EPA/600/R-12/732
                         April 2013
Environmental Technology Verification

Baghouse Filtration Products
TTG Inc.
TG800 Filtration Media
(Tested August 2012)
              Prepared by

    RTI International           ETS Incorporated
 HRTI
 INTERNATIONAL
          Under a Cooperative Agreement with
          U.S. Environmental Protection Agency
              EPA
 ET/ ET/ ET/

-------
Environmental Technology Verification
                      Report

        Baghouse Filtration Products

                      TTG Inc.
                TG800 Filtration Media
                (Tested August 2012)


                       Prepared by
                      RTI International
                      ETS Incorporated
             EPA Cooperative Agreement CR 83416901-0
                     EPA Project Officer
                      Michael Kosusko
              Air Pollution Prevention and Control Division
            National Risk Management Research Laboratory
                Office of Research and Development
               U.S. Environmental Protection Agency
                Research Triangle Park, NC 27711

-------
          THE ENVIRONMENTAL TECHNOLOGY VERIFICATION
                                 PROGRAM
SEPA
U.S. Environmental Protection Agency
                              ET/
                              HRTI
                              INTERNATIONAL
                 ETV Joint Verification Statement
     TECHNOLOGY TYPE:

     APPLICATION:


     TECHNOLOGY NAME:

     COMPANY:

     ADDRESS:

     WEB SITE:
     E-MAIL:
BAGHOUSE FILTRATION PRODUCTS

CONTROL OF PM2 5 EMISSIONS BY BAGHOUSE
FILTRATION PRODUCTS

TG800 Filtration Media

TTG Inc.
7561 South Highway 13
Higginsville, MO 64037
http://ttgtech.net
ttrimble@ttgtech.net
PHONE:  660-584-2448
FAX:     660-584-3422
 The U.S. Environmental Protection Agency (EPA) created the Environmental Technology Verification
 (ETV) Program to facilitate the deployment of innovative or improved environmental technologies
 through performance verification and dissemination of information. The goal of the ETV Program is to
 further environmental protection by accelerating the acceptance and use of improved and cost-effective
 technologies. The ETV Program seeks to achieve this goal by providing high-quality, peer-reviewed data
 on technology performance to those involved in the design, distribution, financing, permitting, purchase,
 and use of environmental technologies.

 The ETV Program works in partnership with recognized standards and testing organizations; stakeholder
 groups, which consist of buyers, vendor organizations, permitters, and other interested parties; and with
 the full participation of individual technology developers. The program evaluates the performance of
 innovative technologies  by developing test  plans that are responsive to the needs of stakeholders,
 conducting field or laboratory tests (as appropriate), collecting and analyzing data, and preparing peer-
 reviewed reports. All evaluations are conducted in accordance with rigorous quality assurance (QA)
 protocols to  ensure that data of known and adequate quality are generated and that the results  are
 defensible.

-------
The Air Pollution Control Technology Center (APCT Center) is operated by RTI International* (RTI), in
cooperation with EPA's National Risk Management Research Laboratory (NRMRL). The APCT Center
evaluates the performance of baghouse  filtration  products  (BFPs) used primarily to control PM2s
emissions (i.e., particles  2.5  urn and smaller in aerodynamic diameter). This  verification statement
summarizes the test results for TTG Inc.'s TG800 filtration media.

VERIFICATION TEST DESCRIPTION

All tests were  performed in accordance with the APCT Center  Generic  Verification  Protocol for
Baghouse Filtration Products, available at http://www.epa.gov/etv/pubs/05_vp_bfp.pdf The protocol is
based on and describes modifications to the equipment and procedures described in Verein Deutscher
Ingenieure  (VDI)  3926,  Part 2,  Testing of Filter Media for Cleanable Filters under  Operational
Conditions, December 1994. The VDI document is  available  from Beuth Verlag GmbH, 10772  Berlin,
Germany. The protocol also  includes requirements for  quality management and QA, procedures for
product selection, auditing of the test laboratories, and the test reporting format.

Outlet particle  concentrations from a  test fabric  were measured with  an impactor equipped  with
appropriate substrates to filter and measure PM2 5 within the dust flow. Outlet particle concentrations were
determined by weighing the mass increase of dust collected in each impactor filter stage and dividing by
the gas volumetric flow through the impactor.

Particle size was measured while injecting  the test dust into the air upstream of the baghouse filter
sample. The test dust was dispersed into the flow using a  brush-type dust feeder. The  particle size
distributions in the air were determined both upstream  and downstream of the test filter fabric to provide
accurate results for penetration of PM2 5 through the test filter. All  tests were performed using a constant
18.4 ± 3.6 g/dscm (8.0 ±  1.6  gr/dscf) loading rate,  a  120 ± 6.0 m/h (6.6 ± 0.3  fpm) filtration velocity
[identical to gas-to-cloth ratio (G/C**)], and  aluminum  oxide test  dust with a measured mass mean
aerodynamic diameter maximum of 1.5 urn (average of three impactor runs). All BFPs are tested in their
initial (i.e., clean) condition.

