Upload
stanford
View
0
Download
0
Embed Size (px)
Citation preview
UCID- 19751
Organic antiPyriticSulfur Determination in Oil Shale
Sandra K. FadeffAlan K. Burnham
Jeffery H. Richardson
March 1, 1983
_—-
DISCLAIMER
This document was prepared as an account of work sponsored by an agency of the United States Government. Neitherthe United States Government nor the University of California nor any of their employees, makes any warranty, expressor implied, or assumes any legal liability or responsibility for the accuracy, completeness, or usefulness of anyinformation, apparatus, product, or process disclosed, or represents that its use would not infringe privately ownedrights. Reference herein to any specific commercial product, process, or service by trade name, trademark,manufacturer, or otherwise, does not necessarily constitute or imply its endorsement, recommendation, or favoring bythe United States Government or the University of California. The views and opinions of authors expressed herein donot necessarily state or reflect those of the United States Governrnent or the University of California, and shall not beused for advertising or product endorsement purposes.
This report has been reproduceddirectly from the best available copy.
Available to DOE and DOE contractors from theOffice of Scientific and Technical Information
P.O. Box 62, Oak Ridge, TN 37831Prices available from (615) 576-8401, PTS 626-8401
Available to the public from theNational Technical Information Service
U.S. Department of Commerce5285 Port Royal Rd.,
Springfield, VA 22161
...—.
ORGANIC AND PYRITIC
SULFUR DETERMINATION IN OIL SHALE
.
“
.
.
.
.
Abstract
Sulfur forms in oil shale are defined according to their reduction rates
to H2S in the presence of hydrogen-donor solvents. A linear increase in
temperature with time is applied to a reaction system of oil shale and
hydrogen-donor solvents. The different temperatures at which H2S is
detected corresponds to specific sulfur-functionality reductions and produces
a reaction profile, or kinetogram. The kinetograms of 10 standards and 13
different oil shales are given. The method of analysis is simple. Aromatic
and aliphatic disulfides, sulfides, thiols, and pyrite can be detected,
however we are not yet sure about the detection of thianthrene structures and
thiophenic structures. Our present results
approach, but improvements in the procedure
analytical technique.
Introduction
indicate that this is a promising
must be made to optimize the
The U.S. has extensive oil reserves as oil shale deposits in both the East
(Kentucky and Ohio) and West (Colorado, Utah, and Wyoming). A significant
problem in the development of a viable oil-producing industry from these oil
shale reserves is the production of hydrogen sulfide, sulfur dioxide, and
other gaseous sulfur compounds during retorting. In order to develop retort
conditions minimizing the emission of these noxious gases, the reactions
producing them need to be minimized (in conjunction with the use of gas
-2-
scrubber systems). To better understand the reactions producing sulfur gases,
the sulfur compounds in the raw oil shale, reaction pathways, and reaction
kinetics need to be characterized.
Sulfur compounds in oil shale are classified as sulfate, pyrite, and
organic. A frequently used method
“Standard Test Method for Forms of
solution of HC1 is used to extract
to define the sulfur speciation is the
Sulfur in Coal” (ASTM).l A dilute
sulfates from the sample (coal and oil
shale). Sulfates are determined gravimetrically by precipitation as BaS04.
Leaching this sample with dilute HN03 is supposed to extract the pyrite,
oxidizing the ferrous iron to ferric iron and sulfide sulfur to sulfate
sulfur. The Fe(III) is determined titrimetrically or via atomic absorption
spectrophotometry and is directly related to the pyrite content. The organic
sulfur content is determined by subtracting the sulfate and iron sulfide
content from the total sulfur content, which can be determined by a Fisher
total sulfur analyzer or other techniques.
Unfortunately, problems are associated with the application of the ASTM
sulfur determination in coal to sulfur determination in oil shale. The pyrite
sulfur content often is found to exceed the total sulfur content in the
sample. Smith et al.z point out that the predominantly inorganic matrix in
oil shale may cause interferences and errors in interpretation of results.
They developed an alternative method for the determination of sulfate, pyrite,
and organic sulfur based on the decomposition of pyrite by lithium aluminum
hydride. This analysis technique is relatively complicated and the lithium
aluminum hydride can be dangerous to handle.
