ccps an aiche technology alliancerisk analysis screening tools (rast) overview / demonstration march...
TRANSCRIPT
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 1
Risk Analysis Screening Tools (RAST)
Case Study – DPC Industries
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance
DPC Enterprises – Chorine Release
Festus, Missouri
August 14, 2002
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 2
Case Study – DPC IndustriesHazard Identification and Risk Analysis (HIRA) Study
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
Analyze Consequences
AnalyzeRisk
IdentifyAdditional Safeguards as Needed
DevelopScenarios
Identify Equipment
or Activity to be Analyzed
Manage Barriers
for Life Cycle of Facility
We begin the study by Identifying the Equipment or Activity for which we intend to perform
an analysis. RAST uses 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.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 3
Case Study – DPC Industries
Process DescriptionWe have been asked to perform a HIRA study of a chlorine repackaging facility. The DPC Enterprises
facility in Festus Missouri repackages chlorine from railcars into smaller containers. DPC captures
chlorine vented from these operations in one of two caustic scrubbers that also produce household
bleach for sale as a byproduct.
The chlorine repackaging operation involves the following:
• Connecting a 90-ton (180,000 pounds) chlorine tank car to one of three unloading stations.
• Transferring liquid chlorine from the tank car through the process piping system to filling stations.
• Loading the filled 150-pound cylinders and 1-ton containers onto trucks for distribution.
• Cleaning and preparing empty cylinders and containers for reuse.
In addition to repackaging chlorine, the Festus facility also runs a continuous bleach manufacturing
process. We will start with the chlorine railcar unloading operation
This is an illustrative example and does not reflect a thorough or complete study.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 4
Case Study – DPC Industries
Process DescriptionTank cars are brought into the facility through a
rail spur along the northwest corner of the site. A
storage area located on the eastern side of the
repackaging building contains several bulk
storage tanks of sodium hydroxide (caustic soda),
bleach, and wastewater. The three chlorine tank
car unloading stations are located along the
northern side of the repackaging building.
Pad air is used to help push the liquid chlorine
out of the tank car into the plant piping. An
eduction pipe is used to unload liquid material. It
is a long steel pipe attached to the liquid valve
and extends to the bottom of the tank car.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 5
Case Study – DPC Industries
Process DescriptionEach unloading station is equipped with three chlorine transfer hoses, each approximately 11 feet in
length and 1 inch in diameter. The chlorine system is designed to shut off accidental releases
utilizing chlorine detectors and automatic air-actuated ball valves. These valves may be activated
either automatically or manually by pressing one of several Emergency Shut Dow buttons located
throughout the facility. Hoses remain pressurized to approximately 8 bar (115 psig) throughout
normal operations although flow is stopped during breaks and lunch.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 6
Risk Analysis Screening Tools (RAST)
Case Study – DPC Industries
We will start by entering information for chlorine rail car. At some point, we may decide to
include other equipment associated with the facility in the study.
One the Main Menu, enter the equipment identification as the Chlorine Rail Car, equipment
type as Tank Truck/Rail Car/Tote and location as Outdoors.
Chemical Data – RAST requires a chemical or chemical mixture that is representative of the
hazards. RAST does not perform time-dependent or location-dependent composition
changes (such as within a reactor or distillation column). In this example, we will merely
enter chlorine as the chemical.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
Import from Previous Study
Merge Data from Another Study into this Study
Update Previously Saved Information
Access LOPA Workbook from Scenario Results
Update Notes and Comments for Entire Workbook
Select Default Units: Study File: Copy of Risk Analysis Screening Tool.xlsm
Session Date: Participants:
Equipment Identification =
Equipment Type =
Equipment Location =
Data Entry Status or Notes:
Plant Section or Sub-Area:
P&ID Number:
Min
Complete
RAST
Input Data Sufficient to Proceed with Analysis
Input Information
Tank Truck/Rail Car/Tote
Outdoors
Chlorine Rail Car
Evaluations and Reports
Risk Analysis Screening Tools (V 2)Latest Revision Date 3/02/19
Import from RAST File
Equipment Parameter Input
Chemical Data Input
Reaction Input and Evaluation
Fire & Explosion Index / Chemical Exposure Index
English Units SI Units
Relief Effluent Screening
Scenario Identification
Check Inputs
Save Inputs toEquipment Table
Go to Equipment Table >
Process Conditions Input
Plant Layout Input
Hazards & Consequences
LOPA Menu >
Clear Input
Update Scenarios for Equipment Loaded
Input Guidance Information
CLEAR EVERYTHING IN WORKBOOK
Pool Fire Evaluation
Merge Data from Another File
Go to Workbook Notes >
Go to Revision Log >
Go To Scenario Results >
Go To Instructions >>
March 20, 2019 Slide - 7
Enter Equipment Identification,
Equipment Type and Location
Risk Analysis Screening Tools (RAST)
Case Study – DPC InstrustriesBegin by entering
information on the
Main Menu worksheet.