Each of the three test runs consisted of the following segments:

•   Conditioning period—10,000 rapid-pulse cleaning cycles
•   Recovery period—30 normal-pulse cleaning cycles
•   Performance test period—six-hour filter fabric test period with impactor.

VERIFIED TECHNOLOGY DESCRIPTION

Baghouses are air pollution control devices used to control particulate emissions from stationary sources
and are among the technologies evaluated by the APCT Center. Baghouses and their accompanying filter
media have long been one of the  leading particulate control techniques for industrial sources.  Increasing
emphasis on higher removal efficiencies has  helped the  baghouse to be continually more competitive
when compared to the  other generic PM control devices to the point  where the baghouse is now the
control option of choice for most industrial  applications. The  development of new and improved filter
media has further enhanced baghouse capability to control fine PM over an expanded range of industrial
applications.
 RTI International is a trade name of Research Triangle Institute.
  Filtration velocity and gas-to-cloth ratio are used interchangeably and are defined as the gas flow rate divided by
the surface area of the cloth.

-------
TTG Inc. provided the following information about their filter media product. The TTG Inc. TG800
filtration media is a 16 ounces per square yard (oz/yd2) scrim-supported polyphenylene sulfide (PPS) felt
laminated with an ePTFE (expanded polytetrafluoroethylene) membrane. Figure 1 is a photograph of the
fabric.  Sample material was received as nine  46 x 91 cm  (18 x 36 in.) swatches marked  with the
manufacturer's model number, year and month  of manufacture, and cake  side (the upstream side of the
fabric, which is exposed to the particle-laden air on which the filter cake builds up). Three of the swatches
were selected at random for preparing three circular test specimens 150 mm (5.9 in.) in diameter.
                              TG800  PPS
                                  Membrane
                 Figure 1. Photograph of TTG Inc.'s TG800 filtration media

VERIFICATION OF PERFORMANCE

Verification testing of the TTG Inc.'s TG800 filtration media was performed during the period of August
9 - 16, 2012, for standard test conditions at the test facility of ETS Incorporated, 1401 Municipal Road
NW, Roanoke, VA 24012. Test conditions are listed in Table 1. The overall test results summarized in
Table 2 represent the averages of three individual tests.

The APCT Center quality manager has reviewed the test results and the quality control (QC) data and has
concluded that the data quality objectives given in the generic verification protocol and test/QA plan have
been attained.

This verification  statement  addresses  five aspects of filter fabric  performance: filter outlet  PM25
concentration, filter outlet total mass concentration, pressure drop, filtration cycle time, and mass gain on
the filter fabric. Users may wish to consider other performance parameters, such as temperature, service
life, and cost when selecting a filter fabric for their application.

-------
                Table 1. Test Conditions for Baghouse Filtration Products
                      Brand/Model: TTG Inc.'s TG800 Filtration Media
Test Parameter
Dust concentration
Filtration velocity (G/C)
Pressure loss before cleaning
Tank pressure
Valve opening time
Air temperature
Relative humidity
Total raw gas stream flow rate
Sample gas stream flow rate
Number of cleaning cycles
During conditioning period
During recovery period
Performance test duration
Value
18.4 ± 3.6 g/dscm (8.0 ± 1.6 gr/dscf)
120 ±6 m/h (6.6±0.3fpm)
1, 000 ±12 Pa (4 ±0.05 in. w.g.)
0.5 ± 0.03 MPa (75 ± 5 psi)
50 ± 5 ms
25 ± 2 °C (77 ± 4 °F)
50 ±10%
5.8 ± 0.3 m3/h (3.4 ± 0.2 cfm)
1.13 ± 0.06 m3/h (0.67 ± 0.03 cfm)
—
10,000 cycles
30 cycles
6h±1 s
Beginning of table  description.  Table  1  is titled Test Conditions for Baghouse Filtration  Products; the
Brand/Model is listed as TTG Inc.'s TG800 Filtration  Media. The table describes the test conditions that
are specified in the QA/QC requirements for the test;  all conditions were achieved for this test. The table
lists the test parameters in one column and their values in the next column. The test parameters include
such items as the dust concentration, filtration velocity, flow rates, air temperature and humidity, and the
number of cleaning cycles during the test. End of table description.

-------
           Table 2. Baghouse Filtration Product Three-Run Average Test Results
                            for TTG Inc.'s TG800 Filtration  Media
                       Verification Parameter
                      At Verification Test
                          Conditions
 Outlet particle concentration at standard conditions3
    PM25, g/dscm
          (gr/dscf)
   Total mass, g/dscmb
          (gr/dscf)
                         <0.0000167C
                         (<0.0000073)
                         <0.0000167C
                         (<0.0000073)
Average residual pressure drop (A P), cm w.g. (in. w.g.)
Initial residual A P, cm w.g. (in. w.g.)
Residual A P increase, cm w.g. (in. w.g.)
Filtration cycle time, s
Mass gain of test sample filter, g (gr)
Number of cleaning cycles
2.76 (1 .09)
2.74 (1 .08)
0.06 (0.02)
218
0.10(1.54)
98
   Standard conditions: 101.3 kPa (14.7 psia) and 20 °C (68 °F). One or more of the impactor substrate
   weight changes for these results were near the reproducibility of the balance.
b  Total mass includes the mass of PM2.5 and larger particles that passed through the fabric.
c  The measured value was  determined  to be below the detection limit of 0.0000167 grams per cubic
   meter. The detection limit is for a six-hour test and based on VDI 3926.
Beginning of table description.  Table 2 is titled  Baghouse Filtration  Product Three-Run Average Test
Results for TTG Inc.'s TG800 Filtration Media. The table lists the verified test results for this product. The
table lists the verification parameters in one column  and their values at the verification  test conditions in
the next column. The verification parameters listed include the outlet particle concentration, the pressure
drop characteristics, the filtration cycle time,  the mass gain of the test  sample, and number of cycles
during the test. End of table description.