Attar and Dupuis developed a method for organic sulfur determination in
Coa, 3,4,5. It involves reacting the sulfur species with a hydrogen donor
produce H2S. The basic concept of their method is applied here to the
determination of organic sulfur speciation in raw oil shale.
to
.
.
.
.
-3-
Under favorable conditions, sulfur compounds can be reduced to hydrogen
sulfide and other by-products. A source of hydrogen must be available and the
reaction must be favored kinetically. All sulfur of one functionality will
have similar reaction kinetics and will be reduced at one temperature to form
H2S. Conversely, sulfur of
hydrogen at different rates
reactive sulfur groups will
different functionalities will react with the
and at different temperatures. Since the more
be reduced at a lower temperature than the more
stable sulfur groups, the sulfur reduction reactions can be separated in time
by increasing the temperature of a reaction system with time. The temperature
at which reduction occurs is characteristic of the sulfur functionality.
Experimental Procedures
A schematic of the apparatus used is presented in Figure 1. The test
sample of approximately 10 mg was mixed with three hydrogen donor solvents:
0.15g pyrogallol, 0.2g resorcinol, and 0.2g tetralin. The mixture was placed
in a porcelain reaction boat and covered with a molded quartz cover slip with
a slit at one end for gas escape. The reaction boat was placed in the quartz
reaction tube in the programmable Lindberg oven. A thermocouple rested in an
indentation in the reaction tube near the reaction vessel. The oven was
controlled with the HP85 and HP3497A data acquisition/control system and the
temperature was increased at ll°C per minute. Nitrogen flowed through the
quartz tube over the reaction boat at 62 cm3/min (NTP). The effluent gas
stream passed through a dry ice-acetone cold trap (-77°C) where most organic
compounds were frozen out. The remaining product gases (H2S and lightweight
organic gases) were carried on to the Tracer Instruments flame photometric
detector (FPD). Undoubtable, H2S accounts for essentially all of the sulfur
-4-
content of the gas. Due to the approximately 2.5 minute lag time required for
gases to travel from the reaction boat to the detector, the temperature
recorded is offset about 27°C. This offset is partial ly cancelled by a 10
to 15°C difference between the recording thermocouple and the reaction
vessel. The total temperature uncertainty at the time of FPD measurements is
10° to 20°c. The flame in the detector was fueled with air (170
cm3/min) and hydrogen (77 cm3/min)(NTP). These gas flow rates provided
optimal flame stability and sulfur sensitivity. Sulfur emission from the
flame was detected by a photomultiplier tube (pint)proceeded by a 394 nm
optical filter. The pmt current was converted to voltage by an electrometer.
The voltage was recorded, along
the HP85 system.
The FPD was calibrated with
with the
standard
oven temperature, on magnetic tape by
gases of hydrogen sulfide in
nitrogen: 14.3 ppm H2S, 59 ppm H2S, and 104 ppm H2S (from Matheson Gas
Products). According to the FPD manual, the instrument response increases
approximately with the square of the concentration. The following equation
was derived and used to calculate concentration from electrometer voltage (V):
Concentration (ppm) = 370 x V0”54
The sulfur standards analyzed and their corresponding
listed
the ac”
adding
and dr
functionalities are
made by dissolvingin Table 1. The carboxylic acid sodium salts were
d in ethanol, adding concentrated NaOH until pH7 was reached, and
an excess of IN NaOH. The solution was roto-evaporated to near dryness
ed under vacuum overnight.
Oil shale samples were obtained from Utah (Geokinetics), and Colorado
(Anvil Points and Tract C-a). The sample location, grade, depth of burials
weight percent organic carbon, and weight percent total sulfur (determined by
-5-
9
a Fisher sulfur analyzer) are given in Table 2. Sulfur speciation by the ASTM
method is given in Table 3 for a few selected samples. All oil shale samples
were taken from previously collected and crushed stock stored in closed jars
under air. Each sample was further ground to a talc consistency. The samples
(except as noted below) were placed in a 10% HC1 solution for about one hour,
releasing the carbonates, sulfates and pyrrhotite, and increasing pore space.
The shale was collected” and dried under nitrogen.
