP3 Lb.  Steam.  Hr.
10-16
     17-100
  101-250
251-500
FUELS
Oil Only
Gas Only
Coal Only
Oil & Gas and
Gas & Oil
Oil & Coal and
Coal & Oil
Gas & Coal and
Coal & Gas
Misc. Fuels
(Alone or With
Alternate Fuels)
TOTAL


35
45
3

16






1
100%
Table

35
35
10

18






2
100%
4

30
22
18

26

0.5

0.5


3
100%


22
22
22

23

3

3


5
100%

       Population Breakdown by Burner Type (Percentage Basis)  for
        All Coal Fired Industrial Boilers Now in Service in U.S.
COAL BURNERS
   Spreader
   Underfeed
   Overfeed
   Pulverized
   Other (Hand-firing,
    Miscellaneous and
    Unreported)
      TOTAL COAL
Source for Above Table:
10-16

  15
  70
  10
Approximate 10"
     17-100

       20
       60
       15
   5
 100%
        5
      100%
Lb. Steam/Hr.
  101-250

     50
     20
     10
     15

      5
    100%
251-500

   30
   15
   10
   40
    5
  100%
D. W.  Locklin, et al,  "Design Trends  and
Operating Problems in Combustion Modification of Industrial  Boilers",
April - 1974, NTIS PB-235-712.
                                 _ 13 _

-------
                                              Table  5
Estimated Trends
Boilers
Rated Capacity
Year 19—
FUEL CAPABILITY
Oil
Gas
Coal
Oil & Gas and
by Fuel Capability (P<
jrcenti
we Basis) for All Industrial
Installed In Years Noted, Includina Conversions
10-16
30
17
5
75
*
50
43
20
10
25
70
30
30
5
30
90
13
6
30
45
30
13
10
75
*
17-100
50
30
30
30
5
70
30
30
5
30
9£
10
4
40
40
101-250
30 50_
5 20
5 20
90 38
* 10
70 90
24 *
24 *
15 50
25 30
251-500
30 50
5 15
5 15
90 60
* 5
70
20
20
20
20
90
*
*
60
20
   Gas & Oil

   Oil & Coal and                                            *     5    5   10     *     3   10   10
   Coal & Oil

   Gas & Coal and                                            *555*2105
   Coal & Gas

   Misc. Fuels     3256      2556*2    25     *     *    *    5

      TOTAL      100% 100% 100% 100%   100%  100%  100%  100%   100% 100% 100% 100%   100% 100% 100% 100%


Source for Above Table:   D.  W.  Locklin, et al,  "Design Trends and Operating Problems in Combustion
Modification of Industrial  Boilers", April -  1974, NTIS PB-235-712.

-------
                                                  Table 6
                      Estimated Trends by Burner  Type  (Percentage  Basis)  for All Industrial
                                          HR
                             Boilers Installed In  Years  Noted  iTncTucnng Conversions)
cn
i
Rated Capacity
Year  19—
COAL BURNER
  Spreader
  Underfeed
  Overfeed
  Pulverized
  Others
   TOTAL COST
                               10-16
                         30   50   70   90
 *    10   25   35
 60   60   70   50
 35   25   *    10

  5    5    5    5
100% 100% 100% 100%
       17-100
30   50   TCI   9CI

*    40   50   65
60   25   15   10
35   30   25   15
                                                5     5     5    10
                                              100% 100%  100%  100%
                                                  101-250
251-500
30.
*
50
45
*
5
100%
50
50
20
15
10
5
100%
70
60
*
10
20
10
100%
90
35
*
10
40
15
100%
30.
*
25
60
10
5
100%
50.
25
10
10
50
5
100%
7Q
10
*
*
80
10
100%
90
5
*
*
85
10
100%
       *nil
       Source for Above Table:   D.  W.  Locklin,  et  a!,  "Design Trends and Operating Problems in Combustion
       Modification of Industrial  Boilers",  April  -  1974,  NTIS  PB-235-712.

-------
                                                                                          Table 7

                                                                        Baghouse  Installations  on Coal  Fired Boilers
Facility
rjiir^Qrunfiuni
Ind. Boiler



P.SJ. * J3NJ
Mercer
SCE Almltos

Pennsylvania
Power & Llcjh

du Pont



du Pont

_
Pennsylvania
Glass & Sand
Manes Dye &
Finish tns_£a



Location
Hiaa&rx Fall*
., ,,N...JL_ ..



.Trenton
N.J.
Long Beach
Calif.
Sunberry
; Pa.

Boiler Data
Yype
—Spreader
f—Stoker


-- — - -
. .Pulverized
	


.Eulverized
_

Waynesboro
Va.

—
Parkersburg._Sloker
_ W...Va.. 	 __
. . j . 	 	
Huntlngton
Pa-.
W1nston-Sa1<
N.C.



„ 	
	
SL_$toker




Size





20.0QO acfm



2 Boilers
400 x IQ3 pph




4 Boilers
Total Capacit,
500.x 103 pph



40 x 1Q3 pph
75 x 103 pph


Date
Inst.
1968




1965

1965

1973


1973



' 1974
-

1972

1974



Present
Status
Operating




Dlsmantlec

On Stand-
by
Operating


Operating
Coal Flue Gas
*Ash/J!S T F/Vol.
Bag Design
Dla'VL'/IBags
: 375/104 ;




270/7500 11. §'739. 5'/
680/15,000
011/1.6 285/8. 2x10* H.5'738.81
+ gas
4x , 4x
2/1,3 325/220x10^ 11.5'730'/1260
:
:
AP
"H^O
3






6

2.5


.7/1.2 375/125x10^ 3-4


!
i
_ -._.
Operating 7/2.5 350/variouS 6"/9V
2.-3
. . : . . — , 	 	
. . 	 j 	 ._. .
	 700/300/25.,QQQ_.

Operating



.
/I. 5 310/19 x 10^
' 310/34 x lOJ




6V121/





6-8


	 	 - i-
A/C
3/1



•
1.8
3.5
6-7
Fabric
;ia$sy
Nomex


. 	 	
Glass

Glass.

2/1 . Glass
Cleaning




	 — , 4
Rev. A1r
.


Rev. Air
; 	 . 	 _,
I 1
8/1 ; Homex__[__Pulse Jet
| 	 !

- •— 	
4/1 Teflon& Pulse Jet
Glass

> i
;' Nomex

6-7


• ' • —

Glass






.Rev, .Air..




Des.
Eff .

Manufacturer
& Remarks
^anaborn
Pilot, unit


	 	 	 	




_99+
	













L 	

	 ., ,.., . _ _
Air Preheatei
_Co. JJilqtjJt,
JLiJtMenardi

Western
Precipitator
1
Std. Havens
pilot unit


Std. Havens


Fuller-Draco
Pilot unit
Bus tax


. 	 . i
cn
 i

-------
              Table 7 (cont'd.)
Baghouse Installations on Coal Fired Boilers
Facility
B ft H
U. Notre
Dane
Colorado Ut
Elec. Assoc
f
Sorg Paper
i
Crisp Countj
Power Conn.
du- Pont
(Cerr ._ _
Industries
Carborundum
Ref. D1v.



Location
fiakerton
South Bend_.
Ind.
:. Hulca Stati<
Nulca,_.Cplt);
Middle town
Ohio
Cordele
Ga.
tew Johnsonvil
rennessee
Concord
N.C.
Buffalo
N.Y.



Boiler Data
Type

—
n ^Stoker
Pulverized
Pulverized
le — Stoker

_Stoker
Stoker




Size

3 Boilers
120 x 103. ppl
55x 103 pph
120xl03 pph
135 x 103 pph
SOxlO3 pph
75xl03 pph
Date
Inst.
1973
1973
1-1973
1-1974
1973
1975
1975
197.2-74
1967
Present
Status
.Operating.
. .Dismantle!
Operating
Operating
Start-up _
Jn 'or Ju.
In
Construct!
Jiat.
Operating

Coal Flue Gas
SAsh/fS r F/Vol.
7.Hlgh I
125-/
10/2-4 _ - 300/4.8x10 .
:
... ;
12/0.7 310/86xl03
10/1.0 .350/105
,10/1.0 . 280-325.°F
	 60,000 acfm
7/3,2 .400/57 x 103
Jn 	 i 	 - .. -
!
J/CLL. ; 300/35, 000
12.7



Bag Design
D1a'7L7«ags

„ ..61797 	
8"/22 73x672
H.5'7307
11.57307
6V7971200
!_
_5J78'8'7216 .


«$ ^C

6% 7/1
&i 3.35
2.5- .
3.5 ;
4-5.5 2.8
i
-5^0. [ 3.2
.
2-7 3-14
i
Fabric
Glass &
Felts
Glass
Glassw/
Teflon
Glassjrf./1
Teflon
--, - -
Tof. on
Various
.

Cleaning

	
	 —
Rev. Air
+ Shake
Slow Col
Rev. Air.
JSlow Col .
Rev. Air
Pulse Air
Rev . Ai r
.- . „ -

Des.
Eff.
h— •'-— i
99+
:"
99+

Manufacturer
& Remarks
B 4 H
pilot unit
Wheel a brator-
Frye/pilot ur
Wheel abrator-
Frye
Zurn
Zurn
Standard
Havens
Enviro-Sys.
& Res. Inc.
£ijot..mjt...




-------
             Table 7 (cont'd.)
Baghouse Installations on Coal Fired Boilers
Facility
Pennsylvani
£awer . JL _Lig
.AflMJgjunated
Sugar Co.

Harrison Rad
Dlv. of G.M.
i
t
_t

j ... ; „..
1
1
1












- )
A/C
Fabric
2,42, Glass.
Cleaning

•i '!
. t . .
,3*66 j 61 MS

1
4.5- Nomtx
5.5 w/Ume
	


Des.
Eff.
s
Manufacturer
& Remarks
._29+..iJ(lh.eela.brator.
j Frye
...99+. Wheelabrator
i Frye 	


pulse-jet 91+.| West- fPt-

	 r— 	
i :
i j.
;„ 	 ,„ 	 1
:
!
.3.02: Glass.. ,!.
— - •
99+


i

i

*
!


i

.. .





_. 	 	





— ..


:



t
Wheelabrator
Frye










i

-------
requirements, high gas temperatures and fabric or bag durability.
Existing  baghouses on coal  fired boilers typically operate at an air-to-
cloth ratio of 2/1 (ACFM/Ft.2 Cloth) and use glass fiber bags.  The low
filtering velocity  dictated by allowable outlet loadings and lack of
durability of the bags leads to high capital and maintenance costs.  In
order to  improve and expand the availability of fabric filters as
viable controls for coal  fired boilers it is necessary to provide
systems capable of operating at air-to-cloth (A/C) ratios greater than
presently used, and to employ fabrics which will be durable at the
higher filtering velocities.

     While it has been demonstrated that baghouse dust collectors can
be applied to fly ash removal, there was a need for a techno-economic
evaluation of fabric filters as specifically applied to industrial
size coal fired boilers.   There have been some recent developments in
bag technology which may affect application problems previously
encountered by others and the economics of fabric filters applied to
fly ash removal.
                                  - 19 -

-------
                            PROGRAM DESCRIPTION

     The fabric filter pilot unit installed at Kerr Industries in
Concord, North Carolina was operated during the summer of 1974 from
May until September.  The operating mode and testing schedule were
designed to accomplish the purpose and scope of work outlined below.

Purpose
     The purpose of the subject program was to conduct, via a pilot
plant, a techno-economic evaluation of the application of fabric filter
dust collection to coal fired industrial boilers.

Scope of Work
Task 1 - Using the existing pilot baghouse located at Kerr Industries,
         Concord, North Carolina, the contractor shall operate the
         unit so as to provide data for:
         A.  A family of curves of pressure drop and size efficiency
             vs. air-to-cloth ratio for three levels of reverse air
             for Nomex felt.
         B.  A family of curves of pressure drop and size efficiency
             vs. air-to-cloth ratio for Teflon felt.
         C.  A family of curves of pressure drop and size efficiency
             vs. air-to-cloth ratio for expanded Teflon coated woven
             Nomex (Gore-Tex/Nomex).
         D.  A family of curves of pressure drop and size efficiency
             vs. air-to-cloth ratio for acrylonitrile homopolymer.
         E.  Relationships among reverse air volume, air-to-cloth
             ratio and outlet grain loadings by size.
         F.  Baghouse operating and capital costs for the fabrics
             studied which meet existing Federal or State emission
             codes.
                                 - 20 -

-------
         G.   Relationships between reverse air durations for less than
             30 seconds and pressure drop across the bags.

Task 2 - Using the data obtained in 1 above, the Contractor shall write
         a report containing suitable graphs and tables to  show:
         A.   Pressure drop vs.  air-to-cloth ratios for the  various
             levels of reverse air volumes and bag material  types.
         B.   Outlet loadings by size versus air-to-cloth ratios for
             the various levels of reverse air volume and bag
             material types.
         C.   SOg, SOg, inlet loadings and particle size distributions.
         D.   Capital and operating cost comparisons for the different
             bag materials.
         E.   Boiler load for the various tests performed.

Kerr Industries
     Kerr Industries is a textile dye and finishing plant located in the
textile belt of central  North Carolina.  There are some 22 textile
facilities in a two county area around Concord-Kannapolis,  North Carolina
Therefore, the local economy is relatively dependent on this industry.

     Kerr's  normal production schedule is three shifts per day, five
days per week with 450-500  employees.  Plant capabilities  include
processes to bleach, mercerize, dye, nap, finish and sanforize both
cotton and synthetic fabrics, as well as cutting and preparing corduroy.
Production capacity is 4 million yards finished cloth per month.
                                - 21 -

-------
                             PILOT PLANT DESCRIPTION

     The  fabric filter pilot plant employed for the program is shown in
Figure 1.   The house consists of two modules with two cells per module.
Each cell  has two doors on top of the house for access to the bags; all
visible in the schematic drawing, Figure 2.  A general arrangement drawing
of the baghouse is presented in Figure 3.

     Each  of the four separate cells contains fifty-four bags.  The bags
are 5 inches in diameter and 8 feet - 8 inches long.  Each bag has 11.48
ft.2 of cloth giving 620 ft.2 of cloth per cell and 2,480 ft.2 of cloth
for the house.  The bags are set into the tube sheet, see Figures 2 and 4
located approximately 13 inches from the top of the house, by the use of
two snap  rings incorporated into the bag itself.  The snap rings lock in
place, one above and one below the tube sheet.  A spiral cage (not shown
in figures) is set inside the bag and keeps the bag from collapsing.  As
shown in  Figure 4, the dirty gasses enter one end of the unit, pass
through the tapered duct, into the classifier, and then through the bags.
The classifier forces the dirty gases to change direction 90°, then 180°.
This quick directional change forces the larger and heavier particles out
of the flow so that they fall directly into the hopper.  Dirty gases
enter the  classifier thru a central duct which is tapered to feed the
same volume of gas into each of the four cells.  The gases are forced
thru the fabric filter into the center of the bags, leaving the particu-
late on the outer surface of the bags where it is removed periodically
during the cleaning cycle.  The cleaned gases are drawn up and out thru
the center of the filtering bag into a center exit plenum via an open
damper in  the cell above the tube sheet.  The bags are cleaned one cell
at a time  by activating the pneumatic cell  damper.  When the damper is
in the up  position, the flow is thru the bags from the dirty side to the
center plenum or clean side.   When the damper is dropped to the down
position,  the flow is from the reverse air plenum thru the bags to the
dirty side or hopper.   As the solid matter collects on the outside of
                                 - 22 -

-------
i )
<
                                                    Figure 1

                                            Fabric Filter Pilot Plant

                                                Installed at Kerr

-------
                               Figure  2
                                                    Top of  House
                                                     210-230° F
Outlet
 180-
 200° F
       Reverse Air
       170-190° F
                                                           Inlet
                                                            290-
                                                            310°F
                                                    230-250° F
                      Pilot Plant  Temperature Profile
                                - 24 -

-------
                                                                           r Ttftirt:  a
ro
en
                   \\L-
                                                                                  i--~Jii.:"- v--------. ---"•
                                                                                  /  If
                                                                             PLAN ffvML.lt WAV       '/    }j


                                                                                                  --
                                                                  ' L INSIDt CMi
                                                                                                          CEVtlttAlt FAN
                                                                                                          (WHIN MOO',
                                             V •(
                                              iU~.
                                              ,x     ,  -T
                                  CU6TOMCBS
                                  KCgUfCMCNT




A-.—.

•

L^-
^
!
































1

i , J















5

1









!















/
/
f
f

i
J

/


                                                            "r,
                                                            i  I
                                                    ,  .
                                                   •' '*•
                                              it  "
                               11
                                                                  ACCMSOOOB,
COTAZY DISCUAetSE  ;''i
VALVE (WHEN etQ'o.)  . j.
                                                           V OTUEU)
                                                                                                            CAGEOHLADDE8&
                                                                                                            Wtt EO'-O" M)CM
                   UID V1KW
                                                                      ELEVATION
                                                              General  Arrangement  Drawing

-------
                                                   Figure 4
• :
 •
                                          Baghouse Pictorial  Showing Gas Flow

-------
the filter bag,  it builds a cake or crust which begins to restrict the
flow of the gases.  During the cleaning cycle,  clean air enters  the cell
thru the pneumatic damper.  The clean air is forced down the filter bag,
opposite to the  normal  flow direction.  The bag expands with a shock
so that the cake is cracked and the particulate falls off the bag into
the hopper.  After the shock has expanded the filter bag and broken
off the cake, the clean air continues to flow providing a drag which
pushes and pulls the dust particles away from the fabric.  The smaller
particles are thus forced out of the fabric and fall into the hopper for
removal from the unit.  Damper system and control panel arrangements
allow for variations in main gas volume, reverse air volume, duration
of cleaning and  frequency of cleaning.  The existence of four cells
allows for the repetitive sequential testing of different bag types
without the need to change bags.

Filter Media Employed
    Four types of filter media were evaluated.   These were Nomex felt -
a polyamide, Teflon felt, Dralon-T felt - a homopolymer acrylic, and
Gore-Tex laminate - an expanded Teflon on Nomex backing.  Specifications
for these filter media are given in Table  8.  Bench results of the Gore-
Tex had shown promise of higher A/C capabilities as well as quick
release properties.  The bench results on Gore-Tex were presented
earlier.(3)

Description of Kerr Industries' Boilers
    Two Babcock & Wilcox boilers are  in operation at the Kerr facilities.
Each has a design capacity of sixty thousand pounds of steam per hour and
both are equipped with spreader stokers.  Both boilers are equipped with
fans for supplying draft; and unit number two, the unit tapped for the
pilot plant slip stream, has overfire steam injection for better combus-
tion control.  In January, 1973, emission tests were conducted on these
boilers by the North Carolina Office  of Water and Air Resources, Air
                                - 27 -

-------
                                Table 8

Filter
Media
NomeJ^Felt1
Teflon® Felt2
Filter Media Characteristics

Weight ,, Permeability
Ozs. Yd/ CFM/Sq. Ft.
14 25-35
22-24 15-35
Mullen
Burst
psi
450
250
Style 2663

Teflon^ Felt
Style 2063
Gore-1
               18-20
              4-5 +
              Laminate
                   25-65
                    8-15
                   250
                 329-400
Oral or
Felt
13-15
20-30
250
"''High Temperature Resistant Nylon Fiber (Polyamide)

2Tetrafluoroethylene  (TFC) Fluro-Carbon

Expanded Teflon (Polytetrafluroethylene) with Interfacing Air
 Filled Pores
 *Homopolymer of 100X Acrylonitrile
                                 - 28 -

-------
Quality Division,  and I.E.  Wooten and Company.   The complete stack
                                           (3}
emission test report was presented earlier.   '   The particulate
emission rates were found to be approximately 130 pounds/hour versus
an allowable of about 25 pounds/hour.   Gas volumes were determined to
be about 35,000 acfm at a temperature  of about 355° F.   Thus the grain
loading measured was about 0.4 grains  per acfm.   Orsat analysis indi-
cated 9.5% C02, 10% 02, 0% CO and 80.5% Ng.   Coal analysis indicated  the
percent sulfur at  that time to be about 0.6%.  An analysis of the coal
burned during the  subject test program is presented in Table 9.

Installation at Kerr
     The pilot plant was installed on  a slip stream from boiler number
two at Kerr Industries.  The slip stream was 18" duct - 40 feet long
with a 90° elbow directed down into the gas flow of the Kerr boiler
stack, see Figure   5.   A typical temperature profile was shown in
Figure   2.  The reverse air used for  cleaning the bags is taken from
the pilot plant exhaust stack.  Both the slip stream duct and the pilot
plant were uninsulated.
                                 - 29 -

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                        Table 9
                      Coal  Analysis
                               As Received          Dry

% Mositure                          2.7
% Volatile Matter                  35.0            36.0
% Fixed Carbon                     55.7            57.2
% Ash                               6.6             6.8
    TOTAL                         100.0           100.0
% Sulfur                           0.71            0.73
BTU/Pound                        13,650          14,000

Fusion Temperature of Ash:    2800 Plus  °F
Size of Coal:  IV X V
Coal from Island Creek Coal Sales, Bluefield, West Virginia,
Mine Guyan Eagle #5 located at Kelly, West Virginia.
Analysis conducted by General Testing & Engineering Company,
Whitewood, Virginia
                         - 30 -

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                   48
                                        Figure 5
CO


I
               BOILER
                MAIN
               STACK
                                                                                   PILOT
                                                                                   PLANT
                                   Schematic Showino Slip Stream Duct Installation

-------
                      PILOT PLANT OPERATING PROCEDURES

     Standard operating procedures were established for the pilot plant
at the beginning of the program.   These were followed precisely through-
out the program in order to establish and maintain a normal operating
mode.   The basic operating procedures are outlined briefly below.   All
data reported was  obtained with the system operating in the normal mode
unless specified otherwise.