In accordance with the generic  verification protocol,  this verification statement is applicable to  filter
media manufactured between the signature date of the verification statement and three years thereafter.
signed by Cynthia Sonich-Mullin   3/7/2013
Cynthia Sonich-Mullin            Date
Director
National Risk Management Research Laboratory
Office of Research and Development
United States Environmental Protection Agency
sisned by Jason Hill               11/1/2012
Jason Hill                        Date
Director
Air Pollution Control Technology Center
RTI International
NOTICE: ETV verifications are based on an evaluation of technology performance under specific, predetermined
criteria and the appropriate quality assurance procedures. EPA and RTI make no express or implied warranties as to
the performance of the technology and do not certify that a technology will always operate as verified. The end user
is solely responsible for complying with any and all applicable federal, state, and local requirements.  Mention of
commercial product names does not imply endorsement.

-------
Environmental Technology Verification Report                                     TTGInc., TG800
                                           Notice

This document was prepared by RTI International* (RTI) and its subcontractor ETS Incorporated (ETS)
with partial  funding from Cooperative Agreement No. CR 83416901-0 with the U.S. Environmental
Protection Agency (EPA). The document has been  subjected to  RTI/EPA's peer and  administrative
reviews and  has  been approved  for  publication. Mention of corporation  names,  trade  names, or
commercial products does not constitute endorsement or recommendation for use of specific products.
 RTI International is a trade name of Research Triangle Institute.

-------
Environmental Technology Verification Report                                     TTGInc., TG800
                                          Foreword

The  Environmental  Technology Verification (ETV)  Program, established  by the  U.S.  Environmental
Protection Agency (EPA), is designed to accelerate the development and commercialization of new or
improved technologies through third-party verification and reporting of performance. The  goal of the
ETV Program is to verify the performance of commercially ready environmental technologies through the
evaluation of objective  and quality-assured data  to  provide  potential  purchasers and permitters  an
independent, credible assessment of the technology that they are buying or permitting.

The  Air Pollution Control Technology Center (APCT Center) is part of the  EPA's ETV Program and is
operated as a partnership between RTI International  (RTI) and EPA.  The APCT Center  verifies the
performance of commercially ready air pollution control technologies. Verification tests use approved
protocols,  and verified performance  is reported in verification statements signed by  EPA and RTI
officials. RTI contracts with ETS Incorporated (ETS) to perform verification tests on baghouse filtration
products, including filter media.

Baghouses are air pollution control devices used to control particulate emissions from stationary sources
and are among the technologies evaluated by the APCT Center. Baghouses and their accompanying filter
media have long been one of the leading particulate control techniques for industrial sources. Increasing
emphasis on higher removal efficiencies has helped the baghouse to be continually more  competitive
when compared to the other generic  PM  control devices to the point where the baghouse is now the
control option of choice for most  industrial applications. The  development of new and improved filter
media has further enhanced baghouse capability to control fine PM over an expanded range of industrial
applications. The APCT Center developed (and  EPA approved) the Generic Verification Protocol for
Baghouse Filtration Products to provide guidance on these verification tests.

The  following report reviews the performance of TTG Inc.'s TG800 filtration media. ETV testing of this
technology was  conducted during August 2012 at ETS. All testing was performed in accordance with an
approved test/quality assurance (QA) plan that implements the requirements of the generic  verification
protocol at the test laboratory.

-------
Environmental Technology Verification Report                                    TTGInc., TG800


                   Availability of Verification Statement and Report


Copies of this verification report are available from the following:

RTI International
Discovery & Analytical Sciences
P.O. Box 12194
Research Triangle Park, NC 27709-2194

U.S. Environmental Protection Agency
Air Pollution Prevention and Control Division (E343-02)
109 T. W. Alexander Drive
Research Triangle Park, NC 27711
Web Site: http://www.epa.gov/etv/vt-apc.html (electronic copies)
                                             in

-------
Environmental Technology Verification Report                                     TTGInc., TG800
                                    Table of Contents
                                                                                         Page
Notice	i
Foreword	ii
Availability of Verification Statement and Report	iii
List of Figures	v
List of Abbreviations and Acronyms	vi
Acknowledgments	viii
1.0   Introduction	1
2.0   Verification Test Description	2
      2.1   Description of the Test Rig and Methodology	2
      2.2   Selection of Filtration Sample for Testing	4
      2.3   Control Tests	4
      2.4   Analysis	5
3.0   Description of Filter Fabric	7
4.0   Verification of Performance	8
      4.1   Quality Assurance	8
      4.2   Results	8
      4.3   Limitations and Applications	9
5.0   References...                                                                         .. 10
                                              IV

