&EFA
United States
Environmental Protection
Agency
Office of Air Quality
Planning and Standards
Research Triangle Park NC 27711
EPA-450/3-79-022
October 1978
Air
Evaluation of Benzene-
Related Petroleum
Processing Operations
-------
EPA-450/3-79-022
Evaluation of Benzene-Related
Petroleum Processing Operations
by
Dr. Terry Briggs and Vijay P. Patel
PEDCo Environmental, Inc.
11499 Chester Road
Cincinnati, Ohio 45246
Contract No. 68-02-2603
Project No. 20
EPA Project Officer: Kent C. Hustvedt
Prepared for
U.S. ENVIRONMENTAL PROTECTION AGENCY
Office of Air, Noise, and Radiation
Office of Air Quality Planning and Standards
Research Triangle Park, North Carolina 27711
October 1978
-------
This report is issued by the Environmental Protection Agency to report
technical data of interest to a limited number of readers. Copies are
available free of charge to Federal employees, current contractors and
grantees, and nonprofit organizations - in limited quantities - from the
Library Services Office (MD-35), U.S. Environmental Protection Agency,
Research Triangle Park, North Carolina 27711; or for a nominal fee,
from the National Technical Information Service, 5285 Port Royal Road,
Springfield,Virginia 22I6I.
This report was furnished to the Environmental Protection Agency by
PEDCo Environmental, Inc., 11499 Chester Road, Cincinnati, Ohio 45246,
in fulfillment of Contract No. 68-02-2603. The contents of this report are
reproduced herein as received from PEDCo Environmental, Inc. The opinions,
findings, and conclusions expressed are those of the author and not necessarily
those of the Environmental Protection Agency. Mention of company or product
names"is not to be considered as an endorsement by the Environmental Protection
Agency.
Publication No. EPA-450/3-79-022
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CONTENTS
Page
Figures iv
Tables iv
Acknowledgment vi
1. Introduction 1
2. Survey of Benzene-related Petroleum Processing
Operations 2
2.1 Survey Results 2
2.2 Generalized Process Descriptions 7
3. Process Descriptions 16
3.1 Glycol BTX Process 16
3.2 Sulfolane Process 24
3.3 Other Aromatic Solvent Extraction Processes 29
3.4 Toluene Dealkylation Processes 29
3.5 Toluene Disproportionation Processes 36
4. Model Plant Development 40
Appendix
A. Estimation of Benzene Emission From Receiver Vents 50
111
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FIGURES
No. Page
2-1 Refinery block flow diagram showing location of
solvent extraction and toluene dealkylation units 9
2-2 Simplified process flow diagram of a sulfolane unit 10
2-3 Simplified process flow diagram of a glycol BTX unit 12
2-4 Simplified process flow diagram of BTX fractionation 12
2-5 Simplified process flow diagram of a toluene
dealkylation unit 14
3-1 Flow diagram of a glycol BTX unit process 19
3-2 Sulfolane unit process flow diagram 25
3-3 Process flow diagram of a toluene hydrodealkylation
unit 31
TABLES
No. Page
2-1 Results of Survey of Refinery Benzene Processes 3
2-2 Analysis of Reformate Aromatics 11
3-1 Properties of Selected Solvents 18
3-2 Glycol BTX Unit Material Balance 22
3-3 Typical Operating Conditions of a Glycol BTX Unit 23
3-4 Sulfolane Unit Material Balance 27
IV
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TABLES (continued)
No. Page
3-5 Sulfolane Unit Operating Conditions 28
3-6 Toluene Dealkylation Unit Material Balance 33
3-7 Comparison of Toluene Dealkylation Yields Based on
Different Feed Compositions 34
t
3-8 Toluene Dealkylation Unit Operating Conditions 35
4-1 Sulfolane Unit Pump Listing 41
4-2 Listing of Valves in Sulfolane Units 42
4-3 Relief Valves on Sulfolane Unit Listing 42
4-4 Sulfolane Unit Sample Connection Listing 43
4-5 Glycol BTX Unit Pump Listing 44
4-6 Glycol BTX Unit Valve Listing 45
4-7 Glycol BTX Unit Relief Valve Listing 45
4-8 Glycol BTX Unit Sample Connections Listing 46
4-9 Toluene Dealkylation Unit Pump Seal Listing 46
4-10 Toluene Dealkylation Unit Valve Listing 47
4-11 Toluene Dealkylation Unit Relief Valve Listing 47
4-12 Connection for Toluene Dealkylation Unit Sample
Valve Listing 48
v
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ACKNOWLEDGMENT
This report was prepared by PEDCo Environmental, Inc., under
the direction of Mr. Richard W. Gerstle. The PEDCo Project
Manager was Dr. Terry Briggs. Dr. Briggs and Mr. Vijay P. Patel
were the principal authors. Mr. Kent C. Hustvedt was the Project
Officer for the Office of Air Quality Planning and Standards.
VI
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SECTION 1
INTRODUCTION
The classification of benzene as a hazardous air pollutant
prompted an investigation by the Environmental Protection Agency
(EPA) regarding the need for hazardous air pollutant standards
under Section 112 of the Clean Air Act. This assessment of
benzene emissions from petroleum-based operations that process
liquids with high concentrations of benzene is part of this
effort. The refinery processes included in the assessment are
aromatics solvent extraction, toluene hydrodealkylation, toluene
disproportionation, and benzene-toluene-xylene (BTX) fractiona-
tion.
Section 2 presents the results of a survey of all domestic
petroleum-based producers of benzene and identifies the relevant
processes and their capacities (when they are known). Section 3
describes all the major operations identified and presents
typical operating characteristics and simplified material bal-
ances, focusing particular attention on the benzene concentration
in each process flow stream. Section 4 identifies model plants
for sulfolane, glycol BTX, and toluene deal kylation processes,
and includes a listing of major equipment.
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SECTION 2
SURVEY OF BENZENE-RELATED PETROLEUM PROCESSING OPERATIONS
All domestic petroleum refineries producing benzene were
surveyed to collect information on benzene-producing processes.
This information was needed to assure that all relevant processes
would be identified and described in this report. These proc-
esses are also introduced with brief process descriptions.
2.1 SURVEY RESULTS
Table 2-1 presents the results of the survey of refinery
chemical plants. It lists all the plants that process petroleum
or petroleum fractions and produce benzene for sale or inter-
mediate use. Whenever possible, data were obtained from the
literature, ' from EPA files, or through personal contact with
EPA State and Regional officials. When no data were available,
specific refineries were contacted directly. A few plants had
still not responded as of the date of this report.
All but 5 of the 45 plants reported to have solvent extrac-
tion processes had glycol* or Sulfolane solvent processes. The
remaining five had the Aromex process (one plant uses two units,
*
The specific gylcol solvent is listed when known; otherwise the
term UDEX is employed. Throughout the report the term glycol
BTX process will be used to describe solvent extraction proc-
esses containing glycol solvents.
