United States
               Environmental Protection
               Agency
National Risk Management
Research Laboratory
Research Triangle Park, NC 27711
              Research and Development
EPA/600/SR-96/065 June 1996
EPA       Project  Summary
               Evaluation  and  Analysis  of  Gas
               Content and  Coal Properties  of
               Major Coal Bearing  Regions of the
               United  States

               Sushma Masemore, Stephen Piccot, Eric Ringer, and William P.  Diamond
                The report presents a compilation of
              quality assured data on  gas content
              and coalbed reservoir properties for 11
              major coal bearing regions in the U.S.
              The primary source of these data is the
              U.S.  Bureau of Mines (BOM) gas con-
              tent measurements program conducted
              during the 1970's and 1980's. In order
              to enhance the utility of the BOM data,
              an evaluation was conducted to com-
              pile and quality assure the original data,
              and to adjust the data as needed to
              improve quality and representativeness.
              The  report was compiled to provide
              access to these improved data at the
              basin level. Under this effort, the origi-
              nal  raw data records for the core
              samples were provided  by the BOM.
              The raw data  were digitized to allow a
              computer to accurately and consistently
              perform routine quality  assurance
              checks, consistently determine lost gas
              and total gas contents for each sample,
              and examine various corrections to the
              data. In addition, desorption constants
              for each coal  sample were determined
              from time series desorption curves gen-
              erated from the original data. Additional
              data presented include the results of
              equilibrium adsorption isotherm tests
              performed  by the Department of  En-
              ergy (DOE) in 1983 for approximately
              100 of the BOM coal samples. These
              results give important, basin level  in-
              formation on  the capacity of various
              coalbeds to store and release meth-
              ane. In order to provide  context and
              background, the report also character-
              izes the geology and coal and coalbed
              methane resources in each major U.S.
              coal basin.
   This Project Summary was developed
 by EPA's National Risk  Management
 Research Laboratory's Air Pollution
 Prevention and Control Division, Re-
 search 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
   The U.S. Environmental  Protection
 Agency's (EPA) Air  Pollution  Preven-
 tion and Control Division (APPCD) has
 undertaken a study to identify the most
 practical and  cost effective means to
 use coalbed methane control and utili-
 zation technologies to reduce methane
 emissions into the atmosphere. An ini-
 tial phase of this study was to charac-
 terize methane gas content in minable
 coalbeds of active coal  producing re-
 gions across the country. A joint evalu-
 ation with the U.S.  Bureau of Mines
 (BOM) was conducted to compile and
 quality assure the data gathered from
 the BOM's gas content measurements
 program executed during the 1970's
 and  1980's. The result of  this  multi-
 tiered quality assurance and computa-
 tional effort is a  database titled the
 Refined Gas Content (RGC) database.
 This database and the results of gas
 content trend  analysis are reported in
 the full report. The report presents a
 compilation of the gas content data and
 coalbed reservoir properties for  major
 coal bearing regions of the U.S. The
 following paragraphs summarize the
 sources of data, data management and

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quality assurance activities, and key find-
ings on a national level.
  In 1972, the BOM developed the "Direct
Method" (DM) for determining the gas con-
tent of coal  cores. The  DM  is based on
measurements of the gas volume evolved
from coal  cores  sealed  in airtight canis-
ters, where  the total gas  content is ob-
tained  as  the sum  of three gas volume
determinations identified as desorbed gas,
residual gas, and lost gas. The desorbed
gas volume  is determined from  cumula-
tive volume measurements made overtime
as  gas desorbs  from the coal surfaces
and microporous  structure. A desorption
rate curve  may  be developed from the
cumulative desorbed gas volume versus
time. This curve  initially increases rapidly
and eventually flattens out as gas sorbed
onto the coal reaches equilibrium with at-
mospheric pressure and methane concen-
tration. The  residual gas  content is de-
fined as the gas volume that is released
when  the core is crushed  to a fine  pow-
der. Lost gas is  defined as the gas that
evolves from the core samples from the
time that the coalbed is first encountered
by the drill to the time the sample is sealed
in the desorption canister.
  Since the  development of the DM, sev-
eral shortcomings have been identified that
have raised questions about the quality of
the  original data.  Examples of items not
included  in  the  DM  are:  accounting for
oxygen sorption onto coal, accounting for
liberation of other hydrocarbons  in addi-
tion to methane,  correcting the gas vol-
umes  for  standard  conditions, and cor-
recting for ash and moisture content. The
original DM  data were compiled and cal-
culated manually. This introduced some
quality and consistency problems. In par-
ticular, the lost gas derivations were con-
ducted somewhat inconsistently by differ-
ent  investigators  and technicians over the
years.
