ccps case study bp texas city an aiche technology alliance
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CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 1
Chemical Hazard Engineering Fundamentals (CHEF)Case Study – BP Texas City
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance
REFINERY EXPLOSION AND FIRE
Texas City, Texas
March 23, 2005
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 2
Chemical Hazards Engineering Fundamentals (CHEF)For the Current Presentation, Please Join Us at:
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 3
Case Study – BP Texas CityHazard Identification and Risk Analysis (HIRA) Study
We begin the study by Identifying the Equipment or Activity for which we intend to perform
an analysis. We will often use the operation of a specific equipment item containing a
specific chemical or chemical mixture to define the activity. For example, the operation of a
storage tank, a reactor, a piping network, etc. Inputs are chemical data, equipment designinformation, operating conditions, and plant layout.
What are the Hazards?
What can go Wrong?
How Bad could it Be?
How Oftenmight it
Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 4
Case Study – BP Texas City
Process Description
The ISOM unit provides higher octane components for unleaded gasoline, consists of four
sections: an Ultrafiner14 desulfurizer, a Penex15 reactor, a vapor recovery / liquid recycle
unit, and a raffinate splitter. At the BP Texas City refinery, the ISOM unit converted straight-
chain normal pentane and hexane into branched-chain isopentane and isohexane for
gasoline blending and chemical feedstocks.
We will start with the raffinate splitter section where a hydrocarbon mixture is separated into
light and heavy components. About 40 percent of the raffinate feed was recovered as light
raffinate (primarily pentane/hexane). The remaining raffinate feed was recovered as heavy
raffinate.. The raffinate splitter section could process up to 45,000 barrels per day
(approximately 1300 gallons/minute) of raffinate feed.
This is an illustrative example and does not reflect a thorough or complete study.
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An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 5
Case Study – BP Texas City
Process DescriptionThe process equipment in
the raffinate splitter section
consisted of a feed surge
drum; a distillation tower; a
furnace with two heating
sections, one used as a
reboiler for heating the
bottoms of the tower and the
other preheating the feed;
air-cooled fin fan condensers
and an overhead reflux
drum; various pumps; and
heat exchangers. Figure 1: Raffinate Splitter Tower System of the ISOM Unit
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An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 6
Liquid raffinate feed was pumped into the raffinate splitter tower near the tower’s midpoint.
An automatic flow control valve adjusted the feed rate. The feed was pre-heated by a heat
exchanger using heavy raffinate product and again in the preheat section of the reboiler
furnace, which used refinery fuel gas. Heavy raffinate was pumped from the bottom of the
raffinate splitter tower and circulated through the reboiler furnace, where it was heated and
then returned below the bottom tray. Heavy raffinate product was also taken off as a side
stream at the discharge of the circulation pump and sent to storage. The flow of this side
stream was controlled by a level control.
Light raffinate vapors flows overhead, is condensed by air-cooled fin fan condensers, and
then deposited into a reflux drum. Liquid from the reflux drum, was then pumped back into
the raffinate splitter tower above the top tray.
Case Study – BP Texas City
Process Description
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An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 7
What are the Hazards?
What can go Wrong?
How Bad could it Be?
How Oftenmight it
Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
The scope of this presentation is focused on the Raffinate Column. As this evaluation is
related to an incident investigation, little emphasis will be placed on Frequency Evaluation
(the incident has already occurred) or Risk Analysis (evaluation of protection layers).
However, a “worst case” consequence such as might be evaluated during risk analysis will be addressed.
Case Study – BP Texas CityHazard Identification and Risk Analysis (HIRA) Study
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June 28, 2021 Slide - 8
Case Study – BP Texas City
Raffinate Composition
Typical Raffinate composition per Refinery Explosion
and Fire, CSB Report No. 2005-04-I-TX page 259
For entry into CHEF, the mixture is
simplified to:
0.06 n-pentane (including isopentane)
0.45 n-hexane
0.31 n-heptane
0.18 n-octane
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June 28, 2021 Slide - 9
Case Study – BP Texas City
Chemical DataA composition (weight fraction):
0.06 n-pentane
0.45 n-hexane
0.31 n-heptane
0.18 n-octane
was used as representative.
The operating pressure was 25
psig (172 kPa gauge) and the
operating temperature of 112 C
was estimated as the saturation
temperature or temperature
such that the estimated vapor
pressure matches the operating
pressure for a boiling liquid.
CHEMICAL HAZARDS AND CHEMICAL MIXTURE INPUT INFORMATION
Inputs for one or more chemical components must be entered in shaded "yellow" fields if Table Data Value is not used
Process Inputs: Input Value Input Units
Temperature, T 112 112 C
Physical State of Contents Liquid Assumed liquid if blank
Estimated Vapor Pressure at Specified Temperature: 172.149 kPa gauge
Chemical Inputs: Table Name Wt FractionSecond Liq
Phase
Mol Wt Data
Table Value
Mol Wt Input
Value
Mol Wt for
EquationHealth Flammability Stability
0.06 72.15 72.15 2 4
0.45 86.2 86.2 2 3
0.31 100.2 100.2 1 3
0.18 114.23 114.23 2 3
1
Input Name
NFPA Hazard Ratings (Table Values)
Note that Weight Fraction, Molecular Weight and Vapor Pressure data, in addition
to physical State of Contents, must be entered to estimate Vapor Composition
Pentane
Hexane
Heptane
Octane
Clear Inputs
Temperature is adjusted
until the estimated vapor
pressure matches the
operating pressure.
Up to 5 chemicals with the
associated weight fraction may
be added to create a mixture.