Start with the Chlorine
Rail Car.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 8
Case Study – DPC Industries
Chemical Data
The chemical name is
entered as chlorine and the
weight fraction as 1.0
The operating pressure was
entered as 8 barg and the
operating temperature is
entered at 25 C. That that
units may be changed such
as an operating pressure of
115 psig and operating
temperature of 77 F.
Chemical Data Input
Equipment Identification: 25 C
Equipment Type: 8 bar
Location: 30.4 C
Key Chemical: Reference:
Chemical Comments:
Reg. Agency Considers Toxic? Yes
ERPG-3 Values, LC1, LC50, and/or Categories for Aquatic Toxicity or Dermal Toxicity must be entered
Chlorine 1.000 1.000 1.0000 70.91 3 20
Sum = 1.00 Vapor Mixture Properties: 70.9 3.0 20.0
Mixture azeotrope? No
Melting Point = -101 deg C
Flash Point = deg C
Est Mixture Flash Point =
1 Not “Sustained Burning”?
AutoIgnition Temperature = deg C
Ease of Ignition =
Fuel Reactivity =
Dermal Toxicity =
Aquatic Toxicity =
Model as a single Pseudo-Chemical? Mixture NFPA Flammability = 0
Mixture NFPA Health = 4
Reactivity Category =
Mixture NFPA Reactivity = 0
Estimated Boiling Point = -34.0 C Liquid Conductivity = Non-Conductive
Vapor Pressure at Operating Temp = 7.709 atm
Liquid Density at Operating Temp = 1.38 gm/ml
Liq Heat Capacity at Op Temp = 0.25
Liq Heat Capacity at Boiling Point = 0.22 micron
Heat of Vaporization at Op Temp = 60 micron
Heat of Vaporization at Boiling Point = 69 mJoule
Boiling Point at Relief Set or MAWP = 79.5 C
Boiling Point at Burst Pressure = 119.4 C
From the above vapor composition: Estimated 1 hour LC 1 74.3 ppm Estimated 1 hour LC 50 404.3 ppm
State Mol Weight ERPG-2 (ppm) ERPG-3 (ppm) LFL (vol %) Flash Pt (C )
Pad Gas Properties Vapor 29
Heat Transfer Fluid
High Viscous Material (for F&EI)?
Mixture Properties
Wt Fraction
Feed
Molecular
Weight
Second Liq
Phase
Relative
Volatility
Wt Fraction
Vapor
User ValuesMixture
Estimates
ERPG-3 (ppm)ERPG-2 (ppm) LFL (vol %)
Liquid
Operating Temperature =
Chlorine
Chlorine Rail Car
Outdoors
Tank Truck/Rail Car/Tote
Second Liq
Phase
Chemicals (the first chemical listed is the 'key'
chemical)
Wt Fraction
Feed
Saturation Temperature =
Physical State =
Operating Pressure (gauge) =
Solids Mean Particle Size =
cal/gmDust Min Ignition Energy =
Name
Dust-flammable hybrid?
Particle Size at 10% Fraction =
Solids Bulk Density >160 g/liter (>10 lb/ft3)?
Summary of Chemical Properties
cal/gm C
Standard Mixture (the key chemical has been
defined as a mixture)
Dust CharacteristicsDust/Solids Hazard Class =
Go To Process Conditions >Save All Input to Equipment TableEnter New Chemical Clear Input
<< Go To Main Menu
Go To Plant Layout >
Show Chemical Details Hide Chemical Details
Go To Equipment Input >
Saturation temperature is
displayed and physical
state as “liquid”
RAST allows up to 5
components.
Chemical details may
be shown or hidden
The operating pressure
and temperature
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
Equipment Input
Equipment Identification:
Equipment Type:
Location:
17300 gal Pipe Length = m
375 psi Piping Vulnerable to Damage?
Apply Screwed Connection Penalty?
C
C
1 in Pump Type =
Seal or Containment Type =
Remote Start Pump?
43965 kg Pump Automated Suction or Discharge?
kg Estimated User Entry
Pump Volume (including piping to block valves), liter 0.3
Pump Surface (including piping to block valves), m2 0.06
Kwatt
Equipment or Piping Connection =
76 sq m
sq m Replacement Cost & Business Loss
m Drum Oven Volume = cu m
mm High Speed Rotating Equipment?
Bellows or Expansion Joint Used?
Sight Glass Used?