  In response to these shortcomings, the
BOM  developed  and tested  a modified
version of the DM known as the "Modified
Direct Method"  (MDM).  The  primary
change in the MDM  is that the composi-
tion of the desorbed and residual gas is
determined and used to quantify the ac-
tual volume  of methane  released, and to
correct for the oxygen sorption effect. This
change accounts for most of the differ-
ence between DM and MDM results. Cor-
rections are  also made for ambient atmo-
spheric conditions during  sampling and
testing, and for the ash and moisture con-
tent of the samples. The  currently  pub-
lished  BOM  data are based only on the
DM results, and do not include MDM data.
Regardless  of the  shortcomings of the
original method, the large and geographi-
cally representative data set compiled us-
ing the DM  is valuable for  conducting
mine ventilation  analyses,  coal  mine
degasification analyses, coalbed methane
development assessments, and methane
emission inventory development studies.

Development of the RGC
Database
  The BOM obtained gas content data for
1511 coal samples. Original raw data files
were available for 1100 of these samples.
Many of the  available  BOM files were
incomplete.  Missing data included coring
time parameters required to calculate  lost
gas, sample weights required to calculate
gas  content, and  incomplete  or  missing
pages from the records of the desorption
experiment.  Due to lack of pertinent data
required to  determine total gas content,
complete calculations could  not  be per-
formed with  confidence  on  423  of  the
samples. That  is, complete data  neces-
sary for RGC analysis were available for
677  of the  original  1511  BOM samples
(about 45 %).
  Several data processing, screening, and
calculational steps were completed to as-
sure the quality of the data, make neces-
sary corrections and  modifications, and
develop total  gas  content and sorption
time information for the samples. Examples
of some  of the exercises conducted in-
clude: digitization of the data which auto-
mated  error checking  and calculations;
screening  the data  for  completeness of
information  necessary  for calculation of
total gas content;  developing time series
desorption  curves and  screening graphi-
cal data to identify outliers that might indi-
cate errors  in the original data; calculating
lost gas values, using a standardized, com-
puter assisted routine to ensure consis-
tent results; and determining sorption times
from desorption curves  and Langmuir  iso-
therm  constants  from DOE  adsorption
data. In addition, the gas content on an
ash/moisture free basis was calculated for
samples where coal  analysis data were
available, and the effect of corrections for
site barometric pressure and temperature
conditions was examined using available
national weather service  data for a sub-
stantial subset of the  samples.
  Desorbed gas volume versus time plots
(defined as desorption curves) can be used
to determine rate constants such as sorp-
tion time. Time constants are important in
defining coalbeds which have the poten-
tial to quickly outgas the largest quantities
of gas.  Sorption time  is defined  as  the
amount of time required to release 63% of
the total gas contained in the coal at at-
mospheric  pressure. Sorption time  has
been identified as an effective measure of
the diffusion rate  and  is used in  coalbed
methane  reservoir  simulator  modeling.
Sorption rate constants are useful to both
coal mining  and coalbed methane recov-
ery operations.
  Adsorption isotherm  data were gener-
ated by the U.S.  Department  of Energy
(DOE) for approximately 100 coal samples
collected by the BOM.  The volume of gas
adsorbed  was reported at five pressure
stages ranging from 5 to 50 atm.* The
DOE data were used to develop adsorp-
tion isotherms (a plot of total gas adsorbed
as  a function  of  pressure) according  to
the Langmuir adsorption model. The iso-
therm curve relates the gas storage ca-
pacity as a  function of coalbed reservoir
pressure and is used to predict gas pro-
duction potential as reservoir pressure is
reduced.  The  equation for this isotherm
curve is  described  by two  constants:
Langmuir volume  and Langmuir pressure.
  Initial Corrections to BOM Gas Con-
tent Data: Some  errors and  inconsisten-
cies were  found  in the original desorbed
and lost gas values. Residual gas results
were determined directly from BOM labo-
ratory experiments, and there was no need
for  corrections in the RGC data. Errors in
the original desorbed gas values  resulted
from incorrect data  entry,  calculation er-
rors, and failure to include all of the incre-
mental desorbed  gas volumes in the cu-
mulative result. Errors in original  lost gas
values resulted mainly from imprecise ap-
plication of DM procedures used to deter-
mine lost gas values.