Sample sizes for standards ranged from 0.2 mg to 5 mg depending on the
weight percent sulfur. Oil shale sample size ranged from 0.5 mg to 20 mg,
also depending on the total sulfur content. These were mixed with the
hydrogen donors and analyzed as previously discussed. Six samples from
Geokinetics and Anvil Points were also run without added hydrogen donors but
otherwise under identical conditions.
Because of reaction characteristics to be discussed below, four untreated
oil shale samples and the corresponding samples treated with the
were heated under autogenous conditions. A sample was placed in
capillary tube sealed at one end, and a small plug of quartz woo’
HC1 solution
a quartz
was placed
on top of the sample. The tube was positioned so the open end pointed
downstream from the nitrogen flow. The temperature was ramped and H2S was
.monitored as described.
.
Technique Development4
Attar and Dupuis used a sulfidized CO-MO catalyst (Harshaw 0402), the
three hydrogen donor solvents, and the organic sulfur-containing sample to●
form the reaction system. They determined that the catalyst promoted the
reduction of the sulfur species to H2S using the hydrogen from the hydrogen
donor solvents. However, in this work, we found that the presence or absence
of the catalyst makes no difference on the kinetogram characteristics.
-6-
Furthermore, the sulfur from the sulfidized catalyst, when mixed with the
solvents, was released as H2S at 220°C. This could cause significant
errors in analyzing the kinetograms. It is also doubtful that two solid
species, the catalyst and the shale particle, and the hydrogen donor solvent
can come into proper chemical contact for reduction to occur. The catalyst
could only catalyze the reaction of the hydrogen donor solvent with bitumen
and pyrobitumen, since they will dissolve allowing for proper intimate
chemica”
species
The
contact between the catalyst, hydrogen donor solvent, and sulfur
oil shale samples were pretreated in a 10% HC1 solution to release
carbonates from the oil shale matrix and increase the pore space. More H2S
was released and more clearly defined reation peaks were obtained when the
pretreatment step was utilized.
The FPD output signal (from H2S detection) increased as the starting oil
shale mass was increased. For Geokinetics 68’-69’ (1.06wt% sulfur), the
function was linear in the low mass range of O mg to 17 mg (O mg to 0.18mg
sulfur), and tapered off for masses above 17 mg (refer to Figure 2). Thus for
best comparisons between the various oil shale samples, the total sulfur
content should not exceed 0.18 mg in each sample analyzed.
Three blanks were run to test if hydrocarbons may give spurious signal
response. One blank consisted of the three hydrogen donor solvents in the
quantities normally used; a second was a 500-ppm methane gas standard in
nitrogen. No signal response was recorded from either sample. However, when
no cold trap was used in a third blank, tetralin at its room temperature vapor
pressure (or an impurity) did give a signal comparable to 30 ppm H2S, thus
uncondensed hydrogen-donor mixture would give an erroneous signal.
●
.
.
●
.
9
.
-7-
Results and Discussion
The reaction temperatures and peak characteristics for the various
standard functionalities analyzed are presented in Table 4. Representative
kinetograms are shown in Figure 3. The sulfides, disulfides, and thiols,
aromatic or aliphatic, react between 200°C to 260°C. The reaction peaks,
although sharp and distinct by themselves, occur at temperatures only 10°C
apart, which is about a one minute difference in time. Since they are
difficult to resolve from each other, a reaction peak in the 200°C to
260°C temperature range cannot be specifically assigned. (Slowing the
heating rate spreads the peaks out more in time, not improving the
resolution.) Pyrite produces a clear reaction peak at about 280°C as well
as a sharp peak at about 550°C. The relative amounts of H2S generated in
the two peaks depends on the effectiveness of contact with the hydrogen donor,
which in turn depends on the particle size and how evenly distributed the
pyrite is in the boat. The second peak is probably caused by unreacted pyrite
decomposing to pyrrhotite and S2, which subsequently reacts to form H2S.