Relief Device Identification
Relief Type =
Relief Discharges to:
Relief Set Pressure (gauge) = bar
sq m Relief Size (equiv. diameter) = mm
Kwatt /sq m C Relief Design Actual Flow Rate = kg/min
C Release Pipe Diameter = mm
bar Release Elevation m
Closest Distance From Relief to Elevated Work Area = m
Heat Transfer Fluid Name = Furthest Distance from Relief to Elevated Work Area = m
Elevation of Nearest Work Area = m
Enter Distances from Relief Location ONLY if Different from Equipment Location
mm Relief Distance to Property Limit or Fence Line = m
Relief Distance to Occupied Bldg 1 or Area = m
sq m Relief Distance to Center of Occ Bldg 1 = m
Kwatt /sq m C Occ Bldg 2 in Same Wind Direction for Relief?
C Relief Distance to Occupied Bldg 2 = m
Relief Distance to Center of Occ Bldg 2 = m
Piping Parameters
Pump / Agitator Parameters
MAWP (gauge) =
Equipment Description
The tank car was a U.S. Department of Transportation (DOT) 105J500W specification car.
Equipment Volume =
Tank Truck/Rail Car/Tote
Equipment Parameters
Full Vacuum Rated?
Estimated High Temperature Failure =
Estimated Embrittlement Temperature =
Equipment Elevation to Surface =
Drain Valve Size
Chlorine Rail Car
Outdoors
Susceptible to Vibration Fatigue?
Motor Power =
User Equipment Max. Wetted Area =
Heat Transfer Fluid State =
Vessel/Tank Parameters
Material of Construction
Internal Corrosive or Stress Cracking Potential?
Equipment Mass =
Number of Flanges or Nozzles =
Nozzle or Pipe Size =
Estimated Equip Mass based on C. Steel
Other Equipment Parameters
Transportation Equipment or Piping Parameters
Tube Failure Release to Atmosphere?
Hose
Insulation
Estimated Equipment Max Wetted Area =
Heating Fluid Temperature =
Heating Transfer Area =
Tracing ?
Vessel/Tank Geometry?
Insulation Heat Reduction Factor =
Warning: Operating Pressure Greater than Relief Set Pressure
Low Pressure Tank with Weak Seam Roof?
Coolant Temperature =
Conductive Dip Pipe or Bottom Fill?
Cooling Transfer Area =
Tube (or Leak) Diameter =
Quantity Hot Oil Handled (for F&E) =
Cooling Overall U =
Number of Tubes =
Relief Device Parameters
Heat Transfer Parameters
Heating Overall U =
Heat Transfer Fluid Pressure (gauge) =
Vessel/Tank Considered as "Storage"?
Clear InputSave Input to Equipment Table< Go To Chemical Data
<< Go To Main Menu Go To Process Conditions Input >
Go To Plant Layout >
Go To Reaction Input >
March 20, 2019 Slide - 9
Case Study – DPC Industries
Equipment Input
A chorine rail car contains a
maximum of 82000 kg chlorine
(90 m3 or 17300 gal). The
maximum allowable working
pressure is 26 barg or 375 psig.
Liquid connections are 1 inch.
The equipment volume
and maximum allowable
working pressure
A largest “working” nozzle
of 1 inch is entered
A connection type of “Hose”
is also entered.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 10
Case Study – DPC Industries
Process ConditionsThe maximum flowrate to the
railcar is zero as railcars are
only unloaded at this facility.
A 0.9 maximum fill fraction is
entered as the rail car is
received approximately 90% full
(versus the default 80% if the
entry is blank).
The default ambient
temperature of 25 C has been
assumed (based on no entry for
ambient temperature).
Process Conditions Input
Equipment Identification:
Equipment Type:
Location:
Ambient Temperature = Operating Temperature = 25 C
Inventory Limit (blank is unlimited) = kg Operating Pressure (gauge) = 8 bar
Liquid Head within Equipment, Dh = m Physical State =
Limiting Maximum Fill Fraction = 0.9 Saturation Temperature = 30.4 C
Limiting Minimum Fill Fraction = Contained Mass = 81592 kg
Maximum Feed Press (gauge) = bar Maximum Contained Mass = 90658 kg
Maximum Feed or Flow Rate = 0 kg/min Inventory for Reference = 90658 kg
Maximum Feed Temperature = C
Type of Feed (Batch or Continuous)
Non-Ignitable Atmosphere Maintained?
Potential for Aerosol or Mist?
Pad Gas Name = Percent of Time in Operation =
Max Pad Gas Pressure (gauge)= bar
Maximum Pad Gas Rate = kg/min
Downstream Pressure (gauge) = bar
Maximum Back Flow Rate = kg/min
Equipment Vents to .. =
Use Time-based Release for Equipment Rupture? sec
Chlorine Rail Car
Tank Truck/Rail Car/Tote
Process Description
The rail cars are only unloaded such that the maximum fill
rate is zero.