-------
TABLE 2-1. RESULTS OF SURVEY OF REFINERY BENZENE PROCESSES
State
California
Delaware
Illinois
Kansas
Kentucky
Louisiana
Company
Atlantic
Richfield
Chevron
Chevron
Getty
Shell Oil
Union Oil
Skelly Oil
(Getty)
Ashland Oil
Cities
Service
Exxon
Gulf Oil
City
Wilmington
El Segundo
Richmond
Delaware
City
Wood River
Lemon t
El Dorado
Ashland
Lake
Charles
Baton Rouge
Alliance
Solvent extraction
Process
TEGC
solvent
Phenol
UDEXC
UDEXC
Sulfolanec
UDEXC
UDEXC
Sulfolanec
Lurgic
UDEXC
Sulfolanec
Throughput,
103 bbl/day
4.0C
1.2C
8.1e
34C
11. 4C
4.8C
4.0e
12. Oc
15C
11. le
TDAa
Process
HDA
THDC
Throughput,
103 bbl/day
2.5a
5.4e
Benzene
produced ,
10 3 bbl/day
0.78d
1.5c'd
0.75C
2.7b - 2.9d
l.ld
0.85d
4.1d
1.5 - 1.6C
1.6C
4.6d
4.6d
Comments
Phenol used in
an azeotropic
process
Produces a BTX
mixture
Vapor recovery
at loading
area and on
tank vents
Relief valves
vented to flares
Process vents to
flares are monitor-
ing benzene;
N-methyl per-
ibidone solvent
used
Closed drains and
sump system
U)
(continued)
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TABLE 2-1. (continued)
State
Louisiana
(continued)
Michigan
Mississippi
New Jersey
New York
Ohio
Oklahoma
Pennsyl-
vania
Company
Penzoil
United
(Atlas
Refinery)
Tenneco
Union
Carbide
Dow Chem.
Chevron
Texaco
Ashland
Oil
Sun Oil
Sun Oil
Gulf Oil
Sohio
(BP oil)
Sun Oil
City
Shrcvepor t
Chalmette
Taft
Bay City
Pascagoula
Westville
North
Tonawanda
Toledo
Tulsa
Philadelphia
Marcus Hook
Marcus Hook
Solvent extraction
Process
Phono lc
Sulfolanec
TEGC
Sulfolanec
Sulfolanec
Sulfolanec
TEGC
UDEXC
TEGC
UDEX
TEGC
Throughput,
103 bbl/day
14e
12C
7.6C
14. 7C
5.5C
14. OC
14. Oc
TDAa
Process
HDAC
Hydeal0
THDC
TDPC
Throuahput ,
103 bbl/day
4.2C
0.95C
2.2C
3.6C
Benzene
produced,
103 bbl/day
1.0C
0.6C
0.65C
4.6^
1.96d
2.3-J
0.8C
1.54
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TABLE 2-1. (continued)
State
Puerto
Rico
Texas
Company
Commonwealth
Oil
Phillips
American
Retrof ina
(Cosden Oil)
Amoco
Atlantic
Richfield
Champlin
(Union
Pacific)
Charter
Interna-
tional
Crown
Central
Petroleum
Coastal
States
Dow Chem.
Exxon
Gulf Oil
City
Ponce
Guayama
Big Spring
Texas City
Houston
Corpus
Christi
Houston
Houston
Corpus
Christi
Free port
Baytown
Port Arthur
Solvent extraction
Process
Sulfolanec
Aromexc
(Two units)
Sulfolane
(Two units)
Sulfolane0
UDFX and
Sulfolane
UDEXC
UDEXC
Sulfolane0
Sulfolane
TEC0
Throughput,
103 bbl/day
12. 5C
5.0°
48.8, 17.0°
10. 6e
8.0°
2.2°
3C
50. 0C
24. 0C
TDAa
Process
HDA°
HDAC
Dispro-
portiona-
tion unit
Detol0
Hydealc
Throughput,
103 bbl/day
7.2°
4.0C
6.0e
Benzene
produced,
103 bbl/day
12. 1^
7.2d
2.9C
3.6
-------
TABLE 2-1 (continued)
State
Texas
Virgin
Islands
Company
Howe 11
Independent
Refining
Marathon
Oil
Mobil
Monsanto
Phillips
Quintana
Howe 11
Shell Oil
Shell Oil
South-
western
Sun Oil
Texaco
Union Oil
Amer.
Petrof ina
Americal
Petrofina
Amerada
Hess
City
San Antonio
Winnie
Texas City
Beaumont
Chocolate
Bayou
Sweeney
Corpus
Christi
Deer Park
Odessa
Corpus
Christi
Corpus
Christi
Port Arthur
Beaumont
Port Arthur
St. Croix
Solvent extraction
Process
Arosorb
UDEXC
UDEXC
UDEXC
TEGC
Sulfolane
Sulfolane0
UDEXC
Sulfolane
UDEXC
UDEXC
UDEXC
Sulfolane
(Two units)
Throughput,
103 bbl/day
0.75C
0.4e
6.3C
7.9C
7.2C
10. 5C
16. Oe
0.8C
1.1
11. 0C
5.4C
50. Oc
TDA3
Process
HDAC
HDAC
Hydeal0
Hydeal0
HDAC
Throughput ,
103 bbl/day
8.16
0.8d
1.8C
1.04°
Benzene
produced ,
103 bbl/day
0.20
Q.55d
0.39d (1978)
3.9d
5.5°'d
1.4d - 0.65d
(1978)
0.8d - 5.87d
(1978)
5.87d
1.8d
2.3C (1978)
2.93d
1.4d
1.3d
0.8C
4.24d
Comments
Does not produce
pure benzene
No information
Most benzene
production is from
pyrolysis gasoline"
No information
Flare off-gases
TDA = Toluene Dealkylation.
Where specific glycol solvent is known, it is presented; otherwise, glycol
BTX process is designated as UDEX.
c Data from telephone or written conversation with EPA Regional officials,
EPA state officials, or direct plant contacts.
d SRI Chemical Directory 1978.
' Data taken from The Oil and Gas Journal Annual Refining Survey, March 20, 1978.
-------
two use a solvent extraction process using phenol with an
azeotropic separation, one uses the Arosorb process, and the
remaining plant uses the Lurgi process, which uses n-methyl
peribidone as the solvent. Feed rates were reported for 17 of 18
Sulfolane units and 18 of 23 glycol BTX units. Based on these
data the mean Sulfolane unit feed rate is 2576 m /day (16,200
barrels/day) and the median rate is 1908 m /day (12,000 barrels/
day) '. The corresponding glycol BTX unit mean is 1522 m /day
(9300 barrels/day) and the median is 1244 m /day (7600 barrels/
day). Of the units with a feed rate greater than 2455 m /day
(15,000 barrels/day), five used the Sulfolane process and one
used glycol BTX.
Although fewer plants use toluene dealkylation units, the
variety of processes was greater. As shown in Table 2-1, 14
plants have toluene dealkylation units and two plants have a
toluene disproportionation process. Plants having toluene deal-
kylation units reported the following processes: Hydeal, Detol,
Hydrodealkylation (HDA), and Thermal Hydrodealkylation (THD).
Based on the 12 plants that reported the feed rates of their
toluene dealkylation process, the mean feed rate is 573 m /day
(3500 barrels/day) and the median feed rate is 540 m /day (3300
barrels/day).
2.2 GENERALIZED PROCESS DESCRIPTIONS
The operating processes of interest are solvent extraction,
toluene dealkylation, and toluene disproportionation. These
processes are briefly introduced in this section, primarily to
describe how they fit into the overall refinery processing
-------
picture. Figure 2-1 presents a block flow diagram of an inte-
grated modern petroleum refinery. As the figure indicates, feed
to the solvent extraction (shown as BTX extraction) unit is in
the gasoline-blending-stock boiling range (60 to 204°C or 140° to
400°F). Feed is normally prefractionated to remove low- and
high-boiling-range components.
2.2.1 Solvent Extraction
Solvent extraction selectively separates aromatics from the
remaining paraffins in the hydrocarbon feed stream. The high-
purity aromatics are then fractionated to produce individual
aromatic products. Reformate, the major solvent extraction
feedstock, is formed by the catalytic reforming of the naphtha-
boiling-range hydrocarbons (93° to 190°C or 200° to 375°F) from
crude oil. Reforming provides the refiner with the flexibility
to meet motor fuel and aromatics production needs. Operating
conditions can be varied over relatively narrow limits so that
increased severity of catalyst operating conditions reduces yield
while increasing the reformate octane number. This is usually
accomplished by simultaneously increasing aromatic yield and
decreasing the concentration of heavy paraffins. The typical
aromatics concentration in high-octane reformates is 45 to 70
4
volume percent. While severity adjustments account for a por-
tion of this variation, the chemical composition of the naphtha
feed is the major factor affecting aromatics content. Table 2-2
presents a breakdown of the aromatics in different reformates.