Mixtures are assumed “ideal”.
The chemical property inputs for the various worksheets will then
be estimated from this composition at the appropriate temperature
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An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 10
Case Study – BP Texas City
Chemical Hazards
Mol Fract Vapor
/ LFL
0.15581
0.53656
0.14130 -48.15 C
0.03813
S yi / LFLi = 0.87180
LFLMixture = 1 / (S yi / LFLi) = 1.15 Vol %
ERPG-2 (t /60)1/nMol Fract Vapor /
ERPG-2 (t /60)1/n ERPG-3 (t /60)1/n
Mol Fract Vapor /
ERPG-3 (t /60)1/n
32500.0 0.00001 190000.0 0.00000
2900.0 0.00020 8600.0 0.00007
800.0 0.00019 4900.0 0.00003
385.0 0.00009 5000.0 0.00001
S yi / ERPG-2'i = 0.00050 S yi / ERPG-3'i = 0.00011
ERPG-2'Mixture = 1 / (S yi / ERPG-2'i) = 2005.61 ppmv ERPG-3'Mixture = 9196.07 ppmv
ESTIMATED MIXTURE ERPG-2 and ERPG-3
Dose adjusted ERPG per equation 3-1 and mixture ERPG per equation 3-3
Chemical Name
The Minimum Flash Point for any
Component is:
ESTIMATED MIXTURE LFL and MINIMUM FLASH POINT
equation 2-1
Hexane
Heptane
Octane
Chemical Name
Pentane
Hexane
Heptane
Octane
Pentane
Note: n is assumed 2 for interpolation of exposure duration less than one hour and 1 for
extrapolation of exposure duration to greater than one hour if not entered
Based on Exposure Duration of 60 min
✓ An estimated mixture flashpoint of -48 C
(the minimum of any component) and
estimated lower flammable limit of 1.15
volume % indicates a potentially high
flammability hazard.
✓ An estimated ERPG-2 of >2000 ppm would
indicate a low to moderate toxicity hazard.
The NFPA Health Ratings for these
materials range from 1 to 2 also indicating a
low to moderate hazard.
✓ There may be other hazards to consider
such as thermal due to a maximum process
temperature greater than 60 to 80 C.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 11
What are the Hazards?
What can go Wrong?
How Bad could it Be?
How Oftenmight it
Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
Case Study – BP Texas CityHazard Identification and Risk Analysis (HIRA) Study
CCPSCenter for Chemical Process Safety
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June 28, 2021 Slide - 12
Drain or Vent Valve
OpenFlow-Loss of Containment All
Procedure Failure (Human Error)
Flow Control FailureDrain or Vent Leak
Flammable Release
Toxic Release
Chemical Exposure
Excessive Heat Input -
Heat Transfer
Temperature-High
Pressure-High
Heat Input-High
All with Heat Transfer Capability
Temperature Control Failure
Residence Time Failure (Solids)
Feed rate Control Failure
Relief Venting
Equipment Rupture
Equipment Damage
Flammable Release
Toxic Release
Flash Fire or Fireball
Physical Explosion
Business Loss
Excessive Heat Input -
Pool Fire Exposure
Temperature-High
Pressure-High
Heat Input-High
AllScenarios involving spill plus ignition in nearby
liquid-containing equipment
Relief Venting
Equipment Rupture
Equipment Damage
Flammable Release
Toxic Release
Flash Fire or Fireball
Physical Explosion
Business Loss
Overfill, Overflow, or
Backflow
Level-High
Flow-BackflowAll Liquid Containing Equipment
Level Control Failure
Procedure Failure (Human Error)
Overflow Release
Equipment Damage
Equipment Rupture
Flammable Release
Toxic Release
Physical Explosion
Business Loss
Overflow - Flooding or
PluggingLevel-High
Adsorber/Scrubber
Distillation
Vapor Quench
Level Control Failure
Pressure Control Failure
Flow Control Failure
Overflow Release
Equipment Damage
Equipment Rupture
Flammable Release
Toxic Release
Physical Explosion
Business Loss
Relief Device Failure Flow-Loss of Containment All Mechanical Failure Relief Hole Size Leak
Flammable Release
Toxic Release
Chemical Exposure
Vacuum Damage Pressure-Low AllPressure Control Failure
Mechanical Failure
Full-Bore Leak
Equipment Damage
Flammable Release
Toxic Release
Business Loss
Case Study – BP Texas CityPartial List of Hazard Scenarios per CHEF Example Scenarios
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Case Study – BP Texas City
Suggested Scenarios for Raffinate Column
WORKING WITH YOUR EVALUATION TEAM:
❑ Review the suggested list of scenarios. Do these represent what you
would expect for a distillation column?
❑ Are there scenarios that have been “screened out” (shown in gray) that
should be considered?
❑ Are there scenarios missing? (Possibly similar scenarios with different
Initiating Events)
❑ Do you agree with the “worst” Consequence (Tolerable Frequency
Factor) for the scenario listed?
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 14
Case Study – BP Texas City
Suggested Scenarios for Raffinate Column
WORKING WITH YOUR EVALUATION TEAM:
❑ Utilize an Appropriate Hazard Evaluation Technique (HAZOP, What If, etc.)
to capture additional scenarios.
❑ Capture existing Safeguards and Recommendations for each Scenario.
Note the Dates and Names of participants in the Study.
❑ Select which Scenarios warrant more detailed Risk Evaluation (such as
Layers of Protection Analysis).
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June 28, 2021 Slide - 15
What are the Hazards?
What can go Wrong?
How Bad could it Be?