Process/Operating Conditions
Outdoors
Summary for Chlorine
Frequent Turnaround or Cleanout?
Operating Procedures
Liquid
Review Date:
Review of Operating Procedures for
Selected Equipment Item by:
Centralized Ventilation Shut-Off Bldg 1?
Centralized Ventilation Shut-Off Bldg 2?
Clear InputSave Input to Equipment Table< Go To Chemical Data
Go To Plant Layout ><< Go To Main Menu
< Go To Equipment Input
Go To Reaction Input >
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 11
Case Study – DPC Industries
Site LayoutIn addition to the site office building 50 m
south of the rail car station (~ 5 occupants),
various businesses and residential areas
surround the DPC Festus facility:
• Blue Fountain residential mobile home
park, consisting of about 100 homes, is
approximately 100 m southwest.
• Goodwin Brothers Construction and
Intermodal Tire Retreading are located
about 100 to 200 m to the east, separated
from DPC by Highway 61. Each business
has about 18 full-time employees.
• Interstate 55 is located less than 0.5 mile
to the east Approximately 500 m
Railcar Station
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
2E-4 people/m2
Residential homes
on very large plots
5E-5 people/m2
Rural homes/farms
Case Study – DPC Industries
Site Layout
March 20, 2019 Slide - 12Approximately 500 m
RAST allows for entry of two offsite
populated areas referred to as Zone 1
and beyond Zone 1. Zone 1 begins at
the “Distance to Property Limit”
extends to “Distance to End of Zone 1”
on the Plant Layout worksheet.
A free software program, MARPLOT
(from the US EPA), may be used to
determine population density in the
United State. Outside the US or
where data is not available from
MARPLOT, the following pictures give
an idea of offsite population density.
Examples of Sparsely populated areas
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
3E-4 people/m2
Mobile Homes (upper
end of Moderate)
1.5E-3 people/m2
Typical suburban
residential area
5E-3 people/m2
Multifamily dwellings –
multi-story apartments
closely spaced
4E-3 people/m2
Multifamily dwellings
– 2 story apartments
and duplexes
4E-3 people/m2
Very closely spaced
single family dwellings
Examples of Moderately populated areas Examples of Densely populated areas
March 20, 2019 Slide - 13
Case Study – DPC Industries
Site Layout
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 14
Case Study – DPC Industries
Site LayoutThe Blue Fountain mobile home park
(noted as Zone 1) is located adjacent to
the DPC property and extends to
approximately 500 m from the rail car
station. The population density is higher
than a typical residential area at roughly
0.003 people/m2. The region beyond
the mobile home park (in the same wind
direction) denoted as beyond Zone 1 is
rural with a very low population density
(maybe 0.00005 people/m2).
The site office and offsite businesses
are entered as occupied buildings.
Plant Layout Input
Equipment Identification:
Equipment Type:
Location:
Distance to Property Limit or Fence Line = 100 m Occupied Building 1 Name =
Furthest Distance to Fence Line ( > 100 m ) = m Distance to Occupied Bldg 1 or Area = 50 m
Max. Onsite Outdoor Population Density people/m2 Elevation of Occ Bldg 1 Ventilation Inlet = m
Personnel Routinely in Immediate Area? Yes Distance to Center of Occupied Bldg 1 = m
Distance to end of Offsite Zone 1 500 m Occupied Bldg Type =
Offsite Population Density within Zone 1 0.003 people/m2 Occupied Bldg Ventilation Rate = changes/hr
Offsite Population Density Beyond Zone 1 0.0001 people/m2 Number of Building Occupants = 5
Effective Egress from Work Area? Occ Bldg 2 in Same Wind Direction? No
Access for Emergency Services? Occupied Building 2 Name =
Degree of Equipment Congestion in Area? Distance to Occupied Bldg 2 200 m
Containment or Dike Surface Area = sq m Elevation of Occ Bldg 2 Ventilation Inlet = m
Consider Dike or Bund Failure for Vessel Rupture? Distance to Center of Occ Bldg2 = m
Credit Fire Heat Adsorption for Drainage/Indirect? Occupied Bldg 2 Type =
Distance to Nearest Fired Equipment = Occupied Bldg 2 Ventilation Rate = changes/hr
Quantity of "Other" Flammables in Immediate Area kg Number of Occupants Bldg 2 = 30
Quantity of Flammables in Adjacent Area kg
Adjacent Containment or Dike Surface Area = sq m
Automated EBVs to limit spill quantity?
Spills to Soil Require Remediation?
Potential for Water Contamination?
Enclosed Process Volume = cu m High Population Downstream of Facility?