-------
Environmental Technology Verification Report                                    TTGInc., TG800




List of Figures

                                                                                        Page

Figure 1. Diagram of filtration efficiency media analyzer test apparatus	3
Figure 2. Photograph of TTG Inc.'s TG800 filtration media	7
List of Tables
Table 1. Summary of Control Test Results	5
Table 2. Summary of Verification Results for TTG Inc.'s TG800 Filtration Media	9

-------
Environmental Technology Verification Report
TTGInc., TG800
                          List of Abbreviations and Acronyms





APCT Center      Air Pollution Control Technology Center




BFP              baghouse filtration product




cfm               cubic foot/feet per minute




cm               centimeter(s)




dia.               diameter




AP               pressure drop




DQO             data quality objective




dscmh            dry standard cubic meter(s) per hour




EPA              U.S.  Environmental Protection Agency




ePTFE            expanded polytetrafluoroethylene




ETS              ETS  Incorporated




ETV              Environmental Technology Verification




FEMA            filtration efficiency media analyzer




fpm               foot/feet per minute




g                 gram(s)




g/dscm            gram(s) per dry standard cubic meter




g/m3              gram(s) per cubic meter




G/C               gas-to-cloth ratio (filtration velocity)




gr                grain(s)




gr/dscf            grain(s) per dry standard cubic foot




GVP              generic verification protocol




h                 hour(s)




in.                inch(es)




kPa               kilopascal(s)




m                meter(s)
                                              VI

-------
Environmental Technology Verification Report                                     TTGInc., TG800






m/h               meter(s) per hour




m3/h              cubic meter(s) per hour




mbar             millibar(s)




min.              minute(s)




mm               millimeter(s)




MPa              megapascal(s)




ms               millisecond(s)




oz/yd2            ounce(s) per square yard




Pa               pascal(s)




PM               particulate matter




PM25             particulate matter 2.5 micrometers in aerodynamic diameter or smaller




PPS              polyphenylene sulfide




psi               pound(s) per square inch




psia              pound(s) per square inch absolute




QA               quality assurance




QC               quality control




RTI              RTI International




s                 second(s)




t                 time




VDI              Verein Deutscher Ingenieure




w.g.              water gauge




urn               micrometer(s)




 C               degree(s)  Celsius




 F                degree(s)  Fahrenheit




 R               degree(s)  Rankine
o
                                               Vll

-------
Environmental Technology Verification Report                                    TTGInc., TG800
                                   Acknowledgments

The authors acknowledge the support of all those who helped plan and conduct the verification activities.
In particular, we would like to thank Michael Kosusko, U.S. Environmental Protection Agency's (EPA's)
Project Officer, and Bob Wright, EPA's Quality Manager, who both work as part of EPA's National Risk
Management Research Laboratory in Research Triangle Park, NC. Finally, we would like to acknowledge
the assistance and participation of TTG Inc. personnel, who supported the test effort.

For more information on TTG Inc.'s TG800, contact the following:

Mr. Tim Trimble
TTG Inc.
7561 South Highway 13
Higginsville, MO 64037
660-584-2448
ttrimble@ttgtech.net
For more information on verification testing of baghouse filtration products, contact the following:

Mr. Jason Hill
RTI International
P.O. Box 12194
Research Triangle Park, NC 27709-2194
919.541.7443
APCTVC@rti.org
                                            vni

-------
Environmental Technology Verification Report                                     TTGInc., TG800


1.0    INTRODUCTION

This report reviews the pressure drop (AP) and filtration performance of TTG Inc.'s TG800 filtration
media. Environmental Technology Verification (ETV) testing of this technology/product was conducted
during a series of tests in August 2012 by ETS Incorporated (ETS), under contract with the Air Pollution
Control Technology Center (APCT Center). The objective of the APCT Center and the ETV Program is
to verify, with high data quality, the performance of air pollution control  technologies. Control of fine-
particle emissions  from various industrial and electric utility sources  employing baghouse control
technology is within the scope of the APCT Center. An APCT Center program area was designed by RTI
International (RTI) and a technical panel of experts to evaluate the performance of particulate filters for
fine-particle  (i.e., PM2 5) emission control. Based on the activities  of this technical panel, the Generic
Verification Protocol for Baghouse Filtration Products1 was developed. This protocol was  chosen as the
best guide to verify the  filtration  performance of baghouse filtration products (BFPs).  The specific
test/quality assurance (QA) plan for the ETV test of the technology was developed and approved in May
2000, followed by an approved update in February 20062. The goal of the test was to measure filtration
performance of both PM25 and total particulate matter (PM), as well as the AP characteristics of the TTG
Inc. technology identified above.