How Oftenmight it
Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
Case Study – BP Texas CityHazard Identification and Risk Analysis (HIRA) Study
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June 28, 2021 Slide - 16
Case Study – BP Texas City
Site Layout
Approximately 500 m
Several wooden trailers are located
approximately 200 m from the
raffinate splitter housing 20 people.
The trailers are “low strength”
construction. In addition, the process
area appears to be relatively “low”
equipment congestion.
The blowdown tank which receives
the discharge from the raffinate
splitter relief devices is located 60 m
from the wooden trailers and vents at an elevation of 36 m.
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Estimated Pool Temperature = 74.9 C ( 348.05 K )
Vapor Pressure at Pool Temp, Psat
= 101.300 kPa
Assumed Wind Speed ( Location ) = 3 m/sec
(may be conservative as does not account for evaporative cooling)
Evaporation Rate (equation 11-27) , mP = 0.0021 Mw2/3
u0.78
Psat
/ TP
0.0021 ( 86 )^2/3 ( 3 )^0.78 ( 101.3 ) / ( 273.15 + 74.9 ) = 0.028096 kg/sec m2
Release Duration, tL = Inventory / L = / 55 = 3600 sec
Estimated Liquid Rate to Pool, L' = L ( 1 - Fv ) ( 1 - FD ) =
55 ( 1 - 0.334 ) ( 1 - 0.4409 ) = 20.4798 kg/sec
AP = 100 M [FV+(1-FV) FD] / rL
Estimated Pool Area (equation 11-24) , AP = L' / [ rL / ( 100 tL ) + mP / 2 ] =
20.4798 / [ 577 / { 100 ( 3600 ) } + 0.028096 / 2 ] = 1310 m2
Pool Evaporation = mP AP = ( 0.028096 ) ( 1310 ) = 20.4798 kg/sec
limited to pool fill rate
Liquid Release - Airborne Quantity = L [ Fv + FD ( 1 - Fv ) ] + mP AP =
55 [ 0.334 + 0.4409 ( 1 - 0.334 ) ] + 20.4798 = 55 kg/sec - or - 7260 lb/min
Liquid Release - Airborne Quantity for Equipment Rupture
If Initial Vapor / Total Vapor or 0 kg / 198000 kg < 0.01, Use Maximum Pool Evaloration Rate
or kg/sec - or - lb/min
1 hour Airborne Quantity = 198000 kg - or - 435600 lb
based on pool evaporation for 1 hour
LIQUID RELEASE - ESTIMATED AIRBORNE QUANTITY
LIQUID RELEASE - ESTIMATED POOL EVAPORATION
Flash Fraction (equation 11-19) , Fv = CS ( T-TB ) / DHV = ( 2.67 ) ( 112 - 74.9 ) / ( 297 )
Fv = 0.334 Initial Fraction Vapor = 0.334
Selected Liquid Release Rate, L = 55 kg/sec
Aerosol Temperature, T' = 74.9 C ( 348.05 K )
Vapor Pressure at Aerosol Temp, Psat
= 101.300 kPa
Flashing Fluid Density, r ' = 1 / [ Fv / r V + ( 1 - Fv ) / r L ] =
577 kg/m3
Liquid or Two-Phase Release Velocity (equation 11-5), vd = 1.27 L / [ d2 cd r' ] =
or vd = 1.524 [ 1000 (P0 - PA) / r' + 9.8 h' ]0.5
=
1.27 ( 55 ) / [ ( 0.087 )^2 ( 0.61 ) ( 577 ) ] = 26.3 m/sec
Estimated Droplet Diameter (equation 11-21), dd = 170 (1 - FV) / vd2 =
170 ( 1 - 0.334 ) / 26.3^2 = 0.1632 mm
Liquid Spray Distance (equation 11-4 ), s = vd t = 0.45 vd h1/2
=
0.45 ( 26.3406529539294 ) ( 1 )^0.5 = 11.9 m - or - 38.9 ft
Aerosol Fraction (equation 11-22) , FD = 0.043 vd2 Mw
2/3 P
sat h
1/2 / [ r
L T' ( 1 - Fv ) ] =
0.043 ( 26.34 )^2 ( 86 )^2/3 ( 101.3 ) ( 1 )^1/2 / [ 577 ( 273.15 + 74.9 ) ( 1 - 0.334 ) ]
FD = 0.4409
LIQUID RELEASE - ESTIMATED FLASH FRACTION
LIQUID RELEASE - ESTIMATED AEROSOL FRACTION
SOURCE MODELS INPUT INFORMATION
Required Inputs are Shaded "Yellow"
STEP 1 - Select Type of Release
"
STEP 2 - Enter Required Release Information
Release Inputs: Input Value Input Units Equation Input Equation Units
Hole Size, d 0.0867995 m
Coefficient cd (typically Square Edged Hole) 0.61 dimensionless
Heat Input Rate, q kWatt
Specified Rate (at either specified Hole 55 55 kg/sec Size or Release Pressure) Mismatch in Hole Size and Pressure Inputs, Equivalent Release Pressure = 172.369 kPa
Process Inputs: Input Value Input Units Equation Input Equation Units
Release Temperature, T 112 112 C
Release Pressure (gauge), P0 - PA 25 psi 172.36892 kPa gauge
Total Inventory (Leave Blank for 1 hour leak) kg
STEP 3 - Enter Chemical Properties (or Select Chemical Name from Pic List)
Cas No.