In oil shales, most, if not all the pyrite reacts at 280°C; the reaction
rate may be enhanced because the pyrite is embedded in kerogen. The reaction
characteristics of marcasite (rhom. FeS2) are quite similar to pyrite (cubic
FeS2). The heterocyclic structures, thianthrene and thiophene, require high
energy to react; hydrogen sulfide is produced at a temperature of at least
400°c. Our results above about 350°C are not always reliable because of
(1) reaction of hydrogen donors with sulfur-containing
runs at the end of the tube and (2) hydrogen-donor fog
through the condenser and giving a false signal.
residue from previous
sometimes passing
-8-
The reaction profile, or kinetogram, of each oil shale examined is
unique. Certain properties are shared between the kinetograms such as peak
position: a reaction peak corresponding to pyrite reduction is present at
260°C to 320°C; a large diffuse peak occurs at 360°C and/or 420°C.
But the presence or absence of a peak at 200°C and the relative intensity of
these peaks vary between the different samples of oil shale. Refer to Figures
4 and 5 for examples of the oil shale kinetograms.
For extremely low sulfur containing oil shales (Geokinetics 78’-79’,
80’-81’, 56’-57’), the pyrite signal peak constitutes less than 5% of the
total signal output. The major portion of the sulfur appears to react at
temperatures above 400°C. Unfortunately, this signal may not be completely
real because of the problems discussed above. In oil shales of higher sulfur
content (Geokinetics 63’-64’, 47’-48’, 73’-74’ and 68’-69’; Anvil Points 24
and 60; and Tract C-a 18 and 25), the pyrite reduction peak is more
significant. Geokinetics 63’-64’, 47’-48’, 73’-74’, 68’-69’ and Anvil Points
24 also have a reaction peak at 200°C to 250°C, probably the reduction of
a sulfide, thiol, or disulfide.
To demonstrate the effect of hydrogen donors on H2S evolution and to
provide a comparison with previous work, seven treated oil shale samples were
run without the hydrogen donors. The kinetograms shown in Figure 6 are
similar to those obtained previously in a flowing argon atmosphere. The
peak at 480°C-5500C was attributed to “loose” pyrite (in contrast to
pyrite surrounded by kerogen), and the peak(s) around 400°C were attributed
to kerogen pyrolysis and the reaction of “surrounded” pyrite with organic
matter. The peak at 200°C was not previously observed. By comparison of
the kinetograms in Figure 6 with those in Figures 4 and 5, it can be seen that
●
*
-Y-
the pyrite peak shifts completely with added hydrogen donors, but the peaks at
200°C and around 400°C are affected substantially less. No significant
sulfur evolution occurs above 600°C without added hydrogen donors.
Hydrogen used to form H2S originates from the hydrogen-donor solvents
and/or from the kerogen. The H2S peaks at 200°C, 360°C, and 400°C are
from sulfur species mostly reduced by the hydrogen in the kerogen. These
peaks are nearly identical in shape and position whether the oil shale sample
is run in the absence or presence of hydrogen-donor solvents. (Compare
kinetograms in Figures 4, 5 and 6.) Therefore, the reaction kinetics are
unchanged for these species, indicating an internal source of hydrogen.
Conversely, the reaction kinetics of pyrite is altered in the presence of
hydrogen-donor solvents. When oil shale is run alone, pyrite reacts to form
H2S at 510°C; with the solvents, pyrite reacts to form H2S at 280°C.
The presence of an active hydrogen source may increase the frequency factor
and/or decrease the activation energy for pyritic sulfur reduction at 280°C.
It has been previously shown6 that the pyrite will react more
effectively with the native organic matter if no sweep gas is used. To check
those experiments and to gain further insight into the peak at 200°C, four
oil shale samples were run both before and after HC1 treatment in capillary
tubes as described above to more closely simulate autogenous conditions. The
results from the untreated samples
but the treated samples again
at 200°C. We do not know why
It may be either that organic
that they give H2S at a lower
are scrubbing the H2S, giving
show
this
agree well with previous experiments,6
the appearance to varying extents of a peak
peak appears after the HC1 pretreatment.
sulfur groups are being hydrolyzed by the HCl so
temperature, or that the carbonate minerals
metal sulfides and C02. Much more total
-1o-
sulfur, presumably H2S, is given off from the treated samples. The general
kinetogram shape in the region of 350°C to 500°C closely resembles that of
the untreated oil shales.