The high-octane blending values shown for these aromatics
8
-------
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and toluene dealkylation units.3
-------
EXTRACT
RECOVERY
EXTRACTOR
CHARGE
EXTRACTIVE! "ly COLUMNJT
. STRIPPER A D p^
w»
I
r
RAFFINATE
RAFFINATE
WATER
WASH
J
•^ 6
Figure 2-2. Simplified process flow diagram of a Sulfolane unit.
-------
indicate their value in raising the octane ratings of a motor
gasoline pool. Other feed streams to solvent extraction units
are pyrolysis gasoline (primarily from ethylene plants) and other
refinery hydrocarbon streams containing light aromatics.
Solvent extraction feed is normally prefractionated to
remove light ends (C5 hydrocarbons) and also heavy ends (C_
hydrocarbons). Some plants also remove C_ and/or C0 hydrocar-
/ o
bons, resulting in a C, or C,-C_ feed stream for benzene and
toluene production only.
Table 2-2. ANALYSIS OF REFORMATS AROMATICS
Source
Benzene
Toluene
Ethylbenzene
P-xylene
M-xylene
O-xylene
Cg aromatics
Volume % of reformate
A4
5
24
4
4
9
5
4
B5
3.5
13.9
3.6
4.5
10.1
5.2
31.4
c6
2.2
17.3
7
28.6
18.8
Octane blending
values4
0 g Pb
108
112
113
114
114
100
103
3 g Pb
112
115
116
115
116
96
107
Figure 2-2 presents a simplified flow diagram of a Sulfolane
unit handling.a reformate charge, and Figure 2-3 shows a similar
diagram for a glycol BTX unit. Extract refers to the aromatics
stream, and the raffinate refers to the remaining paraffin stream
separated from the reformate. After it is treated, raffinate is
normally used for gasoline blending or olefin plant feedstock.
As shown in Figure 2-4, the extract from glycol BTX or sulfolane
units is fractionated into individual components.
11
-------
EXTRACTOR
STRIPPER
LEAN SOLVENT"
FEEDSTOCK
START —«
REFLUX
RICH SOLVENT
RAFFINATE
WATER WASH
RAFFINATE
AROMATICS
WATER WASH
PRODUCT
. . 6
Figure 2-3. Simplified process flow diagram of a glycol BTX unit.
START
EXTRACT
FEED
CLAY
TOWERS
tvl
CD
I
I
L
XYLENES
•-TOLUENE
•-BENZENE
Figure 2-4.
Simplified process flow diagram of BTX
fractionation.4
12
-------
2.2.2 Toluene Dealkylation
Toluene dealkylation processes are used to increase benzene
production by the conversion of toluene to benzene. The attrac-
tiveness of this process depends on the price difference between
benzene and toluene. Because this price differential fluctuates,
the process is sometimes operated on an intermittent basis.
Process feed toluene normally comes from a solvent extraction
unit or is purchased. The feed stream is normally either pure
toluene or a toluene-rich hydrocarbon.
Figure 2-5 presents a simplified process flow diagram of a
Hydeal unit. The process flow of other toluene dealkylation
units is similar. These cracking processes use heat and a
hydrogen atmosphere to convert toluene and other higher aromatics
to benzene and methane. Some processes use a fixed-bed catalyst;
the rest are thermal processes. Unreacted toluene in the reactor
effluent is recycled back to the feed after fractionation.
Although at least three toluene disproportionation processes
are available, only one unit was reported to be in operation in
the United States. The process flow of these processes is sim-
ilar to toluene dealkylation; however, these catalyzed processes
convert toluene to benzene and xylenes. The yield ratio of
4
benzene to xylene is variable.
13
-------
HEATER REACTOR
SEPARATOR STABILIZER
BENZENE
COLUMN
MAKEUP
GAS
A
A P
ALKYLBENZENE
Figure 2-5. Simplified process flow diagram of a toluene
dealkylation unit (Hydeal unit shown).7
-------
REFERENCES FOR SECTION 2
1. Ailleen Cantrell. Annual Refining Survey. The Oil and Gas
Journal, Vol. 76, March 20, 1978. pp. 108-140.
2. Stanford Research Institute Directory of Chemical Producers.
Menlo Park, California, 1978.
3. Maclean, W.D. Construction site selection - A U.S. view-
point. Hydrocarbon Processing, June 1977. pp. 111-116.
4. Mager, E.M. Aromatics Production. In: U.S. Petrochem-
icals, A.M. Brownstein, ed., Petroleum Publishing Co.,
Tulsa, Oklahoma, 1972.
5. Pollitzer, E.L., J.C. Hayes, and V. Haensel. The Chemistry
of Aromatics Production via Catalytic Reforming in Refining
Petroleum for Chemicals. In: America Chemical Soc. Advances
in Chemistry, L.J. Spillane and H.P. Lefton, eds, Series 97,
Washington, D.C., 1970.
6. Refining Handbook. Hydrocarbon Processing, 55(9), September
1976. pp. 216-217.
7. Refining Handbook. Hydrocarbon Process, 47(9), September
1968. p. 189.
15
-------
SECTION 3
PROCESS DESCRIPTIONS
This section presents detailed process descriptions of
solvent extraction, toluene dealkylation, and BTX fractionation,
and identifies potential atmospheric emission sources. It also
serves as a basis for the information on atmospheric emissions
presented in Sections 4, 5, and 6. The Sulfolane, glycol BTX,
and toluene dealkylation processes are addressed separately. The
fractionation associated with each process is included in each
process description.
3.1 GLYCOL BTX PROCESS
Glycol BTX processes rely on the greater solubility of
aromatic hydrocarbons in a glycol solvent compared with that of
the paraffinic components of a feed stream. Several glycol
solutions have been used in these processes, including a solution
of diethylene glycol and water, diethylene and dipropylene
glycols, and water and tetraethylene glycol .(TEG) . The tendency
in the refining and chemical industry is to use higher-molecular-
weight glycols to increase the benzene-producing capacity and
simultaneously recovering more of the higher-molecular-weight
1 2
hydrocarbons and reducing operating costs. ' Glycol solvent
systems can be changed by minor equipment modifications that in-
volve no change in royalty status; therefore it is not uncommon
16
-------
2
for refineries and chemical plants to switch solvents. This
report is restricted to a glycol BTX unit using TEG solvent
because TEG is commonly used by refiners and because it is the
solvent used at all four refineries with glycol BTX units visited
by PEDCo in conjunction with this project. Although plant oper-
ation is similar when different solvents are used, flow ratios
vary. (See Table 3-1.) Table 3-1 also shows solvent properties,
including those for Sulfolane.
The glycol BTX unit feed stream is normally reformate;
however with proper feed treatment, other refinery feed streams
containing aromatics can be used. Reformate used for aromatic
extraction is normally prefractionated to give a Cfi-Cp fraction
for BTX production or a Cg-C7 fraction when only benzene and
toluene are recovered. To obtain these "heart-cut" reformate
fractions, reformate is first depentanized to remove C5 paraffins
then a second fractionator removes hydrocarbons with higher
boiling points.
