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CHEMICAL EXPOSURE INDEX GUIDE
SEPTEMBER 1993 Second Edition
ii
D0 A 046841 CONFTDFNTTAl
TABLE OF CONTENTS
Page Preface ..................................................................................................................................................... i
Introduction ........................................................................................................................................... 1
Procedure for Chemical Exposure Index Calculations .................................................................. 2
Scenarios for Estimation of Airborne Release Rates..................................................................... 4
Emergency Response Planning Guidelines (ERPG) and Dow Emergency Exposure Planning Guideline (EEPG) ................................................................................................................ 5
Guidelines for Estimating the Amount of Material Becoming Airborne Following a
8
Release.....................................................................................................................................................
Estimating the Airborne Quantity for Gas Releases...................................................................... 11
Estimating Airborne Quantity for Liquid Releases........................................................................ 12
CEI and Hazard Distance Calculation .............................................................................................. 16
Chemical Exposure Index Summary Form ..................................................................................... 20
Figures Figure 1 -- Procedure for Calculation of Chemical Exposure Index (CEI) ..................... Figure 2 -- Flowchart for Calculating the Airborne Quantity ............................................. Figure 3A -- CEI vs. Airborne Quantity (SI Units)............................................................... Figure 3B -- CEI vs. Airborne Quantity (US/Brit Units) ....................................................
3 10 18 19
Tables Table 1 -- Emergency Response Planning Guidelines: ERPGs/EEPGs........................... Table 2A -- Physical Property Table for CEI (SI Units) ...................................................... Table 2B -- Physical Property Table for CEI (US/Brit Units) ..............................
6 21 22
Appendices Appendix 1 --Chemical Exposure Index Review Process ................................................... Appendix 2 --Containment and Mitigation Checklist............................................................ Appendix 3 --Example CEI Calculations (4 examples)........................................................ Appendix 4 -- Chemical Exposure Index for Selected Chemicals for Releases................. for Releases from a 2-inch Diameter Hole
23 26 27 38
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PROCEDURE FOR CHEMICAL EXPOSURE INDEX (CEI) CALCULATIONS
1. To develop a Chemical Exposure Index (CEI), the following items are needed: a. An accurate plot plan of the plant and the surrounding area. b. A simplified process flow sheet showing containment vessels, major piping and chemical inventories. c. Physical and chemical properties of the material being investigated, as well as the ERPG/EEPG (pages 5-7) values. d. A CEI Guide (Second edition). e. A CEI Form (page 20). Figure 1 (page 3) is a schematic overview of the CEI calculation. This chart will be helpful as you proceed through this guide.
2. Identify on the process flow sheet any process piping or equipment that could contribute to a significant release of an acutely toxic chemical.
3. Determine the Chemical Exposure Index and the Hazard Distances as explained in the following pages of this guide.
4. Fill out CEI Summary Sheet (page 20). 5. Determine if further analysis or review is necessary as outlined in the Corporate Process Risk
Management Guidelines for Facilities and Distribution.
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FIGURE 1_____________________________________________ PROCEDURE FOR CALCULATION OF CHEMICAL EXPOSURE INDEX (CEI)
po A 3
SCENARIOS FOR ESTIMATION OF AIRBORNE RELEASE RATES
The purpose of scenario selection is to determine which process piping or equipment has the greatest potential for the release of significant quantities of acutely toxic chemicals. Since the CEI now serves as a screening tool for further process hazards analysis, it is important that the calculations be done consistently on a global basis. The scenario selection process for determining airborne release rate has, therefore, been standardized to help achieve this goal. The selections listed below were chosen to include the most probable credible events based on historical performance of the chemical industry.
Evaluating several scenarios will aid in determining the largest potential airborne release. Process conditions such as temperature, pressure and physical state should be considered as well as pipe size since they have a significant impact on airborne release rates.
Scenario Selection for CEI: Select the scenario that gives the largest airborne release.