     A.  Start-Up Procedure
         1.  Open clean air port at baghouse inlet.
         2.  Start compressor - allow pressure to reach 80 psig.
         3.  Start reverse-air fan.
         4.  Start main system fan.
         5.  Turn damper control switch to automatic.
         6.  Open inlet blast gate.
         7.  Close clean air port.

     B.  Air-to-Cloth Ratio
         The filtering velocity or A/C ratio was the primary variable
         throughout the program.  The filtering velocity was established
         in the following manner.
         1.  Start-up system and run until outlet temperature reaches
             equilibrium.
         2.  Turn off reverse-air fan.
         3.  Run velocity traverse on outlet; calculate volume at outlet
             temperature and A/C ratio.
         To Change air-to-cloth ratio:
         4.  Open or close outlet duct blast gate  (located between fan
             and house) as required.
         5.  Run velocity traverse on outlet; calculate volume at outlet
             temperature and A/C ratio.
         6.  Repeat steps  4 and  5 until desired A/C ratio  (+_ 10 percent)
             is obtained.
                                  -  32 -

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                PILOT PLANT OPERATING  PROCEDURES
                          (continued)

C.  Normal  Cleandown Mode
    Each cell  is cleaned for 7 seconds once every  140 seconds.
    Reverse air volume is to be such that cleaning A/C ratio  is
    greater than 10/1.  Except for the evaluation  of cleaning
    durations  less than 30 seconds vs. pressure drop across the
    bags and except for the evaluation of the effect of volume
    of reverse air on outlet loading at three A/C  ratios for
    Nomex felt, the system was in the  normal  cleandown mode for
    all testing.

D.  System Monitoring
    The following parameters were monitored and manually recorded
    hourly:  pressure drop across the house, pressure drop across
    active cells, inlet and outlet gas temperature, reverse air
    temperature, reverse air static pressure, main fan static
    pressure,  boiler load and boiler excess air.

    The above parameters were also recorded whenever the A/C  ratio
    of reverse air level were changed.

E.  System Inspection
    Daily checks, generally in the morning before start-up, were
    made of the system for condition of the bags and cake
    characteristics.

F.  System Shutdown
    1.  Open clean air port at baghouse inlet.
    2.  Close inlet  blast gate.
    3.  Run for fifteen minutes to flush house with clean air.
    4.  Shut off main fan.
    5.  Shut off reverse air fan.
    6.  Turn damper  control switch to OFF.

                              - 33 -

-------
                 PILOT PLANT OPERATING PROCEDURES
                           (continued)

F.   System Shutdown (continued)
    7.  Shut off compressor, bleed tank to drain moisture.
    8.  Close clean air port.
                             -  34 -

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                              TEST METHODS

     The intent of this section is to describe briefly and to docu-
ment the test methods employed and the operating procedures followed
in obtaining the data.  It is assumed that the reader is familiar with
the accepted ASME and EPA test methods, therefore the procedures  for
these are not elaborated.

Vel oci ty
     Velocity traverses, performed with a Stauscheibe pi tot tube  and
inclined draft gauge, were conducted in general accordance with EPA
Method 2 for determining inlet, outlet and reverse air volumetric flow
rates.  All velocity data was obtained in this manner.  An orifice plate
was installed in the outlet stack to provide a continuous flow monitor
but this proved unreliable during calibration and was not used.

Static Pressure
     Magnehelic pressure gauges (0-15 inches w.g.) and twelve inch U-
Tube manometers were utilized for monitoring static pressure differentials
^p)-throughout the system.  Locations of pressure taps for the variousAp
measurements are given below.

     Pressure Drop Across the House:  One tap located in the inlet
     transition to the house and one in the transition from the
     house to the outlet duct ahead of the system fan.
     Pressure Drop Across the Cells:   One common tap located in the
     inlet transition to the house and individual taps located above
     the tube sheet on the clean air side of each cell.

     System  Fan Static Pressure:   Pressure taps located in duct ahead
     of system fan and in stack downstream from the fan.
                                  -  35  -

-------
     Reverse Air Static Pressure:   One tap located at end of
     reverse air plenum and one to atmosphere.
     The system fan and reverse air static pressures were used solely as
operational checks on the system and are not reported in the data.

Temperature
     All-metal dial thermometers (50-500° F) with eight inch stainless
steel stems were employed for temperature measurements.   Accuracy of
these thermometers was h of 1% of total scale reading.  These were
permanently mounted and well sealed in the following locations: inlet
and outlet transitions of the house, reverse air duct between outlet
stack and reverse air fan and in the hooper.

so2-so3
     EPA Method 8 was employed for determination of SO- and sulfuric acid
mist concentrations in the inlet to the baghouse.  Sulfuric acid mist
including SOg was reported as SOq.

Particulates
     Parti oil ate concentration measurements were conducted in general
accordance with the methods specified in ASME Power Test Code 27.  The
sampling train consisted of a stainless steel nozzle, alundum thimble
holder, heated cyclone and fiberglass filter, impingers for moisture
determinations, dry gas meter, and vacuum source (see Figure 6).

     Particle size analysis was performed with an Andersen in-situ
particle size analyzer.  Use of the Andersen inertia! impactor followed
the procedures recommended in "Guidelines to Conduct Fractional Efficiency
Evaluations of Particulate Control Systems" prepared April, 1974, by
Process Measurements Section of the Control Systems Laboratory of EPA at
Research Triangle Park, North Carolina.  Since this guideline necessarily
allows for certain options in Andersen methodology, the procedures
                                 - 36 -

-------
                                                   Figure 6
                                   Stack
                                   Wall
                                                           Heated Box
                                                           Containing
                                                           Cyclone and
                                                           Filter
              Alundum
              Thimble &
              Holder
Hose
u>
•-J
                Particulate Sampling Train
                                                                                                  Dry Gas Meter
                 Vacuum
                 Pump

-------
utilized are given below:
     1.  One sample was conducted for each test.   All  sampling was
         in-situ,
     2.  Special glass fiber impaction stage substrates  and a 2% inch
         diameter glass fiber substrate as a back-up filter were
         employed.
     3.  The impactor was oriented horizontally inside both the inlet
         duct and the outlet stack during sampling.
     4.  The impactor was heated by means of electrical  heat tape and
         a thermocouple feedback temperature controller.  Gas exiting
         the Impactor was maintained at a temperature of 250° F or
         20° F above the stack temperature, whichever was greater.
     5.  No precutter was used.
     6.  ;Flow rate thru the impactor was adjusted so as  not to exceed
         the critical velocity for the last stage.
     7.  Inlet sample time was two minutes.
     8.  Outlet  sample time varied from 1-2 hours, depending on the
         rate of loading - a function of the media and A/C ratio being
         tested.
     9.  Sampling time was designed to avoid overloading any single
         stage.
    10.  Sampling rates were maintained as close to isokinetic condi-
         tions as possible without exceeding recommended stage
         velocities.
    11.  All substrate weighings were accomplished on a Type 28N
         Ainsworth analytical balance which has a sensitivity of 0.1
         milligrams.  Substrates were oven dried and dessicated prior
         to weighing.
     Except when investigating the relationship of reverse air level to
outlet loading at different filtering velocities, particle size analyses
were run at zero reverse air in all cases.  Zero reverse air signifies
the reverse air  fan was off and no cleaning was achieved over the dura-
tion of the test.  The zero reverse air was necessary since only one
                                      - 38 -

-------
cell  contained the filter media being tested,  and operation of the
reverse air would have created velocity fluctuation at the test point.

     The Andersen impactor has been calibrated by several  independent
laboratories to arrive at the current respective size cuts for each
stage.   The calibrations were referenced to unit density (lg/cc),.
spherical particles so that the aerodynamically equivalent sized
particles collected on each stage are always identical for any given
flow rate.  Therefore, a stack sample containing a mixture of shapes
and densities is fractionated and collected according to its aerody-
namic characteristics and is aerodynamically equivalent in size to the
unit density spheres collected on each specific stage during calibra-
tion.  The effective aerodynamic diameter at 70° F is determined for
each Andersen sample based on the flow rate thru the impactor.  A
correction factor for determining the physical diameter of spherical
particles having other than unit density must be used.  This correction
factor yields the effective aerodynamic diameter for a specific density,
Also a correction factor is used for determining the effective aero-
dynamic diameter for elevated temperatures.

     All particle size presented was corrected for particle density
and gas temperature using correction factor curves supplied by the
impactor manufacturer.

Permeability
     Permeability tests on the fabrics employed were performed on a
Frazier air permeability instrument.  All testing was conducted in
accordance with the manufacturers specifications.  Obtaining initial
data before exposure presented a problem due to the fact  that the bag
could not be cut up for testing and  testing an intact bag  necessi-
tated air flow from the inside of the bag out - the latter being
opposite to the flow of dirty gas thru the bag in the baghouse.  After
testing several fabrics it was determined that direction  of flow did
                                    - 39 -

-------
not alter the permeability data significantly either  for  dirty or  exposed
bags or for clean ones.  Therefore testing data  represents air flowing
from inside the bag to the outside.
                                    - 40 -

-------
                              DATA OBTAINED

Introduction
     Operation  of the pilot plant was  tied directly to the dye and
finishing  plant operations via the boiler slip stream.  The boiler load
and on stream time was dictated solely by plant production requirements.
All day-time  boiler flue gas conditions were incurred by the pilot
facility;  however, when inlet and outlet loadings were measured care
was taken  to  avoid boiler grate cleaning times.

Inlet Conditions
     Measurements of inlet mass concentrations with the particulate
sampling train described previously indicated the loading to be from
0.41 to 0.48 grains/SCFD* (See Table 10).

     Particle size analyses using the Andersen inertia! impactor indi-
cated the inlet loading to be less than the above.

     Analyses of the inlet flue gas indicated S03 concentrations were
between 3.6 and 6.1 parts per million (ppm) by volume, and S0£ concen-
trations ranged from 250 to 500 ppm.

     Since it was not feasible within the scope of the program to run
inlet loadings simultaneously with each outlet loading determination for
fractional efficiency, an average inlet concentration by particle size
was established.  The average was derived from numerous inlet particle
size determinations over the duration of the program.  The average inlet
conditions was used to develop all fractional efficiencies reported.

     Table 11 gives the average inlet concentrations by particle size.
The inlet particle size distribution is shown in  Figure 7.

*SCFD, Dry Standard Cubic Feet
                                    - 41 -

-------
                              Table 10
                    Particulate Concentration Data
                            Flue Gas Data
Test
No.
1
2

Date
5/22/74
5/29/74
Temp.
°F
275
280
Volume Moisture
ACFM %
1724 6.9
2380 5.6
Concentration
Grains/SCFD*
0.48
0.41
*SCFD - Dry Standard Cubic Foot  (29.92 in H  and 70' F)
                                  - 42 -

-------
                             Tabled

               Inlet Concentration by Particle Size
          Average  Particle
           Diameter  (Dp)*
             Microns
   Average
Concentration
   mg/SCFD
   Average
Concentration
 Grains/SCFD
> 8.72
5.45
4.02
2.47
1.55
.86
.51
.35
< .35
9.4273
2.4951
1.7127
.8341
.8270
.3191
.1750
.1923
.2781
.14546
.03850
.02643
.01287
.01276
.00492
,00270
.00297
.00429
                                16.2607
                      .2509
*Corrected for particle density (2.6 grams/c.c.)  and stack
 temperature.
                                - 43 -

-------
                         Figure  7

               Inlet  Pirtlcle Size Distribution
    10
     8
          Note:   Corrected  for Density and Temperature
o
s_
o
01
4->
OJ
(U

O

4->
S-

-------
     Simultaneous  sampling  at each  end  of the  slip  stream  duct  indicated
that some of the particulate was  dropping out  and therefore not present
in the baghouse inlet.   Table 12  gives  the results  of these analyses.

     Baghouse operating temperature was also a variable which could  not be
maintained as a constant.   Since  the slip stream duct and  the house  were
uninsulated the system temperature  was  a function of velocity or acfm
thru the unit and  to a lesser extent the boiler stack temperature.   Table
13 shows the effect of gas  volume on the baghouse operating temperatures.

     At approximately the mid point of  the test program, a transmissometer
{Lear Siegler, RM 4 Cross Stack Portable Unit) was  installed on the
baghouse inlet.  No attempt was made to calibrate the transmissometer
in order to obtain quantitative data.  It was intended only as  a quali-
tative check to monitor relative  levels of particulate in  the inlet.
Table 14 shows outlet emissions at  different A/C ratios with the corre-
sponding boiler load and transmissometer readings.

     The general indication was that while the inlet conditions did  vary
they did not have a significant effect on the outlet loading from the
baghouse.

Permeability
     Permeability data for clean bags is given in Table 15 and Figure  8.
Fabric specifications give a permeability range at 0.5 inches of water;
the permeabilities at higher pressure drops were obtained to determine if
the different fabrics would have similar pressure drop vs. permeability
curves.

     The effect of exposure time on permeability and the results of
vacuum cleaning the exposed bags are shown in Table 16.  Nomex felt and
Dralon T exhibited higher permeabilities after cleaning than initially.
                                  -  45  -

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                                Table  12

                  Inlet Concentrations by  Particle Size

               .Sampling Time Period 1116-1120. August 14
   Average
Particle Diam.
   Microns
Inlet to Baghouse
  Average Cone.
    Gr./SCFD
Beginning  of Slip Stream Duct
        Average Cone.
          Gr./SCFD
    >10.0
      6.2
      4.18
       .84
       .79
       .96
       .58
       .39
       .39
     .02642
     .04333
     .03276
     .01902
     .01797
     .01163
     .00739
     .00211
     .00106

     .16169
           .09686
           .05181
           .03829
           .02365
           .01689
           .02140
           .01126
           .00788
           .01577
           .28381
                Sampling Time Period 1400-1404, August  14
   >10.0
      6.2
       .18
       .84
       .79
       .96
       .58
       .39
       .39
     .14007
     .04669
     .02668
     .01334
     .02001
     .00778
     .00333
     .00111
     .00445

     .26346
           .1543
           .03630
           .03744
           .01815
           .01702
           .01815
           .00908
           .00567
           .00567

           .30178
Above sampling conducted while baghouse was operating  at  an  A/C ratio
of 6.7 to 1.
                                - 46 -

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                                Table  13
                      Effects of  Gas  Volume on the
 Date
6/14/74
8/6/74
6/17/74
6/18/74
6/18/74
7/30/74
7/31/74
Baghouse Operating Temperatures
Temperatures,
Gas Volume
ACFM
5721
5909
1080
1068
975
2828
2812
Inlet
°F
305
312
250
265
255
282
285
Outlet
°F
250
230
140
140
115
200
191
Reverse Air
°F
195
198
100
no
105
162
164
                                                               Ambient
76
80
76
76
83
89
                                  - 47  -

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                                               Table  14
I

CO
Andersen
Test No.
  39
  40
  53
  54
  55
  64
  65
  66
  67
  68
  69
  70
Air-to-Cloth
   Ratio,
ACFM/Ft/
   8.7/1
   8.2/1
   6.4/1
   6.4/1
   6.4/1
   8.5/1
   8.9/1
   6.1/1
   6.1/1
   6.1/1
   3.3/1
   3.3/1
Effects of
Inlet Conditions on Outlet Emissions
Fiter Media - Nomex Felt
Boiler Load
Pounds Steam
Per Hour
29,500
38,400
46,500
46,600
47,600
36,200
40,600
40,600
39,700
45,400
50,500
__
Ratio 3
1.23
1.32
1.47
2.01
1.78
Filter Medi
1.30
1.35
1.12
1.26
1.42
1.84
__ •
Transmissometer*
Readings Percent
Absorbance
24
29
31.7
23.2
26.8
a - Oral on T
27.8
30
36.3
31.5
32
27.4
24.5
Ratio j
0.41
0.82
0.85
0.62
0.92
0.69
0.68
0.63
0.73
0.53
0.54
__
Outlet
Emissions
Grains/SCFD i
.00719
.00469
.00549
.00747
.00516
.00525
.00595
.00647
.00545
.00853
.00934
.00801
Ratio »
C^X }Q
0.33
0.62
0.58
0.31
0.52
0.53
0.50
0.56
0.58
0.38
0.29
0.31
*Transmissometer located on inlet duct just prior to  inlet  sampling port  about  two  feet  from the
 pilot plant.

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                                Table 15
                      Permeabilities  of  Clean  Bags
                        Permeabilities ACFM/Ft.2
Pressure
Drop
H00"
0.5
1.0
3.0
5.0
7.0
Nomex
Felt
35.6
78.11
201.8
306.6
409.46
Oral on
T
29.06
56.78
148.74
227.52
301.12
Teflon
Felt
26G3
24.92
49.84
123.10
184.88
_
Gore-Tex/Nomex
12.77
24.68
70.20
109.5
141.8
Data obtained on clean cloth while varying the pressure drop on the
Frazier perm gear.
                              - 49 -

-------
6f"
CO
01
u
c
3
V)
(/>
0)

Q.
                                Figure 8

                      PermeabiVities of  Clean Bags
                     (Pressure Drop vs.  Permeability)
                 KEY:

            Q  Gore-Tex/Nomex

            O  Teflon

            A  Oralon T

            O  Nomex
                                     i  i
    10
            20      30   40     60   80  100

                            Permeability - ACFM/FtJ
200    300  400
                                    -  50 -

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                               TABLE 16


                      FILTER MEDIA PERMEABILITY
                         CFM A1r/Ft.2 Cloth

Bag Material      Before Exposure  After Exposure  After Cleaning*

Nomex Felt          34.4-35.6        8.5-10.7          44.51
(After 195 Hrs.)

Nomex Felt          34.4-35.6          21.79           40.26
(After 50 Hrs.)

Gore-Tex/Nomex      13-16.4          1.66-2.5           5.79
(After 105 Hrs.)

Gore-Tex/Nomex      13-16.4          Not Available     10.63
(After 50 Hrs.)

Teflon Felt         37.8-54.8        6.4-10.6          16.24
(After 50 Hrs.)

Oral on T            19.4-31.1      18.7-21.9           26.55-30.95
(After 50 Hrs.)
* Bag was vacuumed on dirty side and retested in  laboratory with
  air flow passing thru bag from clean side to dirty side.
                                 - 51 -

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Teflon Felt - Style 2663
     Two styles of Teflon felt were Investigated in the  program.   First
Teflon Felt - Style 2063, was evaluated.  However,  this  media proved
unsatisfactory with respect to removal efficiencies and  has  since become
unavailable commercially.  In its place the manufacturer offered  Teflon
felt, Style 2663, a heavier weight fabric.  This fabric  was  evaluated at
the end of the test program and the data reported in lieu of reporting
data on Style 2063, not generally available to industry.   The data for
Teflon felt - Style 2063 is included in the Appendix for information
only.

    Twenty Teflon felt - Style 2663 bags were placed in  Cell  #3.   Since
each cell has a capacity for fifty-four bags, plugs were used to  seal
the empty tube sheet holes.  The positioning of the Teflon felt bags
is shown in Figure 9.  Although the number of bags  employed  was not
the same for the four fabrics, this general arrangement  was  used  for
each fabric to minimize any position effects, if present, on overall
performance.

    The Andersen sampler was used to obtain in-situ particle size data
at air-to-cloth (A/C) levels of 5.4/1, 8.4/1 and 14.1/1.   Inlet flue gas
volumes ranged from 1180 to 3260 acfm.  Because of  the limited amount of
Teflon cloth on hand, difficulty was experienced in trying to operate at
the lower A/C levels.  In order to reach an A/C ratio of 5.4/1, the main
fan was almost completely throttled.  The reverse air volume, although
not used during sampling periods, was 3500 acfm.

    The particle size distribution for the individual runs was averaged
at each of the three levels of A/C.  The particle sizes  and  fractional
loadings for all individual Andersen tests may be found  in the Appendix.
The comparison of the data is graphically displayed in Figure 10.  The
mass mean particle diameters were 1.36, 1.94 and 1.20 micrometers
(micron, urn) for A/C ratios of 5.4, 8.4 and 14.1 respectively.

                                   - 52 -

-------
             Figure 9
en
OJ
©eeeeee
  000XDOO
   0CDOOOO0
OQdXDOOOCXr)
      OOOOCD
      O.OOOQ
               t
          •Damper
          Opening
                        KEY:
              Cell 2
          Positioning of Teflon Felt Bags
            Style 2663
                         Teflon Felt

                         Plugs

-------
                           Figure 10
                Outlet Particle Size Distribution
    10
     8
VI
o
O   9
•t-   c
Q>
N
I—
CO
01
*y
E 1.0
s-
40
°-  .8
    .6


    .4

    .3
             Case:  Teflon Felt - Style 2663
Note:  Corrected for Density and Temperature
             KEY;
          A/C Ratios
          O   5.4/1
          O   S-4/1
              14.1/1
                  10    20       40     60       80
                   % Less Than Size Indicated
                                                90
                               - 54 -

-------
     The particle size distribution curves  indicate that about 67%  was
less than 3 microns  at the lowest A/C,  while 64% of the  particulate,  by
weight, was less than 3 microns at 14.1/1.

     Average outlet  concentration, cumulative percent and penetration
by particle size* are given in Table 17.    Figure 11 shows outlet
concentration for four particle sizes versus (vs) A/C ratio.   It can
be seen here that the largest particle size fraction is  most  sensitive
to increases in the  velocity or A/C ratio.   Generally an increase in
A/C ratio resulted in an increase in outlet loadings.  For the smaller
size fractions the curve does appear to flatten above an A/C  of about 8.
This curve is in general agreement with the data for the other materials
tested.   Penetration or 1- collection efficiency vs. particle diameter
is presented in Figure 12.   Three curves are shown, one for  each of
the three levels of A/C ratio.  All three show the same general trend,
with the curve sloping  downward to the right indicating less penetra-
tion of the larger particles.  Two of the curves indicate some leveling
or decrease of penetration for the very small fractions.  This improved
collection of the finest fractions is also present and in some cases
even more pronounced in the data for the other media.