Section 2 of this  report documents the procedures used for the test and the  conditions over which the test
was conducted. A description of TTG Inc.'s TG800 filtration media is presented in Section  3. The results
of the test are summarized and discussed in Section 4, and references are presented in Section 5.

This report contains summary information  and data from the test and the verification statement. Complete
documentation of the test results is provided in a separate data package report and an audit of data quality
report. These reports include the raw test  data from product testing and supplemental testing as well as
QA and quality  control (QC) activities and results. Complete documentation of QA/QC  activities and
results, raw test data, and equipment calibration results are retained in ETS's files for seven years.

-------
Environmental Technology Verification Report                                     TTGInc., TG800


2.0    VERIFICATION TEST DESCRIPTION
The BFPs were tested in accordance with the APCT Center Generic Verification Protocol for Baghouse
Filtration Products1 and the Test/QA Plan for the Verification Testing of Baghouse Filtration Products2
These documents incorporate  all the requirements for quality management, QA, procedures for product
selection, auditing of the test laboratories, and reporting format. The Generic Verification Protocol (GVP)
describes the overall procedures used for verification testing and defines the data quality objectives. The
protocol  is based on and  describes modifications to the equipment and procedures described in Verein
Deutscher  Ingenieure  (VDI)  3926,  Part  2,  Testing  of Filter Media for  Cleanable Filters  under
Operational Conditions, December 1994.3 The values for inlet dust concentration, raw gas flow rate, and
filtration velocity used for current verification testing have been revised in consultation with the technical
panel since posting of the GVP. These revisions are  documented in Section 4.1. The test/QA plan details
how the test laboratory at ETS implemented and met the requirements of the GVP.

2.1    Description  of the Test Rig and Methodology

The tests were conducted in ETS's filtration efficiency media analyzer (FEMA) test apparatus (Figure  1).
The test apparatus is based on the VDI 3926 Type 1  vertical duct design. The test  apparatus consists of a
brush-type dust feeder that disperses test dust into a  vertical rectangular duct (raw-gas channel). The dust
feed rate is continuously  measured and recorded via an electronic scale located beneath the dust feed
mechanism. The  scale has a continuous readout  with a resolution of  10 grams  (g). A radioactive
polonium-210 alpha source is used to neutralize the dust electrically before its entry into the  raw-gas
channel. An optical photo sensor monitors the concentration of dust and ensures that the flow is stable for
the entire duration of the test.  The optical photo  sensor does not measure absolute concentration, and is,
therefore, not the primary concentration measurement for the test.  A portion of the gas flow is extracted
from the raw-gas channel  through  the test filter,  which is mounted  vertically  at the entrance to a
horizontal duct (clean-gas channel). The clean-gas  channel  flow is  separated into two  gas streams, a
sample stream and a bypass stream. An  aerodynamic "Y" is used for this purpose. The aerodynamic "Y"
is designed for isokinetic  separation of the clean gas with 40% of the clean gas entering the sample-gas
channel without change in gas velocity. The sample-gas channel contains an Andersen impactor for
particle separation and measurement. The bypass channel contains an absolute filter. The flow within the
two segments of the "Y" is continuously monitored and maintained at selected rates by adjustable valves.
Two vacuum pumps maintain air flow through the raw-gas and clean-gas channels. The flow rates, and
thus the gas-to-cloth ratio (G/C) through the test filter,  are kept constant and measured using mass flow
controllers. A pressure transducer is used to measure the average residual AP of the  filter sample. The
pressure  transducer  measures the differential pressure across the filter samples every 3 seconds;  the
residual AP measurements are those taken 3 seconds after the cleaning pulse. The AP measurements are
then averaged, as described in  Appendix C, Section 4.4.1 of the GVP.1 High-efficiency filters are installed
upstream of the flow controllers and pumps to prevent contamination or damage caused by the dust. The
cleaning  system consists of a  compressed-air tank set at 0.5  megapascals (MPa) (75 pounds per square
inch (psi)), a quick-action diaphragm valve, and a blow tube [25.4 millimeters (mm) (1.0 inches (in.))
diameter (dia.)] with a nozzle [3 mm (0.12 in.) dia.] facing the downstream side of the test filter.

Mean outlet particle concentration is determined when a portion of the gas flow is extracted from the raw-
gas channel through the test filter, which is mounted vertically at the entrance to a horizontal duct (clean-
gas channel). The clean-gas flow is separated using  an aerodynamic "Y" so that a representative sample
of the clean gas flows  through an Andersen impactor that determines the  outlet  particle concentration.
Outlet particle concentrations  were determined by weighing the mass increase of dust collected in each
impactor filter stage and dividing by the  gas volumetric flow through the impactor.