Chemical Name
(Leave Input Value Blank to accept Chemical Data Table Values)
Data Table Value Input Value Input Units Equation Input Equation Units
Physical State Liquid Liquid
Molecular Weight, Mw 86 86
Normal Boiling Point, TB 74.9 74.9 C
Liquid Properties at Release Temperature :
Vapor Pressure, Psat 273 273 kPa absolute
Liquid Density, rL 577 577 kg/cu m
Liquid Heat Capacity, CS 2.67 2.67 kJ/kg C
Heat of Vaporization, DHV 297 297 kJ/kg
STEP 4 - Enter Equipment and Plant Layout Information
Input Value Input Units Equation Input Equation Units
Equipment Location (Assumed Outdoor if Blank)
Equipment Volume, VEquip cu m
Estimated Contained Mass (for Reference if volume and density entered) kg
Liquid Height within Equipment, h' m
Diked Area (Leave Blank if No Dike) No Dike sq m
Leak Elevation above Surface, h 1 m
Input Units may be changed - Input Values in "blue" will be converted to appropriate equation units
Specified Rate
Square Edged Hole
Clear InputsClear Inputs
June 28, 2021 Slide - 17
Use a Specified Release rate equal to
feed rate of 55 kg/sec for Overfill at
the Release Temperature of 112 C
Chemical Properties at
Column Release
Temperature of 112 C
Leave Elevation Blank for now as Discharge was to a
Blowdown Tank which then Overflowed to the AtmosphereTotal Airborne Rate of 55 kg/sec
with a liquid pool of 1310 m2
Case Study – BP Texas CityConsequence Analysis – Source Models
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per Correlation Details with Concentration in ppmv
Plume or Continuous: C m = 8.1E+08 1.76 )
Puff or Instantaneous: C m = )
per Correlation Details for 1.5 m/sec F Stability with Concentration in ppmv
Plume or Continuous: C m = 3.5E+08 1.74 )
Puff or Instantaneous: C m = )
Test for Plume versus Puff Model at Dispersion Conditions: (equation 12-20)
If Q > (a*/a) u Q* Xb-b* ---> Instantaneous Model (from equating Puff and Plume correlation at X)
Alternate weather Puff versus Plume Model
Estimated Exposure Duration - Continuous Dispersion (Equations 12-21, 12-23)
t = Q* / Q for Continuous or 2 (0.2) [Q* T amb / (Mw C)]0.37
/ Wind Speed for Instantaneous
t = 3600 = 3600.0 sec
Alternate weather Estimated Exposure Duration
t = 3600 = 3600.0 sec
Maximum Downwind Distance to Concentration of Interest (equations 12-9, 12-13)
Continuous (equation 37): X = a [ Q / ( u Mw Cm ) ]b - X0
r air = 1.18 Kg/m3 = 113800 [ ( 55 ) / { ( 3 ) 85 ( 11600 ) } ]^0.57 - 0 = 235 m
at ambient conditions Instantaneous (equation 41): X = a* [ (Q* / ( Mw Cm ) ]
b* - X0
m
( Q* / Mw ) / ( X ^
Continuous
for 3 m/sec Wind Speed, Class D Atmospheric Stability, and Residential Surface Roughness
( Q* / Mw ) / ( X ^
SIMPLE VAPOR DISPERSION
( Q / Mw ) / ( u X ^
Continuous
( Q / Mw ) / ( u X ^
Maximum Concentration at Ground Elevation
Effective Release Elevation
Release Elevation
Ground Elevation
Cloud Centerline
Concentration at Specified Distance
and Elevation
Maximum Concentration at Specified Distance
Outdoor Vapor Release
Initial Dilution
Distance Correction for
Initial Dilution, DXt
Show Correlation Details
Hide Correlation Details
VAPOR DISPERSION INPUT INFORMATION
Required Inputs are Shaded "Yellow"
STEP 1 - Select Location, Type of Release, Concentration and Distance of Interest
Release Location (Assumed Outdoor if Blank)
Type of Release
Use Averaging Time Correction for Flammable Release Yes
Input Value Input Units Equation Input Equation Units
Concentration of Interest 1.16 vol % 11600 ppm
Concentration of Interest for Hazard Analysis is typically 1/2 LFL, LFL, ER-2, ER-3 or LC 50
Outdoor Downwind Distance of Interest, X m
Distance of Interest is typically to the property limit, to an unrestricted work area, or to an occupied building
Note that Concentration of Interest must be entered for estimation of Instantaneous (or puff) release
STEP 2 - Enter Chemical Properties (or Select Chemical Name from Pic List)
Cas No.
Chemical Name
Data Table Value
Lower Flammable Limit, LFL vol %
ERPG-3 Concentration ppm
ERPG-2 Concentration ppm
Input Value Equation Input
Vapor Molecular Weight, Mw 85 85
Normal Boiling Point, TB C
STEP 3 - Enter Process Information
Process Inputs: Input Value Input Units Equation Input Equation Units
Airborne Rate, Q 55 55 kg/sec
Vapor Temperature, T 74.9 74.9 C
Total Release Quantity, Q* (Leave Blank if Unlimited) kg
Liquid or Two-Phase Release Velocity* (Flashing Liquid) m/sec
Initial Fraction Vapor*, f 0 (Flashing Liquid Only) Fraction
kPa absolute
*Note that these inputs may not significantly change results
STEP 4 - Enter Equipment and Plant Layout Information
Equipment and Plant Layout Inputs: Input Value Input Units Equation Input Equation Units
Diameter of Hole or Discharge Piping, d0 m
The hole size for vapor release estimate or diameter of relief system discharge piping. If blank, no jet mixing used.