Figure 3-1 presents a process flow diagram of a typical
glycol BTX unit using a TEG solvent. The drawing has been sim-
plified, particularly with regard to the heat exchangers and
control loops on control valves. Aromatics are separated from
the feed by the solvent in the trayed rotating disc extractor or
sieve tray extractor by the liquid-liquid solvent extraction
method. Aromatics-free raffinate leaves the top of the extractor,
while the solvent containing dissolved aromatics (rich solvent)
leaves the bottom. The light hydrocarbon reflux strips paraffins
from the rich solvent. The rich solvent goes to the stripper,
17
-------
TABLE 3-1. PROPERTIES OF SELECTED SOLVENTS'
Solvent name
Molecular weight
Specific gravity 20/20'C
Normal boiling point, "C ("F)
Freeze point, "C (°F)
Viscosity, cst at 50°C
cst at 20°C
Flash point, open cup °C (°F)
Specific heat at 300°F, Btu/lb
Pure solvent
Solvent + 10% water
Latent heat or vaporization
(Btu/lb) J/g
Extraction temperature, °C (°F)
Recovery column bottom
Temperature, °C (°F)
Pressure, psig (mmHg)
Water, wt. »
Solvent/feed vol. ratios
Reflux/feed vol. ratios
Price, $/kg (S/lb)
Diglycolamine
105
1.06
221(430)
-9.4 (15)
8
30
127 (260)
0.68
0.72
510 (220)
121-149 (250-300)
149-177(300-350)
6
3-10
3-4
0.6-0.9
0.605(0.275)
Diethylene
glycol
106
1.12
246 (474)
-7.8 (18)
10
32
143 (290)
0.65
0.71
557 (240)
132-154 (270-310)
149-154 (300-310)
6
8-10
6-8
1.0-1.4
0.209(0.095)
Depropylene
glycol
134
1.02
231 (448)
Super cools
10
90
127 (260)
0.58
TEG
194
1.13
Decomp.
-3.9 (25)
55
182 (360)
0.52
132-154(270-310)
149-154(300-310)
6
5-10
4-5
0.7-1.0
0.363(0.165)
Sulfolane
120
1.27
Decomp .
5
0.43
93 (200)
177 (350)
(500)
0.5
2-3.5
0.5
1.38(0.63)
CD
Note: Some of these properties and data are rough estimates.
-------
UHs "*
FC riOM CH«PT
1C LEVEL CONTROL
PC PRESSURE CONTROL
Figure 3-1. Flow diagram of a glycol BTX unit process.
3,4,5
-------
where the extract is steam-stripped from solvent and light ends.
A significant amount of extract purification (nonaromatics
7
separation) also takes place in the stripper. The stripper feed
goes through a two-stage flash to remove the light ends and
water, which go to the stripper receiver. The stripper separates
hydrocarbons from the solvent and strips nonaromatics from the
extract. The extract is removed as a side-cut, and the lean
solvent is the bottom fraction. Both the extract and raffinate
are water-washed to remove any dissolved solvent before they go
to fractionation and gasoline blending. After the extract is
heated, it flows through a clay tower that removes any olefins
present. The pure benzene, toluene, and xylenes are separated by
conventional fractionation. Benzene is sometimes drawn off as a
side-cut near the top of the benzene column to remove paraffinic
and water impurities. The toluene product normally contains
considerably less than 1 percent benzene.
The solvent regenerator and solvent filters, which remove
liquid and solid impurities (primarily due to solvent degrada-
tion) in the solvent, are operated on an intermittent basis
456
and/or as a small slip stream. ' ' Some plants have replaced
5 8
the solvent regenerator with a charcoal filter bed. ' The water
still, which removes solvent from the recirculation water, can
also be operated on an intermittent basis. '
20
-------
Table 3-2 presents a simplified materials balance for a
glycol BTX unit (based on a Cg-C., feed).* Table 3-3 gives the
operating conditions of some of the major process streams.
3.1.1 Glycol BTX Unit Emission Sources
Benzene and total hydrocarbon emission sources in glycol BTX
units (as well as Sulfolane and toluene dealkylation units) can
be classified into two groups: process vents and fugitive
emissions. Categories of potential onsite fugitive emissions
that are common to each process are control, process, and relief
valve leaks; pump seal leaks; sampling connections; wastewater
sump; and flange leaks. Although some glycol BTX units do not
4 5
vent receivers to the atmosphere, ' others vent certain ones,
notably the stripper overhead receiver and benzene column re-
ceiver. In some instances extract and toluene column receivers
are also vented to the atmosphere. A natural gas sweep is com-
monly used on the process receivers to keep their pressure from
going negative.
No data are available on emission rates. Estimates are
shown in Appendix A. Vent rates depend on receiver liquid com-
position, gas-sweep rate and composition, and receiver pressure.
Because most volatile fractions in the feed (C^'s) that dissolve
in the solvent go to the stripper overhead receiver, its vent
would have the highest off-gas rate. These atmospheric emissions
can be eliminated by reducing C5's in the feed and routing these
*
The material balances presented in Section 3 (for glycol BTX,
Sulfolane, and toluene dealkylation units) do not represent
operating conditions in any specific unit. Engineering judge-
ment was used where data were lacking.
21
-------
tv)
TABLE 3-2. GLYCOL BTX UNIT MATERIAL BALANCE2'4'5'6'7
(Basis 7500 bbl/day feed)
Extractor - Feed
- Lean solvent
- Rich solvent
- Raffinate
- Light HC reflux
Stripper-Extract
to benzene column
Benzene product
Toluene column feed
Toluene product
Toluene column bottoms
Composition, wt *
, Flow Rate
m /d (bbl/day)
1193 (7,500)
4771 (30,000)
5144 (32,350)
819 (5,150)
1193 (7,500)
382 (2,400)
163 (1,025)
219 (1,375)
195 (1,225)
24 (150)
Benz
14.0
3.2
0.5
45.0
42.7
99.9
0.1
0.1
Tol
17.0
3.8
1.0
30.0
51.1
0.1
99.0
99.9
0.5
Xyl
2.0
0.5
6.2
98.0
C_Arom
0.1
1.5
Paraf
67.0
97.5
25.0
Solv
90.0
92.5
1.0
"2°
10.0
-------
to
U)
TABLE 3-3. TYPICAL OPERATING CONDITIONS OF A GLYCOL
BTX UNIT4'5'6'7
Extractor - top
Stripper - top flash drum
Stripper - second flash
drum
Stripper receiver, extract
receiver
Benzenes toluene column
receivers
Solvent regenerator
receiver
Temperature,
°C (°F)
135-149 (275-300)
38 (100)
38 (100)
38 (100)
Pressure,
kPa (psig)
689-827 (100-120)
172-345 (25-50)
34-69 (5-10)
3.4 (0.5)
3.4 (0.5)
68.9 (~10)
-------
vents to flare headers or using hot-vapor bypass or comparable
pressure-control systems.
3.2 SULFOLANE PROCESS
The Sulfolane process, a more recent development than the
glycol BTX unit, has come into common use because the solvent
2
properties of Sulfolane are superior to any of the glycols. As
shown in Table 2-1, all but one of the solvent extraction units
with a feed capacity greater than 15,000 barrels/day use the
Sulfolane process. Major factors preventing refineries from
switching to Sulfolane on existing glycol BTX units are the major
2
equipment changes and high royalty rates involved. Tetrahydro-
thiophene dioxide (the solvent used in the Sulfolane process) is
highly polar, permitting reduced solvent-to-feed ratios in the
extractor while increasing the total recovery of xylenes and
9
heavy aromatics.
Feed sources and preparation for Sulfolane units are similar
to glycol BTX units. Sulfolane feed is normally C^-CQ or C,-C~ ,
whereas the process feed to glycol BTX units often consists only
of Cg-C_ fractions.