-------
Environmental Technology Verification Report
           TTGInc., TG800
The particle size was measured while a fine dust was injected into the air stream upstream of the filter
fabric sample. The particle size distributions in the air were determined both upstream and downstream
of the test filter fabric to provide accurate results for penetration through the test filter of PM2 5.
                                                    DUST FEED FROM EXTERN.*!.HOPPER

                                                    DUST CHARGE NEUTRALIZER

                                                    RECTANGULAR CHANNEL
                                                    111 x292 mm (4-3/8 X11-1C1;)
                                                    PHOTOMETER

                                                    FILTER FIXTURE AND TEST FILTER

                                                    CYLINDRICAL EXTRACTION TUBE

                                                    CLEAN-GAS SAMPLE PORT

                                                    RAW-GAS SAMPLE PORT

                                                    CLEANING SYSTEM
                                                                               BACKUP
                                                                               FILTER
                                                                                   MASS FLOW
                                                                                   CONTROLLER
                                                     ABSOLUTE FILTER AND
                                                     ANDERSEMIMPACTOR
ADJUSTABLE
  VALVES
                                                                           CALIBRATED
                                                                           ORIFICE
                                                                BLOW TUBE
                                                                DIRTY AIR
                                                                FILTER
                                                                        CLEAN AIR PUMP
                                                           MASS FLOW
                                                          CONTROLLER
      DIRTYAJR
       PUMP
                                DUST
                                CONTAINER
             Figure 1. Diagram of filtration efficiency media analyzer test apparatus.

-------
Environmental Technology Verification Report                                      TTGInc., TG800


The following series of tests was performed on three separate randomly selected filter fabric samples:

    Conditioning period
    Recovery period

    Performance test period.
To simulate long-term operation, the test filter was first subjected to a conditioning period, which consists
of 10,000 rapid-pulse cleaning cycles under continuous dust loading. During this period, the time between
cleaning  pulses was  maintained at 3 seconds.  No  filter performance parameters  are  measured in this
period.

The conditioning period  is immediately followed by a recovery period, which allows the test filter fabric
to recover from  rapid  pulsing.  The recovery period  consists of 30  normal filtration cycles under
continuous and  constant dust loading. During a normal filtration cycle, the dust cake is allowed to form
on the test filter until a differential pressure of 1,000 pascals (Pa) (4.0 in. water gauge (w.g.)) is reached.
At this point, the test filter is cleaned by a pulse of compressed  air from  the clean-gas side of the fabric.
The next filtration cycle begins immediately after the cleaning is  complete.

Performance  testing occurred for a  6-hour period immediately following  the  recovery period (a
cumulative total of 10,030 filtration cycles after the test filter had been installed in the test apparatus).
During the performance test period, normal  filtration cycles  are maintained and,  as in the case of the
conditioning and recovery periods, the test filter is subjected to continuous and constant dust loading.

The filtration velocity (G/C) and inlet dust concentrations were maintained at 120 ± 6 meters (m)/hour (h)
(6.6 ± 0.3 feet  per minute (fpm)) and  18.4 ± 3.6 g/dry  standard  cubic  meter (dscm)  (8.0 ±1.6 grains
(gr)/dry standard cubic foot (dscf)), respectively, throughout all phases of the test.

2.2    Selection of Filtration Sample for Testing

Filter fabric samples of TG800 filtration  media were supplied to ETS  directly from  the manufacturer
(TTG Inc.), with a letter  signed by Tim Trimble, Owner/Engineering Director, TTG Inc., attesting that the
filter media were selected at random in  an unbiased manner from commercial-grade media and were not
treated differently in any manner from the media provided to customers. The manufacturer supplied the
test laboratory with nine 46 x 91 cm (18 x 36 in.) filter samples.  The test laboratory randomly selected
three  samples and prepared them for testing by cutting one test specimen of 150 mm (5.9 in.) diameter
from each selected sample for insertion in the test rig sample holder. The sample holder has an opening
140 mm (5.5 in.)  in diameter,  which  is  the dimension used to  calculate  the face area of the tested
specimen.

2.3    Control  Tests

Two types of control tests were  performed during the verification test series. The  first  was a  dust
characterization, which is performed monthly. The reference dust used during the  verification tests was
Pural  NF aluminum oxide dust. The Pural  NF dust was oven dried for two hours and sealed in an airtight
container prior to its insertion into the FEMA apparatus. The criteria for the dust characterization test are
a maximum mass mean  diameter of 1.5 ± 1.0 micrometers (um) and a concentration between 40% and
90% of particles less than 2.5 (im. These criteria must be met in order to continue the verification test
series.

The second control test, the reference value test, is performed quarterly using the reference fabric and the
FEMA apparatus.  The reference value test determines the weight gain of the reference  fabric, as well as
the maximum AP  (final residual pressure drop). The results of the test verified that the  FEMA apparatus