Release Elevation, h (Blank assumed at Ground) 36 36 m
Release Direction (Assumed Horizontal if Blank)
Enclosed Process Area Volume, VBldg cu m
Enclosed Process Area Ventilation Rate Air Changes/Hr (Assumed 1 if Blank)
Vertically Upward
Vapor Pressure at Release Temp
(Subcooled Liquid Only)
Outdoor
Flashing Liquid
Input Units may be changed - Input Values in "blue" will be converted to appropriate equation units
If "Yes" dispersion concentration
is approximately doubled
For reference in determining
concentration of interest
Leave Blank to accept
Chemical Data Table
Mw
Clear InputsClear Inputs
June 28, 2021 Slide - 18
Use a Flashing Liquid Release
with Averaging Time Correction
for Flammable Evaluation
Chemical Properties at
Blowdown Tank Release
Temperature of 74.9 C (estimated normal boiling point)
Elevation of Blowdown stack is 36 but release will
be assumes ground elevation for a flashing liquid
Distance to Concentration of
Interest (lower flammable
limit) is 235 m at the default
wind speed of 3 m/sec and
Class D Stability
Vapor Rate from Source
Model of 55 kg/sec. Leave
two-phase velocity and initial
fraction vapor blank for now
Case Study – BP Texas CityConsequence Analysis – Vapor Dispersion
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Release
Location
Wind
Direction
Explosion
Distance
XLFL
Vapor Cloud
Explosion
Epicenter
The entire vapor cloud is considered
a single Potential Explosion Site with
epicenter at the center of the
flammable cloud (0.5 XLFL).
An single overall level of congestion
and confinement for the entire cloud
is used.
Wind direction is assumed toward
greatest population or building with
highest occupancy.
Vapor Cloud ExplosionSimple Modeling Approach within CHEF and RAST
Methodology is described in the CHEF Guide
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June 28, 2021 Slide - 20
Site LayoutCongestion or Obstacle Density Categories
Low
High
Medium
Low – Only 1-2 layers of obstacles.
One can easily walk through the area
relatively unimpeded.
Medium – 2-4 layers of obstacles.
One can walk through an area, but it
is cumbersome to do so. Medium
Congestion is assumed in RAST if a
category is not entered by the user.
High – Many layers of repeated
obstacles. One could not possibly
walk through the area and little light
penetrates the congestion .
The method described in
CHEF is limited to
consideration of the entire
cloud volume as a single
Potential Explosion Site
(PES) at an overall or
average category of
process equipment
congestion. This technique
does not account for small
localized areas of higher
congestion where blast
overpressure will be higher.
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EXPLOSION INPUT INFORMATION
Required Inputs are Shaded "Yellow"
STEP 1 - Select Type of Explosion and Distance of Interest
Type of Explosion:
Input Value Input Units Equation Input Equation Units
Distance of Interest, X 60 60 m
STEP 2 - Enter Equipment Burst Pressure and Volume for Physical Explosion Skip Step
Physical Explosion Inputs: Input Value Input Units Equation Input
Burst Pressure (gauge), PB - P0 kPa gauge
Equipment Volume, VEquip cu m
Burst Temperature, TBurst C
Fraction Liquid Level (if Superheated), FF
Flash Fract during Depressurization, FV
STEP 3 - Enter Quantity and Heat of Reaction for Condensed Phase Explosion Skip Step
Condensed Phase Detonable Inputs: Input Value Input Units Equation Input
Mass of Material, M kg
Heat of Reaction per Mass, DHR kJ/kg
STEP 4 - Enter Chemical Properties (or Select Chemical Name from Pic List)
Cas No.
Chemical Name
Data Table Value User Value Equation Input
Vapor Molecular Weight, Mw 85 85
Liquid Density, rL (at Burst Temperature) kg/m3
Lower Flammable Limit, LFL 1.16 1.16 vol %
Fuel Reactivity based on Fundamental Burning Velocity Medium(Leave User Value Blank to accept Data Table Value)
Ideal Gas Vapor Density, rV (at Burst Temperature) 3.78 kg/m3
STEP 5 - Enter Information for Building or Head Space Explosion Skip Step
Building or Head Space Explosion Inputs: Input Value Input Units Equation Input
Building or Head Space Volume, VB cu m
Degree of Internal Congestion Assumed "Medium" if Blank
1 D Confinement? (such as Fire Tube Boilier) Assumed "No" if Blank
STEP 6 - Enter Information for Vapor Cloud Explosion
Vapor Cloud Explosion Inputs: Input Value Input Units Equation Input
Distance to LFL from Dispersion Model , XLFL 235 235 m
Vapor Rate 55 55 kg/sec
Wind Speed (Assumed 3 m/sec if Blank) 3
Degree of Outdoor Congestion Low Assumed "Medium" if Blank
Vapor Cloud Explosion
Input Units may be changed - Input Values in "blue" will be converted to appropriate equation units
Clear Inputs
Vapor Cloud Explosion (based on 3 m/sec wind speed)
Low Medium High
High 0.5 >1 >1
Low-Medium 0.35 0.5 1
Flammable Cloud Volume (equation 13-4), VC = 2440 Q XLFL / ( F u Mw CLFL) =