A flow diagram of a Sulfolane unit (Figure 3-2) shows that
the process flow is similar to that of a glycol BTX unit; how-
ever, unlike the glycol BTX processes (which separate the rich
solvent in one distillation step in the stripper) the Sulfolane
unit requires two steps. First, rich solvent from the extractor
enters the extractive stripper, where partial stripping of the
hydrocarbon takes place. In this column light hydrocarbons,
24
-------
K)
SOLVENT
REGENERATOR
CONDENSER OR COOLER
HEATER OR REBOILER
o PW
FC FLOU CHART
LC LEVEL CONTROL
PC PRESSURE CONTROL
CLAY
TREATERS
BENZENE
COLUMN
TOLUENE
COLUMN
XYLENE
COLUMN
Figure 3-2. Sulfolane unit process flow diagram.
10,11
-------
including some benzene, are removed overhead and recycled to the
extractor. The extractive stripper bottoms, consisting of sol-
vent, aromatics, and a few nonaromatics, enter the extract re-
covery column, which is operated under vacuum. Here the extract
is separated from the solvent, which is recycled to the extractor
as lean solvent. Solvent cleanup is accomplished by sending a
small slip stream of lean solvent to a solvent regenerator and
filters for removal of solvent degradation products. The solvent
regenerator is usually operated under a vacuum, and steam jet
ejectors are normally used to maintain a vacuum in the two vacuum
columns.
Some variations in the water circulation loops occur among
Sulfolane units. ' Raffinate from the extractor is contacted
with water to remove dissolved Sulfolane, and the resulting rich
water is either returned to the extract recovery column or to a
water stripper to reclaim the Sulfolane content.
The fractionation section of the Sulfolane unit, which is
preceded by clay treaters to remove olefins, is similar to a
glycol BTX unit.
Table 3-4 presents the material balance for a typical
Sulfolane unit, based on 2455 m /day (15,000 bbl/day). Table
3-5 presents operating conditions of selected process streams.
3.2.1 Sulfolane Unit Emission Sources
Most emission sources in Sulfolane units are similar to
those in glycol BTX units. Other potential sources are the
vacuum system on the recovery columns and solvent regenerators
26
-------
TABLE 3-4. SULFOLANE UNIT MATERIAL BALANCE2'10'11
[Based on feed of 2385 m /day (15,000 bbl/day)]
ro
Extractor - feed
- Lean solvent
- Rich solvent
- Raffinate
- Light HC reflux
Extractive stripper bottom
- Extract
Solvent Regenerator Feed
Nash water from raffinate wash
Benzene Product
Toluene column feed
Toluene product
Xylene column feed
Xylene product
Xylene column bottoms
Composition, wt. %
Flow Rate
mJ/day (bbl/day)
2385 (15,000)
4771 (30,000)
6118 (38,470)
1059 (6,660)
954 (6,000)
1347 (8,470)
31.8 (200)
318 (2,000)
200 (1,255)
1126 (7,055)
712 (4,480)
410 (2,575)
355 (2,230)
55 (345)
Benz
8.5
3.3
15.0
15.0
100.0
0.3
0.5
Tol
30.0
13.3
25.0
53.2
63.1
99.0
0.7
0.8
Xyl
15.0
26.6
31.1
85.0
97.0
7.0
C,-A
2.5
4.4
4.7
13.0
1.1
90.0
Paraf
44.0
0.2
98.0
60.0
0.8
99.0
0.8
0.5
1.3
1.1
3.0
Solv
100
80
2.0
99.0
1.0
-------
to
co
TABLE 3-5. SULFOLANE UNIT OPERATING CONDITIONS2'10'11
Temperature
°C (°F)
Pressure
Kpa-gauge psig
Raffinate
Extractive stripper-top
Recovery column-top
Recovery column-bottoms
Water stripper (if used)
Solvent regenerator-top
93 (200)
127-135(260-275)
177 (350)
110-121(230-250)
166 (330)
276-345 (40-50)
34.5-48.3 (5-7)
-75.8 (-11)
55.1 (8-20)
-96.5 (-14)
-------
that can be vented to the atmosphere. Process receivers could be
vented to the atmosphere; however, no available information indi-
cates that this is done.
3.3 OTHER AROMATIC SOLVENT EXTRACTION PROCESSES
Other solvent extraction processes have been commercially
developed, but not as many of these have been installed. The
configurations of such processes, Formex (which uses n-form-
glmorpholine as the solvent) and Aromex (which uses diglycol-
2 12
amine) are very similar to glycol BTX and Sulfolane processes. '
As shown in Table 3-1, the solvent properties of diglycolamine
are similar to other commonly used solvents. Therefore, the
emission characteristics of the Aromex process are likely to be
similar to those from glycol BTX and Sulfolane units.
3.4 TOLUENE DEALKYLATION PROCESSES
Naphtha reformers yield two to three times more toluene than
benzene; however, because the demand for benzene continues to be
substantially greater than that for toluene, some refiners have
installed toluene dealkylation units to convert toluene to
9
benzene. For this process to be feasible, the price differen-
tial between benzene and toluene must be large. The generally
low price differential over the past 15 years has caused some
refiners to shut these units down or to run them on an inter-
9
mittent basis.
There are a number of commercially available toluene deal-
kylation processes, all of which have similar process flow
29
-------
configurations. The processes can be divided into two groups,
thermal and catalytic. The survey results (shown on Table 2-1)
identified four processes in domestic operation:
1. Hydeal - catalytic process licensed by UOP
2. Detol - catalytic process licensed by Houdry
3. HDA - thermal process licensed by Atlantic Richfield
and HRI
4. THD - thermal process licensed by Gulf Oil
Other commercialized processes are Shell's Bextol process (cata-
lytic) and Mitsubishi's MHC process (thermal). Pure toluene or
toluene mixed with other aromatics and paraffins can be used.
The reactions take place in a hydrogen atmosphere at 540° to
760°C (1000° to 1400°F) and 3445 to 4820 kPa (500 to 700 psig).
The catalytic processes typically operate at 200° to 300°F lower
9
temperature, but they are more sensitive to coke laydown.
Toluene conversion per pass is 70 to 80 percent, and the overall
yield is about 97 percent of theoretical. The major reactions
are the dealkylation of alkylbenzenes to benzene and cracking of
essentially all nonaromatics to methane and ethane.
Figure 3-3 presents the process flow diagram of a typical
toluene dealkylation unit. Because the dealkylation reaction is
highly exothermic, cold hydrogen is used in some designs as a
9
quench for temperature control in the reactor system." The
reported overall mole ratio range of hydrogen-to-feed is 3:1 to
459
8:1. ' ' Recycle hydrogen purity is maintained above 50 mol
percent to minimize coking and for economic reasons. Among the
various configurations used to maintain recycle gas hydrogen
30
-------
RECYCLE GAS
COMPRESSOR
U)
—WJ FC
Ugfo^a^
o
I BENZENE
PRODUCT
DRAG STREAK
Figure 3-3. Process flow diagram of a toluene hydrodealkylation unit.4'5'14'15
-------
purity above a minimum level are purification of makeup gas,
which is normally reformer hydrogen; adding hydrogen from a
hydrogen unit; and purification of recycle gas. Purification is
normally accomplished by compression, cooling, and absorption or
with a cryogenics unit. A condensate rich in benzene is re-
covered by these processes. Other process variations are the use
of a low-pressure (LP) separator after the high-pressure (HP)
separator to flash off a methane-rich gas, ' the recycling of a
light liquid stream from the stripper overhead receiver, and
the use of a recycle column after the fractionator (or benzene
column) to separate toluene overhead for recycle from a bottoms
drag stream.
Table 3-6 presents the material balance of a toluene dealky-
lation unit based on 2500 barrels/day of toluene feed. The
amount of toluene recycle is dependent upon process economics.
Table 3-7 compares the yields of different feed compositions. A
pure toluene feed results in the lowest process flow rate per
unit of benzene produced. Net gas rates are noticeably lower.
Table 3-8 shows typical unit operating conditions.