  Since the lost  gas  volume cannot be
quantified  directly, it is  inferred from an
empirical relationship  between time and
desorbed volume.  This relationship is that,
within the  first hours after a core is ex-
posed,  the desorbed volume is  a  linear
function of the square  root of time. Some
errors in lost time  calculations in the origi-
nal data were found and corrected.  In the
RGC analysis, lost time calculations were
automated, and a computerized linear re-
gression  was  executed on  the  first 10
desorbed  gas  volumes to determine lost
gas.
  The impact  of the corrections and re-
finements  that were made is  most signifi-
cant for the  lost gas values. On average,
(*) 1 atm = 98 kPa.

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RGC lost gas values are about 24% less
than the published BOM values. RGC lost
gas values are lower in each of the ba-
sins, ranging from -37 to -4% at the basin
level. The largest differences were for the
Arkoma and Raton Mesa Basins (-35 and
-37%, respectively); however, the overall
average is driven  by the large number of
samples  from  the  Northern Appalachian
Basin where the average difference was
-22%. RGC desorbed gas values range
from -9 to +19% at the basin level, but the
overall average difference  is zero.  The
relatively large  increase  evident  for
samples  from  the Greater  Green  River
Basin  (+19%) is  notable.  Except  for
samples  from  the Greater  Green  River
Basin, there is little overall  difference  in
total gas content  between the published
BOM  and the  RGC  samples. Since lost
gas values typically  make  up less than
5% of the  total gas, relatively small in-
creases in the corrected desorbed gas
values tend to  offset the larger decreases
in lost gas values.
  Corrections for Ash  and Moisture
Content: The BOM conducted coal analy-
ses on a selected number of the original
coal samples.  The BOM's original  publi-
cation presented ash content and appar-
ent coal  rank  for  each sample,  and the
remaining data were not published. These
data are presented in the full report. Since
it is generally true  that methane is not
adsorbed onto non-coal material,  ash and
moisture values can be  used to  make
appropriate corrections on the total mea-
sured gas contents. Total gas values for
ash and moisture  content were corrected
for RGC  samples. The ash  and moisture
weight percent distribution  for the RGC
samples is used to determine changes in
total gas content when ash  and moisture
are corrected. Ash/moisture  free gas con-
tents are higher than the as received gas
content by +9 to +34%  at the basin level
with an overall average of +21%.
  Corrections for Ambient Temperature
and Pressure: It has been recommended
that the volume of gas measured at ambi-
ent or atmospheric conditions in the field
be corrected for standard temperature and
pressure. In the original BOM data, only
the volume of gas at ambient conditions
was used to determine total gas content
of coal cores.  Unfortunately, temperature
and pressure at the sampling sites and
during  desorption  analysis  were not re-
corded, so the correction to standard con-
ditions could not be applied.
  In order to examine the effect of ambi-
ent pressure and  temperature variations
on gas content data, temperature and pres-
sure for the BOM sampling sites and sam-
pling dates were obtained from National
Weather  Service data.  Temperature and
pressure  data for 395  of the RGC  coal
samples  were obtained, and  conversion
from actual  to  standard  conditions  (de-
fined as 60°F* and 1 atm) was applied to
these samples.  The analysis may be lim-
ited somewhat  by  the  fact  that ambient
conditions during desorption testing  may
not be reflected if the samples were trans-
ported away from the site for testing. How-
ever, during the BOM sampling program,
samples  often  remained  at  or near  the
site during much of the desorption testing.
Thus, these corrections may be  consid-
ered reasonably representative overall.The
corrections to total gas  content values
ranged from -3 to -21% at the basin level
with an overall average  of -6%.

Data Summary and Trends
  The BOM/RGC database was reviewed
and analyzed to examine (1) representa-
tiveness of the data in terms of U.S. coal
production, and (2) basin level trends in
terms of gas content,  gas  content rela-
tionships (e.g., with depth, coal rank), and
reservoir properties (sorption  time, and gas
carrying capacity).
  The BOM/RGC database provides broad
geographic coverage of major coal  pro-
ducing regions in the  U.S. Nearly 90% of
1992  U.S.  coal production  is in  the 11
major coal basins that are the focus of the
full  report. The BOM samples represent
coals from 81 counties in 17  states. Some
of the counties represented in the original
data are no longer producing  coal. In 1992,
only 59 of the 81 counties represented in
the original data were still producing coal.