2440 ( 55 ) ( 235 ) / [ 2 ( 3 ) ( 86 ) ( 1.16 ) ] = 30000 m3
Distance to Explosion Epicenter, X EE = 0.5 X LFL = 0.5 ( 235 ) = 117.5 m
Potential Explosion Site Volume limited to 30000 cu m
Explosion Energy (equation 13-3), QE = 3500 VPES = Note: P A = 101.3 kPa
3500 ( 30000 ) = 105000000 kJ
Scaled Overpressure at 1 psi = 0.068
Scaled Distance, R = X / (2 QE / P0 )1/3
= 1.5
Distance to 1 psi = R (2 QE / P0 )1/3
+ XEE =
1.5 [ 2 ( 105000000 ) / 101.3 ]^1/3 + 117.5 = 307.8 m
From Graph, Scaled Distance, R = ( X - XEE) / (2 QE / P0 )1/3
=
( 50 - 117.5 ) / [ 2 ( 105000000 ) / 101.3 ]^1/3 = 0.01
Scaled Overpressure = 0.22
Overpressure at 50 m = 3.2 psi or 22.3 kPa
Distance of Interest is less than the distance from leak source to explosion epicenter
Fuel
Reactivity
Obstacle Density or Congestion
Use Mach 0.35 for Low-
Medium Fuel Reactivity and
Low Confinement
BAKER-STREHLOW-TANG MODEL
0.01
0.1
1
10
100
0.1 1 10
Sca
led
Ove
rpre
ssu
re,
PS
= P
0/
P a
Scaled Distance, R = X / (2 QE / Pa)1/3
Baker-Strehlow-Tang Overpressure Curves
Mach > 1
Mach 1.0
Mach 0.7
Mach 0.35
Mach 0.5
1 psi overpressure
June 28, 2021 Slide - 21
Case Study – BP Texas CityConsequence Analysis – Explosions
Use Vapor Cloud Explosion and
Distance of Interest as 60 m from
Release Point to Project Trailers
Chemical Properties at
Blowdown Tank Release
Temperature of 74.9 C (estimated normal boiling point)
Estimated Distance to 1 psi
Blast Overpressure is 308 m
and Estimated Overpressure
at 50 m Distance of Interest
is 3.2 psi
Enter Distance to LFL from
Vapor Dispersion estimate,
vapor rate and “low” degree
of congestion
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
A simplification in RAST is wind
direction toward the highest population.
This is quite reasonable in Risk Analysis
where the wind direction is unknown.
In the actual incident, the wind direction
was toward the southeast rather than
west toward the wooden trailers.
Wind Direction represents a key
difference between estimates for Risk
Analysis versus Incident Investigation.
Blast overpressure at the wooden
trailers would likely have been higher if
the wind direction was toward the
trailers.June 28, 2021 Slide - 22
Case Study – BP Texas City
Consequence Analysis
CHEF estimated
explosion epicenter as
the center of LFL cloud
REPORT NO. 2005-04-I-TX , US Chemical Safety Board,
Figure H-2 Blast Overpressure Map
Release Point –
Blowdown Stack
CHEF estimated maximum 308
m 1 psi overpressure distance
from release point assuming
“low” equipment congestion..
CHEF estimated 235 m
distance to LFL concentration
using default 3 m/sec wind
speed and class D
atmospheric stability
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 23
Case Study – BP Texas City
Consequence Analysis – Impact Estimation
Flash Fire
Distance to 1/2 LFL of 349 m Exceeds 3 m Threshold for Severe Impact.
Impact Area (Equation 14-1), = 0.3 XMultiple LFL2
= 0.3 ( 349 )^2 = 36540.3 m2
N = ( 36540.3 sq m ) 0.0002 people/sq m + 1 = 8.308
Vapor Cloud Explosion (VCE)
Total Airborne Release of Unlimited Kg Exceeds 100 Kg Thresold for Vapor Cloud Explosion
Overpressure at Nearest Wall of 3.2 psi Exceeds 1.3 psi Thresold for Building Damage
Impact to Occupied Building (Figure 14.11), Vulnerability = 0.918
N = 0.918 ( 20 ) = 18.36
Total Personnel Severely Impacted = Flash Fire + Occupants Impacted = 26.67
OUTDOOR FLAMMABLE IMPACT
Flash Fire Personnel Seriously Impacted, N = Impact Area times
Population Density plus Personnel in Immediate Area
Number of Building Occupants Severely Impacted = Vulnerability times
Total Building Occupants =
ONSITE IMPACT ASSESSMENT INPUT INFORMATIONRequired Inputs are Shaded "Yellow"
STEP 1 - Select Location and Scenario Outcome
Release Location (Assumed Outdoor if Blank)
Scenario Outcome
Equation Input
Number of Personnel Routinely in the Immediate Vicinity? 1.00
STEP 2 - Enter Chemical Properties (or Select Chemical Name from Pic List)
Cas No.
Chemical Name
(Leave Input Value Blank to accept Chemical Data Table Values)
Data Table Value Input Value Equation Input
Lower Flammable Limit, LFL 1.16 1.16 vol %
Fuel Reactivity based on Fundamental Burning Velocity Medium
ERPG-3 Concentration ppm
ERPG-2 Concentration ppm
LC1 as Multiple of EPPG-3 Concentration 2 2 typically 1 to 2
LC50 as Multiple of EPPG-3 Concentration 5 5 typically 3 to 5
Dose Exponent 2 2 typically 1 to 2
Fraction Indoor/Outdoor Concentration 0.5 0.5 typically 0.2 to 0.5
Dermal Toxicity Risk Phrase
Does Process Temperature Represent a Thermal Hazard?
Input Value Input Units Equation Input Equation Units
Release or Exposure Duration (leave blank if not limited) 1.0000 hr
Total Airborne Quantity, AQTotal kg
Vapor Cloud Explosion
Outdoor
Personnel in the Immediate Vicinity include those associated with procedures requiring operator attendance such as unloading a tank truck,
sampling, in addition to personnel using nearby walkways, etc.