Enclosed Process Ventilation = changes/hr
No. Enclosed Area Personnel =
Note that Environmental Scenarios are Excluded
Enclosed Process Area Data
Occupied Building DataLocation Information
Environmental Inputs
Goodwin Bothers/Intermodal Tire
Site Office
Chlorine Rail Car
Tank Truck/Rail Car/Tote
Outdoors
Layout Description
Clear InputSave Input to Equipment Table< Go To Process Conditions
Go To Reaction Input ><< Go To Main Menu
< Go To Equipment Input
< Go To Chemical Data
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 15
Risk Analysis Screening Tools (RAST)
Case Study – DPC Industries
Input Data for an Equipment Item
stored in one row by Equipment Tag
Retrieve Information for an Equipment
Item by selecting any cell in the desired
row and entering Load Selected
Select Save Inputs to Equipment Table (blue macro button). All Input Information
will be stored in the Equipment Table in a single row identified by a unique Equipment
Identification or Tag.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
Risk Analysis Screening Tools (RAST)
Risk Matrix
March 20, 2019 Slide - 16
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 Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 17
Case Study – DPC Industries
Suggested Scenarios for Rail Car
HAZOP Node: HAZOP Design IntentPlant Section =
Equipment Type = Tank Truck/Rail
Car/ToteEquipment Tag = Chlorine Rail Car
LOPA Menu Filters:
Scenario Type Scenario CommentsParameters and
DeviationInitiating Event (Cause) Initiating Event Description Loss Event Outcome
Off
-Sit
e T
oxi
c R
elea
se
On
-Sit
e T
oxi
c R
elea
se
Ind
oo
r T
oxi
c R
elea
se
To
xic
Infi
ltra
tio
n
Ch
emic
al E
xpo
sure
Fla
sh F
ire
or
Fir
ebal
l
Vap
or
Clo
ud
Exp
losi
on
Bu
ild
ing
Exp
losi
on
Eq
uip
men
t E
xplo
sio
n
Pro
per
ty D
amag
e o
r B
usi
nes
s L
oss
En
viro
nm
enta
l D
amag
e
Damage from Movement
Spill caused by Truck or car
movement while transfer is in
progress
Flow-Loss of
Containment3rd Party Intervention Driver inadvertantly moves truck or car Full Bore Hole Size Leak
Off-Site Toxic Release, On-Site
Toxic Release, Toxic Infiltration6 5 6
Drain or Vent Valve OpenDrain or Vent Valve left open following
loading/unloading or batch transfer
Flow-Loss of
Containment
Human Failure Action more than once
per quarter
Operator leaves Drain or Vent Open
following unloading or clean-outDrain or Vent Leak
Off-Site Toxic Release, On-Site
Toxic Release, Toxic Infiltration6 5 5
Hose or Loading Arm ConnectionSpill associated with improper
connection of hose or loading arm
Flow-Loss of
Containment
Human Failure Action more than once
per quarter
Operator fails to ensure a proper connection
before starting material transferGasket Failure
Off-Site Toxic Release, On-Site
Toxic Release, Toxic Infiltration6 5 5
Piping or Equipment Leak - Full
Bore
Assessment Excludes Mechanical
Integrity Scenarios
Flow-Loss of
ContainmentUnloading/Loading Hose Failure Failure of Hose from fatigue,etc. Full Bore Hole Size Leak
Off-Site Toxic Release, On-Site
Toxic Release, Toxic Infiltration6 5 6
Excessive Heat Input - Heat
Transfer
No Heating Media Temperature was
notedPressure-High BPCS Instrument Loop Failure Failure of Flow Control
Criteria for Triggering Incidents Not
Met
Excessive Pad Gas Pressure
Maximum Pad Gas Pressure Does
Not Exceed the Maximum Allowable
Working Pressure or Relief Set
Pressure
Flow-High Regulator FailureRegulator Fails causing high flow or
pressure
Criteria for Triggering Incidents Not
Met
Overfill, Overflow, or Backflow
Overfill or Backflow of liquid with spill
rate equal to the feed rate to a
maximum quantity of the available
inventory minus contained mass
Level-High or Flow-
BackflowBPCS Instrument Loop Failure
Failure of Level Indication with continued
addition of material
Criteria for Triggering Incidents Not
Met
Pad Gas Compression
Maximum Feed or Downstream
Pressure does not exceed the
Maximum Allowable Working
Pressure or Relief Set Pressure
Pressure-High BPCS Instrument Loop Failure Failure of Pressure ControlCriteria for Triggering Incidents Not
Met
Vacuum Damage Equipment is rated for Full Vacuum Pressure-LowHuman Failure Action more than once
per quarter
Operator leaves valves closed allowing
vacuum during emptying of equipment
Criteria for Triggering Incidents Not
Met
Potential Outcome / Tolerable Frequency Factors
Suggested Scenarios from the RAST Library
Scenarios in gray were
considered but are excluded for
reason noted
Scenarios with NO IPL's Required will NOT be reported.Mechanical Integrity Scenarios will NOT be reported
Chlorine Rail Car is a Tank Truck/Rail Car/Tote containing Chlorine that operates at
25 C and 8 bar. The volume is 18000 gal with a maximum allowable working
pressure of 375 psi. The maximum feed or flow rate is 0 kg/min.