     Pressure drop versus A/C data is presented  in  Figure 13, while
examples of typical  cleandown cycles are shown  in  Figure  14.   Although
Teflon felt exhibited the highest dust penetration of the materials
tested, it was capable of operating with the lowest  pressure  drops.  As
shown  in Figures  13 and 14 it would be economically  feasible  to operate
at even the higher A/C ratios.

     After fifty-eight hours on  stream the  bags  were inspected.  They
showed no sign of wear with only slight evidence of  pearling  in a  3/16"
cake of a friable dust.
 *Particle size is actually the aerodynamically equivalent particle size
  corrected for density  and temperature.
                                    -  55  -

-------
                                                     Table  17
en
crt
tion, Cumulative %
and Penetration
Ion Felt, Style 2663
Air-to-Cloth Ratio 8.4/1
Avg.
Outlet
Cone.
Gr./SCFD
.00257
.00082
.00108
.00108
. 00082
.00087
.00072
.00093
.00134
.01023


Cuml .
%
100
74.89
66.87
56.31
45.75
37.73
29.23
22.19
13.1



Pene-
tration
.0177
.0213
.0409
.0839
.0643
.1768
.2667
.3131
.3124
.0408
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00321
.00079
.00107
.00080
.00082
.00069
.00110
.00092
.0029.7
.01237


Cuml .
%
100
74.06
67.67
59.02
52.55
45.92
40.34
31.45
24.01

14.1/1


Pene-
tration
.0221
.0205
.0405
.0622
.0643
.1402
.4074
.3098
.6923
.0493
           Air-to-Cloth  Ratio  5.4/1
 Avg. CD    Avg.   (2)
 Part.      Outlet
 Diam.      Cone.       Cuml>3)  Pene-  (4>
  um       Gr./SCFD     %      tration
>8.38       .00091
  5.29       .00041
  3.55       .00043
  2.47       .00045
  1.57       .00051
   .79       .00052  .
   .49       .00036
   .33       .00046
 <.33       .00053
TOTAL       .00458
1.  Corrected for particle density (2.6 grams/C.C.) and stack temperature.
2.  At 5.4/1 two (2)  tests averaged, at 8.4/1 one (1) test averaged, at 14.1/1  two (2)  tests averaged,
3.  Percent of total  outlet concentration less than size indicated.
4.  Penetration based on average inlet concentration at corresponding impactor  stages.

-------
   .0035
   .0030
o
u_
in
c
•I—
IO
o
at
+J
0)
4J
0>
O
   .0025
   .0020
   .0015
   .0010
               Figure 11
   Outlet Concentration by Particle Size
                   vs.
            Air-to-C16th Ratio
Case:  Teflon Felt, Style 2663
    KEY:
  Q  .36 urn
  O 2.84 urn
     5.87 urn
           of all
            >9.37
               O  Total
                   Sizes
   .0005
                                     8
                                 10
12
14
                        Air-to-Cloth Ratio (ACFM/Ft. )
                                     -  57  -

-------
                Figure  12
               Ptnetratfan
                  vs.
            Particle  Diameter
          Case:   Teflon  Felt,  Style 2663
  KEY:
  ••MMH
A/C Ratio
O  5.4/1
O  8.4/1
D 14.1/1
          .4    .6   .8 1.0       2        4    6   8 10
            Particle Diameter, Microns
                      -  58  -

-------
                           Figure J
                    Pressure  Drop  Across  Bags
                                vs.
                      A1r-to-Cloth  Ratio
   10
    8
CD
  6

CO
o

o
OL
O

O

0)
l_
3
in
i/r

t
o.
   Case:  Teflon Felt - Style 2663



Q   After One Hour Without Cleaning

A   Before Cleandown

O   After Cleandown

 RA Volume - 3500 ACFM
 Cleaning Duration 7 Seconds
 Cleans Once Very 140 Seconds
    2.5
                                10

             Air-to-Cloth Ratio (ACFM/Ft.2)
15
                                 -  59  -

-------
                                 Figure 14


                          Typical Cleaning Cycles
           Case:   Teflon Felt - Style 2663
 in
 CO

 I/I
 I/I
 o

 u
o

V)

£
o
    8
                                          D  Before Cleandown

                                          O  After Cleandown


                                              RA Volume - 3500 ACFM
  A/C  14.1/1
o

o
in
w
0)
  A/C   8.4/1

•s
                              A/C 5.4/1
                             B            C

                             Cleaning Cycles
                                 - 60 -

-------
Gore-Tex/Nomex
    Thirty Gore-Tex/Nomex bags were placed in Cell 4.  Location of the
bags in the cell is shown in Figure 15.

    Inlet flue gas volumes ranged between 1000 and 3100 acfm.  In-situ
particle size data was obtained at A/C ratios of 3.2/1, 6.1/1 and 8.8/1.
Test periods lasted up to two hours during which time the reverse air
fan remained off.  No testing was carried out during boiler grate
pulling operations.

    The particle size distribution for the individual runs was averaged
at each of the three levels of A/C as shown in Figure 16.  The comparison
of this data indicates that about 57% of the particulate by weight was
less than three microns at the lowest A/C.  The two higher A/C levels
showed 54 and 49%, respectively, of the particulate, by weight, was less
than three microns.

    The mass mean particle diameters were 2.55, 2.7 and 3.05 respec-
tively.  The performance of the Gore-Tex on sub-micron particles seemed
essentially the same at the three levels of A/C.

    Average outlet concentration, cumulative percent and penetration by
particle size are given in Table 18.  Figure 17 shows outlet concentration
for four particle sizes versus A/C ratio.  Like the Teflon felt case, the
largest particle size fraction, i.e. the total of all sizes greater than
9.35 microns, are most sensitive to increases in A/C ratio and an increase
in velocity results in an increase in the outlet  concentration.

    Figure 18 shows penetration versus particle size.  Three curves are
shown, one for  each of the A/C ratios.  These curves indicate an increase
in penetration  as  the fractions become smaller from  10 microns down to
about h micron.  Below h micron there is a sharp  decrease in penetration
for all three A/C  ratios.  The performance of the Gore-Tex on sub-micron
particles seems  essentially the same at the three levels of A/C.

                                    -  61  -

-------
            Figure IS
      ©0
      (DO   _ . .
      0©oooooo
      00OOOOO
en
ro
      OXDOOQQQQCD
              t
• Damper -

Opening
            Cell 4
KEY;


O Gore-Tex


 Plugs
         Positioning of Gore-lex Bags

-------
                          Figure 16

              Outlet Particle Size Distribution
    10

     8
c
o
u

-------
                                              Table 18
Outlet Concentration, Cumulative %



Air-to-Cloth Ratio
Avg. CD
Part.
Diam.
urn
>9.35
6.05
4.03
2.81
1.78
.92
.56
.38
<.38
TOTAL
Avg. C2)
Outlet
Cone.
Gr./SCFD
.00071
.00051
.00083
.00067
.00071
.00039
.00040
. 0001 0
.00016
.00448


Cuml .C3>
%
100
84.16
72.78
54.25
39.29
23.44
14.73
5.80
3.57


3.2/1


Pene- (4)
tration
.0049
.0132
.0314
.0521
.0556
.0909
.1481
.0337
.0373
.0179
and Penetration
Gore-Tex/Nomex
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00116
.00016
.00045
.00057
.00050
.00031
.00029
.00006
.00017
.00367


Cuml .
%
100
68.39
64.03
51.77
36.24
22.62
14.17
6.26
4.63

6.1/1


Pene-
tration
.0080
.0042
.0170
.0443
.0392
.0723
.1074
.0202
.0396
.0146
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00173
.00082
.00149
.00078
.00124
.00036
.00068
.00012
.00023
.00745


Cuml .

100
76.78
65.77
45.77
35.30
18.66
13.83
4,70
3.09

8.8/1


Pene-
tration
.0119
.0213
.0564
. .0606
.0972
.0839
.2519
.0404
.0536
.0297
1.  Corrected for particle density (2.6 grams/C.C.) and stack temperature.
2.  At 3.2/1 three (3) tests averaged, at 6.1/1 six (6) tests averaged, at 8.8/1  two (2) tests
    averaged.
3.  Percent of total  outlet concentration less than size indicated.
4.  Penetration based on average inlet concentration at corresponding impactor stages.

-------
   .0025
o  .0020
CO
£
CD
c  .0015
o
Ol
o
c
   .0010
OJ
   .0005
                              Figure 17


                 Outlet Concentration by Particle Size

                                  vs.

                          Air-to-Cloth Ratio
               KEY:


            Q    .38 um

            Q   2.81  um


            /v   6.05 um
                                    Case:  Gore-Tex/Nomex
                 Total  of All

                 Sizes  >9.35 um
                    2468

                        Air-to-Cloth Ratio (ACFM/Ft.2)
                                      - 65 -

-------
                      Figure 18
           Penetration vs. Particle Diameter
       Filter Media:  Gore-Tex/Nomex
 .01
CM
.02
 .04  .06 .08 1.0      2
Particle Diameter, Microns
                                                          8 10
                             . 66 -

-------
     The data would seem to indicate that we experienced the heaviest dust
penetration at either end of the A/C spectrum.

     Pressure drop comparisons at the three levels of A/C are presented in
Figure 19.  Examples of typical cleandown cycles are shown in Figure 20.

     Because of the failures of the Gore-Tex due to vibrational  fatigue
                                (•})
experienced in the earlier work,  ' certain precautionary steps  were
taken to alleviate this problem.  The bags were fixed on a rigid cage,
i.e. strips were v/elded lengthwise along each side of the spiral cages
to reduce flexing.  The cages were also painted to provide a smooth
surface.  In addition, the bottoms of the bags were strapped to  tie rods
which had been placed beneath Cells 3 and 4.  The strapping of the
bottoms of the bags was to reduce the sway which occurs when the light-
weight bags are subjected to the gas flow through the baghouse.

     After forty-eight hours run time the bags were inspected and
appeared in good condition, a 1/32" - 1/16" friable dust had built up
on the bags and there was no evidence of pearling.

     After sixty-eight (68) hours four damaged bags were removed.  The
bottoms of the bags had ripped directly above the seam.  This tear was
also just above the strap which was provided for securing the bag to the
tie rod.  The bags were inspected daily thereafter and after twenty-six
additional hours, two more were found to be damaged.  In both cases, the
bag failures were discovered after running at the highest air-to-cloth
level.

     One possible explanation for the failures is that in securing the
bottom of the bags in a fixed position they were subjected  to unusual
stress at the high gas velocities.

     Thus, the main problem associated with Gore-Tex bags,  that of dura-
bility, remains unresolved.  Obviously before Gore-Tex bags can be
considered seriously as a viable filtering alternative, this problem must
be  corrected.
                                   - 67 -

-------
                              Figure  19


                      Pressure  Drop  Across  Bags
                                  vs.
                          A1r-to-Cloth  Ratio
  10
   8
 t/i
 01
JC
 CJ
en
ic
CO
10
o

I

e *
(U
           Case:   Gore-Tex/Nomex
Q  After  2  Hr.  Test

A  Before Cleandown

Q  After  Cleandown
                     Reverse Air Volume  3200  ACFM
                 3                 6                 9

                   Air-to-Cloth Ratio (ACFM/Ft.2)
                                    - 68 -

-------
   8-
to


I
                                Figure 20


                         Typical Cleaning Cycles





                        Case:    Gore-Tex/Nomex
                                A/C 8.8/1
u
e
Q
«n
vt

t
Q.
                                A/C 6.1/1
Reverse Air Volume 3200 ACFM
Before Cleandown

After Cleandown
                             B           C

                             Cleaning Cycles
                                            D
                                    -  69 -

-------
Dralon-T
     Twenty-six Dralon-T bags were placed in Cell 4 (See Figure 21 for
bag positioning).

    Inlet flue gas volumes ranging from 980 to 2,800 acfm and A/C levels
of 3.3/1, 6.1/1 and 8.7/1 were explored.

    Average particle size data indicates that 47% of the material pene-
trating the bags was less than 2 microns at the lowest A/C, 54% was less
than 2 microns at 6.1/1, while only 44% was less than 2 microns at an
A/C of 8,7/1.

    The mass mean particle diameters were 2.8, 1.62 and 2.5 microns for
the air-to-cloth ratios in ascending order.  The size distribution data
is presented in Figure 22.

    As is evident in Table 19, Dralon-T exhibited greater filtering
capabilities as the A/C ratio increased.  This result is further
supported by Figures 23 and 24 which show that both overall and particle
size efficiency improved as the A/C ratio increased.

    Pressure drop comparisons at the three levels of A/C are presented in
Figure 25.  Examples of typical cleandown cycles are shown in Figure 26.

Nomex Felt
    Thirty bags were positioned in Cell 4 as per Figure 27.  The reverse
air fan was off during testing periods.  Particle size and concentration
data was obtained at air-to-cloth levels of 3, 6 and 8.5 to 1.

    A numerical average of the particle size data for the three levels of
air-to-cloth is presented in Figure 28.

    The curves indicate that the dust penetration by particle size was
essentially the same for the three levels of air-to-cloth, with 43% of
                                    - 70 -

-------
     .Figure 21
  .   .
OCDOOOOOCDQ
(D0OOOO(DO(D
CDCDOOQOOOCD
          •Damper-

          Opening
      Cell 4
KEY;

O Ora Ion T


(D P
   Positioning of Oral on T Bags

-------
        10,.
                               Figure 22


                   Outlet Particle Size Distribution


                              Dralon  T


              Note:  Corrected for Density and Temperature
 to
 c
 o

 u
 
-------
                                                    Table 19
CO

I
Outlet Concentration, Cumulative %
and Penetration
Oral on T
Air-to-Cloth Ratio 3.3/1
Part.
Diam.
urn
>9.37
5.86
3.89
2.7
1.73
.89
.55
.36
<.36
TOTAL
Avg. (2)
Outlet
Cone.
Gr./SCFD
.00122
.00106
.00144
.00133
.00114
.00092
.00061
.00046
.00050
. 00868
% '
100
85.94
73.73
57.14
41.82
28.69
18.09
11.06
5.76
Pene- (4)
tration
.0084
.0275
.0545
.1033
.0893
.1873
.2559
.1549
.1166
.0346
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00202
.00039
.00048
.00060
.00087
.00094
.00066
.00048
.00038
.00682
Cuml .
100
70.39
64.67
57.63
48.83
36.07
22.29
12.61
5.57
6.1/1
Pene-
tration
.0139
.0101
.0182
.0466
.0682
.1911
.2444
.1616
.0886
.0272
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00144
.00052
.00055
.00051
.00073
.00074
.00055
.00034
.00022
.00560
Cuml .
of
fO
100
74.29
65.00
55.18
46.07
33.03
19.82
10.00
3.93
8.7/1
Pene-
tration
.0099
.0135
.0208
.0396
.0572
.1504
.2037
.1145
.0513
.0223
        1.   Corrected for particle density (2.6  Grams/C.C.)  and  stack  temperature.
        2.   At 3.3/1  two (2)  tests averaged,  at  6.1/1  six  (6)  tests  averaged,  at  8.7/1  two  (2)  test  averaged
        3.   Percent of total  outlet concentration  less than  size indicated.
        4.   Penetration based on average inlet concentration at  corresponding  impactor  stages.

-------
                               Figure 23


                Outlet Concentration by Particle  Size


                                  vs.


                          Air-to-Cloth Ratio
               Case: Oral on T
   .0020
 in
•c
 J_
cs


 '  .0015
-M
(D

-M
G
9.37 um
                      3                 6


                Air-to-Cloth Ratio (ACFM/Ft.2 )
                                      - 74 -

-------
                        Figure 24

            Penetration vs. Particle Diameter
           Filter Media:  Oral on T
                                             \    '   I  I  .  I I I
0,1
0.2
0.4   0.6    1.0       2       4
        Particle Size, nitrons
                                                         8  10
                              - 75 -

-------
                       Figure 25

               Pressure Drop Across Bans

                           vs.

                   Air-to-Cloth Ratio
       Case:   Oralon T
in

-------
                                 Figure 26^

                         Typical  Cleandown Cycles

                                 Oralon T
 V)
 O)
 
 e
0)
x:
o
c
Q.
e
Q  £
A/C 8.7
                              A/C  3.3
                Cleaning duration  7  sec.
                Cleans once every  140  sec.
                Reverse Air Volume   3800  ACFM
                      Key:
                      D  Before Cleandown
                      O  After Cleendown
                            B             C
                            Cleaning Cycles
                                   - 77 -

-------
       figure 27
00

f
            _^
  (DOOOQOO0
00OOOOOO®
©(DOOOOOO©
       0.0000)
          Damper .
          Opening
      Cell 4
   Positioning of Nomex Felt Bags
                 KEY:
                         Nomex Pel t

                         Plugs

-------
   10

    8
tn

I
o
OJ
N
T-
co

0)

o
•r—
•P

10
Q.
  no

    .8


    .6



    .4

    .3
                         Figure 28

            Outlet Particle Size Distribution

                         Nomex Felt



Note:  Corrected for Density and Temperature
Key:

A/C Ratios

 O3/1
 O6/1
 D8.5/1
                    10
                 20
40
60
80
                  % Less Than Size Indicated
                                 - 79 -

-------
the participate, by weight, less than 2 microns at A/C of 3 to 1 and
5.8/1 and 54% less than 2 microns at 6/1.

     When compared with the other bag materials, Nomex showed the greatest
propensity for filtering efficiency.

     Average outlet concentration, cumulative percent and penetration by
particle size, for the three levels of air-to-cloth are listed in Table 20.
Figure 29 shows outlet concentration by  particle size.

     Penetration vs. particle diameter is plotted in Figure 30.  Again
the  higher efficiency for the larger particles is evident.  All three
curves indicate a significant decrease in penetration of the two smallest
fractions.

     In addition to the aforementioned tests, a number of other parameters
were studied with Nomex felt as  the filter media.  These included the
effect of duration and volume of cleaning air on particle size efficiency,
cleandown and operating pressure drop.

     To determine the effect reverse air volume has on filtering effi-
ciency, the Andersen sampler was utilized in obtaining in-situ particle
size data at air-to-cloth ratios of 3.4, 6.4 and 8.9 to 1 and reverse
air  volumes of 1,400, 3,160 and  4,000 acfm.  The reverse air fan was
employed continuously (including during  sampling periods).  Duplicate
tests were performed at each combination of air-to-cloth ratio and
reverse air volume.  Outlet concentration, cumulative percent and pene-
tration by particle size for three levels of reverse air at A/C ratios
of 3.4/1, 6.4/1 and 8.9/1 are given in Tables  21, 22 and 23 respectively.

     As shown in Figure 31, the  data indicates that higher collection effi-
ciencies are possible when the reverse air fan is not employed and that
varying the volume of reverse air (once  in operation) has little effect
on overall efficiency.
                                    - 80  -

-------
                                                        Table 20
j
00
Outlet Concentration, Cumulative %
Nomex Felt - Zero
Air-to-Cloth Ratio 3/1
Avg.^
Part.
Diam.
urn
>8.98
5.62
3.76
2.68
1.73
.85
.52
.35
<.35
TOTAL
Avg. <2>
Outlet
Cone.
Gr./SCFD
. 00064
.00017
.00032
.00029
.00027
.00020
.00011
.00008
.00008 -
.00216
Cuml.(3) Pene- (4)
%
100
70.37
62.5
47.68
34.26
21.76
12.5
7.4
3.7
tration
.0044
.0044
.0121
.0225
.0212
.0406
.0407
.0269
.0186
.0086
Air-to-Cloth
Avg.
Outlet
Cone.
Gr./SCFD
.00074
.00021
.00037
.00026
.00048
.00023
.00034
. 0001 0
.00022
.00295
Cuml
%
100
74.
67.
55.
46.
30.
22.
10.
7.
RA
and Penetration

Ratio 6/1



9
80
25
44
17
37
85
46
Pene-
tration
.0051
.0045
.0140
.0202
.0376
.0467
,1259
.0337
.0513
.0118
Air-to-Cloth Ratio
Avg.
Outlet
Cone.
Gr./SCFD
.00171
.00064
.00109
.00065
.00084
.00032
.00043
.00007
.00019
.00594
1. Corrected for particle density (2.6 Grams/C.C.) and stack temperature.
2. At 3/1 three (3) tests averaged, at 6/1 three (3) tests averaged, at 8.5/1 two
3. Percent of total outlet concentration less than size indicated.
4, Penetration based
on av
erage inlet
concentration
at
corresponding
Cuml
%
100
71.
60.
42.
31.
17.
11.
4.
3.
(2)



21
44
09
14
0
62
4
2
8.5/1
Pene-
tration
.0118
.0166
.0412
.0505
.0658
.0650
.1593
.0236
.0443
.0237
tests averat
impactor stages.

-------
     .002
                   Figure  29


    Outlet Concentration  by  Particle  Size


                      vs.