(Assumed 1 if
Blank)
Clear InputsClear Inputs
STEP 3 - Enter Plant Layout Information
Input Value Input Units Equation Input Equation Units
Distance to Property Limit or Offsite Population (Fence Line) m
Fraction of Offsite Population Outdoors 0.1 (Assumed 0.1 if Blank)
Fraction of time for Night Weather 0.2 (Assumed 0.2 if Blank)
Offsite Population Density 0.0015
Occupied Building Type
Maximum Number of Occupants in Occupied Building 20
Onsite Outdoor Population Density 0.0002
Enclosed Process Area Volume, VBldg cu m
Maximum Number of Personnel within Enclosed Process Area 2(Assumed 2 if Blank)
STEP 4 - Enter Hazard Distances
Input Value Input Units Equation Input Equation Units
Concentration at Distance to Fence Line or Public ppm
Concentration at Distance to Occupied Building ppm
Explosion Overpressure at Distance to Occupied Building psi
Explosion Overpressure at Center of Occupied Building 3.2 3.2 psi
Spray Distance m
Distance to Multiple of Lower Flammable Limit 349 349 m
Distance to LC50 Concentration - Daytime Conditions m
Distance to LC50 Concentration - Nighttime Conditions m
Distance to LC1 Concentration - Daytime Conditions m
Distance to LC1 Concentration - Nighttime Conditions m
Distance to Severe Blast Impact m
Maximum Fragment Range m
Number of Fragments (typically 3 to 10)
Concentration within Enclosed Process Area ppm
Outdoor Population Density should account for maintenance and other personnel who may occasionally be in nearby outdoor
process areas.
(Assumed 0.0015
people/m2 if Blank)
Low Strength (Assumed Typical
Construction if Blank)
(Assumed 0.0002
people/m2 if Blank)
Use Outdoor Release Location
and Vapor Cloud ExplosionEnter Low Strength
Building with 20 Occupants
Enter Blast Overpressure at
Distance to Center of Occupied
Building from Explosion Worksheet
Enter Distance to Fraction of LFL
concentration (0.5 in this example) for Flash
Fire Impact from Vapor Dispersion Worksheet
Estimate of 18 fatalities within Occupied
Building and addition 6 to 7 outdoors from
Flash Fire at default population density
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 24
What are the Hazards?
What can go Wrong?
How Bad could it Be?
How Oftenmight it
Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
Case Study – BP Texas CityHazard Identification and Risk Analysis (HIRA) Study
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
Risk Analysis Screening Tools (RAST)
Risk Matrix
June 28, 2021 Slide - 25
To understand the Consequence
Severity and Tolerable Frequency, the
values for key Study Parameters and a
Risk Matrix may be viewed on the
Workbook Notes worksheet. These
values may be updated on hidden
worksheets and should reflect the
company’s specific risk criteria.
For this case study, the Risk Matrix
(right) has been used. The Human
Harm criteria is based on an estimated
number of people severely impacted
(severe injury including fatality).
2 3 4 5 6 7
Description Human Harm Environment Business Loss 10^-2/year 10^-3/year 10^-4/year 10^-5/year 10^-6/year 10^-7/year
Reportable Incident to Environmental Agency OR
< 10 kg Very Toxic to Waterway OR < 100 kg NFPA-H4 to Soil
< 100 kg Toxic to Waterway OR < 1000 kg NFPA-H3 to Soil
< 1000 kg Harmful to Waterway OR < 10000 kg NFPA-H2 to Soil
Environmental Contamination Confined to Site OR
< 100 kg Very Toxic to Waterway OR < 1000 kg NFPA-H4 to Soil
< 1000 kg Toxic to Waterway OR < 10000 kg NFPA-H3 to Soil
< 10000 kg Harmful to Waterway OR < 100000 kg NFPA-H2 to Soil
Environmental Contamination of Local Groundwater OR
< 1000 kg Very Toxic to Waterway OR < 10000 kg NFPA-H4 to Soil
< 10000 kg Toxic to Waterway OR < 100000 kg NFPA-H3 to Soil
< 100000 kg Harmful to Waterway OR < 1000000 kg NFPA-H2 to Soil
Incident Requiring Significant Off-Site Remediation OR
< 10000 kg Very Toxic to Waterway OR < 100000 kg NFPA-H4 to Soil
< 100000 kg Toxic to Waterway OR < 1000000 kg NFPA-H3 to Soil
> 100000 kg Harmful to Waterway OR > 100000 kg NFPA-H2 to Soil
Incident with Significant National Media Attention OR
< 100000 kg Very Toxic to Waterway OR < 1000000 kg NFPA-H4 to Soil
> 100000 kg Toxic to Waterway OR > 1000000 kg NFPA-H3 to Soil
Acceptable
Tolerable - Offsite
Tolerable - Onsite
Unacceptable
Low
Con
sequ
ence
Hig
h
Con
sequ
ence
Low
Frequency
High
Frequency
Consequence Severity Description Frequency
Severity Level-1
Minor Injury On-site
(or < 0.01 Person Severely Impacted On-site)
Potential for Adverse Local Publicity
Property Damage and
Business Loss < $50M2 Orange Yellow
Green
Green
Yellow> 10 People Severely Impacted On-site
> 1 Person Severely Impacted Off-site
Property Damage and
Business Loss > $50 MM6 Red
Red Red Orange Yellow GreenSeverity Level-41 to 10 People Severely Impacted On-site
0.1 to 1 People Severely Impacted Off-site
Property Damage and
Business Loss $5 MM to
$50 MM
Legend
6
Yellow Green GreenSeverity Level-2
Major Injury On-site
(or 0.01 to 0.1 Person Severely Impacted On-site)
Public Required to Shelter Indoors
(or Minor Injury Off-site)
Property Damage and
Business Loss $50 M to
$500 M
3 Red
Red Orange Yellow GreenSeverity Level-3
Potential Fatality On-site
(or 0.1 to 1 Person Severely Impacted On-site)
or Potential Major Injury Off-site
Property Damage and
Business Loss $5 MM to
$50 MM
4 Red
Severity Level-5
6
Red Orange
5 Red
Risk Matrix: Risk = Consequence Severity times Frequency
Red Red
Green Green Green Green
Orange
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 26
Case Study – BP Texas City
Risk Analysis / Layers of Protection Analysis (LOPA)
Initiating Event – either Basic Level Control System failure (instrument was not
indicating the correct level) or Human Performance Failure as “operators routinely
deviated from written procedures maintaining a high liquid level during startup to
minimize the potential for costly damage to the fired heaters”. From the CCPS Book,
Layers of Protection Analysis, a frequency of 0.1 per year may be appropriate.