In 1992, there were 247 counties  produc-
ing  coal in the U.S. Approximately 55% of
1992 production is in counties represented
by  BOM/RGC samples. Within  each of
the basins,  gas content  data for many
different coalbeds are available.
  Gas Content Summary: The aggre-
gated RGC and "as-published" BOM data
were used to develop  a  range of com-
monly encountered gas  content values for
each of the  11  basins. The data  were
grouped  into five categories:  500 - 709,
300 - 499, 100 - 299, 50 -  99, and less
than 50 ft3/ton.* The  full report presents
the number  of coal samples within each
of these  ranges in each basin  and  the
average sample depth.
  Total gas content can vary  widely across
a given basin and within a given coalbed
depending on depth, rank, and other fac-
tors; however, some  trends  are evident.
Coalbeds  in the Arkoma, Black Warrior,
Central  Appalachian,  Northern Appala-
chian, Greater Green River,  and  Raton
Basins can  contain very high levels  of
gas. Within these basins, the  Mary Lee
coalbed  in Black Warrior, the Pocahontas
No. 3 coalbed in Central Appalachian, the
Williams  Fork coalbed in Greater  Green
River, and the Peach Mountain coalbed in
Northern Appalachian have  coals which
contain the highest gas contents; over 600
ft3/ton. The Arkoma and Black Warrior Ba-
sins exhibit the most consistently high gas
contents.  Samples  from the Central Ap-
palachian Basin are  evenly distributed
across the full range of gas contents. Most
Northern Appalachian Basin samples have
gas contents less than  300 ft3/ton,  with
most  between  100 and 300  ft3/ton. Most
Illinois Basin coal samples have gas  con-
tents  less than 100  ft3/ton. Samples  from
the Greater  Green  River Basin also ex-
hibit the  full range of gas contents,  includ-
ing some of the highest values  repre-
sented; however, many samples have low
gas content and are associated with  rela-
tively  shallow coal. San  Juan and  Raton
Basin samples generally contain less  than
300 ft3/ton, and are more concentrated  at
the lower gas content levels (less  than
100 ft3/ton). Piceance Basin samples cover
a  broad  range,  but with most samples
containing less than 100 ft3/ton. Powder
River Basin  coalbeds contain the least
gas (generally less than 50 ft3/ton).
  The relationship of total gas  content  to
coalbed  depth  and coal  rank was  exam-
ined based on the  complete RGC/BOM
data set. In general, gas content is thought
to increase with both depth and coal rank.
Higher rank coals are  associated with in-
creased  gas  generation,  and deeper
coalbeds are associated with  increased
methane adsorption (due to  higher pres-
sures) and a higher probability of gas  con-
tainment. Gas content has been observed
to increase  more  rapidly  at  shallower
depths, then level off with  increasing depth.
A logarithm curve (i.e., Gas  Content  =  a*
In (depth) +  b, where a and b are  con-
stants) provides  a  simple  mathematical
description of this general relationship.  This
functional  form is used to represent the
relationship  of  gas content with  depth
throughout the report.
  The relationship of increasing gas  con-
tent with coalbed depth  and rank  is evi-
dent in the RGC/BOM data.  Gas content
O °C = 5/9 (°F - 32).
O 1 ft=/ton = 3.1218 x ia5 m3/kg.

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is  seen to  increase with depth,  and low
volatile coals are associated with the high-
est gas contents, followed by medium and
high volatile coals. In addition, the  loga-
rithm model appears  to describe  the data
reasonably. There are also clear  differ-
ences at the basin level in the relationship
of gas content and depth, both in overall
gas content and  in the rate of increase of
gas content with  depth.
  While the increasing trend of gas con-
tent with depth and coal  rank is evident in
the data, this simple relationship does not
fully explain the variability observed in the
RGC/BOM  gas content data.  Regression
(using  the  logarithm  model) of total gas
content versus depth  is generally  weak (r2
<  0.5),  even  when the data are segre-
gated by rank. More robust relationships
are sometimes observed  locally within spe-
cific  coalbeds or counties, indicating that
changes in local coal properties are im-
portant. For example, it has been  found
that  the microporous structure of coal is
related to methane storage capacity. This
is  discussed in more detail below.  Local
relationships of  gas  content  with  depth
are examined  within basin level discus-
sion of the full  report.
   Sorption Time: Sorption time was com-
puted  from the  time series desorption
curves for each RGC coal sample.  Sorp-
tion  time can  vary significantly  within  a
given basin; however, there are clear dif-
ferences in sorption time among basins.