            Air-to-Cloth  Ratio



Case:   Nomex Felt
     .001
    .0005
•a
t~
tr
U
C
o
o
    .0002
    .0001
   .00005

        1
                                  KEY;

                                  .35 urn

                              Q 2.68 um


                              A 5.62 um

                              O Total  of All  Sizes
                                  >8.98 um
                                       v

                            Air-to-Cloth (ACFM/Ft.2)
                                     - 82  -

-------
                          Figure 30


              Penetration vs. Particle Diameter
     0.2r
           Filter Media:   Nomex  Felt
c
o
•I—
-M
rtj

-1-5
O)
C
0)
a.
   .001
                0.2
0.4  0.6 0.8          2

  Particle Diameter, urn
8  10
                                     - 83 -

-------
                                                      Table 21
I
OD


Outlet
Concentration, Cumulative % and Penetration
Norn ex Felt
- Three Levels Reverse Air
A/C 3.4/1
c\ \
Avg.(1)
Part.
Diam.
urn
>9.31
5.89
3.88
2.73
1.82
.89
.54
.36
< .36
TOTAL
Reverse
Avg. (2)
Outlet
Cone.
Gr./SCFD
.00126
.00041
.00046
.00019
.00048
.00041
. 00030
. 00039
. 00027
.00417
Air 1400
Cuml f3)
100
69.77
59.94
48.91
44.. 3 5
32.84
23.01
15.82
6.47

ACFM
Pene-(4)
tration
.0087
.0106
.0174
.0148
.0376
.0833
.1111
.1313
.0629
.0166
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00110
.00033
.00029
.00016
.00021
.00022
. 00006
.00013
.00007
.00257
Air 3100
Cuml .
100
57.19
44.35
33.07
26.84
18.67
10.11
7.78
2.72

ACFM
Pene-
tration
.0076
.0086
.0110
.0124
.0165
.0447
.0222
.0438
.0163
.0102
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00109
.00034
.00031
.00029
.00033
.00028
.00020
.00017
. 00009
.00310
Air 4000
Cuml.
100
64.83
53.86
43.86
34.51
23.86
14.83
8.38
2.9

ACFM
Pene-
tration
.0075
.0088
.0117
.0225
.0259
.0569
.0741
.0572
.0210
.0124
          1.  Corrected for particle density  (2.6 grams/C.C.) and stack temperature.
          2.  Two  (2) tests averaged for all  cases.
          3.  Percent of  total outlet concentration less than size indicated.
          4.  Penetration based on average inlet concentration at corresponding impactor stages.

-------
                                                    Table 22
I

00

Outlet
Concentration, Cumulative % and Penetration
Nomex Felt
- Three Levels Reverse Air
A/C 6.4/1
Reverse
Avg. (2)
Outlet
Cone.
Gr./SCFD
.00133
.00096
.00076
.00080
.00037
.00049
.00003
.00041
.00010
.00525
Air 1400
Cum! f3)
%
100
74.67
56.38
41.90
26.66
19.61
10.28
9.71
1.9
ACFM
Pene-(4)
tration
.0091
.0249
.0288
.0622
.0290
.0996
.0111
.1380
.0233
.0209
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00182
.00078
.00073
.00073
.00061
.00058
.00040
. 00054
.00029
.00648
Air 3100
Cum! .
%
100
71.92
59.88
48.61
37.34
27.93
18.98
12.8]
4.48
ACFM
Pene-
tration
.0125
.0203
.0276
.0567
.0478
.1179
.1481
.1818
.0676
.0258
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00107
.00074
.00094
.00071
.00065
.00052
.00051
.00044
.00043
.00601
Air 4000
Cum! .
%
100
82.20
69.89
54.25
42.44
31.62
22.97
14.48
7.15
ACFM
Pene-
tration
.0074
.0192
.0356
.0552
.0509
.1057
.1889
.1481
.1002
.0240
        TOTAL

        1.  Corrected for particle density (2.6 grams/C.C.) and stack temperature.
        2.  Two (2) tests averaged for all cases.
        3.  Percent of total outlet concentration less than size indicated.
        4.  Penetration based on average inlet concentration at corresponding impactor stages.

-------
                                                      Table 23
00
01
Outlet Concentration, Cumulative % and Penetration


Nomex Felt
- Three Levels Reverse Air
A/C 8.9/1
Reverse
Avg. (2)
Outlet
Cone.
Gr./SCFD
.00322
.00141
.00186
.00145
.00159
.00038
.00069
.00008
.00020
.01088
Air 1400
Cum! .(3)
%
100
70.41
57.45
40.35
27.02
12.41
8.92
2.58
1.84
ACFM
Pene-(4)
tration
.0221
.0366
.0704
.1127
.1246
.0772
.2556
.0269
.0466
.0434
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00226
.00102
.00175
.00187
.00217
.00070
.00059
.00053
.00020
.01109
Air 3100
Cuml .
%
100
79.62
70.42
54.64
37.78
18.21
11.90
6.58
1.8
ACFM
Pene-
tration
.0155
.0265
.0662
.1453
.1701
.1423
.2185
.1785
.0466
.0442
Reverse
Avg.
Outlet
Cone.
Gr./SCFD
.00252
.00117
.00131
.00114
.00053
.00065
.00007
.00042
.00002
.00783
Air 4000
Cuml .
%
100
67.81
52.87
36.14
21.53
14.81
6.51
5.62
.26
ACFM
Pene-
tration
.0173
.0304
.0496
.0886
.0415
.1321
.0259
.1414
.0047
.0312
         1.  Corrected for particle density (2.6 grams/C.C.) and stack temperature.
         2.  Two (2) tests averaged for all cases.
         3.  Percent of total  outlet concentration  less than size indicated.
         4.  Penetration based on average inlet concentration at corresponding impactor stages.

-------
                               Figure 31


                Outlet  Concentration vs.  Air-to-Cloth

              Ratio  for Different  Levels  of Reverse Air
                  Case:  Nomex  Felt
     .0125
     .0100
o
to
to
c:

-------
     Figures 32, 33, 34 and 35 further illustrate that air-to-cloth
ratio, rather than varying the level of reverse air volume, is the key
parameter in predicting baghouse efficiency.  It is significant that
these four figures show an increase in outlet loading with increasing
velocity for the three larger fractions while the outlet loading for
the smallest fraction do not seem to increase above an A/C ratio of 6/1.

    The reverse air volume has a significant influence on the operating
pressure of the baghouse.  Figure 36 demonstrates quite vividly that
increasing the reverse air volume decreases the pressure drop across the
bags.

    Tests were conducted on duration of cleaning time.  These studies
were made at 7, 15 and 25 seconds.  As shown in Figure 37, no signifi-
cant improvement in the cleandown pressure drop was observed when the
cleaning duration was increased.  Obviously, there is a point where
duration of cleaning time has a significant influence on bag cleaning
efficiency; apparently this takes place at some duration less than 7
seconds.

    The Nomex bags were subjected to a total of 195 hours on stream.
Table 24 shows a comparison of Nomex bag characteristics for new bags
and bags exposed for 195 hours.  The physical property measurements show
a significant 40-60% reduction in tensile level which undoubtedly results
from hydrolytic attack by the S02-S03-H20 in the .flue gas.  Better than
90% property retention would be expected for Nomex in a neutral environ-
ment.  The drop in inherent viscosity (a measure of chain scission)
confirms the hydrolytic attack theory.

    The hydrolytic attack was anticipated based on earlier studies! '
An attempt was made to minimize the degeneration of Nomex felt bags by
coating the bags with lime at the time of installation and daily there-
after.   The lime coating was accomplished by introducing 100 Ibs.  of
lime into the house thru the clean air port while the system fan was
running.   The liming procedure was conducted during the daily start-up

                                   - 88 -

-------
    .0006
                       Figure 32


Outlet Concentration  (Particle Diameter .3^6 Microns)
                         vs.

Air-to-Cloth Ratio at Different  Levels of Reverse Air


 Key:
             ney:
           ""RTD
     evels
    .0005
       *
 Q 1400

 O 3100

 O 4000
O
to

in
c

id

cfl
i
    .0004
    .0003
a

•P
c
0)
O

§
a*
r^
•P
a
o
    .0002
    .0001
Case:  Nomex Felt
                     369


                    Air-to-Cloth Ratio   (ACFM/Ft.  2)


               * Particle Diameter  .35 Microns  for Zero Reverse Air
                                     -  89 -

-------
                               Figure 33


        Outlet Concentration  (Particle Diameter  2.73  Microns
                                   .vs.
        A1r-to-Cloth  Ratio  of Different Levels of Reverse Air
                        Case:  Nomex  Felt
    .0025
o
CO

to
c
C9
C
O

4J

2
o

o
o
Ctf

+J
=1
o
.0020
.0015
    .0010
    .0005
   KEY;

 RA Levels  (ACFM)

      0

     1400

O   3100

O   4000
                           Air-to-Cloth Ratio (ACFH/Ft/)
                                 - 90 -

-------
o
to
•v^
M
C
s-
C3
C
o
f
•P
(0

•P
C

-------
   .003
                               Figure 35

       Outlet Concentration  (Particle  Diameter> 9.31  Microns)

                                 vs.

       Air-to-Cloth Ratio At Different Levels  of Reverse  Air
   .003
   .002
o
1/1
It}
i-
C3
4J
rtJ
CJ

O
.002
   .0015
   .0010 -
   .000!
        Case:  Nomex Felt

          Key:
          RA Levels
          (ACFM)
              n  1400
              O  3100
              O  4000
                      0*
             _L
                           J.
       1            3                6

            Air-to-Cloth Ratio (ACFM/Ft. 2  )

      * Particle Diameter>8.98 for Zero Reverse Air
                                - 92 -

-------
                             Figure 36


                           Pressure Dro£

                               vs.

             Air-to-Cloth for 3 Levels of Reverse Air


          (Values obtained just after cleandown during normal
           cleaning cycle.*)
         CASE:   Nomex Felt
VI

O


I

D.
O

O
to
tn
(U

0.
     KEY:

Reverse Air Level
    (acfm)
    D
    O

    O
1400

3100

4000
                                      *Cleaning Cycle - 7 Seconds
                                       Cleaning Every 140 Seconds
                       468

                    Air-to-Cloth Ratio (ACFM/Ft.2)
          10
                                  -  93  -

-------
i

UD
         V)
         01
|

10

o
           2.0
            1.5
        o 1.0
        •r-
        •M
        O
O>
OC

Q.
O

o  0.5
        a>

        a.
                        7 Sec
                   i   1	I  I  1  I
                                              Figure 37

                                     Comparison of  Bag  Cleaning at

                                        3 Cleaning  Durations

                                              Filter Media:
                AB  CDE   FG  HIJ
                                                       15 Sec.
                                             AB  CDE   FGH  I  J
                                                                                                   25  Sec.
                                                                                                  i
AB  CDE  FGH   I   J
                                              Cleaning Cycles

-------
                               Table 24
                  Analysis of Nomex Felt Properties*
                                                  Properties
                                         New Bag
          Exposed 195 Hrs
 Weight, Oz./Yd/
 Thickness,  Mils
 Strip Tensile (MD/XD)**
   Breaking  Strength,  Lbs./In.
   Elongation, %
   Work-to-Break, Lbs./In.
 Inherent Viscosity
15.9
99
 14.7
112
74/211
25/53 '
13/66
57/125
14/33
5/26
 1.5
  0.78
 *Analysis  conducted October 10,  1974  by  H.  H.  Forsten,  E.  I.  duPont,
  Wilmington,  Delaware
**Machine Direction and Cross Direction
                                     - 95 -

-------
procedure.  Due to the program constraints the lime coating was stopped
after 57 hours on stream.  Analyses of coated vs. uncoated Nomex bags
showed very little difference between the two with respect to hydrolytic
attack.  This observation was due to the short exposure time and there-
fore no conclusions can be made regarding lime coating to retard
chemical degradation.

    The bags were routinely checked throughout their usage and never
exhibited any signs of wear.  A dust layer of %" was attained after 20
hours and remained about the same for other observations during the
program.  Nomex, more than any other material, exhibited evidence of
pearling  in the dust layer.
                                  - 96 -

-------
                      ECONOMIC CONSIDERATIONS

     An economic analysis was performed similar in scope and methodology
to that accomplished under Contract No. 68-02-1093.^  The cost figures
presented herein are generally higher due to design improvements in the
baghouse and inflation.  One additional variable, introduced for calcu-
lating operating and annualized cost, changed slightly the relationship
between the cost curves.  This variable is pressure drop across the
house.  Actual  observed pressure drops for each bag material were used
here whereas in the prior work equal assumed values were employed.

    The economics of applying a fabric filter to the coal fired boilers
at Kerr Industries were evaluated and comparative costs for an electro-
static precipitator (ESP) were developed.  Installed costs, flange-to-
flange hardware costs plus installation costs, were determined for a
fabric filter dust collector sized for 70,000 ACFM at 350° F.  Instal-
lation costs were based on in-house engineering cost estimates.  This
was done for five fabric materials:  Nomex Felt, Gore-Tex/Nomex, Gore-
Tex/Gore-Tex, Dralon-T and Teflon Felt.  Air-to-cloth (A/C) ratios
considered for each fabric were 2.9, 5.8, 8.9 and 11.3.  Fabric filter
 f
(baghouse) sizes versus air-to-cloth ratios are given in Table 25.
Annual operating and annualized (total costs of control) costs were also
determined for each case.  The methods used are those presented by
                    I A)
Edmisten and Bunyardx '.  Example calculations for computing annua
operating and annualized costs may be found in the Appendix.
    The installed costs for a fabric filter employing Nomex felt were
based on the following assumptions.  First, that it is necessary to
insulate the house, hopper and inlet ducts and second that continuous
lime coating of the bags is required.  Capital costs were found to be
$244,870, $133,590, $109,560 and $99,960 respectively at air-to-cloth
ratios of 2.9, 5.8, 8.9 and 11.3, or on the basis of dollars per ACFM
$3.50, $1.91, $1.57 and $1.43.  These cost estimates were based on a
bag price of $17.30 each (vendor quote - September, 1974).

                                   -  97  -

-------
                          Table 25

       Fabric Filter Unit Size vs. Air-to-Cloth Ratio
Air-to-Cloth        Number          Number         Net Filter
    Ratio           of Cells        of Bags        Area Sq. Ft.


    2.9*               60            2,160            23,980

    5.8                30            1,080            11,990

    8.9                20              720             7,850

   11.3                16              576             6,200
*Based on two (2) units; each with 30 cells, 1,080 bags and 11,990
 square feet net filter area.
                                - 98 -

-------
      Installed costs for the case of Gore-Tex on Nomex backing are
$218,120, $120,220, $98,250 and $89,460.  On a $/ACFM basis these costs
are $3.12, $1.72, $1.40 and $1.28.  Costs assume no insulation and no
lime coating are required.  These costs were based on a bag price of
$22.00 each (vendor quote - September, 1974).

     The Gore-Tex on Gore-Tex case installed costs are $267,800, $145,060,
$114,810 and $102,710.  Or on a $/ACFM basis they are $3.83, $2.07, $1.64
and $1.47.  Again it was assumed that no insulation and no lime coating
would be required.  The price used for Gore-Tex/Gore-Tex bags was $45.00
each (vendor quote -September, 1974).

     Installed costs for Oral on T were $192,200, $107,260, $89,610 and
$82,550 or $2.75, $1.53, $1.28 and $1.18 on a $/ACFM basis.  Costs assume
no insulation and no Hme coating required.  The price for Dralon T bags
was $10.00 each (vendor quote - September,  1974).

     Finally, installed costs for a baghouse employing Teflon felt
(Style 2663) were determined.  Because of the quick release properties
of the Teflon and its resistance to chemical attack, it was assumed that
no insulation and no lime coating would be required.  The capital costs
were found to be $332,600, $177,460, $136,407 and $119,990.  On a $/ACFM
basis these costs are $4.75, $2.54, $1.95 and $1.71.  These costs were
based on a bag price of $75.00 each (vendor quote- September,  1974).

     A graphical comparison of the installed costs for the five bag
materials is made in Figure 38.  Teflon felt is seen to be the most
expensive cost for all four (4) air-to-cloth ratios investigated and
Dralon T is seen to be the least expensive.  The curves draw closer
together as the air-to-cloth ratio increases.  Obviously this is due to
a decreasing percentage of the total costs attributed to the bags as the
size of the house decreases.  Table 26 shows the cost of the bags as a
percentage of installed costs.
                                    - 99 -

-------
                                Figure 38
                   Installed Costs vs. A1r-to-C1oth Ratio
     350-
     300-
                                                       KEY:
                                                    Nomex Felt
                                                    Gore-Tex/Nomex
                                                    Gore-Tex/Gore-Tex
                                                    Oral on T
                                                    Teflon Felt
 «o
 o
 o
CO
 o
 I/}
 to
 O
01
ria
v>
     250
     200
     150
    100
     50.
                               6           8
                           Air-to-Cloth  (ACFM/Ft.2)
                                                       10
12
                                    -  100  -

-------
                                Table 26

                 Bag Costs  as  Percent of  Installed  Cost
                       Installed Costs
                  Bag Costs
             % of Installed
             Cost for Bags
Nomex
   2.9
   5.8
   8.9
  11.3

Gore-Tex/Nomex
   2.9
   5.8
   8.9
  11.3

Gore-Tex/Gore-Tex
   2.9
   5.8
   8.9
  11.3

Oral on T
   2.9
   5.8
   8.9
  11.3

Teflon
   2.9
   5.8
   8.9
  11.3
244,866
133,591
109,563
 99,952
218,118
120,217
 98,247
 89,459
267,798
145,057
114,807
102,707
192,198
107,257
 89,607
 82,547
332,598
177,457
136,407
119,987
 37,368
 18,684
 12,456
 9,965
 47,520
 23,760
 15,840
 12,672
 97,200
 48,600
 32,400
 25,920
 21,600
 10,800
  7,200
  5,760
162,000
 81,000
 54,000
 43,200
15.3
14.0
11.4
10.0
21.8
19.8
16.1
14.2
36.3
33.5
28.2
25.2
11.2
10.1
 8,0
 7.0
48.7
45.6
39.6
36.0
                                    -  101  -

-------
     The installed costs for an electrostatic precipitator capable of
handling 70,000 ACFM at 350° F were determined  for three  (3) levels of
efficiency.  These were 90, 95 and 99% removal  efficiency.  The basis
for development of these costs is provided  in the Appendix.  The corre-
sponding installed costs were found to be $412,970,  $471,590 and
$600,100.  These  are shown 1n Figure  39.  On a  $/ACFM  basis, these costs
are $5.90, $6.74  and $8.57.  Thus the installed costs  of  the electro-
static  precipitator, even at 90% collection efficiency, are higher than
all cases  for  the fabric filter; the  greatest cost differential being
Teflon  with  an air-to-cloth ratio of  2.9 at $332,600.  The ESP capital
costs may  have been more favorable if the coal  utilized for the case in
point had  not  been low in sulfur.  In fact, several  of the ESP manu-
facturers  who  were asked to furnish quotes  for  the Kerr boilers refused
to quote due to the low sulfur coal.

    Operating  costs were determined for the five (5) bag  materials.
Four  (4) year  bag life was assumed for all  fabrics.  The  cost of replacing
the bags was divided equally over the four  years and treated as an annual
operating  cost equivalent to 25% bag  replacement per year.  The actual
pressure drops observed for each fabric at  the  different  air-to-cloth
ratios, plus two  inches w.g. for the  inlet  duct and  house, were used for
determining  power costs.  These costs are presented  in Figure 40.

    The curves for operating costs are very different  except for the two
types of Gore-Tex which exhibit similarly shaped curves.  The shape of
the curve is determined ty the two variables used in the  equation for
computing operating costs, namely bag price and  pressure  drop (Ap).
Values for these are given in Table 27.   While  bag price  is constant
for a given  fabric the pressure drop increases  as the  A/C ratio increases.
The rate of Ap increase is  different for each  bag material except the
two Gore-Tex, thus the reason for the similarity of the two Gore-Tex
curves.   As can be seen in Table 27,  the Ap's for Gore-Tex/Nomex and
Gore-Tex/Gore-Tex are  identical.   Gore-Tex/Gore-Tex was not tested in
the pilot plant,  hence the Ap's  were assumed to be the same as Gore-
Tex/Nomex.

                                   -  102 -

-------
                                 Figure 39


                       Installed Cost vs. Efficiency
    6*0
             CASE:  Electrostatic Precipitator
 ^  500
 o
 o

CO
 o
 in
 O
 o

 -o
 0)
 to
 c
     400
                                           90% - $412,970

                                           95% - $471,588
                                           99% - $600,100
     300
      _L
                   90
      95

Efficiency %
100
                                     - 103 -

-------
                               Figure 40


             Annual 6pci»j»%1ng Costs vs. Alr-td-Cl6th  Ratio
    50
    40
 to

 CO

 •M
 in
 o
 o

 01
 a
 10
 t-
 (U
     30
20
                                                 KEY:


                                              Q  Tef1 on


                                              A  6ore-Tex/Gore-Tex

                                              Q  Nomex

                                              O  Gore-Tex/Nomex

                                                  Oral on
     10
                                6           8

                              Air-to-Cloth (ACFM/Ft.2)
                                                   10
12
                                       - 104  -

-------
                                   Table 27

                       Pressure Drop Values for Five Bag
                          Materials at Four A/C Ratios
                                                              (1)
   Bag Material            Bag Price        A/C Ratio      AP   In.  H?0
Nomex                        $17.30            2.9               3.5
                                               5.8               8.2
                                               8.9               8.5
                                              11.3               8.7
Gore-Tex/Nomex               $22.00            2.9               4.2
                                               5.8               5.3
                                               8.9               8.9
                                              11.3              11.0
Gore-Tex/Gore-Tex<2)         $45.00            2.9               4.2
                                               5.8               5.3
                                               8.9               8.9
                                              11.3              11.0
Dralon T                     $10.00            2.9               2.8
                                               5.8               6.0
                                               8.9               7.5
                                              11.3               8.1
Teflon Felt                  $75.00            2.9               2.5
                                               5.8               3.4
                                               8.9               5.9
                                              11.3               9.2
       Ap for each case is the operating pressure in Figure 52 plus
   two (2) inches pressure drop added to allow for pressure drop
   across the Inlet duct and the house.
       for Gore-Tex/6ore-Tex assumed to be the same as those for Gore-
     Tex/Nomex.
                                   - 105 -

-------
     As stated above, bag life for all five materials was assumed to be
four (4) years, equivalent to 25% bag replacement per year.  Operating
costs for Dralon T and Teflon felt were also determined for other
periods of bag life.  These were 1, 2, 3 and 5 years which correspond to
100%, 50%, 33 1/3% and 20% replacement per year.  Figures 41  and 42  show
the resultant curves for Dralon T and Teflon felt respectively.
Obviously, the shorter the bag life the higher the annual operating
costs.  It is interesting, however, that the curves for average bag  life
of three (3) years and greater are relatively close together.  Therefore,
the impact of bag life on operating cost is extremely significant up to
three  (3) years but for periods greater than three (3) years the costs
do not decrease as significantly with increasing bag life.  The same data
is presented in Figures 43 and  44, with annual operating costs vs.
percent bag replacement per year instead of A/C ratio.  Again the sharp
drop in costs is evident for the two shorter periods of bag life.  Also
the slope of the curve can be seen to increase as the size of the house
increases.