The percentage of sulfur reduced to H2S is in the
determined by the Fisher total sulfur analyzer (refer
graphical representation). The very low sulfur-conta
0.35% sulfur) give substantially greater total sulfur
general range of that
to Figure 8 for
ning samples (less than
values than obtained by
the Fisher sulfur analyzer. This is probably due to an erroneous signafl
created by the mist bypass and reaction with residue at the end of the tube.
Conversely, the samples of greater sulfur content give values below those
obtained from the Fisher sulfur analyzer. In this latter case, the pyrrhotite
may not be completely reduced or hydrocarbon gases may be quenching the sulfur
emission signal.
Conclusion
Hydrogen sulfide is successfully formed from the reaction of pyritic and
organic sulfur with hydrogen donor solvents and kerogen. The reactions are
qualitatively consistent in mass of H2S detected (peak area) and kinetics
(or temperature) of reaction. From the reaction profile, the approximate
distribution of
thiophene types
This method
Little time and
sulfides or thiols, pyrite, and perhaps thianthrene types, and
of sulfur in oil shale may be determined.
for sulfur determination in oil shale is simple in principle.
effort is required for sample preparation, reactions, and data
analysis. Sulfides or thiols and pyrite can be qualitatively distinguished in
the oil shale. Unfortunately, contamination of the reactor tube made the
results above 350-400°C unreliable. Further work also needs to be done to
eliminate the hydrogen-donor mist from giving a false signal. After these
-11-
.
problems can be solved, the approximate distribution between these different
sulfur types can be determined from H2S peak area. The analysis method
could also be applied to specially treated oil shales to analyze reactions and
reaction products of these sulfur types. More work needs to be done for
quantitative conversion of sulfur to H2S, and to understand the complex
sulfur chemistry involved. Further work along these lines is currently in
progress.
Acknowledgments
We would like to express our thanks to Linda Ott for providing the
computer programs needed for data collection and processing, to Joseph
Ronchetto for setting up the electronics, to Jim Taylor and Cal Hall for
constructing the special hardware, to Melvin Bishop for making the specialized
glassware, to Eugene Bissell for helping synthesize the sulfur standards and
for many useful comments, to Robert Taylor for providing the pyrite standards,
and to Lew Gregory for providing the sulfur analyses.
References
1. Gaseous Fuels; Coal and Coke; Atmospheric Analysis, Part 26, (American
Society of Testing and Materials, 1977) PP 322-326.
2. Smith J. W., Young, N. B and Lawler, D. L., “Direct Determination of
Sulfur Forms in Green River Oil Shale,” Anal. Chem. ~, 618-622, 1964. .
3. Attar, A., “Sulfur Groups in Coal and Their Determinations,” Analytical
Methods for Coal and Coal Products, Vol. 3 (Academic Press, Inc., 1979),
pp 585-624.
4. Attar, A. and Dupuis, F., “On the Distribution of Organic Sulfur
Functional Groups in Coal,” Prepr. ACS Div. Fuel Chem., 23 (2), 44-53,—
1978.
—
5.
6.
-12-
Attar, A. and Dupuis, F., “Data on the Distribution of
Functional Groups in Coal,” Prepr. ACS Div. Fuel Chem,
1979.
Organic Sulfur
24 (l), 166-177,—
Burnham, A. K., Kirkman Bey, N. and Koskinas, G. J., “HydrogenSUlfide
Evolution from Colorado Oil Shale,” ACS Symposium Series, No. 163, Oil
Shale, Tar Sands and Related Materials, (American Chemical Society) 61-77,
1981.