3.4.1 Toluene Dealkylation Unit Emission Sources
Potential benzene and hydrocarbon emission sources are the
fractionator receiver vents and the same general leak sources as
listed for glycol BTX units (in Section 3.1.1). The fired-charge
heater, which uses fuel gas or fuel oil, is a source of hydro-
carbon emissions. The recycle gas compressor seals are also
potential sources of benzene and hydrocarbon leaks. The
32
-------
TABLE 3-6. TOLUENE DEALKYLATION UNIT MATERIAL BALANCE
4,5,11,13,14,15,16,17
Toluene feed
Makeup hydrogen.
Recycle hydrogen
HP separation net gas
HP separator liquid
Stripper off-gas
Fractionator feed
Benzene product
Recycle toluene
Drag stream
Composition, %
Flow Rate
m-Vday (bbl/day)
397.6 (2500)
0.12 (4.4)
0.64 (22.8) ,
1.4 x 103 (5.2x10°)
459.8 (2891)
2435 (86,000)
453.2 (2850)
318.1 (2000)
132.0 (830)
3.2 (20)
Basis
wt
vol
vol
wt
vol
wt
wt
wt
wt
Benz
0.1
0.1
70.2
100
Tol
100
0.1
29.1
100
Other
Arom
0.7
100
Non-
arom
10
45
45
H2
90
55
55
OJ
CO
Assumptions: 80 weight percent overall conversion of toluene to benzene
75 percent conversion per pass
Purification of makeup water to 90 volume percent
Recycle gas rate is 4 mol H2/mol of toluene in the feed.
-------
TABLE 3-7.
COMPARISON OF TOLUENE DEALKYLATION YIELDS BASED ON
DIFFERENT FEED COMPOSITIONS17
u>
Feed
Net
- Toluene, wt . %
Benzene, wt . %
Nonaromatics, wt.%
Total feed m /day (bbl/day)
Gg/day (103 Ib/day)
H2 consumed m /day (10 x sdf/day)
Products benzene, Gg/day (10 Ib/day)
Tar, Mg/day (103 Ib/day)
Net off-gas, m /day (10 scf/day)
Case A
59.0
20.5
20.5
517.8 (3256)
0.36 (792)
0.15 (5.22)
0.25 (548)
4.2 (9.3)
0.16 (5.62)
Case B
65.0
10.0
25.0
560.6 (3525)
0.39 (852)
0.17 (6.11)
0.25 (548)
4.5 (9.9)
0.19 (6.61)
Case C
100.0
0
0
415.5 (2613)
0.30 (660)
0.10 (3.66)
0.25 (548)
3.6 (7.9)
0.10 (3.66)
-------
TABLE 3-8. TOLUENE DEALKYLATION UNIT
OPERATING CONDITIONS4'5'13'14'16
Reactor inlet
Temperature, °C (°F)
Pressure, MPa (psig)
Hj-to-feed molar ratio
H
- purity of recycle gas, %
HP separator
Temperature, °C (°F)
Pressure, MPa (psig)
Recycle compressor discharge
Pressure, MPa (psig)
Stripped overhead
Pressure, MPa (psig)
Fractionator overhead
Temperature, °C (°F)
Pressure, MPa (psig)
Recycle column overhead
Temperature, °C (°F)
Pressure, MPa (psig)
Recycle column bottoms
Temperature, °C (°F)
537-704 (1000-1300)
3.1-4.8 (450-700)
3:1-8:1
50-60
38 (100)
2.4-3.8 (350-550)
3.4-5.2 (500-750)
1.4-1.7 (200-250)
93 (200)
0.007-0.04 (1-6)
121 (250)
0.03-0.07 (5-10)
199 (390)
-------
off-gases from the HP separator (and LP separator, if used) and
stripper are of sufficient value to be used for fuel and, in some
cases, for recovery of heavier fractions for further processing.
3.5 TOLUENE DISPROPORTIONATE ON PROCESSES
Because of the marginal economics associated with toluene
dealkylation, processes have been developed for disproportioning
toluene into benzene and xylene. The disproportionation of
toluene can be represented as follows:
Toluene Benzene Xylenes
Since only one operating toluene disproportionation is listed in
Table 2-1, the process does not merit detailed description.
Three available commercial processes are low temperature
disproportionation (LTD), licensed by Mobil Oil; Tatoray, li-
censed by UOP; and Xylenes-Plus, licensed by Atlantic-Richfield.
All are catalytic processes. When the feed is 100 percent
toluene, 37 percent benzene and 55 percent xylene are obtained
rather than 50 percent each as the basic toluene disproportiona-
9
tion reaction would predict. The Xylene-Plus process also can
be used to transalkylate some Cq aromatics in the feed by re-
9
acting them with toluene to form more xylenes. As a result in
this process the benzene-to-xylene ratio can be varied from 1.5:1
9
to 10:1 depending upon the amount of Cq aromatics in the feed.
36
-------
The Tatoray and LTD processes use a hydrogen atmosphere (but
consume less hydrogen than the toluene dealkylation process) to
9 18 19
prevent coke layover on the catalyst. ' ' Although the
process flows are similar, the operating conditions are less
severe than those for toluene dealkylation. The process flow
diagram for a typical toluene dealkylation unit (Figure 3-3) is
also representative of toluene disproportionation. The major
differences are an LP separator can be used after the HP sepa-
rator, a xylene column and possibly a Cg column are used,
hydrogen purification generally is not needed, and (for the
Xylene-Plus process) no makeup hydrogen is needed. The off-gases
from the HP and LP separators and stripper go to fuel; however,
flow rates should be considerably lower than the corresponding
rates for toluene dealkylation units because far less cracking
18
takes place (reported aromatic ring yield is 97 to 97.5%) . The
reactor operates at lower temperatures than those used in dealky-
lation, and the conversion per pass (typically about 45 per-
/- I Q
cent) ' is also considerably lower, thus requiring more toluene
recirculation. Reactor operating conditions are as follows:
temperature 260° to 540°C (500° to 1000°F) and 3445 to 4480 kPa
(500 to 650 psig).18'19
Emission sources are similar to those of toluene dealkyla-
tion units.
37
-------
REFERENCES FOR SECTION 3
1. Somekh, G.S. Part 1: Ethylene Glycols; How to Improve
Aromatics Extraction. Hydrocarbon Processing and Petroleum
Refiners, 42(7), July 1963. pp. 161-164.
2. Jones, W.T., and V. Payne. New Solvent to Extract Aro-
matics. Hydrocarbon Processing, 52(3), March 1973. pp. 91-
92.
3. Somekh, G.S. New Union Carbide Aromatics Extraction Proc-
ess. In: International Solvent Extraction Conference,
Paper 65, The Hague, Netherlands, Society of Chemical
Industry, London, U.K., 1976. pp. 323-328.
4. Trip report by T.M. Briggs. PEDCo, Covering visit to Gulf
Oil Refinery, Philadelphia, August 1978.
5. Trip report by T.M. Briggs. PEDCo, on a visit to Sun Petro-
leum, Toledo, Ohio Refinery, September 19, 1978.
6. Trip report by T.M. Briggs. PEDCo, Covering visit to Sun
Petroleum Refinery, Marcus Hook, Pennsylvania, September 18,
1978.
7. Somekh, G.S., and B.I. Friedlander. TETRA Best Aromatics
Extractant. Hydrocarbon Processing, December 1969. pp.
127-130.
8. Trip report by T.M. Briggs. PEDCo, Covering visit to
Phillips Petroleum, Sweeney, Texas Refinery, August 1978.
9. Mager, E.M. Aromatics Production. In: U.S. Petrochemicals,
A.M. Brownstein, ed., Petroleum Publishing Co., Tulsa,
Oklahoma, 1972.