     Operating costs were also determined for an electrostatic precipi-
tator at 90, 95 and 99% collection efficiency (sample calculations in
appendix).  These costs were found to be $5,840, $6,380 and $8,150
respectively, see Figure  45.   Thus the ESP operating costs are lower
than all cases of the fabric filter, even for Dralon T with air-to-
cloth ratio of 2.9/1 at $9,880.    This difference is due primarily to
costs related to percent annual  bag replacement and higher pressure
drops in the fabric filter.

     The annualized costs or total  costs of control were developed from
the proceeding Installed and operating costs.  These results, shown in
Figure 46 were based on the following assumptions:  First, hardware and
installation costs are depreciated over fifteen (15) years.  Second,
the straight line method of depreciation (6 2/3 percent per year) is
used.  This method has the simplicity of a constant annual write-off.
Third, other costs called capital charges, which include interest, taxes,
                                   - 106 -

-------
                                   Figure 41

                                   Dralon T

                  Annual  Operating  Cost vs.  Air-to-Cloth  Ratio
                       for Different Bag Life Assumptions
    30i-
    25
                        1 Year,  Cost  Per Year  100%
                        2 Years, Cost Per Year 50%
                        3 Years, Cost Per Year 33 1/3%
                        4 Years, Cost Per Year 25%
                        5 Years, Cost Per Year 20%
V)

(U
O
O
o

X
O
o
 0)
«§-
 (O
    20
                                                             -O
    15
10
                              _L
                                      J_
_L
                              6           8          10
                        Air-to-Cloth Ratio (ACFM/Ft.2)
                                                             12
                                  - 107 -

-------
                                    Figure 42
   175T
   150-
   125
 to
   100
CO
 o
 X
 (/>

 8  75
 o
 «O
 ^ 50
 
-------
                                  Figure 43
                                  Dralon T
              Annual Operating Costs  vs. % Bag  Replacement
               Per Year at bifferent  Alr-to-Cloth  Ratios
    30
     25-
 CO
 i.
 to
 120
CO
 o
 V)
 O
 O
 en
 c
  
-------
    T75i-
     150
     125
 ia
 o
 O
CO
 o
 V)
 O
 u
 o>
 c
 
-------
                             Figure 45

               Annual  Operating Costs vs.  Efficiency
    8
           CASE:   Electrostatic Precipitator
o
Q
•M
10
O
O
(O

I
o
                                           90% - $5,840
                                           95% - $6,380
                                           99% - $8,150
                90
                                        95

                            Removal Efficiency %
100
                                  -  in  -

-------
    90 r-
    80
    70
 CO
 at
 ;= 60
 8
CO
 o
 W»
 o
 N
    50
    40
    30
    20
                                   Figure 46

                   Annualized  Costs vs.  Air-to-Cloth Ratio
    KEY:
O  Teflon
&  Gore-Tex/Gore-Tex
Q  Nomex
Q  Gore-Tex/Nomex
    Oralon
                              6            8          10
                             Air-to-Cloth  (ACFM/Ft.2)
                                 - 112 -

-------
insurance and other miscellaneous costs, are assumed equal  to the amount
of depreciation, or 6 2/3% of the initial  installed cost.   Therefore,
depreciation plus these other annual  charges amount to 13  1/3 percent
of the installed costs.  See example calculation of annualized cost in
the Appendix.

     Annualized cost for the ESP case at 90, 95 and 99% collection
efficiencies were determined to be $60,766, $69,097 and $87,960 respec-
tively, see Figure 47.  The annualized cost for 90% is higher than all
cases of the fabric filter at A/C ratio of 5.8 and greater.  Even at
A/C ratio of 2.9 the fabric filter annualized cost is less than that
for the ESP at 90% for three (3) of the five (5) bag materials with only
Teflon and Gore-Tex/Gore-Tex being higher.  All costs are  tabulated in
Tables 28 and 29 for easy reference.

     A cursory attempt was made at determining the effect  of accelerated
depreciation on annualized cost.  The resultant costs are  presented in
Table 30 and Figure  48.  Accelerated depreciation was based on straight
line depreciation over five (5) years (20% per year) plus  6 2/3 percent
used again for other capital charges.  This basis for capital charges
was used only to be consistent and is not meant to be indicative of the
real case.  To establish a realistic factor for "other capital charges"
would involve a detailed cash flow analysis with the result applicable
only to a single case.  The basis chosen was discussed with by Mr. F.  L.
       C4\
Bunyard   , EPA Cost Analysis Section.  It was felt that the comparison
of accelerated and standard depreciation was worthwhile as long as the
basis was clearly established.   The net result as seen in Figure 48 was
an accentuation of the difference between annualized costs for fabric
filters as opposed to electrostatic precipitators.

     Finally, outlet loading versus annualized cost is presented in
Figure 49 for the fabric filter employing four  (4) types of bags and  the
electrostatic precipitator.  This comparison indicates that the fabric
filter may be capable of competing with the electrostatic precipitator
                                   -  113  -

-------
   90r
                       Figure 47


           Annualized Costs vs.  Efficiency
   85
CASE:  Electrostatic Precipitator
   80
i.
(O
o
O
   75
in
-M
in
O
o
-o  70
   60
                                               90% - $60,766
                                               95% - $69,097
                                               99% - $87,960
   55
                 90
                             95

                   Removal Efficiency  %
!00
                                  - 114 -

-------
                                                     Table 28
01
I
       Nomex
       Gore-Tex/Gore-Tex
       Gore-Tex/Nomex
       Oral on T
       Teflon Felt
Nomex
Gore-Tex/Gore-Tex
Gore-Tex/Nomex
Oral on T
Teflon Felt
       Nomex
       Gore-Tex/Gore-Tex
       Gore-Tex/Nomex
       Oral on T
       Teflon Felt
A/C 2.9
244.87 (3.50)
267.80 (3.83)
218.12 (3.12)
192.20 (2.75)
322.60 (4.75)
14.57 (0.21)
30.53 (0.44)
18.16 (0.26)
9.88 (0.14)
44.98 (0.64)
47.14 (0.67)
66.19 (0.95)
47.17 (0.67)
35.15 (0.50)
89.22 (1.27)
Fabric Filter Costs Data
Installed Costs X 103
A/C 5.8
133.59 1.91)
145.06 2.07)
120.22 1.72)
107.26 (1.53)
177.46 (2.54)
Annual Operating Costs X
Dollars & ($/ACFM)
A/C 8.9
109.56 (1.57)
114.81 (1.64)
98.25 (1.40)
89.61 (1.28)
136.41 (1.95)
103 Dollars & ($/ACFM)
16.93 (0.24) 15.82 (0.23)
20.07 (0.29) 21.40 (0.31)
13.86 (0.20) 17.26 (0.25)
11.67 (0.17) 13.01 (0.19)
25.93 (0.37) 22.02 (0.31)
Total Annual i zed Cost of Contraol X 103 Dollars &
34.69 (0.50)
39.36 (0.56)
29.85 (0.43) x
25.93 (0.37)
49.53 (0.71)
30.39 (0.43)
36.70 (0.52)
30.33 (0.43)
24.93 (0.36)
40.16 (0.57)
A/C 11.3
99.96 (1.43)
102,71 (1.47)
89.46 (1.28)
82.55 (1.18)
.119.99 (1.71)
15.49 (0.22)
22.92 (0.33)
19.61 (0.28)
13.55 (0.19)
22.76 (0.33)
($/ACFM)
28.79 (0.41)
36.58 (0,52)
31.50 (0.45)
24.52 (0.35)
40.90 (0.58)

-------
                             Table 29
     Electrostatic Precipitator Cost X TO3 Dollars ($/ACFM)
                                        Efficiency
                            90%              95%              99%
Installed Costs         41Z.97 (5.90)    471,60 (6.74)    600.10 (8.57)
Operating Costs           5.84 (.083)      6.38 (.091)      8.15 (0.116)
T. Annual!zed Costs      60.77(0.87)     69.10 (.99)      87.96(1.26)
                                  - 116 -

-------
                                                 Table 30
Case (A/C. Efficiency)
Dralon T (5.8/1, 97.3%)
Teflon (5.8/1, 98.1%)
ESP (90%)
ESP (95%)
ESP (99%)
Annual i zed Costs
Installed Costs
107,260
177,460
412,970
471,590
600,100
Based on Accel ei
Annual
Operating Costs
11,670
25,930
5,840
6,380
8,150
 Annualized
Capital Costs
   28,600
   47,310
  110,100
  125,730
  159,990
       Total
   Annualized Costs
Accelerated (Standard)
   40,260
   73,240
  115,940
  132,100
  168,130
(25,930)
(49,530)
(60,770)
(69,100)
(87,960)

-------
                              Figure 48
                      Annualized Cost Comparison
175r-




150
£
.2 125
§
o
o
X
.2 100

o
o
-o
at
N
(O
1 75
«c

50
25
Accelerated
BS
Depreciation Over Five (5) Years
vs.

j^3 Standard Depreciation Over Fifteen (15)
Years

—

-






1
_ 1

























KXXXXXXXV






























F3
/.
^XXXXXXXX


























I
y
fj
vXXXXXX\XXN


















Dralon T Teflon ESP ESP ESP
A/C=5.8/1 A/C-5.
8/1 90% 95% 99%
97. 3% 98.1%
                            Method  of Control
                               - 118 -

-------
   .025
   .020
£ .015
CO
CJ3

CT)
"3
O
cu
+J
3
O
   .010
   .005-
                         Figure 49

            Outlet Loading vs. Annualized Costs
       20
30
40
50
60
                                                     KEY:
                                                  O  Nomex
                                                  O  Teflon Felt-Style 2663
                                                  A  Dralon-T
                                                  D  fiore-Tex/Nomex
                                                  X  ESP
70
80
                                                                         90
                                     Annualized Costs X 10  Dollars

-------
as a viable economical  method of participate control  for industrial  coal
fired stoker boilers.
                                    -  120  -

-------
                              DISCUSSION

     The performance of the pilot plant indicates that fabric filtration
is a viable control method for industrial  size stoker boilers.   A summary
of overall performance for the four media evaluated is presented in
Figures 48, 49 and 50 and Table 30.  All media proved capable of exceeding
State and Federal requirements for particulate removal.  Nomex felt had
the lowest outlet loading at each respective A/C ratio, while Teflon felt
was capable of performing satisfactorily at A/C ratios as high as 14/1.
Nomex and Gore-Tex operated at pressure drops between 2 and 6 inches of
water while Teflon felt operated at pressure drops up to 7 inches at
14/1.  The pressure drop curves for Nomex and Dralon T appear to be
leveling off at increasing velocities and would indicate that even higher
velocities than those evaluated might prove economically feasible.  The
efficiencies shown in Table 31 might be considered low for a baghouse,
only Nomex achieved greater than 99% removal at an A/C of 6/1.  However,
since this apparent low efficiency is due in part to the low inlet concen-
tration, the outlet concentrations are probably a better tool for eval-
uating overall performance.  These outlet concentrations were less than
0.015 Gr./SCFD in  all cases and less than 0.005 Gr./SCFD for the low and
middle velocities for both Nomex and Gore-Tex.

    As shown in the economic analysis, the operating costs for a bag-
house are higher than those for an electrostatic precipitator.  The higher
baghouse cost is due to bag replacement.  Therefore, bag life is really
the critical factor in determining whether the fabric filter is econom-
ically competitive.  On the basis of installed costs the baghouse costs
are lower even for Teflon felt at an A/C of 2.9/1.  This comparison is
reflected in total annualized costs for the bag life assumption used
where all cases of the fabric filter, except Teflon at 2.9/1, have lower
costs than the ESP at 90% efficiency.  The performance (outlet loading)
versus annualized cost curve (Figure 47) really states the overall case
for the fabric filter as a competitor, both technically and economically
with ESP for control of particulate emissions from industrial size stoker
boilers.
                                   - 121 -

-------
                                               Figure 50


                                           Outlet Cencentration

                                                    vs.
                               Air-to-Cloth Ratio for Various Bag Materials
               .020
ro
ro
          CO
          --,
           00
           c:


           ro
           c
           o
           
-------
    0.4r
    0.1
    .08
                               Figure  5.1
                     Penetration  vs. Air-to-Cloth  Ratio
                        for Different  Bag  Materials
    0.2 -       81.25%  Removal*  Required  by  State  of  North  Carolina
            *Based  on  allowable emissions  of 25  Ib/hr.  (,082  Gr./SCF)
            and  inlet loading  of 0.473  Gr./SCF  at  35,600  scfm.
I   -06
ID
•W
01
41
Q.
    .04
    .02
    .01
   .008
   .005
       0
                                                               12
                            Air-to-Cloth Ratio (ACFM/Ft/)
14
                                       - 123 -

-------
                                              Figure 52


                    Comparison of Operating  Pressures  for Various Bag Materials
            8
ro
.£»
CO
en
rrj
OQ

VI
vt
          2 4
          tj H
          CL
          o

         o
          
          «/>
          (U
                                                          KEY:


                                                       Q   Nomex
                                                            Teflon  Felt - Style 2663

                                                            Gore-Tex/ Nomex

                                                            Oral on  T
                                                 Immediately Before Cleandown During Normal Operation
                                                 (Cleaning Duration 7 Seconds - Cleans Once Every  140  Sec.)
                                                                         12
                                                                            14
                                      Air-to-Cloth Ratio (ACFM/Ft/)

-------
                               Table 31
                Comparison of Particle Size Efficiencies
                       for Various Bag Materials
                         Air-to-Cloth Ratio 6/1
  Particle
Diameter (Dp)*
  Microns          Nomex

    8.37           99.62
    5.29           99.59
    3.54           99.45
    2.47           98.07
    1.57           97.92
     .79           97.44
     .49           96.23
     .36           95.00
   < .36           96.52
  Overal1
  Efficiency       99.12
% Efficiency
Teflon Felt
Style 2663**
99.33
98.95
98.09
96.96
96.96
90.23
86.79
79.10
92.32
Oral on T
98.48
98.99
97.86
95.86
94.82
89.07
87.54
78.66
94.49
98.05
97.27
Gore-Tex/Nomex

    99.33
    99.43
    97.95
    96.07
    96.96
    96.28
    94.53
    97.27
    97.97

    98.61
 *Corrected for particle density and stack temperature.
**Teflon Felt, Style  2663 - A/C 5.4/1
All efficiencies based on the same inlet loadings and therefore assumes
constant inlet conditions.
                                - 125 -

-------
                               REFERENCES
1.  A. E. Vandergrift, "Particulate Pollutant System  Study, Volume  1,
    Mass Emissions", May - 1971,  NTIS PB-203-128.
2.  D. W.  Locklin, et al,  "Design Trends  and Operating  Problems  in
    Combustion Modification  of Industrial  Boilers",  April  -  1974,
    NTIS PB-235-712.
3.  J. D. McKenna, "Applying Fabric Filtration to Coal  Fired  Industrial
    Boilers",  July - 1974, NTIS PB-237-117-7WP.


4.  N. G. Edmisten and F.  L. Bunyard, "A Systematic Procedure for
    Determining the Cost of Controlling Particulate Emissions from
    Industrial Sources", Journal of the Air Pollution Control Association,
    Volume 20, No. 7, July - 1970.
                                   - 126 -

-------
                             BIBLIOGRAPHY


 1.   R. L. Adams,  "Fabric Filters for Control of Power Plant Emissions",
     Paper No.  74-100 presented at 67th Annual Meeting of the Air Pollution
     Control Association, Denver, Colorado, June, 1974.

 2.   F. A. Bagwell, L. F. Cox and E. A. Pirsh, "Design and Operating
     Experience:   A Filterhouse Installed on an Oil Fired Boiler," Journal
     of the Air Pollution Control Association, Volume 19, No. 3, March,
     1969, pp.  149-154.

 3.   F. A. Bagwell and R. G. Velte, "New Developments in Dust Collecting
     Equipment  for Electric Utilities", Journal of the Air Pollution
     Control Association, Volume 21, No. 12, December, 1971, pp. 781-782.

 4.   C. E. Billings and J. Wiler, "Handbook of Fabric Filter Technology,
     Volume 1,  Fabric Filter Systems Study", December, 1970, NTIS No.
     PB-200-648.

 5.   R. H. Borgwardt, R. E. Harrington and P. W. Spaite, "Filtration
     Characteristics of Fly Ash from a Pulverized Coal-Fired Power Plant",,
     Journal of the Air Pollution Control Association, Volume 18, No. 6,
     June, 1968, pp. 387-390.

 6.   R. L. Davison, D.F.S. Natusch, J. R. Wallace and C. A. Evans, Jr.,
     "Trace Elements in Fly Ash - Dependance of Concentration on Particle
     Size", Environmental Science and Technology, Volume 8, No. 13, December,
     1974, pp.  1107-1113.

 7.   N. G. Edmisten and F. L. Bunyard, "A Systematic Procedure for Determining
     the cost of Controlling Particulate Emissions from Industrial Sources",
     Journal of the Air Pollution Control Association, Volume 20, No. 7,
     July, 1970.

 8.   D. N. Felgar  and W. E. Ballard, "First Year's Experience with Full-Scale
     Filterhouse of Alamitos Generating Station", Proceedings of the American
     Power Conference, Volume XXVIII, 1966, pp. 546-555.

 9.   G. H. Glockley, R. P. Janoso and W. R. Small, "Dust Collectors for Low
     Sulfur Fossil Fuel Plants", ASME Air Pollution Control Division,
     Proceedings of the 3rd National Symposium Forum on "Is Demonstrated
     Technology Available to Meet the Standards".

10.   A. E. Gosselin, Jr., "Pilot-Plant Investigation of the Bag Filterhouse
     for Control of Visible Stack Emissions from Oil-Fired Steam-Electric
     Generating Stations", Proceedings of the American Power Conference,
     Volume XXVI,  1964, pp. 128-137.
                                    -  127  -

-------
                                 BIBLIOGRAPHY
11.   A. E.  Gosselin, Jr., "The Bag Filter-house  for  Oil-Fired Power Plants",
     Journal  of the Air Pollution Control  Association,  Volume  15, No. 4,
     April, 1965, pp. 179-180.

12.   A. E.  Gosselin, Jr., and L.  W.  Lemon, "Bag Filterhouse Pilot Instal-
     lation on a Coal-Fired Boiler - Preliminary Report and Objectives",
     Proceedings of the American  Power Conference,  Volume  XXVIII, 1966,
     pp.  534-545.

13.   D. B.  Harris, J. H. Turner,  "Particulate and S02/S03  Measurements
     Around An Anthracite Steam Generator  Baghouse".

14.   R. P.  Janoso, "Baghouse Dust Collectors on a Low  Sulphur  Coal-Fired
     Utility Boiler", Paper No. 74-101 presented at the 67th Annual
     Meeting of the Air Pollution Control  Association,  Denver, Colorado,
     June,  1974.

15.   P. R.  Langston, "Effect of Chemical Environment of Industrial Effluent
     Gas Streams on Wear Life of  Filter Bags, January,  1975, unpublished.

16.   D. W.  Locklin, et al, "Design Trends  and Operating Problems in  Com-
     bustion Modification of Industrial Boilers", April, 1974, NTIS
     No.  PB-235-712.

17.   R. L.  Lucas, "Gas-Solids Separations  - An  Industrial  View of the
     State-of-the-Art", Paper No. 54A presented at  the  66th Annual Meeting
     AIChE, Philadelphia, Pennsylvania, November, 1973.

18.   W. C.  McCrone, R. G. Draftz, J. G. Delly,  The  Particle Atlas, Ann
     Arbor  Science Publishers, Ann Arbor,  Michigan, 1967.

19.   J. D.  McKenna, "Applying Fabric Filtration to  Coal  Fired  Industrial
     Boilers", July, 1974, NTIS No.  PB-237-117/7WP.

20.   B. Quillman, C. W.  Vogelsang, "Control of  Particulate and S02
     Emissions From an Industrial Boiler Plant, Economic Analysis of
     Options", presented at the Industrial Power Conference, May, 1973,
     ASME publication 73-1PWR-S.

21.   S. A.  Reigel, "Reverse Pulse Baghouses for Industrial Coal-Fired
     Boilers", Power Engineering, August,  1974, pp. 56-59.

22.   P. W.  Spaite, D. G. Stephan, A. H. Rose, Jr.,  "High Temperature
     Fabric Filtration of Industrial Gases", Journal of the Air Pollution
     Control Association, Volume  17, No. 5, May, 1967.
                                    -  128  -

-------
                                BIBLIOGRAPHY
23.   P. W.  Spaite  and  R.  E. Harrington,  "Endurance of Fiberglass Filter
     Fabrics", Journal  of the Air Pollution Control Association, Volume
     17,  No.  5, May, 1967.

24.   E. W.  Stenby, J.  L.  York,  K. S.  Cambell,  "Particulate Removal When
     Burning  Western Coal", Paper No. 6c presented at the 78th National
     Meeting  of AIChE,  Salt Lake City, Utah, August, 1964.