-------
Environmental Technology Verification Report
                                                                 TTGInc., TG800
was operating consistently within the required parameters. The average fabric maximum AP (average of
the repeated measurements of final residual pressure drop conducted during the quarter applicable to this
test) in a reference value test must be 0.60  centimeters (cm) w.g.  ± 40%, and the fabric weight gain
average must be 1.12 g ± 40%. Three reference value control test runs were conducted.  The results of the
control tests are summarized in Table 1.
                           Table 1. Summary of Control Test Results
—
Mass mean diameter, urn
% Less than 2.5 urn
Weight gain, g
Maximum pressure drop, cm w.g.
Requirement
1.5± 1.0
40%-90%
1.12 ±40%
0.60 ± 40%
Measured Value
2.38
51.82%
0.70
0.55
Criteria Met
Yes
Yes
Yes
Yes
Beginning of table description. Table  1  is titled Summary of Control Test Results. The table lists the
results of measurements meant  to characterize the operation  of the test apparatus. The mass mean
diameter of the challenge aerosol, the percent less than 2.5 micrometers in diameter, the weight gain of a
reference fabric and the maximum pressure drop of the reference fabric were measured. In  columns, the
table lists the QA/QC requirements, the values measured during the control tests, and whether or not the
criteria were met. For this test, all criteria were met. End of table description.
2.4    Analysis
The equations used for verification analysis are described below.
Af
Cds
C2.5ds
dia.
Fa
Fs
G/C
Mt
M2.5

N
"avg
P,
PS
Qa
Qds
Q2.5ds
Qst
t
to
Exposed area of sample filter, m2
Dry standard outlet particulate concentration of total mass, g/dscm
Dry standard outlet particulate concentration of PM25, g/dscm
Diameter of exposed area of sample filter, m
Dust feed concentration corrected for actual conditions, g/m3
Dust feed concentration corrected for standard conditions, g/dscm
Gas-to-cloth ratio, m/h
Total mass gain from Andersen impactor, g
Total mass  gain of particles equal to or less than  2.5  urn  diameter from Andersen
impactor, g.  This value may need to be linearly interpolated from test data.
Number of filtration cycles in a given performance test period
Average residual AP, cm w.g.
Residual AP for /'th filtration cycle, cm w.g.
Absolute gas pressure as measured in the raw-gas channel, millibars (mbar)
Actual gas flow rate, cubic meters (m3)/h
Dry standard gas flow rate, dry standard cubic meters per hour (dscmh)
Dry standard gas flow rate for 2.5 um particles, dscmh
Standard gas flow rate for a specific averaging time (t), dscmh
Specified averaging time or sampling time, seconds (s)
Average filtration cycle time, s

-------
Environmental Technology Verification Report
TTGInc., TG800
Ts     =       Raw-gas channel temperature, degrees Fahrenheit (°F)
wf     =       Weight of dust in feed hopper following specified time, g. Because of vibrations causing
               short-term fluctuations to the feed hopper, this value is measured as a 1 -minute  (min.)
               average.
w;     =       Weight of dust in feed hopper at the beginning of the specified time, g. Due to vibrations
               causing short-term fluctuations to the  feed hopper, this value is measured as a  1-min.
               average.
Conversion factors and standard values used in the equations are listed below.

460    =   0 °F, in degrees Rankine (°R)
1,013  =   Standard atmospheric pressure, mbar
528    =   Standard temperature, °R

Area of Sample Fabric, Af
           _
Actual Gas Flow Rate, Qa

      rt   n   [(7; +460)* 1013'
                      p * 528
Gas-to-Cloth Ratio, G/C
       G  Q
Standard Dust Feed Concentration, Fs, for a specified time, t
             fwv—
        F, =-r-
              (O:, *t)
Actual Raw Gas Dust Concentration, Fa
                 r(rr+460)*1013'
         s ~  :   [     P.*528
Dry Standard Clean Gas Particulate Concentration, Total Mass, Cds
                       M,
       C.,, = =r-
                            H-,0
             L"3"'     x     10°  L
Dry Standard Clean Gas Particulate Concentration, PM2 5 C2 sd
                 Q-.^*t* 1--
                                100

-------
Environmental Technology Verification Report
TTGInc., TG800
Filtration Cycle Time, tc
Average Residual Pressure Drop, Pavg
       P   =
              .V

3.0    DESCRIPTION OF FILTER FABRIC

The TTG Inc.  TG800  filtration  media  is a  16  ounces per square yard (oz/yd2) scrim  supported
polyphenylene  sulfide  (PPS)  felt  laminated with an  ePTFE  (expanded  polytetrafluoroethylene)
membrane. Figure 2 is a photograph of the fabric. Sample material was received as nine 46 x 91 cm (18 x
36 in.) swatches marked with the manufacturer's model number, year and month of manufacture,  and
cake side (the upstream side of the fabric, which is exposed to the particle-laden air, on which the filter
cake builds up).  Three of the swatches were selected at random for preparing three circular test specimens
150 mm (5.9 in.) in diameter.
                     TTG  Inc.
                     PC* TG800  PPS
                     ePTFE Membrane PPS Felt
                  Figure 2. Photograph of TTG Inc.'s TG800 filtration media.

-------
Environmental Technology Verification Report                                     TTGInc., TG800


4.0    VERIFICATION OF PERFORMANCE

4.1    Quality Assurance

The verification tests were conducted in accordance with an approved test/QA plan.2 The EPA quality
manager conducted an independent assessment of the test laboratory in June 2005 and found that the test
laboratory was equipped and operated as specified in the test/QA plan.