0
Standard
$
L-Cystine
# Dibenzothiophene
2,2’-Dithiodibenzoic acid
disodium salt
Pyrite
Resorcinol sulfide
Thianthrene
Thienylacrylic acid
sodium salt
Thiodipropionic acid
disodium salt
Thioglycolic acid
sodium salt
Thiosalicylic acid
sodium salt
-13-
Table 1. Sulfur Standards
Formula
[H02C CH(NH2)CH2S]2
(C6H4)2S
[(C6H4)C02Na]2S2
FeS2
[C6H3(OH)2]2S
(C6H4)2S2
(C4H3S)C2H2C02Na
(C2H4C02Na)2S
‘HcH2c02Na
SH(C6H4)C02Na
Functionality
Aliphatic disulfide
Thiophenic
Aromatic disulfide
Inorganic
Aromatic sulfide
Thianthrene type
Thiophenic
Aliphatic sulfide
Aliphatic thiol
Aromatic thiol
&
●
Source
Anvil Points
Anvil Points
Tract C-a
Tract C-a
Tract C-a
Geokinetics
Geokinetics
Geokinetics
Geokinetics
Geokinetics
Geokinetics
Geokinetics
Geokinetics
-14-
Table 2. Oil Shale Sample Properties
Grade
!@@!l
24
60
25
36
18
5.65
25.4
52.3
14.21
28.8
11.2
5.80
10.57
Depth ofBurialfeeta
Mz
Mz
432 ‘
432’
560 ‘
47‘-48’
56’-57’
61‘-62’
63’-64’
68’-69’
73’-74’
78’-79’
80’-81 ‘
Wt%Organic C
10.4
27.0
11.0
15.97
8.98
2.73
11.48
22.46
6.62
12.48
5.23
2.405
5.04
Wt%s
0.66
0.98
1.12
1.03
1.69
0.84
0.11
0.34
0.65
1.06
0.94
0.05
0.06
a Mz denotes from an unspecified depth in the Mahogany zone.
-15-
Table 3. Sulfur Speciationa of Selected Samples
% of Total Sulfur asSource Designation Sulfate m -b
Anvil Points 24 gpt o 69 31
Tract C-a 18 gpt 17 81 2
Geokinetics 47’-48’ 0 68 32
Geokinetics 56’-57’ 0 60 40
Geokinetics 68’-69’ 3 90 7
Geokinetics 80’-81 ‘ o %100 Oc
a ASTM method.
bBy difference.
c Some sulfur was detected in the HN03-leached shale which would account
for z35% of the original sulfur.
-16-
Table 4. Standard Kinetogram Results
Temperature (C) Functionality Structure Peak Characteristics\
200
200
230
240
250
260
280
>4130
Moo
Aliphatic disulfide
Aliphatic thiol
Aromatic sulfide
Aliphatic sulfide
Aromatic disulfide
Aromatic thiol
Pyrite
Thianthrene type
Thiophenic
R-S-S-R
R-SH
Q-S-Q
R-S-R
@-s-s-@
o0 -SH
Cubic
cms
6..4)
.
Sharp
Sharp
Sharp
Sharp
Sharp
Sharp
Sharp
Long, drawn out
Long, drawn out
-17-
Vent
Organic Lindberg oven /TCI
<_- Flame photometric
detector < (d~i&/ < I n l<:::~;acetone) reaction boat:
sample andI1 hydrogen donorsI
III
IJ
III
II 1 I
11
I “ectrometert----i~:~1:~l
FIGURE 1 - Schematic of the apparatus used for the reduction of
sulfur compounds to form H2S.
-18-
4
2
0
.
I I I I
0 5 10 15 20
mg of Geokinetics 68’ - 69 ‘
FIGURE 2 - Output signal from the FPD in parts per million as a
function of milligrams of oil shale (Geokinetics 68’-69’)
analyzed.
-19-
.
2’m
NxgD1
600‘ I I I I I 1
L-Cystine
400-
200.
0, t I 1 1100 300 500 700
20 I 1 I I 1 I
2, 2’-dithiodibenzoicacid15- disodium salt
10-
5-
t I 1100 300 500 700
40-
100 300 500 700
80 -
40 -
0 “ t I/. I 1 I100 300 500 700
Dibenzothiophene~
10
5
0LLm:
100 300 500 700
L
80 -
40 :
0- 1 I100 300 500 700
40‘~ [ I I I i I4
t- -1
30 L Thianthrene d
20 -
10j-
0.~ ~
100 300 500 700
200‘ I ? I 1 I I
150 - Thioglycolic acid,Sodium salt
100-
50-
0 t I I I I 1100 300 500 700
Temperature (°C)
FIGURE 3 - Kinetograms of H2S response as a function of temperature
of the various standards heated at ll°C/min in the
presence of hydrogen donor solvents under N7.