Off
-Sit
e T
oxi
c R
elea
se
On
-Sit
e T
oxi
c R
elea
se
Ind
oo
r T
oxi
c R
elea
se
To
xic
Infi
ltra
tio
n
Ch
emic
alE
xpo
sure
Fla
shF
ire
or
Fir
ebal
l
Vap
or
Clo
ud
Exp
losi
on
Bu
ild
ing
Exp
losi
on
Eq
uip
men
t Exp
losi
on
Pro
per
ty D
amag
e o
r B
usi
nes
s L
oss
En
viro
nm
enta
l D
amag
e
Update Go To Scenario Results ><< Go To Main Menu
Create UserScenario
Note that Mechanical Integrity (Residual Failures) have been excluded for the listing based on entering “Yes” to
“Exclude MI Scenarios?” on the LOPA Menu worksheet.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 18
Case Study – DPC Industries
Suggested Scenarios for the Rail Car
❑ Review the suggested list of scenarios. Do these represent what you
would expect for a rail car unloading operation?
❑ 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 Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 19
Case Study – DPC Industries
Consequence AnalysisRAST Version 2
Release Location Outdoors
Airborne Quantity Summary:
Release Temperature, C 25.0 Factor Probability
Release Pressure, barg 8.000
Physical State at Release Conditions Liquid
Heat Input, Kcal/min
Equivalent Hole Size, cm 2.540
Release Rate, Kg/sec 5.75
Release Duration, min 60.00
Spray Distance, m 14.0
Flash + Aerosol Evaporation Fraction 0.784
Estimated Aerosol Droplet Diameter, micron 99
Pool Area, sq m 55.9
Estimated Pool Temperature, C -34.4
Maximum Pool Evaporation Rate, kg/sec 1.9973
Total Airborne Rate, kg/sec 6.50
Total Airborne Quantity, Kg 19821.4
Airborne Quantity Composition:
Mole Fraction Chlorine 1.000
Mole Fraction Pad Gas (at Mw = 29)
ERPG-2 for Vapor Composition, ppm by volume 3.2
ERPG-3 for Vapor Composition, ppm by volume 21.2
LC-50 Concentration, ppm by volume 775.7
One-hour ERPG-3 for Vapor Composition, ppm by volume 20.0
One-hour LC-1 Concentration, ppm by volume 74.3
LFL for Vapor Composition, % by volume
Dispersion Summary (Atmospheric Stability Class D with 3 m/sec wind except as noted):
Max Distance to Time-Scaled ERPG-2, m 3428.0
Max Distance to Time-Scaled ERPG-3, m 1327.6
Max Distance to 1% Lethality for 1.5 F weather, m 2717.0
Max Distance to Estimated LC-50 Concentration, m 219.7
Max Distance to Flash Fire Impact or 0.5 LFL, m
Maximum Ground Elevation Concentration, ppm 1000000.0
Concentration at Distance to Fence Line, ppm 3731.7
Concentration at Distance to Unrestricted Work Area, ppm 1000000.0
Concentration within Occupied Bldg 1, ppm 6798.3
Concentration within Occupied Bldg 2, ppm 430.9
Concentration within Enclosed Process Area, ppm
Conc within Enclosed Process Area w/Ventilation, ppm
Potential Toxic
Impact within
Occupied Building
(Indoor Conc > one-
Prob of Exposure (proximity based)
Fence Line
Concentration
Exceeds ERPG-2
On-Site Toxic POE
Flash Fire POE
Physical Explosion POE
Chemical Exposure POE
CONSEQUENCE SUMMARY Date:
Full Bore Pipe or Nozzle LeakLoss Event for: Tank Truck/Rail Car/Tote; Chlorine Rail Car
Containing Chlorine :
Ground or Work Area
Exceeds Multiple of
LFL or Time-Scaled
ERPG-3
with Personnel in Immediate Area
For the Rail Car, select Full Bore
Pipe or Nozzle Leak as the Loss
Event. This provides a “worst”
Consequence for a total hose failure.
The distance to ERPG-2 is estimated
in RAST to be more than 3400 m or
2.1 miles. Adjusting for the actual
1.5 m/sec wind speed at the time of
the incident, the distance to ERPG-2
would have been estimated at 3.0
miles which is in close agreement
with CPB modeling of 3.7 miles.
