United States
Environmental Protection
Agency
Air and Energy Engineering
Research Laboratory
Research Triangle Park NC 27711
Research and Development
EPA/600/S7-87/023  Feb 1988
Project Summary
Performance  and Modeling  of  a
Hot Potassium  Carbonate  Acid
Gas Removal System  in
Treating  Coal  Gas

J. S. Staton, R. W. Rousseau, and J. K. Ferrell
  Aqueous solutions  of potassium
carbonate, with and without an amine
additive,  were used as the acid gas
removal solvent in the Coal Gasifica-
tion/Gas Cleaning  Test Facility at
North Carolina State University. The
acid gas  removal system consisted of
a packed absorption column, one or
more flash tanks for  intermediate
pressure reduction, and a packed
stripping column operated with a
reboiler.  The  removal  of CO2, H2S,
COS, and other species from the crude
coal gas was studied, and data on the
distribution of these gases in regener-
ation exit streams were obtained.
Operating conditions for the selective
removal  of sulfur species were also
examined.
  A system model for  chemical sol-
vents was developed and incorporated
into a simulation program. The model
was based on the mass transfer rate
of a key component,  CO2, with the
assumption that non-key reactive com-
ponents affect the equilibrium of the
key component, but not  its  mass
transfer  rate. The  absorption and
stripping  of non-key components were
assumed  to be controlled by equilib-
rium between the gas and liquid phases
in these columns. An isothermal flash
model for chemical solvents was also
developed and included in the program.
  The  agreement between program
predictions and  pilot plant  data was
quite good, supporting the validity of
the model. Program simulations are
shown to provide insights into  the
effects of changes in process variables
on system operation.
  This Project  Summary was devel-
oped by EPA's Air and Energy Engi-
neering Research Laboratory, Research
Triangle Park, NC, to announce key
findings of the research project that is
fully documented in a separate report
of the same title (see  Project Report
ordering information at back).

Introduction
  As gasification processes  have
developed  in the U.S.,  it has become
apparent that improved technology in gas
cleaning is needed to meet current
environmental standards. As part of a
program to develop this technology, the
U.S. EPA sponsored a Coal Gasification/
Gas Cleaning Test Facility at  North
Carolina State University. The final gas
cleanup in this facility is accomplished
by an acid gas removal system (AGRS)
in which a solvent is circulated through
a packed absorption column for removal
of acid gases from the coal gas Several
flash tanks and a packed stripping
column are used for regeneration of the
solvent. A process that removes C02 and
H2S from a gas stream is referred to as
an AGRS due to the acidic nature of these
species.
  All previous work at  the facility has
employed refrigerated methanol as the
acid gas removal solvent. The experimen-
tal  work  described  in this report
employed an aqueous solution as potas-
sium carbonate, K2C03, as the  AGRS
solvent. This process is referred to as the

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hot potassium carbonate process since
absorption and regeneration units  are
typically operated at elevated tempera-
tures. The primary difference between
this solvent and methanol is that K2C03
removes the acid gases by a  chemical
reaction,  and  is thus  classified as a
chemical solvent, while methanol phys-
ically absorbs the acid gases, and is thus
termed  a  physical solvent.  Another
important difference is  the solubility of
organic compounds in the two solvents.
Hydrocarbons (e.g., methane,  benzene,
and large cyclic compounds) are essen-
tially insoluble in the aqueous  solution
of KzCOs, and will thus remain in  the
product gas stream.  Such compounds
are, however, highly soluble in methanol,
and they are absorbed and  ultimately
distributed in all gas streams leaving the
regeneration units. These hydrocarbons
are important for their energy values, and
many are also considered environmen-
tally hazardous.

Major Objectives
  The present  work  had two  primary
objectives:  (1) to evaluate the  perfor-
mance of aqueous solutions of hot K2C03
in conditioning  gases  produced from
coal, and (2) to develop a model that could
be used in  the design or simulation of
packed adiabatic absorbers and strippers
that use hot K2COa to  condition gases
produced from coal. An experimental
program was conceived and executed to
satisfy the first objective directly and to
assist with  the second. Several opera-
tional  variables were  purposefully
manipulated to examine the effect on
removal of CO2, H2S, and COS from the
gas  exiting  the absorber.  The model
developed to describe adiabatic absorp-
tion and stripping was incorporated into
a  system model that consisted  of an
absorber, a flash tank, and a stripper, and
a  computational procedure was devel-
oped to predict system performance.

Conclusions
  As a result  of the experimental and
modeling efforts, several conclusions
regarding the use of K2C03 can be drawn:

  1.  The model developed in this study
     predicted gas flow rates and com-
     positions that were in close agree-
     ment with measured values.

  2.  Heat effects with the hot K2C03
     process are less  than with most
     other  acid gas  removal  solvents.
     Calculations assuming isothermal
     absorption, flash  tank,  and strip-
    ping  operations give accurate
    results.

 3.  CO2 removal ranged from 38.1 to
    98.4% at the conditions examined,
    and was, in general, highly sensi-
    tive to AGRS operating conditions
    and solvent composition. The effect
    of H2S and other coal  gas species
    on the mass transfer  rate of C02
    appeared to be small.

 4.  The absorption of COz was found
    to be insensitive to solvent com-
    positon when the absorption of C02
    was  controlled by  equilibrium
    between the gas and liquid phases
    at the top of the absorber column.

 5.  The absorption of C02 was found
    to be highly dependent on solvent
    regeneration.

 6.  The regeneration of COa accom-
    plished by flashing was negligible
    at the conditions examined.

 7.  H2S removal ranged from 97.3 to
    100% at the conditions examined
    and was found to be insensitive to
    solvent composition. The absorp-
    tion of HzS  was found to be con-
    trolled  primarily by  equilibrium
    between the gas and liquid phases
    at the top of the absorption column.

 8.  COS  removal ranged from 20.0 to
    95.8% at the conditions examined
    and  appeared  to  be a function
    primarily of absorber temperature.

 9.  H2S and COS  may be selectively
    removed  with AGRS operating
    conditions that include low K2CO3
    concentrations, low absorber pres-
    sures,   and  high   absorber
    temperatures.

10.  The absorption of coal gas species
    that do not participate  in a reaction
    in  the  solvent was  found  to be
    insensitive to solvent  composition
    at  the conditions  examined.  The
    absorption of these  species was
    found to be controlled by equilib-
    rium  between  the gas and liquid
    phases  at the bottom of  the
    absorber column.

11.  An amine additive, commonly used
    to increase the mass transfer rate
    of C02, appeared to  have no sig-
    nificant effect on the fates of other
coal gas  species. This additive |
appeared to increase the absorp-
tion  of  C02  slightly when  such
absorption was controlled by equil-
ibrium between the gas and liquid
phases in the absorption column.

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     J. S. Staton, R.  W. Rousseau, and J. K. Ferrell are with North Carolina State
       University. Raleigh. NC 27695-7905.
     N. Dean Smith is the EPA Project Officer (see below).
     The complete report,  entitled "Performance and Modeling of a Hot Potassium
       Carbonate Acid Gas Removal System in Treating Coal Gas," (Order No. PB
       88-131 297/AS; Cost: $19.95) will be available only from:
            National Technical Information  Service
            5285 Port Royal Road
            Springfield, VA22161
            Telephone: 703-487-4650
     The EPA Project Officer can be contacted at:
            Air and Energy Engineering Research Laboratory
            U.S. Environmental Protection Agency
            Research Triangle Park, NC 27711
United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268

Official Business
Penalty for Private Use $300
EPA/600/S7-87/023
    0000329    PS

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