The ETS QA officer and the  APCT Center's QA  staff have reviewed the results of this test and have
found that the results meet the overall data quality objectives as stated in the test/QA plan. Because of the
highly efficient nature of the filter medium being tested, one or more of the impactor substrate weighings
for these results were below the reproducibility of the balance. The relative percent error in the post-filter
weighing measurements cannot be computed because some of the values were near zero. As a result of
this occurrence, the  tests do not meet the data quality objectives (DQOs) stated in the test/QA plan for
mass  gain associated  with outlet concentrations. However,  as stated in the test protocol, "for highly
efficient fabrics, the mass gains  stated for these quality objectives may not be achieved  in the specified
test duration. For these tests it is acceptable for the indicated DQO not to be met."

Data on calibration certificates for the flow  meters, flow transducers, weights, low- and high-resolution
balances, thermometer, and humidity logger are maintained at ETS in a separate data package.

Deviations from the test plan include organizational personnel changes.

The ETS QA officer and the APCT Center's QA staff have also reviewed the results of the control tests,
which are  summarized in Section 2.3, Table 1. The dust characterization control test met the appropriate
requirements of the test/QA plan and verification protocol. The reference fabric tests met maximum AP
and weight gain requirements established for reference fabric performance in the GVP, indicating the
measurement system is operating in control.

4.2    Results

Table 2 summarizes the mean outlet particle concentration measurements for the verification test periods.
Measurements were conducted during the six-hour performance test period. The performance test period
followed a 10,000-cycle conditioning period  and a 30-cycle recovery period.

Table 2 summarizes the  three verification  tests that were performed under standard verification test
conditions. The average residual AP across each filter sample at the nominal 120 m/h (6.6 fpm) filtration
velocity [for a flow rate of 5.8 m3/h (3.4 cfin)] is also shown in Table 2. This AP ranged from 2.64 to 2.87
cm w.g. (1.04 to 1.13  in.  w.g.) for the three filter samples tested. The  residual AP increase ranged from
0.04 to 0.10 cm w.g. (0.02  to  0.04  in. w.g.)  for the  samples tested.  All three  standard condition
verification runs  were used to  compute the averages  given in Table  2.  The  PM25 outlet  particle
concentration average  for the three runs is < 0.0000167 g/dscm. The total PM concentration average for
the three runs is < 0.0000167 g/dscm.

-------
Environmental Technology Verification Report
TTGInc., TG800
           Table 2. Summary of Verification Results for TTG Inc.'s TG800 Filtration Media
Test Run Number
PM2.5 (g/dscm)b
Total PM (g/dscm)
Average residual AP (cm w.g.)
Initial residual AP (cm w.g.)
Residual AP increase (cm w.g.)
Mass gain of sample filter (g)
Average filtration cycle time (s)
Number of cleaning cycles
6V2-R1
<0.0000167C
<0.0000167C
2.64
2.64
0.04
0.12
232
92
6V2-R2
<0.0000167
<0.0000167
2.76
2.74
0.04
0.08
214
100
6V2-R3
<0.0000167
<0.0000167
2.87
2.83
0.10
0.10
209
103
Average3
<0.0000167
<0.0000167
2.76
2.74
0.06
0.10
218
98
a  All three verification runs were used to compute averages.

b  One or more of the impactor substrate weight changes for these results were near the reproducibility limit of the
   balance.

c  The measured value was determined to be below the detection limit of 0.0000167  grams per cubic meter. The
   detection limit is for a six-hour test and based on VDI 3926

Beginning of table description. Table 2 is titled Summary of Verification Results for TTG Inc.'s TG800 Filtration Media.
The table lists the verified test results for the three replicate test runs and their averages. The table lists the particle
concentrations downstream of the sample filters, the pressure drop characteristics, the mass gain of the sample filter,
the average filtration  cycle time, and the number of cleaning cycles during the test. In separate columns, results for
these parameters are listed for each of the three test runs and their averages. End of table description.

4.3     Limitations and Applications

This verification  report addresses two aspects of BFP performance: outlet particle concentration and AP.
Users may wish to consider other performance parameters, such as service life and cost,  when selecting a
baghouse filtration fabric for their application.

In accordance with the GVP, the verification statement, which summarizes this test report, is applicable to
BFPs manufactured between the signature date of the verification statement and three years thereafter.

-------
Environmental Technology Verification Report                                     TTGInc., TG800
5.0    REFERENCES

1.      RTI International. 2001. Generic Verification Protocol for Baghouse Filtration Products, RTI
       International, Research Triangle Park, NC, February. Available at
       http://www.epa.gov/etv/pubs/05 vp bfp.pdf (accessed August 28, 2012).

2.      ETS Incorporated and RTI International. 2006. Test/QA Plan for the Verification Testing of
       Baghouse Filtration Products (Revision 2), ETS Incorporated, Roanoke, VA, and RTI
       International, Research Triangle Park, NC, February. Available at
       http://www.epa.gov/etv/pubs/600etv06095.pdf (accessed August 28, 2012).

3.      Verein Deutscher Ingenieure (VDI). 1994. VDI 3926, Part 2, Testing of Filter Media for
       Cleanable Filters under Operational Conditions, December 1994. Available from Beuth Verlag
       GmbH, 10772 Berlin, Germany.
                                              10

-------