The leak rate estimated by CSB was
approximately 2 kg/sec, somewhat
less than a full bore failure..
The actual wind speed was nearly 1.5
m/sec. Wind speed, atmospheric
stability, and surface roughness are
Administrative Parameters that may be
adjusted on hidden worksheets.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
RAST Version 2
Explosion Summary:
VCE or Building Explosion Energy, kcal
VCE or Building Explosion Distance to 1 psi Overpressure, m
Maximum Distance to LFL Concentration, m
Blast Overpressure at Center of Occupied Building 1, psi 0.0
Blast Overpressure at Center of Occupied Building 2, psi 0.0
Distance to Severe Thermal Radiation Impact, m
Rupture Explosion Energy, kcal
Distance to Direct Blast Impact (10 psi), m
Maximum Fragment Range, m
Rupture Distance to 1 psi Overpressure, m
Rupture Overpressure at Center of Occupied Building 1, psi 0.0
Rupture Overpressure at Center of Occupied Building 2, psi 0.0
Incident Outcome and Consequence Summary:
6
Onsite Toxic Impact based on Distance to LC-50 Concentration of 220 m Yes 5
Outdoor Toxic Exposure Duration 600 sec
Onsite Flash Fire Impact based on Distance to 0.5 LFL Concentration of 0 m NA
Chemical Exposure based on Dermal or Thermal Hazards and Spray Distance of 14 m NA
Onsite Direct Blast Impact based on Distance to 10 psi of 0 m
Onsite Thermal Radation Impact based on Distance from Fireball of 0 m
Occupied Building Toxic Impact Yes 6
Number of Potential Serious Impacts for Building 1: 5 people
Number of Potential Serious Impacts for Building 2: 15.8 people
Occupied Building Impact from Vapor Cloud Explosion No NA
Number of Potential Serious Impacts for Building 1: 0 people
Number of Potential Serious Impacts for Building 2: 0 people
Occupied Building Physical Explosion Impact No
Number of Potential Serious Impacts for Building 1: 0 people
Number of Potential Serious Impacts for Building 2: 0 people
Environmental Impact: NA
Estimated Number of
People Impacted
Probability of Ignition (POI)
Probability of Explosion (POX)
LOPA Tolerable Frequency
Factors Based On
CONSEQUENCE SUMMARY Date:
Full Bore Pipe or Nozzle LeakLoss Event for: Tank Truck/Rail Car/Tote; Chlorine Rail Car
Containing Chlorine :
Impact Assessment with Personnel routinely in the immediate
area
Exceeds Threshold
Criteria
YesOffsite Toxic Impact based on Toxic Integration Method and 100 m to Fence Line
March 20, 2019 Slide - 20
Case Study – DPC Industries
Consequence Analysis
The number of people severely impacted
(likely fatalities) within the occupied
buildings is significant depending on any
evasive actions that many have been taken.
The estimated number of severely
impacted people (potential fatalities) is
greater than 10 for either the offsite
occupied businesses or the trailer park.
Fortunately the wind was away from the
trailer park (and most residents were at
work rather than home) and personnel
within the site office and nearby
occupied buildings were able to
evacuate quickly.
In the actual incident, there were no
fatalities but 63 people sought medical
attention and hundreds sheltered in
place for up to four hours.
The number of people severely impacted is
highly inaccurate and represents a “worst”
case assuming no effective evasive actions
or effective safeguards.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
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 east southeast rather
than southwest toward the trailer park or
directly toward the nearby businesses.
Wind Direction represents a key
difference between estimates for Risk
Analysis versus Incident Investigation.
March 20, 2019 Slide - 21
Case Study – DPC Industries
Consequence Analysis
REPORT NO. 2002-04-I-MO , US Chemical Safety Board
Figure 6. Aerial view of DPC Festus facility and surrounding area.
Release Point –
Rail Spot # 3
3 mile radius to ERPG-
2 concentration
Estimated Cloud
plume in RAST
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
Scenario Definition
Protection
Gap
Scenario /
Cross Ref
Description of Undesired ConsequenceLOPA Tolerable Frequency Factor
(chemicals, quantity involved,
and basis for calculations)
Initiating Event Probability of Ignition Probability of Exposure
(Presence Factor)
Time at Risk or Other
Enabling Factor
New
Instrumented
Protection
Credits
Taken
IPL Status? -->
Safety
AnalysisTolerable Frequency Factor 6 Unloading/Loading Hose Failure
5 1 6 1 0 0
12.01
Failure of Hose from fatigue,etc.
Tank Truck/Rail Car/Tote, Chlorine Rail Car, is involved
in a Piping or Equipment Leak - Full Bore event
resulting in a Full Bore Hole Size Leak with
subsequent 19800 kg airborne release of Chlorine at
an airborne release rate of 390 kg/min.