Loss Event – Overfill of the Raffinate Splitter Column to the Blowdown Tank with
subsequent release of flammable material to the atmosphere.
Incident Outcome and Consequence – Vapor Cloud Explosion resulting in greater
than 10 potential fatalities.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 27
Case Study – BP Texas City
Risk Analysis / Layers of Protection Analysis (LOPA)Conditional Modifier – the probability of ignition for an unknown source assuming
“good “ ignition controls
UK HSE Research Report 226, Development of a method for the
determination of on-site ignition probabilities (2004)
Cloud Area ~ 0.3 (235 m)2 = 16568 m2 = 1.66 hectares
~0.15
CCPS, Guidelines for Determining the
Probability of Ignition of a Released Flammable Mass, (2014)
A reasonable probability
of ignition for this case
may be 0.1 to 0.15 as
the process area is
likely electrically
classified with “good
controls”.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 28
Case Study – BP Texas City
Risk Analysis / Layers of Protection Analysis (LOPA)Scenario Number: Equipment Identification:
Raffinate Column
Date:
Consequence Description/
Category
Column Overfill resuting in flammable
release to the atmosphere and vapor
cloud explosion.
Risk Tolerance Criteria
(Category or Frequency)Potential for greater than 10 fatalities 1.E-06
Initiating Event
(typically a frequency)
Failure of Level Control Loop or Human
Performance Failure for filling the colmn
above level reading during startup
1.E-01
Enabling Condition or
Event
Probability of Ignition 1.E-01
Probability of Personnel in Affected Area
Probability of Fatal Injury
Others
1.E-02
Description ProbabilityFrequency
(per year)
Scenario Title:
Overfill Scenario during Startup
Conditional Modifiers (if applicable)
Frequency of Unmitigated Consequence
BPCSHigh Column Pressure shut off of heat to
the column reboiler1.E-01
Human InterventionBlowdown Tank High Level with
Procedure to close manual Feed valves1.E-01
SIFRaffinate Column High Level Alar with
Automated shutoff of Heat and Feeds1.E-01
Pressure Relief Device
Other Protection Layers
(must justify)
Restriced Access near Isom Unit during
Operation or Startup1.E-01
Safeguards (Non-IPLs)
1.E-04
1.E-06
Actions Required to Meet
Risk Tolerance Criteria
Notes
References (link to
originating hazard review,
PFD, P&ID, etc.)
LOPA Analysis (and Team
Members)
Independent Protection Layers (IPLs)
Total PFD for all IPLs
Ensure all Protections are Inspected, Tested, and Maintained to company standards. Restrict
placement of temporary occupied buildings beyond blast contour unless blast resistent
buildings are used.
Meets Tolerable Criteria for Harm to On-Site Personnel
Risk Tolerance Criteria Met? (yes/no)
Frequency of Mitigated Consequence
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 29
Case Study – BP Texas City
Sustaining Performance
The existing safeguards were close to sufficient for managing this scenario to a tolerable risk
level had they been adequately maintained and some actions automated rather rely only on
operator response to an alarm. In addition to those listed in the LOPA worksheet, several other
alarms existed (such as high pressure) that may have contributed to reducing the overall
scenario frequency if the potential for column overfill would have been recognized.
What are the Hazards?
What can go Wrong?
How Bad could it Be?
might it Happen?
Is the Risk Tolerable?
Identify Chemical
and ProcessHazards
Estimate Frequency
AnalyzeConsequences
Analyze Risk
ImplementAdditional
Safeguards as Needed
Develop Scenarios
Select Equipmentor Activity to be
Analyzed
Sustain Performancefor Life Cycle
of Facility
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
June 28, 2021 Slide - 30
Risk Analysis Screening Tools (RAST)
Case Study – BP Texas CityRisk Analysis and Incident Investigation often use similar methods to better understand
the scenario. Risk Analysis “anticipates” what could go wrong and what the potential
consequences may be. For Incident Investigation, the Incident Outcome and
Consequences are known in addition to the actual weather conditions and wind
direction.
For the Raffinate Splitter, a column overfill would be one of many scenarios to consider.
It would need to be recognized that a Vapor Cloud Explosion could be a feasible
Incident Outcome for an Overfill loss event. CHEF was conservative in estimating blast
damage as actual wind direction was not toward the wooden trailers and a simplified
single Potential Explosion Site of “average” congestion and confinement was assumed.
However, the “order of magnitude” estimate of consequences seems reasonable.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Chemical Hazard Engineering Fundamentals – Case Studies
Questions?
June 28, 2021 Slide - 31