-20-
1 I I I I I I 1
40- Thiosalicylic acid,
2\WXN 20 -~CL
o100 300 500 700
200
100
0
r 1 1 1 I I
Thienylacrylic acid,Sodium salt
r:
.,\- -
-%**,. 1
[. 1 I I 1, I
100 300 500
1. -\.lu
J— I d700
Temperature (’C)
FIGURE 3 (cent)
-21-
1 I I I I I
8“- 78’ - 79’
4
500 700
-1
4 -
Ml IE
o “ I I AI100 300 500 700
WImlzg I I 1 1 I I
Q
8 - 63’ - 64’
r
L’”’””’I 1 1
8~ 80’ - 81’ 1t -1
4 -
0’-a100 300 500 700
I I I I I I
8 - 61’ - 62’
4 -
0 . I t100 300 500 700
8Tl_AclJ :‘-C; o
100 300 500 700 100
[“1’ ’’’’ ’’’”18 - 73’ - 74’
4 -
.u
100 300 50CI 700
“’v:&.
100 300 500
Temperature (°C)
FIGURE 4 - Kinetograms of H2S response as a function of temperature
of the Geokinetics samples heated in the presence of
hydrogen donor solvents under N2 at ll°C/min.
-22-
r I I I I 1 1 1i i
8 Anvil Points 24
4
0 . t I I I
100 300 500 700
15
10
5
0
1“’’”’’’’’”Tract C-a 36
100 300 500 700
15
10
5
0
[“’’”’’’’’””!8- Anvil Points 60
4-
0 I t 1 I I I
100 300 500 700
15
10
5
0
I I I I I I
Tract C-a 25
100 300 500 700
* I I 1 I I I
Tract C-a 18
100 300 500 700
Temperature (“C)
J
FIGURE 5 - Kinetograms of H2S resPonse as a function of temperature
of Anvil Points and Tract C-a samples heated in the
presence of hydrogen donor solvents under N2 at
ll°C/min.
-23-
r I 1 I 1- 1 I 1
,
J
f 1 t I I I 1 I
8 Geokinetics 58’ - 57’
4 -
0 I 1100 300 500 700
r I I I I I I 1f
8 Geokinetics 73’-74’
4 -~CnXN~o 1 I
nl 100 300 500 700
~’
8 Anvil Points 24
4
0.100 300 500 700
8 - Geokinetics 47’ - 48’
4 -
0 I
100 300 500 700
1 I I I 1 I
8 Geokinetics 68’ - 69’J
4
0100 300 500 700
I I I I 1 I
8 Anvil Points 60
4
0, I
100 300 500 700
b I I I I I
15 - Tract C–a 18
10 -
5 -
>0
I100 300 500 700
c
Temperature, (°C)
FIGURE 6 - Kinetograms of H9S response as a function of temperature ofIL
Geokinetics, Anvil Points
absence of hydrogen donor
and Tract C-a samples heated in the
solvents under nitrogen at ll°C/min.
-24-
Untreated~., .,r, ,., .l. :
*r Geokinetics 68’ - 69’L 2
4
0100 300 500 700
8
4
0 .-----100 300 500 700
I 1 I I I I
8 Anvil Points 24
4“-
r
o~100 300 500 700
I I I I 1 I .
8 Anvil Points 60
4
(-l100 300 500 700
HC1 treatedI I I I 1 I
8 Geokinetics 68’ - 69’
100 300 500 700
10
5
0100 300 500 700
t 1
I_JxfL3100 300 500 700
I I I I I I
8- Anvil Points 60
r
100 300 500 700
Temperature (“C)
FIGURE 7 - Kinetograms of H2S response as a function of temperature of
HC1 treated and untreated samples heated under autogenous
atmosphere at ll°C/min.
-25-
nONL!
I I 1 I ! t I I1.2
;/
0
cC-a 18
c C-a 360.8 ● GK61_62 .
/
.C-a 25
. GK63-64● GK80-81
.
/
● GK47-48
●AP24 ● AP60
0.4 “ ●GK73_74GK78-79
● ●] .GK68-69GK56-57
0.4 0.8 1.2 1.6
Sulfur content (wt%)
.
FIGURE 8 - The total weight percent sulfur obtained from sulfur
reduction to H2S is presented as a function of the total
weight percent sulfur determined from the Fisher sulfur
analyzer. The solid line indicates 100% sulfur detection
using the assumption of 50% weight loss during acid
pretreatment.