This incident could result in an Off-Site
Toxic Release at a Distance to ERPG-2
Concentration (HD2) of 3430 m which
exceeds Distance to the Fence Line of 100
m with the potential for Severity Level-5
< Back to Scenario Results
+
Expand All Collapse All
> Human Error ++ +> Possible IPLs
March 20, 2019 Slide - 22
Case Study – DPC Industries
Risk Analysis / Layers of Protection Analysis (LOPA)
The initial Initiating Event description
may be modified by the study team to
more clearly describe what happened
Select Loss Event Piping or
Equipment – Full Bore with
Incident Outcome of Off-Site Toxic
for analysis in LOPA (“Yes”), then
select LOPA Worksheet
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 23
Case Study – DPC Industries
Risk Analysis / Layers of Protection Analysis (LOPA)
A time at risk enabling condition of the leak occurring only during a 2000 hour operation per 8760
hour year may be appropriate as the hoses are checked daily for leaks. A conditional modifier for
personnel presence to represent that most trailer park occupants are not present during weekdays
may also be appropriate. The combination of these factors could reduce the scenario frequency or
severity of consequences by a factor of 10 depending on company specific protocol.
Scenario Definition
Protection
Gap
Scenario /
Cross Ref
Description of Undesired ConsequenceLOPA Tolerable Frequency Factor
(chemicals, quantity involved,
and basis for calculations)
Initiating Event Probability of Ignition Probability of Exposure
(Presence Factor)
Time at Risk or Other
Enabling Factor
New
Instrumented
Protection
Credits
Taken
IPL Status? -->
Safety
AnalysisTolerable Frequency Factor 6 Unloading/Loading Hose Failure
USER DEFINED Enabling
Factor = 1
1 1 6 1 0 0 1
12.01
Failure of Hose from fatigue,etc.
Tank Truck/Rail Car/Tote, Chlorine Rail Car, is involved
in a Piping or Equipment Leak - Full Bore event
resulting in a Full Bore Hole Size Leak with
subsequent 19800 kg airborne release of Chlorine at
an airborne release rate of 390 kg/min.
This incident could result in an Off-Site
Toxic Release at a Distance to ERPG-2
Concentration (HD2) of 3430 m which
exceeds Distance to the Fence Line of 100
m with the potential for Severity Level-5
The hose is leak checked
prior to each use such that a
time at risk may be
appropriate. 2000 hours use
per year operation of 8760
hours or 23% of time. As the
greatest risk is likely the
trailer park, greater than
40% of residents are not
home during repackaging
operation. Total factor 0.4
< Back to Scenario Results
+
Expand All Collapse All
> Human Error ++ +> Possible IPLs
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 24
Case Study – DPC Industries
Risk Analysis / Layers of Protection Analysis (LOPA)
The existing safeguards may not have been sufficient for managing this scenario to a tolerable risk
level. The chlorine sensor system is shared between the BPCS alarm and a SIL-2 SIS interlock but
may not have been designed to this level of reliability. The block valves could be operated manually
or via an emergency shutdown “button” but may be the same values for both the BPCS and the SIL-2
SIS and not be sufficiently reliable. Finally, the Excess Flow Valve may not effective as it addresses
leaks less than 15000 lb/hour for which there remains a significant consequence severity.
BPCS Control or
Human Response
to Alarm
BPCS Control or
Human Response
to Alarm
SIS Function A SIS Function BPressure Relief Device SRPS 1 SRPS 2 SRPS 3
Human Response to
Abnormal Condition Alarm >
1/4 hr to respond
SIS - SIL 2
1 2
Excess flow valve closes at
15,000 lb/hour chlorine flow.
However leak rate of less than
15,000 lb/hour is not likely
sufficient to reduce the
consequence by one severity
level (or 0.1)
Notes / Comments Issues to Resolve
Operator responds to audible
alarm from chlorine detectors
at 5 ppm and closes a manual
valve.
Chlorine detectors close
automated block valves when
the concentration reachess 10
ppm.
Not Allowed
+ + + +
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
March 20, 2019 Slide - 25
Risk Analysis Screening Tools (RAST)
Case Study – DPC IndustriesRisk 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 Chlorine Rail Car, RAST did suggest hose failure as one of many
scenarios to consider. RAST also recognized that an Off-Site Toxic Impact
could be a feasible Incident Outcome for this loss event. RAST was
conservative in estimating the number of people severely impacted as actual
wind direction was not toward the highest population. However, the “order of
magnitude” estimate of consequences seems reasonable.
CCPSCenter for Chemical Process Safety
An AIChE Technology Alliance Risk Analysis Screening Tools (RAST) Overview / Demonstration
Questions?
March 20, 2019 Slide - 26