The  median sorption time across all ba-
sins  is about 30  days, and this value can
be used as a benchmark for identifying
regions with high, low, and average  sorp-
tion times. By this measure, Northern Ap-
palachian and  San Juan Basin coals can
be characterized as slow desorbers, while
Powder River and Raton Mesa coals des-
orb most rapidly. Coals in the remaining
basins  can  be considered  "average"
desorbers.  Several figures  in the full re-
port compare the average sorption time of
the basins.
  Sorption  time indicates how rapidly ini-
tial desorption from coal takes place, but
does  not describe diffusion through the
coal matrix. Thus, sorption time alone can-
not be used  as an indicator of coalbed
gas production. However, sorption time is
a useful indicator of direct gas emissions
from a coal  mining operation,  and from
post-mining  coal  handling operations.
Mines producing coal  with high gas con-
tent and low  sorption  time will likely pro-
duce significant quantities  of gas as coal
is continually exposed by mining opera-
tions.  Run-of-mine  coal  emerging  from
such  mines will continue to emit signifi-
cant quantities of gas to the atmosphere
during storage, handling, and transport op-
erations prior to consumption.
  Gas Storage Capacity: The Langmuir
adsorption isotherm is a model describing
the gas storage capacity  of  coal as  a
function of pressure  at a constant tem-
perature. Generally, gas storage capacity
increases  with increasing  pressure; in-
creasing rapidly at  first, and then leveling
off to a  maximum.  For  the full report,
Langmuir adsorption coefficients (Langmuir
volume and pressure) were calculated from
the DOE results. These data are summa-
rized in the full report.
  Langmuir volume  varies  considerably
across the samples analyzed (ranging from
300 to over 3000 ft3/ton), but is symmetri-
cally distributed with an average of about
1075  ft3/ton.  There  is  some variability
among basins; however, variability within
basins is equally significant. That is, there
seems to be no clear trend for coals from
one basin to have  significantly  more or
less  adsorptive capacity than coals from
another  basin.  Langmuir  volume also
seems largely independent of coal rank
and depth.
  Gas content and desorption  data are
available for 36 of the 100 samples ana-
lyzed by DOE. DOE did not specifically
examine the  relationship of gas content
and sorption rate to Langmuir adsorption.
Since the Langmuir curve represents the
maximum gas storage capacity at a given
pressure, the measured gas content should
be less than or equal to the volume indi-
cated by the Langmuir curve. Based  on
generalized information on the hydrostatic
gradient  (psi/foot) at the  basin level and
sample depth, it is possible to obtain a
rough idea  of the fraction of  the volume
indicated by  the  Langmuir curve  repre-
sented by the measured gas content. The
gas  volume  predicted  by the Langmuir
model appears to be about a factor of 2 to
3 higher than  the measured gas volume
(corrected for ash/moisture content). This
is based on calculations for a limited num-
ber of samples  at  pressures exceeding
200  psi* from the Black Warrior, Central
Appalachian,  Northern  Appalachian, and
Raton  Mesa  Basins, and appears  to  be
fairly consistent across basins. For some
shallow samples from the Northern  Appa-
lachian  Basin (less than about  200  psi
bed pressure, or about 500 ft** deep), the
measured gas content is near, and some-
times exceeds the  Langmuir  model pre-
diction.  This  may  be an  artifact of the
pressure gradient's being  non-representa-
tive at shallow depths, or may be related
to the  rapid increase of Langmuir  model
predictions  at low pressures.
                                                                                    O 1 psi = 6.89 kPa.
                                                                                    (**) 1 ft = 0.30 m.

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   Sushma Masemore, Stephen Piccot, and Eric Ringer are with Southern Research
     Institute, Chapel Hill, NC27514; and William Diamond is with the U.S. Bureau of
     Mines, Pittsburg Research Center,  Pittsburgh, PA 15236
   David A. Kirchgessner is the EPA Project Officer (see below).
   The complete report, entitled "Evaluation and Analysis of Gas Content and Coal
     Properties of Major Coal Bearing Regions of the United States, "(Order No. PB96-
     185 491; Cost:  $38.00, subject to change) will be available only from:
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
           Telephone: 703-487-4650
   The EPA Project Officer can be contacted at:
          Air Pollution Prevention  and Control Division
          National Risk Management Research Laboratory
          U. S. Environmental Protection Agency
          Research Triangle Park, NC 27711
United States
Environmental Protection Agency
National Risk Management Research Laboratory (G-72)
Cincinnati, OH 45268

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