10. Broughton, D.B., and G.F. Asselin. Production of High
Purity Aromatics by the Sulfolane Process, Vol. 4. In:
Seventh World Petroleum Congress Proceedings, 1967. pp.
65-73.
11. Trip report by T.M. Briggs. PEDCo, Covering visit to Exxon
Chemical plant, Baytown, Texas. August 1978.
38
-------
12. Cinelli, E., S. Noe, and G. Paret. Extract Aromatics with
FM. Hydrocarbon Processing, 51(4), April 1972. pp. 141-
144.
13. Fowle, M.J., and P.M. Pitts. Thermal Hydrodealkylation.
Chemical Engineering Progress, 58(4), April 1962. pp. 37-
40.
14. Asselin, G.F., and R.A. Erickson. Benzene and Naphthalene
from Petroleum by the Hydeal Process. Chemical Engineering
Progress, 58(4), April 1962. pp. 47-52.
15. Benzene from Toluene by Detol Process. Hydrocarbon Proc-
essing, 40(6), June 1961. pp. 228-229.
16. New process Makes Benzene from Toluene (Bextol). Hydro-
carbon Processing, 42(3), March 1963. pp. 121-124.
17. Masamune, S., et al. A Hydrodealkylation (MHC) Process or
Production of Benzene and/or Naphthalene. In: Symposium on
Foreign Developments in Petrochemicals, Presented before the
Division of Petroleum Chemistry, inc., American Chemical
Society, Atlantic City, September 8-13, 1968. pp. A7-A21.
18. Erandlo, et al. Toluene for Benzene and Xylenes. Hydro-
carbon Processing, 51(8), August 1972. pp. 85-86.
19. Otam, S., et al. Tatoray Process - a New Transalkylation
Process of Aromatics Developed by Toray. Japan Chemical
Quarterly, 4, 6(16), 1968. pp. 16-18.
39
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SECTION 4
MODEL PLANT DEVELOPMENT
Model plant equipment listings are developed, based on the
median plant sizes determined for glycol BTX, sulfolane, and
toluene dealkylation units in Section 2. Equipment itemized are
pumps and compressors, process valves, relief valves, and sample
connections. Generally the total number of each type of equip-
ment is insensitive to plant size. Equipment listings were
developed from plant trip report data and equipment listings from
refinery plot plans (Pacific Environmental Services [PES]). The
toluene dealkylation reactor section equipment listing was taken
2
from a detailed equipment listing (Pullman Kellogg). A ratio
of 337 process valves per process pump, except for the toluene
dealkylation reactor section, was used.
Tables 4-1 to 4-4 present equipment listings for the sul-
folane unit; Tables 4-5 and 4-8, the glycol BTX unit; and Tables
4-9 to 4-13, the toluene dealkylation unit. The model plant
sizes are presented below:
Feed rate,
m-Vday (barrels/days)
Sulfolane 1,908 (12,000)
Glycol BTX 1,244 ( 7,600)
Toluene dealkylation 540 ( 3,300)
40
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TABLE 4-1. SULFOLANE UNIT PUMP LISTING1'3
Service
Extractor feed
Extractor reflux
Raffinate product
Raffinate water
wash recycle
Water stripper
tower charge
Bottoms-solvent
recovery tower
Bottoms water
stripper
Raffinate from
water wash
Extract to
fractionation
Feed to benzene/
toluene column
Benzene product
Toluene product
Feed to xylene
column
Xylene product
Heavy aromatic
product
41
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TABLE 4-2. LISTING OF VALVES IN SULFOLANE UNITS
Service
Extractor
Stripper
Recovery column
Raf f inate
Water stripper
Clay treater
Benzene column
Toluene column
Xylene column
Total
No. of
valves
132
66
66
99
132
66
132
132
198
1023
TABLE 4-3. RELIEF VALVES ON SULFOLANE UNIT LISTING
Service
Extractor
Stripper
Recovery column
Raf f inate
Water stripper
Clay treater
Benzene column
Toluene column
Xylene column
Solvent regeneration
Rundowns
Totals
No. of
valves
3
2
3
3
1
2
2
2
2
3
3
26
42
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TABLE 4-4. SULFOLANE UNIT SAMPLE CONNECTION LISTING
Service
Extractor
Stripper
Recovery column
Raffinate water wash
Water stripper
Clay treater
Benzene column
Toluene column
Xylene column
Solvent system
Water system
Total
No. of
connections
5
2
2
2
1
3
3
2
2
6
3
31
43
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TABLE 4-5. GLYCOL BTX UNIT PUMP LISTING
1,3
NO.
2
2
2
2
2
2
2
2
2
2
2
1
Service
Extractor feed
Extractor overhead
(raf f inate)
Solvent column feed
Solvent column reflux
and product
Solvent column bottoms
to extractor
Benzene column tops
Benzene column bottoms
Toluene column tops
Toluene column bottoms
Hot oil
Miscellaneous pumps for
solvent, acid, soda
and water
Fractionator feed
Extractor reflux
Stripper extractor
RVP class*
C
C
C
C
-
C
C
C
C
D
C
C
C
b
Pump type
C
C
C
C
C
C
C
C
C
R
C
C
C
Seal type
M
M
M
M
M
M
M
M
M
P
M
M
M
C « Liquid vapor pressure « <5 psi (average loss
D = Hot oil service (low vapor pressure).
C « Centrifugal pump.
R « Rotary pump
0.14 Ib/day)
M « Mechanical seal.
P * Packed seal.
-------
TABLE 4-6. GLYCOL BTX UNIT VALVE LISTING
Service
Extractor
Stripped
Clay treaters
Benzene column
Toluene column
Solvent system
Total
No. of
valves
192
66
66
132
132
192
780
TABLE 4-7. GLYCOL BTX UNIT RELIEF VALVE LISTING
Service
Extractor
Stripper and receiver
Solvent cleanup
Water wash
Clay treaters
Fractionation
Total
No. of
valves
2
3
2
1
2
4
14
45
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TABLE 4-8. GLYCOL BTX UNIT SAMPLE CONNECTIONS LISTING
Service
No. of
connections
Extractor
Stripper
Water wash
Water still
Clay treater
Benzene column
Toluene column
Solvent system
3
4
2
1
1
3
3
3
TABLE 4-9. TOLUENE DEALKYLATION UNIT PUMP SEAL LISTING
Service
Toluene feed
Stabilizer reflux
Benzene column
reflux
Toluene recycle
Heavy aromatics to
storage
No. of
pumps
2
2
2
2
1
RVP3
class
C
C
C
C
C
*RVP Class C - 3.4-34 kPa (0.5-5.0 psi)
RVP Class D - 3.4 kPa (0.5 psi).
46
-------
TABLE 4-10. TOLUENE DEALKYLATION UNIT VALVE LISTING
Service
Compression
Furnace
Reactor
Separator
Enrichment
Benzene column
Recycle column
Total
No. of
valves
48V, 7L
24V, 25L
3V, 2L
19V, 13L
15V, 41L
132
132
261
TABLE 4-11. TOLUENE DEALKYLATION UNIT RELIEF VALVE LISTING
Service
Compression
Furnace
Separation
Enrichment
Clay treaters
Stabilizer
Fractionator
Total
No. of
relief valves
4V
IV
2V
2V, 2L
2L
1L, IV
IV, IV
17
47
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TABLE 4-12. CONNECTION FOR TOLUENE DEALKYLATION
UNIT SAMPLE VALVE LISTING
Service
Compression
Furnace
Reactor
Separation
Enrichment
Stabilizer
Fractionator
Total
No. of
samples
IV
IV
2V
2V
IV
1L
3L
11
48
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REFERENCES FOR SECTION 4
1. Powell, D., et al. Development of Petroleum Refinery Plot
Plans. EPA-450/3-78-025. June 1978.