25.   A. Tankha, "Try Fabric Dust Collections on Small Boilers", Power,
     August,  1973, pp.  72-73.

26.   A. E.  Vandergrift, "Particulate  Pollutant System Study, Vol. I -
     Mass Emissions",  May, 1971, NTIS No. PB-203-128.

27.   N. H.  Wagner  and  D.  C. Housenick, "Sunbury Steam Electric Station -
     Unit Numbers  1 &  2 Design  and  Operation of a Baghouse Dust Collector
     for  a  Pulverized  Coal Fired Utility Boiler", paper presented at
     Pennsylvania  Electric Association Engineering Section Power Generation
     Committee, Spring  Meeting  - May  17  and  18, 1973.

28.   A. B.  Walker, "Characteristics of Emissions From Industrial Boilers",
     presented at  the  Industrial Coal Conference, Purdue University,
     Lafayette, Indiana,  October,  1966.
                                    - 129 -

-------
                            APPENDIX
Section                     Contents                        Page
 A-l            Units of Measure - Conversions               132
                Experiment on Nomex.and Teflon               133
 A-2            Teflon Felt, Style 2063                      135
 A-3            Pilot Plant Flow Data                        145
                Particle Size Distribution Data              154
                Fractional Loading Data                      157
 A-4            ESP Installed Cost Basis                     163
                Sample Calculations for Operating            164
                  and Annualized Costs
 A-5            Kerr Boiler Sheets                           168


 A-6            Statistical Analysis                         179
                               - 130 -

-------
         Appendix A-l

Units of Measures - Conversions
Experiment on Nomex and Teflon
              - 131 -

-------
                    UNITS OF MEASURE - CONVERSIONS
     Environmental Protection Agency policy is to express all measurements
in Agency documents in metric units.  When implementing this practice will
result in undue costs or lack of clarity, conversion factors are provided
for the non-metric units used in a report.  Generally, this report uses
British units of measure.  For conversion to  the metric system, use  the
following conversions:
TO CONVERT FROM
°F
ft
ft2
ft3
ft/min (fpm)
ft3/min
in
in2
oz
     2
oz/yd
grains
grains/ft3
Ib force
Ib mass
lb/ft2
in H20/ft/min
in H20/ft/min
    lb/ft2
       TO
°C
meters
      2
meters
      3
meters
centimeters/sec
centimeters /sec
centimeters
           O
centimeters^
grains
           r\
grams/meter
grains
grams/meter3
dynes
kilograms
grams/centimeter2
cm " l^O/cm/sec
cm IL^O/cm/sec
    gm/cm
MULTIPLY BY
_5 (°F-32)
9
0.304
0.0929
0.0283
0.508
471.9
2.54
6.45
28.34
33.89
0.0647
2.288
4.44 x 105
0.453
0.488
5.00

10.24
                                  - 132 -

-------
                            Appendix  A-1

                   Experiment on  Nomex  Felt  (HT)


       Shrinkage, Weiaht Loss, Permeability  -  10/25/74-11/12/74
Description:

    Cut test swatch 6" X 6" - measured,  weighed and  ran  perm  at 0.5"
WG.

    Placed test swatch in oven at 300° F; remeasured,  weighed and  ran
perms weekly.
                    r^        i
               Nomex (HT) Test Swatch
                             Results
Before 10/25
Wt. 11.49 grams
A = 6 1/16"
B = 6
C = 6
D - 6
E = 8 9/16
Perm = 39.94  ,,
       cfm/ft/
   10/29
Wt. 10.73 gr.
A = 6 1/16"
B = 6
C = 6
D = 5 15/16
E = 8 9/16
Perm = 40.18
   11/5

Wt. 10.73 Gr.
A = 6 1/32"
B = 6
C = 6
D = 5 15/16
E = 8V
Perm = 38.83
                           Net Change

                        Wt. - 0.77 grams
                        A = None
                        B = None
                        C = None
                        D = 1/16"
                        E = 1/16"
                        Perm = + 3.3 cfm/ft.
    11/12
Wt. 10.72 Gr.
A = 6 1/16"
B = 6
C = 6
D'= 5 15/16
E = 8^
Perm = 43.24
                               - 133 -

-------
                               Appendix A-1

                   Experiment on Teflon Felt (26 oz.)


       Shrinkage. Weight Loss, Permeability - 9/20/74-9/21/74

Description:

     Cut test swatch 6" X 6" - measured, weighed and ran  perm  at 0.5",
1.0", 3.0", 5.0" WG.

     Placed in oven at 300°F for 24 hours, cooled to  ambient temperature
in dessicator and remeasured, weighed and ran perms.
                            D
   Before

Wt. 19.1115 grams
A = 6 1/32"
B = 6 1/32"
C = 6.0"
D = 6.0"
E = 9 9/16"
A£
0.5
1.0
3.0
5.0
Perms ?
cfin/fr
24.92
49.84
123.10
784.88
       B
Teflon Test Swatch


       Results


        After
  Wt. 18.7870 grams
  A = 5 3/4"
  B = 5 5/16"
  C = 5 23/32"
  D = 5 7/8"
  E = 9 7/16"
  Net Change
Wt. .3245 Grams
A = 9/32"
B = 3/32"
C = 9/32"
D = 4/32"
E = 4/32"
0,5
1.0
3.0
5.0
Perms ,,
cfm/fr
19.38
38.41
97.06
142.6
0.5
1.0
3.0
5.0
Perms 9
cfm/fr
-5.54
-11.34
-26.04
-46.30
                              - 134 -

-------
       Appendix A-2





Teflon Felt Data - Style 2063
          -  135  -

-------
                         Teflon Felt - Style 2063

     Sixteen Teflon felt bags were placed in Cell 2.  (See Figure A-l for
bag positioning).

     The Andersen sampler was utilized in obtaining in-situ particle size
data at air-to-cloth levels of 5.2 to 1, 8 to 1 and 14 to 1.  Inlet flue
gas volumes ranged between 950 and 2600 ACFM.  Because of the limited
amount of Teflon cloth on hand, difficulty was experienced in trying to
operate at the lower air-to-cloth levels.  In order to effect an air-to-
cloth ratio of 5 to 1, the main fan was throttled almost completely.  The
reverse air volume, although not used during sampling periods, was 3500
acfm.

     The particle size distribution for the individual runs was averaged
at each of the three levels of air-to-cloth.  The comparison of this data
is graphically displayed in Figure A-2.  The mass mean particle diameters
were 2, 3 and 4 microns for air-to-cloth ratios of 5.2, 8 and 14 to 1
respectively.

     The size distribution curves indicate that about 50% of the partic-
ulate was less than 2 microns at the lowest air^to-cloth, wh.ile only 37%
of the particulate by weight was less than 3 microns at 14 to 1.

     Average outlet concentration cumulative percent and penetration by
particle size are listed in Table A-l.  Outlet concentration as a function
of velocity is presented in Figure A-3.

     Pressure drop versus air-to-cloth data is presented in Figure A-5
while examples of typical cleandown cycles are shown in Figure A-6.
Although Teflon felt exhibited the highest dust penetration of the
materials tested, it was capable of operating with the lowest pressure
drops.  As shown in Figures A-5 and A-6 it would be economically feasible
to operate at even the highest air-to-cloth levels.
                                 - 136 -

-------
     After fifty-two hours on stream the bags were inspected.   They
showed no signs of wear with only slight evidence of pearling  in  a 3/16"
build-up of a friable dust.
                                   - 137 -

-------
CO

CD
       0000O
           55
00000  ,_
0000OQOO0
000000000
      ooo
               Damper

               Opening
             Cell 2
               KEY:


               Teflon Felt



               Plugs
            Figure A-l



          Positioning of Teflon Felt Bags

            Style 2063

-------
                            Figure A-2

                 Outlet Particle Size Distribution
     10


      8
           Case:   Teflon Felt, 2063

  Note:   Corrected  for  Temperature and Density

  KEY:

A/C Ratio

O    5.2/1

O

a
V)
c
o


I    2

 A
OJ
N
•r~
if)

93
r—
O


t  1.0

D_

     .8
     .6
     .4
                 5    10     20       40     60

                    % Less Than Size Indicated
                                            80
                             - 139 -

-------
                                                     Table  A-l
o
Outlet Concentration, Cumulative %
and Penetration
Teflon Felt, Style 2063
Air-to-Cloth Ratio 5.2/1
Avg . (2)
Outlet
Cone.
Gr./SCFD
.00325
.00084
.00184
.00176
.00181
.00159
.00109
.00055
.00184
.01457
(3)
Cum! .
%
100
77.69
71.92
59.29
47.21
34.79
23.88
16.40
12.63
Pene-(4)
trati on
.0223
.0218
.0696
.1368
.1418
.3232
.4037
.1862
.4289
.0581
Air-to-Cloth Ratio 8/1
Avg.
Outlet
Cone.
Gr./SCFD
.00142
.00019
.00041
.00058
.00026
.00025
.00033
.00008
.00037
.00389
Cum! .
*
100
63.49
58.61
48.07
33.16
26.48
20.05
11.57
9.51
Pene-
tration
.0098
.0049
.0155
.0451
.0204
.0508
.1222
.0269
.0862
.0155
Air-to-Cloth Ratio 14/1
Avg . ' •
Outlet
Cone.
Gr./SCFD
.00967
.00512
.00434
.00359
.00257
.00182
.00092
.00041
.00102
.02946
Cuml .
%
100
67.17
49.79
35.06
22.87
14.15
7.97
4.85
3.46
Pene-
tration
.0665
.1330
.1642
.2789
.2014
.3699
.3407
.1380
.2378
.1174
         TOTAL

        1.   Corrected for particle density (2.6 grams/C.C.)  and  stack temperature.
        2.   At 5.2/1  three (3)  tests  averaged,  at 8/1  two (2)  tests averaged,  at  14/1  two  (2)  tests  averaged.
        3.   Percent of total  outlet concentration less than  size indicated.
        4.   Penetration based on  average inlet  concentration at  corresponding  impactor stages.

-------
                               Figure A-3

                 Outlet  Concentration by  Particle  Size
                                   vs.
                          Air-to-Cloth  Ratio
                        Case:   Teflon  Felt
     .010
a   .008
o
u.
o
V)
10
c
o
TO
+J

0)
u
c
o
o
O)

•M
3
O
   KEY:

Q   .36 um
O  2.84 um

A  5.87 un
O  Total  of All  Sizes
      >9.37 um
     .006
     ,004
    ,002
                            Air-to-Cloth Ratio (ACFM/Ft/)
                                   - 141  -

-------
                             Figure A-4
                 Penetration  vs.  Particle Diameter
O

+3

-------
                         Figure A-5

                 Pressure Dr»p Across Bags
                            vs.
                     Air-to-Cloth Ratio
           CASE:   Teflon Felt
U
c
o>
£
VI
o
Q.
£
o
Ut
Q   Before  Cleandown

     After Cleandown

     Reverse Air Volume
       3500  ACFM
                5                 10

                  Air-to-Cloth Ratio (ACFM/Ft.2)
           16
                                 -  143 -

-------
    8
en
10
fiQ
S  6
e
      Figure A-6
Typical Cleaning Cycles

      Teflon Felt

        A/C - 14/1
v>
§•
                               A/C  - 0/1
V)
§
o.
                                          j
                 0
      2            4
      Time - Minutes
                           O  Before Cleandown
                           O  After Cleandown
                              Reverse Air Volume
                               ,     3500 ACFM
                                     -  144  -

-------
         Appendix A-3

Pilot Plant Flow Data for Andersen
Tests No. 2-80
Particle Size Distribution Data
Fractional  Loading Data
              - 145 -

-------
                           Table A-2


Date
&
Time

5/29
1150
5/30
5/31
1050
6/6
1145
6/6
1600
6/7
1544
6/8
1236
6/10
1342
6/11
1627
6/12
1150
6/12
1600


And.
Test
No.

2

3
4

5

6

7

8

9

10

11

12



Main Slide
Gate Position
% Open

100


100

10

10

_

10

10

5

5

5




Flow Rate
V V
r R
2380 4374


2380

1475

1475

1677

2496

2563 2127

943

1017

1017

Pilot Plant Flow

Air-to-Cloth
Ratio (Ft./Min.)
(A/C)_ (A/C).
	 t 	 K
6.9 12.7


6.6

8.0

8.0

9.1

14

14 12

5.2

5.2

5.2

Data


Temperature
TF (°F) Tp

160 100


170 135

130

120

120

150

150 130

110

120

120


Bags Tested Pressure Drop
& Exposure Across Cell
(Hrs.) at Cell 3 Cell 4
Test Time (In. H^O)
^
Inlet - 8.4

Inlet
Inlet - 7.6

TF 15 //2
4.6
TF 20 #2
4.6
Inlet #2
2.8
TF 31 #2
7.3
TF 36 #2
6.3
TF 42 #2
0.5
TF 46 #2
1.1
TF 50 #2
1.0
*F - foreward flow i.e., flue gas
*R - reverse flow i.e.,  reverse air
TF = Teflon felt

-------
Table A-2
Pilot Plant Flow Data

Date
&
Time
6/18
1056
6/18
1540
6/19
1035
6/19
1533 .
6/20
1133
6/21
1130
6/24
0945
6/24
1435
6/25
1121
6/25
1551
6/26
0950

And.
Test
No.
13

14

15

16

17

18

19

20

21

22

23


Main Slide
Gate Position
'/, Open
5

5

5

60

20

20

20

20

20

30

15



Flow Rate
Q Q
1068 -

1068 -

975 -

2120

2094

2060

1897 -

2422

1988 -

2171

1198

(continued)
Air-to-Cloth
Ratio (Ft./Min.)
(A/C)r (A/C)_
l" IV
3.1

3.1

2.9

6.1

6.1

6.1

5.5

7.0

6,0

6.5

3.6


Bags
Tested
& Exposure
Temperature
Tr (°F) Tr
~-"c' K~~*
120

130 110

125 105

175 140

155

185

160

190 150

180 140

195 145

143

(Hrs
Test
N

N

N

N

N

.) at
Time
89

94

98

103

108

Inlet

G


6

Aborted -,

G

G

G


14

19

23

Pressure Drop
Across Cell
Cell 3 Cell 4
(In. H00)
1.2

1.1

0.9

7.1

4.2

3.5

3.6

2.8

2.9

4.5

2.5

                                N  » Nomex
                                G  « Gore-Tex

-------
      Table A"2
Pilot Plant Flow Data

Date
&
Time
6/26
1453
7/9
1818
7/10
1118
7/11
1125
' 7/12
£ 1035
Oo
, 7/17
1003
7/17
1500
7/18
1519
7/24
1056
7/24
1435
7/25
1030

And,
Test
No.

24

25

26

27

28


29

30

31

32

33

34


Main Slide
Gate Position
% Open

15

20

20

70

100


80

5

100

5

5

20



Flow Rate
V- 	 QR
1258 -

2082 -

2088 3296

3000 3222

2867 3222


2777 -

1004 -

3044

789 -

926

1802

(continued)
Air-to-Cloth
Ratio (Ft./Min.)
CA/C) CA/C)
r '^R^
3.7

6.2

6.3 9.9

9.0 9.7

8.6 9.7


8.3

3.0

9.1

2.7

3.2

6.3


Bags
Tested
& Exposure
Temperature
T_ (°F) T_
r iv^
160

190

197

195 160

193


204
4
132

203

140 130

125 120

180 155

(Hrs
Test

G

G

G

G

G


G

G

G

G

G

G

.) at
Time

28

36

42

52

58


62

68

74

84

88

92

Pressure Drop
Across Cell
Cell 3 Cell 4
(In. HnO)
• • •£—* 	
2.7

4.0

4.2

6.9

7.5


7.3

1.5

7.4

1.8

1.5

5.1

                                        G = Gore-Tex

-------
Table A"2
Pilot Plant Flow Data

Date
&
Time
7/25
1425
7/26
1015
7/26
1400
7/29
1535
. 7/30 '
M 1640
£ 7/31
i 1129
8/6
0745
8/6
1040
8/6
1330
8/7
0740
8/7
1033
8/7
1340

And,
Test
No.
35

36

37

38
39
40

41

42

43

44

45

46


Main Slide
Gate Position
% Open
20

100

100

15
50
80

80

80

80

100

100

100


Flow Rate
Q_ 	 Q
1761 -

2613 -

2547

2107 5000
2972
2812 3100

6425 1420

5909 1420

5910 3160

6670 3160

6670 4000

5390 4000

(continued)
Air-to-Cloth
Ratio (Ft./Min.)
(A/0 (A/0
r K
6.1

9.1

8.9

6.1 14
8.7
8.2 9.0

9.3 2.1

8.6 2.1

8.6 4.6

9.6 4.6

9.6 5,8

7.8 5.8


Temperature
T (°F) T
180 160

208

182

174
200
191 164

223 185

230 196

230 198

220 195

220 195

225 195



Bags Tested
& Exposure
(Hrs.) at
Test
G

G

G

G
N
N

N

N

N

N

N

N
f~t
Time
96

100

104

113
120
124

128

131

135

138

141

143
•^ . 	 j.

Pressure Drop
Across Cell
Cell 3 Cell 4
(In. HnO)
	 i~ 	 2— < 	
5.5

7.8

8.3

n
2.0
6.7
7.6

5.7 6.3

5.6 6.4

4.8 5.2

6.4 6.8

4.8 6.0

5.8 6.0

                                   N " Nomex

-------
                                                     Table A-2
Ul
o
Pilot Plant Flow Data


Date
&
Time

8/8
0750
8/8
1035
8/14
1110
8/14
1110
8/14
1400
8/14
1400
8/15
0800
8/15
1040
8/15
1350
8/16
0740


And.
Test
No.

47

48

49

50

51

52

53

54

55

56



Main Slide
Gate Position
% Open

80

80

80

80

80

80

60

60

60

60




Flow
(£
F
4512

4512

4653

4653

4653

4653

4421

4421

4421

4421




Rate
QR

1400

1400

Off

Off

Off

Off

3100

3100

4000

4000

(continued)

Air-to-Cloth
Ratio (Ft./Min.)
(A/C) (A/C).
• ' ' "f K
6.5 2.1

6.5 2.1

6.7

6.7

6.7

6.7

6.4 4.5

6.4 4.5

6.4 5.8

6.4 5,8







Temperature
T /'"T
i-p V 1

200

200

212

212

205

205

200

210

200

200

?) TR

150

150

175

175

170

170

165

170

170

170


Bags Tested
& Exposure
(Hrs.) at
Test Time

N 147

N 150

Inlet

Inlet

Inlet

Inlet

N 164

N 167

N 171

N 174



Pressure Drop
Across
Cell 3
(In.

6.0

6.1

5.5

5.5

5.7

5.7

5.0

5.8

5.7

5.4

Cell
Cell 4
H00)

6.1

6.1

5.6

5.6

5.9

5.9

5.0

5.9

5.8

5.6

                                                                                 N = Nomex

-------
Table A-2



Pilot Plant
Flow Data


(continued)
Date
&
Time
8/16
1035
8/20
0735
8/20
1100
8/20
1330
1 8/21 '
G 0730
. 8/21
1005
8/26
1150
8/26
1430
8/27
0730
8/27
1035
Bags Tested
And. Main Slide Air-to-Cloth & Exposure
Test Gate Position Flow Rate Ratio (Ft./Min.) Temperature (Hrs . ) at
No. % Open ()„ Q^ (A/C),, (A/C).. !„ (°F) T.. Test Time
57
58
59
60
61
62
63
64
65
66
20
20
20
20
60
60
30
30
30
20
•T i\ r
2129 1400 3.1
2313 1400 3.4
2313 3160 3,4
2313 3160 3.4
2275 4000 3.3
2275 4000 3.3
2550 - 8.5
2550 - 8.5
2666 - 8.9
1817 - 6.1
rv r
2.1 170
2.1 165
4.6 160
4.6 150
5.8 150
5.8 160
190
175
150
162
i\
140 N 177
140 N 180
140 N 183
140 N 186
125 N 190
135 N 192
.135 Aborted
135 DT 27
DT 30
DT 33
Pressure Drop
Across Cell
Cell 3 Cell 4
(In. H.,0)
	 2—t 	
3.1 3.0
2.9 2.8
2.7 2.6
2.5 2.4
2.2 2.2
2.2 2.2
5.6
6.2
5/4
2.9
                          N = Nomex
                         DT = Dralon T

-------
                                                     Table
Ut
to
Pilot Plant Flow Data

Date
&
Time
8/27
1350
8/28
1135
8/29
1110
8/29
1400
11/18'
1405
11/19
0955
11/19
1355
11/19
1615
11/20
1145
11/20
1520
11/21
1140

And.
Test
No.

67

68

69

70

71

72

73

74

75

76

77


Main Slide
Gate Position
% Ooen

20

20

10

10

10

5

5

5

10

10

10



Flow Rate
o. 	 Q_
1817

1817 3810

997

997

3100

1760

1383

1383

3300

1830

3260

(continued)
Air-to-Cloth
Ratio (Ft./Min.)
(A/C),, (A/C)^
F R—
6.1

6.1 13

3.3

3.3

14

7.9

6.0

6.0

14.3

8.0

14.2


Bags
Tested Pressure Drop
& Exposure Across Cell
Temperature
T (°F) T
*r" v ' rt
r K
170

- -

130

140

160

120

100

80

160

130

150

(Hrs
Test

DT

DT

DT

DT

TF

TF

TF

TF

TF

TF

TF

.) at cell 3 Cell 4
Time (in. H00)
• • ' • • 2 '• -
36 - 5.0

42 - 5.2

48 - 2.2

51 - 2.2

25 375

29 3.0

34 1.0

37 1.0

40 6.8

43 3.0

47 7.8

                                                                             DT » Dralon T
                                                                             TF = Teflon felt

-------
                                                   Table A-2
Date
&
Time
11/21
1350
11/21
1555
11/22
0925
And.
Test
No .
78
79
80
 Main Slide
Gate Position
   % Open
5

5
Flow Rate
                 1930   -
1180   -
                                    1180
Pilot Plant Flow Data
      (continued)


    Air-to-Cloth
    Ratio (Ft./Min.)
    (A/C)-   (A/C).
                                                              -R-
                                                 8.4
                                                 5,4
             5.4
                                Temperature
                                IF C°F)  T
                                125
                                                  80

                                                  90
                                                                                   Bags Tested
                                                                                   & Exposure
                                                                                   (Hrs.)  at
                                                                                   Test Time
                                                                 TF
                                                                                   TF
                                                       50
                                                TF     52
                                                                       Pressure  Drop
                                                                       Across  Cell
                                                                       Cell  3  Cell 4
                                                                           (In. HZQ)	

                                                                         4.0
                                                                                                  1.8
                                                       54     1.5
i
M
U1

I
                                                                                  TF = Teflon felt

-------
                                Table A-3

                 PARTICLE SIZE DISTRIBUTION FOR ANDERSEN TESTS
                               D R A L 0 N  T
And.  A/C
Run#  Ratio
Particle Size Distribution
64
65
66
67
68
69
70
Total
Avg.

And.
Runtf
13
14
15
16
17
39
40
38
Total
Avg.

And.
Run//
19
21
22
23
25
26
27
28
32
8.5/1
8.9/1
6.1/1
6.1/1
6.1/1
3.3/1
3.3/1



A/C
Ratio
3.1/1
3.1/1
2.9/1
6.1/1
6.1/1
8.7/1
8.2/1
6.1/1



A.C
Ratio
5.5/1
6.0/1
6.5/1
3.6/1
6.2/1
6.3/1
9/1
8.6/1
2.7/1
>9.8
>9.7
>9.8
>9.3
>9.8
>8.6
>8.6
65.6
>9.37


6.
6.
6.
5.
6.
5.
5.
41.
5.


1
0
1
9
1
4
4
0
86
N

4.1
4.0
4.1
3.8
4.0
3.6
3.6
27.2
3.89
0 M E

Particle Size
>8.5
>8.37
>8.8
>9.8
>9.9
>8.4
>8.4
>9.7
71.87
>8.98


5.
5.
5.
6.
6.
5.
5.
6.
44.
5.


4
29
5
0
2
3
3
0
99
62


3.5
3.48
3.7
4.0
4.2
3.6
3.6
4.0
30.08
3.76


Particle Size
>10.2
>9.7
>9.6
>9.4
>9.3
>9.9
>10.5
>9.2
>7.27
6.
6.
6.
5.
4
1
1
9
5.9
6.
6.
5.
5.
2
6
7
55
4.3
4.0
4.0
3.9
3.8
4.1
4.4
3.83
3.73
2.8
2,8
2.8
2.7
2.8
2.5
2.5
18.9
2.7
X F E

1.
1.
1.
1.
1.
1.
1.
12.
1.
L

79
80
80
72
81
59
59
10
73
T :

.92
.92
.92
.88
.92
.82
.82
6.20
.89
(Zero

.57
.58
.58
.54
.58
.50
.50
3.85
.55
RA)

.39
.38
.38
.36
.36
.34
.34
2.55
.36


Distribution
2.48
2.81
2.5
2.8
2.9
2.52
2.51
2.9
21.42
2.68
G 0 R

1.
1.
1.
1.
1.
1.
1.
1.
13.
1.
89
54
9
77
84
55
55
78
82
73
E - T


.79
.79
.83
.91
.95
.80
.80
.91
6.78
.85
E X

.49
.475
.51
.57
.59
.49
.49
.56
4.18
.52


.33
.32
.35
.37
.40
.33
.33
.38
2.81
.35


Distribution
3.0
2.9
2.8
2.8
2.73
2.9
2.93
2.65
2.57
1.
1.
1.
1.
1.
1.
1.
1.
1.
87
80
79
75
74
82
93
67
62
.97
.91
.92
.90
.88
.94
.99
.871
.847
.59
.56
.57
.55
.55
.58
.61
.536
.515
.41
.38
.38
.37
.36
.39
.41
.36
.35
                                                                 41
                                                                 38
                                                                 38
                                                                 37
                                                                 36
                                                                 39
                                                                 41
                                                               <.36
                                                               <.35
                                   - 154 -

-------
             Table A-3 (continued)
PARTICLE SIZE DISTRIBUTION FOR ANDERSEN TESTS

          GORE-TEX  cont.
And.
Run#
33
34
Total
Avg.

And.
Run//
5
6
8
9
10
11
12
Total
Avg.
A/C
Ratio
3.2/1
6.3/1



A/C
Ratio
8/1
8/1
14/1
14/1
5.2/1
5.2/1
5.2/1


Particle
>7.25
>10
102
> 9


.6
.9
.35


5.55
6.6
66.6
6.05
T E

Particle
>8
>8
>9
>10
>9
>9
>9
65
>9
.96
.96
.3
.8
.2
.04
.3
.56
.37
5.66
5.66
5.98
6.5
5.79
5.6
5.9
41.09
5.87
Size
3.73
4.49
44.28
4.03
FLO

Size
3.69
3.69
3.99
5.0
3.82
3.79
3.9
27.88
3.98
N 0 M E X
And.
Run#
41
42
43
44
45
46
47
48
53
54
55
56
57
58
A/C
Ratio
9.3/1
8.6/1
8.6/1
9.6/1
9.6/1
7.8/1
6.5/1
6.5/1
6.4/1
6.4/1
6.4/1
6,4/1
3.1/1
3.4/1




Particle Size
>9
>9
>9
>9
>9
>9
>9
>9
>9
>9
>9
>9
>9
>9
.6
.7
.5
.7
.6
.0
.52
.3
.0
.0
.0
.0
.57
.16
6.0
6.1
6.0
6.1
6.0
5.8
6.0
5.78
5.77
5.77
5.77
5.77
6.0
5.81
3.9
4.0
4.0
4.0
3.9
3.8
3.9
3.69
3.87
3.87
3.87
3.87
3.96
3.83
Distribution
2.57
3.1
30.95
2.81
N F E

1.62
1.93
.847
1.0
19.54 10.08
1.78
L T

.92
(Style

.515
.62
6.20
.56
2063)

.35
.43
4.19
.38


<-35
<.43
4.19
<.38


Distribution
2.63
2.63
2.79
3.66
2.7
2.66
2.8
19.87
2.84
PEL

1.65
1.65
1.79
1.89
1.7
1.66
1.7
12.04
1.72
1.05
1.05
.93
.98
.527
.527
.54
.603
.856 .54
.86
.89
6.62
.95
.53
.55
3.82
.55
T (Three levels



.329
.329
.37
.413
.36
.36
.37
2.53
.36
RA)

^.329
<.329
<.37
<.413
<.36
<.36
<-37
2.53
<.36


Distribution
2.80
2.8
2.8
2.8
2.8
2.7
2.8
2.65
2.67
2.67
2.67
2.67
2.8
2.66
1.79
1.8
1.77
1.8
1.79
1.67
1.79
1.67
2.04
2.04
2.04
2.04
1.85
1.71
.91
.92
.91
.92
.91
.86
.91
.89
.86
.86
.86
.86
.91
.87
.56
.56
.55
.56
.56
.52
.56
.54
.53
.53
.53
.53
.56
.53
.37
.38
.38
.38
.37
.35
.37
.36
.36
.36
.36
.36
.37
.36
<.37
<.38
<.38
<.38
<.37
<.35
<.37
<.36
<.36
<.36
<.36
<.36
<.37
<.36
                   -  155  -

-------
              Table A-3 (continued)
 PARTICLE SIZE DISTRIBUTION FOR ANDERSEN TESTS

NOMEX  FELT  (Three levels RA) cont.
And.
Run//
59
60
6£
62
Total
Avg.

And.
Run//
77
78
79
80
81
Total
Avg.
A/C
Ratio
3.4/1
3.4/1
3.3/1
3.3/1



Particle
>9.3
>9.3
>9.16
>9.16
5
5
5
5
167.57106


A/C
Ratio
14.2/1
8.4/1
5.4/1
5.5/1
14/1


>9.31


5


.88
.88
.81
.81
.05
.89
T E

Particle
>8.27
>8.25
>8.53
>8.75
>8.08
41.88
>8.38
5
5
5
5
5
26
5
.15
.19
.43
.55
.14
.46
.29

Size
3.83
3.83
3.83
3.83
69.78
3.88






Distribution
2.72
2.72
2.66
2.66
49.05
2.73
F L 0 N F

Size
3.52
3.53
3.62
3.65
3.42
17.74
3.55

1.73
1.73
1.71
1.71
32.68
1.82
E L T

.88
.88
.87
.87
15.95
.89
(Style

.55
.55
.53
.53
9.78 6
.54
2663)

.35
.35
,36
.36
.55 •
.36


<.35
<-35
<.36
^36
6.55
<.36


Distribution
2.51
2.46
2.45
2.55
2.39
12.36
2.47
1.56
1.59
1.55
1.63
1.51
7.84
1.57
.77
.785
.81
.83
.76
3.96
.79
.49
.479
.50
.51
.46
2.44 1
.49
.32
.32
.34
.35
.31
.64
.33
<.32
<.32
<.34
<-35
<.31
1.64
<.33
                  -  156  -

-------
                                           Ta.talo
 And.
 Run*
          Air-To-Cloth  -  3/1

        13        14        15
      .00068
      ,00027
      ,00030
      .00030
      ,00018
      ,00012
      ,00006
*     .00009
      .00006
Total.00206
«J to
rt tofl
O G
4_) "O
o n)
C0 O
w \ 1
.00040
.00014
.00043
.00037
.00040
.00032
.00017
,00009
,00015
.00085
.00010
.00022
.00019
.00022
.00016
.00010
.00006
.00006
               .00247    .00196
          Air-To-Cloth  =  5.2/1
And.
Run#


_<
Fractional
Loadings
Total

10
.00400
.00065
.00142
.00103
.00116
.00090
.00071
. 00065
.00149
.01201

11
.00290
.00088
.00198
.00185
.00185
.00162
.00114
.00057
.00299
.01578

12
.00284
.00098
.00213
.00241
.00241
.00224
.00142
.00044
.00104
.01591
FRACTIONAL LOADING FOR ANDERSEN TESTS*
N 0
i M E X F
E L T (Zero RA)
Air-To-Cloth
Avg.
.00064
.00017
.00032
.00029
.00027
.00020
.00011
.00008
.00008
.00216
TEFL
16_
.00043
.00015
.00011
.00011
.00022
.00025
.00014
.00007
.00011
.00159
ON F E
17.
.00059
.00018
.00022
.00037
.00048
. 00019
.00026
.00015
.00037
.00281
= 6/1
_38_
.00120
.00031
.00078
.00031
.00075
.00024
.00062
.00007
.00017
.00445
Air-To-Cloth = 8.
Avg.
.00074
.00021
.00037
.00026
.00048
.00023
.00034
.00010
.00022
.00295
39.
.00228
.00080
.00135
.00085
.00094
.00039
.00036
.00006
.00016
.00719
4£
.00114
.00047
.00083
.00045
.00075
.00025
.00050
.00008
.00022
.00469
.5/1
Avg.
.00171
. 00064
.00109
.00065
.00084
.00032
.00043
.00007
.00019
.00594
L T (Style 2063)
Air-To-Cloth
Avg.
.00325
.00084
.00184
.00176
.00181
.00159
.00109
.00055
.00184
.01457
5.
.00224
.00015
.00025
.00025
.00021
.00018
.00009
.00006
.00040
.00383
£
.00060
.00022
.00057
.00091
.00032
.00032
.00057
.00009
.00035
.00395
= 8/1
Avg.
.00142
.00019
.00041
.00058 .
.00026
.00025
.00033
.00008
.00037
.00389
Air-To-Cloth
j8
.00573
.00435
.00305
.00275
.00198
.00111
.00050
.00019
.00042
.02008
2.
.01362
.00590
' .00562
.00443
.00316
.00253
.00133
.00063
.00162
r03884
= 14/1
Avg.
.00967
.00512
.00434
.00359
.00257
.00182
.00092
.00041
.00102
.02946












*A11 values are Grains/SCFD

-------
                                                 Table A-4 (continued)
VI
00
FRACTIONAL LOADING FOR ANDERSEN TESTS
And.
Run#


Fractional
Loadings

Air-To-Cloth = 14.1/1
77
.00362
.00086
.00106
.00075
. 00086
.00060
.00161
.00111
.00468
Total, 01515
81
.00281
.00072
.00108
.00084
.00078
.00078
.00060
.00072
.00126
.00959
Air-To-Cloth -
And.
Run#


Fractional
Loadings
Total

70
.00124
.00098
.00124
.00118
.00101
.00087
.00056
.00048
.00045
.00801

60
.00121
.00113
.00164
.00147
.00127
.00096
. 00065
.00045
.00056
.00934
Avg.
.00321
.00079
.00107
.00080
.00082
.00069
.00110
.00092
.00297
.01237
3.3/1

Avg.
.00122
. 00106
.00144
.00133
. 00114
.00092
.00061
.00046
.00050
.00868
TEFL
ON FELT (Style 2663)
Air-To-Cloth - 5.
79
.00087
.00035
.00041
.00035
.00048
.00038
.00024
.00035
.00052
.00395

80
.00095
.00047
.00044
.00055
.00054
.00066
.00047
.00058
.00054
.00520
D R A L
Air-To-Cloth

66
.00218
.00029
.00037
.00048
.00071
.00089
.00066
.00052
.00037
.00647

iZ.
.00149
.00027
.00044
.00061
«00088
.00071
.00054
.00031
. 00020
.00545
4/1
Avg.
.00091
.00041
.00043
.00045
.00051
.00052
.00036
.00046
.00053
.00458
0 N T
- 6.1/1

68
.00239
.00061
.00061
.00071
.00103
.00121
.00079
.00061
.00057
.00853
Air-To-Cloth - 8.4/1





28
.00257
.00082
.00108
.00108
.00082
.00087
.00072
.00093
.00134
,01023





Air-To-Cloth

Avg.
.00202
.00039
.00048
.00060
.00087
.00094
. 00066
.00048
.00038
.00682

64
.00145
.00039
.00050
.00046
.00071
.00075
.00046
.00032
.00021
.00525

j>5
.00143
.00065
.00061
.00057
.00075
.00072
.00064
.00036
.00022
.00595





-8.7/1

Avg.
.00144
.00052
.00055
.00051
.00073
.00074
.00055
.00034
.00022
.00560

-------
                                                   Table A-4  (continued)
FRACTIONAL LOADING FOR ANDERSEN TESTS
GORE-TEX
Air-To-Cloth =
And.
Run#


Fractional
Loadings
Total

27.
.00156
.00034
.00097
.00059
.00114
.00046
.00088
.00021
.00030
.00645

.28
.00189
.00131
.00201
. 00096
. 00134
.00026
.00048
. 00003
.00016
.00844
• 8.8/1

Avg.
.00173
.00082
.00149
.00078
.00124
.00036
.00068'
.00012
.00023
.00745
Air-To-Cloth « 3.2/1

23
.00086
.00040
. 00050
.00083
.00069
.00053
.00030
.00016
.00023
.00450

_32
.00072
.00038
.00110
.00061
.00075
,00029
.00052
.00006
.00015
.00458

33
.00054
.00074'-
.00089
.00057
.00069
.00034
.00040
.00009
.00009
.00435

Avg.
.00071
.00051
.00083
.00067
.00071
.00039
.00040
.00010
.00016
.00448
Ui
VO
                               Air-To-Cloth = 6.1/1
And.
Run#


fractional
Loadings
r~-i
Total

11
.00219
.00023
.00061
.00069
.00073
.00050
.00035
.00008
0
.00538

21
.00142
.00025
.00032
.00046
.00032
. 00025
.00017
.00011
.00011
.00341

25.
.00036
.00007
.00033
.00030
.00026
.00020
.00013
.00007
.00007
.00179

26
.00037
.00011
.00033
.00041
. 00033
. 00011
.00015
.00007
.00033
.00221

J22.
.00064
.00021
.00050
.00057
.00043
.00032
.00018
.00003
.00014
.00302

34
.00198
.00011
. 00060
.00097
.00093
.00045
.00079
0
.00037
.00620

Avg.
.00116
.00016
.00045
.00057
.00050
.00031
.00029
.00006
.00017
.00367

-------
o
 I
Table A-4 (continued)
FRACTIONAL LOADING FOR ANDERSEN TESTS
N 0 M E X

And.
Run//



a) 03
tf 60
o a
•H "rt
0) O
£ ^

Total


And.
Run//



H) (0
0 (3
JJ TJ
O flj
cQ O
^ i"^

Total
RA

57_
.00129
.00057
.00054
.00014
.00061
.00054
.00036
.00061
.00043
.00509

RA

47
.00170
.00094
.00073
.00073
.00048
.00048
.00003
.00042
.00017
.00568
• 1400

58
.00123
.00026
.00039
.00023
.00036
.00029
.00023
.00016
.00010
.00325
N
- 1400

48
.00097
.00098
.00078
.00088
.00026
.00049
.00003
.00039
.00003
.00481


Avg.
. 00126
. 00041
.00046
.00019
.00048
.00041
.00030
.00039
.00027
.00417
0 M E X


Avg.
.00133
. 00096
.00076
.00080
.00037
.00049
.00003
.00041
. 00010
.00525
FELT


59
.00118
.00031
.00028
.00014
.00021
.00024
. 00011
.00014
0
.00261
FELT


53.
.00134
.00062
.00055
.00058
.00040
.00058
.00029
.00076
.00037
.00549
(3 levels of RA)
RA = 3100

60
.00102
.00035
.00031
.00017
.00021
.00021
0
.00011
.00014
.00252
(3 levels
RA - 3100

54
.00230
.00095
.00092
.00089
.00081
.00057
.00050
.00032
.00021
.00747


Avg.
.00110
.00033
.00029
.00016
.00021
.00022
.00006
.00013
.00007
.00257
of RA)


Avg.
.00182
.00078
.00073
.00073
.00061
.00058
. 00040
.00054
.00029
.00648
Air-To-Cloth - 3.4/1
RA =

61
.00107
.00027
.00027
.00027
. 00030
.00027
.00010
.00017
.00017
.00289
Air-To-Cloth
RA -

55
.00086
.00053
.00060
.00071
.00053
.00057
.00057
.00050
.00029
.00516
• 4000

*2
00111
00041
00034
00030
00037
00030
00030
00017
0
00330
- 6.4/1
4000

56_
00128
00095
00128
00071
00078
00047
00044
00037
00057
00685


Avg.
.00109
.00034
.00031
.00029
.00033
.00028
.00020
.00017
.00009
.00310



Avg.
.00107
.00074
.00094
.00071
.00065
.00052
.00051
.00044
.00043
.00601

-------
Table A-4 (continued)
FRACTIONAL LOADING FOR ANDERSEN TESTS

N
0 M E X
FELT
RA = 1400
And.
Run# 41
.00374
.00139
3 «• 00150
g g>. 00160
33.00192
a g. 00032
£ -".00061
0
.00001
Total. 01119

42
.00270
.00142
.00222
.00131
.00127
.00044
.00076
.00015
.00029
.01056

Avg.
.00322
.00141
.00186
.00145
.00159
.00038
.00069
.00008
.00020
.01088

M
.00243
.00091
.00162
.00102
.00120
.00046
.00060
.00063
.00028
.00915
(3 levels of RA)
Air-To-Cloth = 8.9/1
RA - 3100

44
.00210
.00112
.00188
.00271
.00315
.00094
.00058
.00043
.00011
.01302

Avg.
.00226
.00102
.00175
.00187
.00217
.00070
.00059
.00053
.00020
.01109

45
.00284
.00119
.00172
.00113
.00084
.00060
.00007
.00042
0
.00881
RA - 4000

-46_
.00221
.00115
.00090
.00115
.00022
.00070
. 00006
.00042
.00003
.00684

Avg.
.00252
.00117
.00131
.00114
.00053
.00065
.00007
.00042
.00002
.00783

-------
      Appendix A-4

ESP Installed Cost Basis
Sample Calculations for Operating
  and Annualized Cost
           - 162 -

-------
                            APPENDIX A-4
          Electrostatic Preclpitator Installed Cost Basis
     Budgetary quotations for electrostatic precipitators were
solicited from several of the leading ESP manufacturers.   Listed
below are the design parameters furnished with the requests for
quotations.
General Design Parameters
  1.  Coal Analysis - See Table 9
  2.  Emission Rates:
          35,000 acfm/Boiler
          Parti culates, 130 Lbs/Hour/Boiler
          SO-
          C0
          CO
          Temperature
          Moisture
  3.  Particle Size of Ash:
          Particle Diameter
              Microns _
                  6.4
                  4.2
                  2.8
                  1.8
                  0.94
                  0.58
                  0.38
                                                    - 70,000 scfm Total
                                                    - 260 Ibs./Hour Total
                                                    -     250-500 ppm
                                                    -       3'6   Ppm
                                                    -       9.5%
                                                    -         0%
                                                    -        10%
                                                    -        80%
                                                    -       350° F
                                                    - 5.0% By Volume
                                           Percent Less Than
                                             Size Indicated
                                                   49
                                                   38
                                                   27
                                                   18
                                                   12
                                                     8
                                                     7
                    51%  of  particles  are greater  than  6.4 microns.
                                       - 163 -

-------
                            APPENDIX A-4

                      ELECTROSTATIC PRECIPITATOR

               Operating and Annualized Cost Calculations

     Formula for calculating theoretical operating and annualized cost
of control were taken from:  Edminsten, N.G. and Bunyard, F.L., "A
Systematic Procedure for Determining the Cost of Controlling Particulate
Emissions from Industrial Sources", JAPCA  V20  N7, p. 446, July 1970.