2. Cader, G.A., and B.B. Horton. Equipment Component Analysis
for Identification of Potential Fugitive Emission Sources.
U.S. Environmental Protection Agency, Research Triangle
Park, North Carolina. Contract No. 68-02-2619, Task 5.
June 1978.
3. Booz, Allen and Hamilton, Inc., Foster D. Snell Division.
Benzene Emission Control Costs in Selected Segments of the
Chemical Industry. Florham Park, New Jersey. June 1978.
49
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APPENDIX A
ESTIMATION OF BENZENE EMISSION FROM RECEIVER VENTS
Uncontrolled receivers in glycol BTX, Sulfolane, and toluene
dealkylation units typically operate with a purge gas to keep the
receiver pressure positive and vent the net gas to the atmosphere.
The simplest receiver system is the overhead receiver on the
benzene column, which contains essentially pure benzene. This
system is analyzed below and can be used to make estimates of
emission potential from process vents in all similar operations.
Benzene column overhead receiver:
37.8°C, 0.057
(100°F, 2 acfm)
CTC2
37.8°C, 0.07 mVmin
(100°F, 190 gal/m1n)
37.8°C, 0.07 m3/min (100°F, 190 gal/m1n)-*-
50
-------
Assumptions
0 Benzene production is 238 m /day (1500 bbl/day) and
column reflux is 795 m3 (5000 bbl/day). Total benzene
flow is 1033 m3 (6500 bbl/day) or 0.072 m3 (190 gal/min).
0 Bleed gas rate is (5 acfm) at 37.8°C (100°F) and
contains methane and ethane; no benzene.
0 Receiver operates at 117 kPa (17 psia).
o Vessel dimensions are 3.05 m (10 ft) diameter (D),
4.57 m (15 ft) long (L).
0 Vessel operates 50 percent full.
The dynamic benzene material balance is:
pMgas ' Q ' x0 + kg • A • (x£ - x) - PMga£. . Q .x = P_Mgas . v . ||
where
3 3
p = molar density of purge gas, kg mole/m (Ib mole/ft )
JXlCf cl S
V = volume of gas in the receiver, m (ft )
x = benzene mole fraction in the inlet air = 0
o
k_ = mass transfer coefficient, kg molar/m min (Ib molar/
0 min ft )
x = benzene mole fraction in exit gas
x_ = equilibrium mole fraciton of benzene
£j
Q = gas flow rate, 0.142 m /min (5 acfm) = 8.50 m /h (300
acfh)
Solving the above equation, gives
M , -Nt
X = N i - e
where
k
M = —
V PMgas
/kG • A \
N = ^ + Q A
\pMgas /
t = time, h
51
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Calculation of M and N
, . GM
kG = f ' 2-
Receiver vapor space x - area
2
A' = ^§- = 39.27 ft2
o
GM = Q • 60
359 x 560 _,
^—— • A
460 A
= 5 • 60
359 x 560 .
460 ^'^'
= 0.0173 Ib mole/h • ft2
D - receiver vapor space adjusted diameter
= 2 ( A; . = ,np2/8. = D = •
wetted perimeter' vJID/2 ; 2
_ Q _ 5 x 60
V ~ A5" ~ 39.27
=7.64 ft/h
ND = Reynold's number
Ke
D ' v ' pgas _ 5 x 7.64 x 0.05
y'gas 0.0266
= 71.7
= 0.223 x 0.0173
Li • /
2
V = ^§- L = 589 ft3
o
assume bleed gas MW = 22
M = kG x A x XE
V x pMgas
= 1.93 x 10~3 x 10' x 15' x 0.219
589 x 2.65 x 10~3
= 4.06 x 10~2 iT
52
-------
N =( k. A
+ Q
/V
Mgas
-3
= 1.93 x 10 x 150 + 300 /589
= 0.695 h
M ,
= — 1 —
N
= 0.058
2.65 x 10
-1
-3
-Nt
1 - e
-.695t
Residence time, t = V =
Q
589 ft"
5 x 60 f\
= 1.96 h
x = 0.043
Thus 4.3 mole percent of the vent gas is benzene, assuming
vapor-liquid equilibrium
Benzene emission = 0.36 SNm /h (12.9 acfh)
= 1.20 kg (2.65 Ib/h)
Because no data are available on actual receiver purge gas
flow rates, the effect of varying the purge gas on benzene
emissions is shown below.
Q
Purge gas
flow,
m^/min (acfm)
0.06 (2)
0.14 (5)
0.28 (10)
0.57 (20)
t
Gas residence
time,
h
4.91
1.96
0.98
0.49
x
Vent gas
benzene,
mole- fraction
0.0886
0.043
0.0236
0.0121
Benzene emission
rate,
kg/h (Ib/h)
0.994 (2.19)
1.20 (2.65)
1.32 (2.91)
1.36 (2.99)
Thus, the benzene emission rate from the benzene column
receiver is expected to be in the range of 0.91201.36 kg (2 to 3
Ib/h). Other vented receivers all contain far lower percentages
of benzene in the liquid and are expected to result in lower
benzene emissions.
53
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TECHNICAL REPORT DATA
(Please read Instructions on the reverse before completing)
1. REPORT NO.
EPA-450/3-79-022
2.
3. RECIPIENT'S ACCESSION NO.
4. TITLE ANDSUBTITLE
Evaluation of Benzene-Related Petroleum Processing
Operations
5. REPORT DATE
October 1978
6. PERFORMING ORGANIZATION CODE
7. AUTHOR(S)
8. PERFORMING ORGANIZATION REPORT NO.
Dr. Terry Briggs
Vijay P. Patel
9. PERFORMING ORGANIZATION NAME AND ADDRESS
Pedco Environmental, Inc.
11499 Chester Road
Cincinnati, Ohio 45246
10. PROGRAM ELEMENT NO.
11. CONTRACT/GRANT NO.
68-02-2603 - Task 20
12. SPONSORING AGENCY NAME AND ADDRESS
13. TYPE OF REPORT AND PERIOD COVERED
U.S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Emission Standards and Engineering Division
Research Triangle Park. North Carolina 27711
Final
14. SPONSORING AGENCY CODE
15. SUPPLEMENTARY NOTES
EPA Project Officer: Kent C. Hustvedt
16. ABSTRACT
This report describes refinery processing of liquids with high benzene
concentrations. Processes which are addressed include aromatics extraction
(both sulfolane and glycol solvent processes), toluene dealkylation, and
toluene disproportionation. Each process is described and modeled. In
addition, a list and characterization of the 45 plants in the United States
processing liquids with high benzene concentrations is presented.
Characteristics include, where possible, company name, plant location,
benzene process, and benzene production rate.
17.
KEY WORDS AND DOCUMENT ANALYSIS
DESCRIPTORS
b.IDENTIFIERS/OPEN ENDED TERMS
COSATl Held/Group
Petroleum Refining
Hydrocarbons
Benzene
Pump and Compressor Seals
Valves
Pressure Relief Valves
Sulfolane Toluene Dealkylation
Air Pollution Control
Stationary Sources
134
07C
18. DISTRIBUTION STATEMENT
Unlimited
19. SECURITY CLASS (ThisReport)
Unclassified
21. NO. OF PAGES
60
2O. SECURITY CLASS (This page)
Unclassified
22. PRICE
EPA Form 2220-1 (Rev. 4-77)
PREVIOUS EDITION is OBSOLETE
54
-------
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Environmental Protection
Agency
Office of Air, Noise, and Radiation
Office of Air Quality Planning and Standards
Research Triangle Park NC 27711
Official Business
Penalty for Private Use
$300
Publication No. EPA-450/3-79-022
Postage and
Fees Paid
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Protection
Agency
EPA 335
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