     I.  Electrostatic Precipitator Operating Cost:
              G = S  [JHK + M]
         Where,
              G = Theoretical Annual Operating Cost
              S = Design Capacity, ACFM
              J*= Power Required, Kilowatts/ACFM
              H = Annual Operating Time, 6240 Hours
              K = Power Costs, $/KWH
              M = Maintenance Costs, $/ACFM
         *Does not include power for main fan.
         At 90% efficiency,
              G = 70,000 [(.00019) (6240) (.0175) + .02]
              G = 70,000 (.040748)
              G = $2,852
         At 95% efficiency,
              G = 70,000 [(.00026) (6240) (.0175) + .02]
              G = 70,000 (.048392)
              G = $3,387
         At 99% efficiency,
              G = 70,000  [(.0004) (6240) (.0175) + .03]
              G = 70,000 (.07368)
              G = $5,158

                                  - 164 -

-------
         Operating and Annualized Cost Calculations
                       (continued)
     Main fan costs, (F) = S r.7457  PHK,
                             L6356E     J
     Where,
            S = Design Capacity, ACFM
            .7457 = A Constant (1 Horsepower =0.7457 Kilowatts)
            E = Fan Efficiency, 60%
            P*= Pressure' Drop, Inches of Water
            H = Annual Operating Time, 6240 Hours
            K = Power Cost, $/KWH

     F = 70,000      .7457     (2) (6240) (.0175),
                 l(6356) (.6)                    J
     F = 70,000  [.042705]
     F = $2,989
     *Assumes 0.5 inches for ESP plus 1.5 inches for inlet duct,  etc.

      *  . Total Annual Operating Costs = G + F
     at 90% Efficiency,  $2,852 + $2,989 = $5,841
     at 95% Efficiency,  $3,387 + $2,989 = $6,376
     at 99% Efficiency,  $5,158 + $2,989 = $8,147

II.   Electrostatic Precipitator Annualized Costs
     Total  annualized cost of control is equal to the annual
     operating cost plus the annualized capital  cost.
     Annualized Capital Cost* = 0.133 X Installed Cost
     Total  Annualized Cost = 0.133 X Installed Cost + Operating Cost
     at 90% Efficiency = (0.133) (412,970) + 5,841
                       = 54,925 + 5,841
                       = $60,766
     at 95% Efficiency = (0.133) (471,588) + 6,376 = $69,097
     at 99% Efficiency = (0.133) (600,100) + 8,147 = $87,960
     *See fabric filter case (Page 167)  for annualized capital  cost
      assumptions.

                               -  165  -

-------
                           Appendix A-4
                           Fabric Filter
                  Operating and Annualized Costs
                        Sample Calculations
     Formula for calculating theoritical operating and annual i zed cost
of control were taken from:  Edminsten, N.6. and Bunyard,  F.L.,  "A
Systematic Procedure for Determining the Cost of Controlling  Particu-
late Emissions from Industrial Sources", JAPCA V20 N7, p.  446, July
1970.
    I.  Fabric Filter Operating Cost:
          Case - Teflon Felt at A/C = 5.8/1

                         PHK + M]
        Where:  G = Theoretical annual cost for operation and
                    maintenance
                S = Design capacity, acfm
                P = Pressure drop, inches of water
                E = Fan efficiency, assumed to be 60% (expressed
                    as 0.60)
                0.7457 - A constant, 1 horsepower = .7457 kilowatt
                H = Annual operating time, 6240 hours
                    (24 hours/day X 5 days/week X 52 weeks/year =
                       6240 hours/year)
                K = Power costs, $/KWH
                M = Maintenance cost, $/ACFM (based on 25% bag
                    replacement per year)
        In this case:
                S = 70,000 acfm
                P = 3.8 Inches of Water
                E = 60%
                H = 6,240 Hours
                K = $0.0175/KWH
                M = (No. of bags in house X 25% replacement rate X
                    cost per bag) r S

                                     - 166 -

-------
                      Sample Calculations
                          (continued)
             M = 1080 Bags X .25 X $75/Bag _ t ,Q/flrFM
                 - y0'000 ^fm - * - $ ' 29/ACFM
             Assuming a 60% fan efficiency reduces the above
             equation for G to:

                G = S (195.5 X 10"6 PHK + M)

             Substituting the figures above yields:

                G = 70,000 (195.5 X 10"6 X 3.8 X 6240 X .0175 + .29)

                  = 70,000 (.0918 + .2893)

                  = 70,000 (.3811)

                  = 25,929


II.   Total  annuali zed cost of control is equal to the annual  operating
     cost plus the annual ized capital cost.


         Annualized Capital Cost = 0.133 X Installed Costs

         Assumptions:
           1.  Purchase and installation costs are depreciated over
               fifteen (15) years.

           2.  The straight line method of depreciation (6 2/3% per
               year) is used.

           3.  Other costs called capital charges are assumed to be
               equal to the amount of depreciation.  Therefore,
               depreciation plus other capital charges amount to
               13 1/3 percent of the initial  capital costs of the
               equipment.

     In this case:  Teflon Felt at A/C = 5.8/1

     Total  annual ized cost of control = .133  X Installed Costs +
              Operating Costs

              = .133 X 177,460 + 25,929

              = 23,602 + 25,929

              = 49,531
                                 - 167 -

-------
                   Appendix A-5
Kerr Boiler Sheets for August 8th,  15th,  16th,  20th  and
21st.  Corresponds to Andersen  Test Numbers  47  and 48  and
53 thru 62.  Testing Nomex felt at  A/C ratio of 6/1  and
3/1 at three levels of reverse  air.
                         -  168  -

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-------
    Appendix A-6
Statistical Analysis
     - 179 -

-------
                              Appendix A-6
                          Statistical  Analysis
     A statistical analysis was conducted to determine if there was  a
significant relationship between outlet loading and air-to-cloth ratio
(velocity thru the filtering media).  This analysis was done In two  parts,
First, the outlet loading data for each of the four bag materials was
analyzed with respect to the three levels of velocity tested.  Second,
the outlet loading data for Nomex felt at three levels of reverse air
for each of three levels of velocity was analyzed.

     One-sided and two-sided tests for variance were employed utilizing
the F-test for significance.  The outlet loading data was organized  as
shown in Table A-5.  Then the one-sided test for variance was conducted
for each bag material.  Following is an example calculation for the  case
of Nomex felt.

          TL = (.0021) + (.0025) +  (.0020) = .0066
          TM = (.0016) + (.0028) +  (.0045) = .0089
          TH = (.0072) + (.0047) =  .0119

          TG • TL + TM + TH =  '°274
Where     TL = total of the outlet  loading values at low velocity
          TM = total of the outlet  loading values at medium velocity
          Tu = total of the outlet  loading values at high velocity
           n
          TG = total of the outlet  loading values at all three
               velocities
Calculate S$T =  (.0021)2 +  (.0025)2  +-	+  (.0047)2
          SST =  .000119
Where     SSj =  Sum of squares of the outlet loading values  at  all  three
                 velocities.
                                    -  180  -

-------
                              Appendix A-6

                              [continued)
Calculate SSE, variation within velocities




  Where, SSC = SST - T, 2 + TM2 + Tu2
           t.     I    — L —   — FT—    ft

                      332



         SSE = .000119 - (.000015 + .000026 + .000071)
       SS
               .000119 - .000112
         SSE = .000007



Calculate SSy, variation between velocities
Where, SS
               T, 2 + TM2 + T.,2 + Tr2
               -T.—   -M—   — H—   — G—

                3328


         <:<;  - -0000^ . .000079 . .000142    .000751

         bi>V      3    +    3         2         8


         SSV = .000015 + .000026 + .000071 -  .000094



         SSy = .000018




Set-up an analysis of variance table as follows:
Analysis of Variance Table
Variance
ssv
SSC
Source of Variation
Between Velocities
Within Velocities
Sum of
Square
.000018
.000007
Degrees
of Freedom
2
5
Mean Squares
.000009
.0000014
    Then, the F-test gives



              F - -000009    fi
              r " .0000014 " °-'
Conclusion:  The F- Statistic is found to be significant at the 0.05

             level of significance.
                                  - 181 -

-------
                              Appendix A-6
                              (continued)
     The results of similar computation employing the one-sided test for
the other three bag materials as well as Nomex felt are shown in Table
A-9.  Also Included in Table A-9 are the results obtained when the one-
sided test is applied to the Nomex felt data for three levels of reverse
air (RA).

     The two-sided test for variance was utilized to evaluate the Nomex
felt data at three levels of reverse air for each of three velocities.
This allows determination of the significance of reverse air and velocity
upon outlet loading simultaneously and also significance of interactions.

     The computations for the two-sided test proceed as follows:
          U
          o
          'oi
              M
              H
         Reverse Air
  L           M            H
.0051        .0026        .0029
.0032        .0025        .0033
.0057        .0055        .0056
.0048        .0075        .0068
.0112        .0091        .0088
.0106        .0133        .0068
      SSE = .0000013
Source of variation in the table will appear as follows:
                Source               d.f.      SS
            Between RA Levels
            Between Velocities
            Interaction
            Error
                 Total
                   2
                   2
                   4
                   9
                  17
SSRA
SSV
SSI
SSE
SS
Where SSj is corrected
for mean.
                                  - 182 -

-------
                             Appendix A-6
                             (continued)

   SS,^ =  (.0112 +  .0106 +  .0057 + .0048 + .0051 + .0033)2 76 +
           (.0092 +  .0130 +  .0055 + .0075 + .0026 + .0025)2 + 6 +
           (.0088 +  .0068 +  .0052 + .0069 + .0029 + .0033)2 76-
           (0.1149)2 7 18
   SSRA =  (.0407)2  7 6 + (.0403)2 76 + (.0339)2 7 6 - (.1149)2 7 18
   SSm =  .000276 + .000271 +  .000192 - .000733
   SS,^ =  .000006

   SSV =  (.0197)2  7 6 + (.0356)2 7 6 + (.0596)2 7 6 - (.1149)2 7 18
   SSy =  (.000065  + .000211 + .000592 -  .000733)
   SSV =  .000135

   SST =  .000899 - (.1149)2 7 18
   SST =  .000905 - .000733
   SST =  .000166

   SSj =  SST - (SSE + SSV  + SS^)
    SSj =  .000166 - (.000018 + .000135 +  .000006)
   SSj =  .000166  - .000154
    SSj =  .000012

Analysis of Variance Table:
        Mean Squares                           £
    RA    SS^ - 2 = .000003              MSRA/MSE  =  2>U
    Vel.   SSV  - 2  = .0000675             MSV/MS£  =  48.2
    Int.   SSj  - 4 = .000003              MSj/MSE  =  2.14
    Error  S$E  - 9 = .0000014
    F Test for RA is not significant at 0.10  level.
    F Test for V is  significant at 0.001  level.
    F Test for I is  not significant at 0.10 level.
                                   - 183 -

-------
                         Appendix A-6
                         (continued)

The following conclusions can be drawn:
1.  The one-sided test for variance shows a significant change
    in outlet loading with a change in velocity (A/C ratio) for
    each bag material except Teflon felt - Style 2663.  This does
    not say that the 2663 Teflon outlet loadings are not valid,
    only that the number of tests  was too few to show signifi-
    cance.  A time trend appears in the data which may partially
    explain the change in loading with change in velocity.   There-
    fore, from the analysis we cannot actually conclude that an
    increase in velocity produced an increase in outlet loading.

2.  The two-sided test for variance for the case of Nomex felt at
    three levels of reverse air shows  a very significant change
    in outlet loading with a change in velocity.  The reverse air
    and interaction between reverse air and velocity are not signif-
    cant.  However, the F-statistic is large enough to indicate
    the relationship may be there but is not demonstrated due to
    degrees of freedom; i.e. sample size.

3.  The one-sided test for variance for the case of Nomex felt at
    three levels of reverse air shows a significant change in out-
    let loading with a change in reverse air at the high velocity.
    However, the relationship is not found significant at low or
    medium velocity.  This explains why the interaction F-statistic
    was relatively large.  That is there is an interaction  but only
    at the high velocity.

4.  Finally, the high significance of the two sided test for
    increased loading with increased velocity reinforces the signif-
    cance demonstrated in the one-sided test for each bag material.
                              - 184 -

-------
                         Appendix A-6
                         (continued)

4.  (continued)
    It can be concluded that the complication of time trend,  while
    present, does not preclude reliability of the data.
                             -  185  -

-------
                             Table A-5
            Tabulation of Data for Statistical Analysis
Andersen
Test No.
15
13
14
16
17
38
39
40
Air-to-Cloth 9
Ratio ACFM/Ft/
Nomex
2.9
3.1
3.1
6.1
6.1
6.1
8.7
8.2
Outlet Loading
GR/SCFD
Felt
.0020
.0021
.0025
.0016
.0028
.0045
.0072
.0047
Outlet Loading
.000004
.000004
.000006
.000003
.000008
.000020
.000052
.000022
                                         .0274
                                          .000119
                       Teflon Felt - Style 2063
10
11
12
5
6
8
9
5.2
5.2
5.2
8.0
8.0
14
14
.0120
.0158
.0159
.0038
.0040
.0201
.0388
.000144
.000250
.000253
.000014
.000016
.000404
.001505
                                         .1104
                                          .002586
                       Teflon Felt - Style 2663
79
80
78
77
81
 5.4
 5.5
 8.4
14.2
14
.000016
.000027
.000105
.000230
.000092
.000470
                                   -  186  -

-------
                             Table A-5  (cont'd)
Andersen
Test No.
  32
  33
  23
  19
  21
  25
  26
  34
  22
  28
  27
  69
  70
  66
  67
  68
  64
  65
Tabulation of Data for Stati
stical Analysis
Air-to-Cloth ,, Outlet Loading
Ratio ACFM/Ft/ GR/SCFD
Gore-Tex/Nomex
2.7
3.2
3.6
5.5
6.0
6.2
6.3
6.3
6.5
8.6
9.0

Oral on T
3.3
3.3
6.1
6.1
6.1
8.5
8.9

.0046
.0044
.0045
.0054
.0034
.0018
.0022
.0062
.0030
.0084
.0065
.0504
.0093
.0080
.0065
.0055
.0085
.0053
.0060
.0491
Outlet Loading'
   .000021
   .000019
   .000020
   .000029
   .000012
   .000003
   .000005
   .000038
   .000009
   .000071
   .000042
   .000269
    .000087
    .000064
    .000042
    .000030
    .000073
    .000028
    .000035
    .000359
                                   -  187  -

-------
                 Table A-5 (cont'd)
Tabulation of Data for Statistical Analysis
Andersen
Test No,
41
42
43
44
45
46
47
48
53
54
55
56
Air-to-Cloth
Ratio ACFW/Ft.
9.3
8.6
8.6
9.6
9.6
7.8
6.5
6.5
6.4
6.4
6.4
6.4
Reverse Air
Level /ACFM
Nomex Felt
1420
1420
3160
3160
4000
4000
1400
1400
3100
3100
4000
4000
Outlet Loading
GR/SCFD
.0112
.0106
.0092
.0130
.0088
.0068
.0596
.0057
.0048
.0055
.0075
.0052
.0069
Outlet g
Loading
.000125
.000112
.000085
.000169
.000077
.000046
.000614
.000032
.000023
.000030
.000056
.000027
.000048
                                    .0356
.000216
57
58
59
60
61
62


3,1
3.4
3.4
3.4
3.3
3.3


1400
1400
3160
3160
4000
4000


.0051
.0033
,0026
.0025
.0029
.0033
.0197
.1149
.000026
.000011
.000007
.000006
.000008
.000011
.000069
.000899
                     - 1!

-------
                                             Table A-6
I


00

I
Variance
Teflon Felt
ssv
SSE
Source of Variation
- Style 2063
Between Velocities
Within Velocities
Analysis
Sum
of Squares
.000661
.000184
of Variance Table
Degrees of
Freedom
2
4
Mean
Squares F-Statistic
.000331 7.2
.000046
Gore-Tex/Nomex
ssv
ssE
Oral on T
ssv
ss£
Nomex Felt
Between Velocities
Within Velocities
Between Velocities
Within Velocities

.000022
.000016
.000010
.000004

2
8
2
4

.000011 5.5
.000002
.000005 5
.000001

ss,
ssr
                   Between Velocities      .000018


                   Within Velocities       .000007
2


5
.000009


.0000014
                                                                                      Significant  at
                                                                                      .05 level
                                                                                      Significant  at
                                                                                      .05  level
                                                                                      Significant  at
                                                                                      0.10  level
6.43       Significant at
           .05 level

-------
         Table A-6  (cont'd)
Analysis of Variance Table
(continued)
Variance
Teflon Fel
ssv
ssE
Nomex Felt
SSy
ssE
Nomex Felt
SSy
ss£
Nomex Felt
SSy
ssE
Nomex Felt
SSy
SSC
Source of Variation
t - Style 2663
Between Velocities
Within Velocities
at Low Velocity - 3
Between RA Levels
Within RA Levels
at Medium Velocity -
Between RA Levels
Within RA Levels
at High Velocity - 3
Between RA Levels
Within RA Level
Sum
of Squares
.000063
.000016
Levels of RA
.000002
.000013
3 Levels of RA
.000002
.000013
Levels of RA
.000014
.000013
- 3 Levels of Velocity - Assuming RA
Between Velocities
Within Velocities
.000135
.000031
Degrees of
Freedom
2
2
2
9
2
9
2
9
Constant
2
15
Mean
Squares F-Statistic
.000032 4.0
.000008
.000001 0,7
.0000014
.000001 0.7
.0000017
.000007 5.0
.0000014
.0000675 33.8
.000002
Conclusion
Not Significant

Not Significant

Not Significant

Significant at
.05 level

Significant at
.001 level


-------
Table A-6 (cont'd)
Analysis of Variance Table
(continued)
Variance
Nomex Felt
SSRA
ssv
SSj
ssr
Source of Variation
at 3 Velocities and 3
Between RA Levels
Between Velocities
Interaction
Error
Sum
of Squares
Degrees of
Freedom
Mean
Squares
F-Statistic
Conclusion
Levels of Reverse Air
.000006
.000135
.000012
.000013
2
2
4
9
.000003
.0000675
.000003
.0000014
2.14
48.2
2.14
Not Significant
Significant at
.001 level
Not Significant

-------
                                 TECHNICAL REPORT DATA
                          (Please read Instructions on the reverse before completing)
1. REPORT NO.
EPA-650/2-74-058-a
                            2.
4. TITLE AND SUBTITLE
Applying Fabric Filtration to Coal Fired Industrial
   Boilers (A Pilot Scale Investigation)
7.AUTHOH(s)
               D. McKenna, JohnC.  My cock, and
William O.  Lipscomb
                                                       3. RECIPIENT'S ACCESSION-NO.
                                  5. REPORT DATE
                                  August 1975	
                                  6. PERFORMING ORGANIZATION CODE
                                                       8. PERFORMING ORGANIZATION REPORT NO.
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Enviro-Systems and Research, Inc.
P.O. Box 658
Roanoke, VA 24004
                                   10. PROGRAM ELEMENT NO.
                                   1AB012; ROAP 21ADM-033
                                   11. CONTRACT/GRANT NO.

                                   68-02-1093
12. SPONSORING AGENCY NAME AND ADDRESS
EPA,Office of Research and Development, Industrial
   Environmental Research Laboratory, Research Tri-
   angle Park, NC 27711; Enviro-Systems and Research,
   Inc.:  and Kerr Industries. Concord. NC
                                   13. TYPE OF REPORT AND P
                                   Final; 6/74 - 4/75
                                                                       D PERIOD COVERED
                                   14. SPONSORING AGENCY CODE
IS. SUPPLEMENTARY NOTES
16. ABSTRACT The report gives results of a pilot scale investigation to determine the tech-
noeconomic feasibility of applying a fabric filter dust collector to coal fired industrial
boilers. It extends and confirms preliminary work reported in July 1974.  The pilot
facility, on a slip stream of a 60,000 Ib/hr boiler, was capable of handling 11,000
acfm at an air-to-cloth (A/C) ratio of 6/1. Filter media evaluated were Nomex felt,
Teflon felt (two styles), Gore-Tex, and Dralon-T.  Fractional efficiency was deter-
mined using an Anders en-inertia! impactor for the four filter media at three A/C
levels. The effect of reverse air volume on outlet loading and pressure drop across
the bags was evaluated for Nomex felt.  Nomex felt achieved the lowest outlet dust
concentrations while Teflon felt operated at the lowest pressure drop.  All media
tested achieved outlet loadings well within allowable limits. Higher collection effic-
iencies were achieved with Nomex felt by discontinuing reverse air cleaning. Varying
the volume of reverse air from 1400 to  4000 acfm had little effect on removal effic-
iency. Increasing the amount of air used for cleaning does reduce the pressure drop
across the bags. Installed annual operating and total annualized costs for a fabric
filter and an electrostatic precipitator, capable of handling 70,000 acfm of flue gas
from a coal fired boiler, are presented. A full scale demonstration is anticipated.
17.
                              KEY WORDS AND DOCUMENT ANALYSIS
                 DESCRIPTORS
Air Pollution
Filtration
Filter Materials
Coal
Combustion
Industrial Heating
Boilers
Dust Collectors
Feasibility
Te trafluor oe thy le ne
  Resins
                                           b.lDENTIFIERS/OPEN ENDED TERMS
Air Pollution Control
Stationary Sources
 abric Filters
 bmex
 eflon
  re-Tex,  Dralon-T
                                               c. COSATI Field/Group
13B
07D
13K, 14A
21D
21B, 111
13A
18. DISTRIBUTION STAThMENT


Unlimited
                      19. SECURITY CLASS (This Report)
                      Unclassified
                         21. NO. OF PAGES
                             203
                      20. SECURITY CLASS (This page)
                      Unclassified
                                               22. PRICE
EPA Form 2220-1 (9-73)
                                       - 192 -

-------