1. PROCESS PIPES Rupture of the largest diameter process pipe as follows: For smaller than 2-inch diameter -- full bore rupture For 2- through 4-inch diameter -- rupture equal to that of 2-inch diameter pipe For greater than 4-inch diameter -- rupture area equal to 20% of pipe cross section area
2. HOSES Full bore rupture
3. PRESSURE RELIEF DEVICES RELIEVING DIRECTLY TO THE ATMOSPHERE Calculated total release rate at set pressure. Refer to pressure relief calculation or contact process engineering. All material released is assumed to be airborne.
4. VESSELS Rupture based on largest diameter process pipe attached to the vessel using pipe criteria above.
5. TANK OVERFLOWS AND SPILLS
6. OTHERS Scenarios can be established based on the plant's or technology's experience, they can be the outcome of a review or derived from hazard analysis studies. They can also be based on the experience of another technology if the event could occur in this unit. Contact Process Engineering for special cases that may include reactivity or mixtures.
The treatment of instantaneous and very short duration continuous releases is simplified for the CEI calculation. Release from all scenarios are assumed to continue for at least a five minute duration. If a release is instantaneous or exceeds the total inventory within this duration, the release rate is calculated by dividing the total inventory by five minutes.
After this evaluation, choose the largest airborne release rate for the CEI calculation (page 20).___________
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EMERGENCY RESPONSE PLANNING GUIDELINES (ERPG) AND DOW EMERGENCY EXPOSURE PLANNING GUIDELINES (EEPG) #
The American Industrial Hygiene Association (AIHA) has published Emergency Response Planning Guidelines (ERPG) values which are intended to provide estimates of concentration ranges where one might reasonably anticipate observing adverse effects. These guidelines are intended to be used as a planning tool for various Dow programs to determine priority concerns, to evaluate the adequacy of containment, to identify downwind areas which might need to take action during a release and to develop community emergency response plans. The need for an ERPG is based on the volatility of a chemical, its toxicity, the releasable quantity and the public's perception of the potential hazard. The Emergency Exposure Planning Guidelines (EEPGs) are the Dow equivalent to the AIHA published ERPGs. These are provided when AIHA ERPGs do not exist. ERPG/EEPG definitions are as follows: ERPG-l/EEPG-1 is the maximum airborne concentration below which it is believed that nearly all
individuals could be exposed for one hour without experiencing other than mild transient adverse health effects or perceiving a clearly objectionable odor. ERPG-2/EEPG-2 is the maximum airborne concentration below which it is believed that nearly all individuals could be exposed for up to one hour without experiencing or developing irreversible or other serious health effects or symptoms that could impair their abilities to take protective action. ERPG-3/EEPG-3 is the maximum airborne concentration below which it is believed that nearly all individuals could be exposed for up to one hour without experiencing or developing life-threatening health effects.
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GUIDELINES FOR ESTIMATING THE AMOUNT OF MATERIAL BECOMING AIRBORNE FOLLOWING A RELEASE
This section of the CEI guide provides a description of the method to calculate the airborne quantity. The airborne quantity, as used in this guide, refers to the total quantity of material entering the atmosphere over time, directly as vapor or due to liquid flashing or pool evaporation.
CEI scenarios consider materials to be released as liquid or vapor. For example, the contents of a vessel can escape as a liquid through nozzle A, a vapor through nozzle B or "as calculated" through the relief device attached to nozzle C. Complex calculations that consider two-phase flow from ruptures are not included.
Airborne quantity for vapor releases from nozzle (B) or a pressure relief device (C) is the highest total flow rate calculated given the conditions of the vessel when the release occurs.
Liquid releases require a more complex treatment. As a liquid exits a vessel or pipe as a result of a failure, it can simply run out on the ground forming a pool (see Figure A), partially vaporize forming both a pool and a vapor cloud (see Figure B) or flash to such an extent that all the residual liquid exists as small droplets that are carried away with the vapor (see Figure C).
{\
)
Figure A
VJ Figure C
000OOo
A simple treatment of these events uses the operating conditions of the process to estimate the behavior of the material after the release.
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Liquids reaching the ground form a pool that spreads according to the terrain. If the vessel is surrounded by a dike, the liquid usually flows to the walls of the dike and the pool assumes the area within the dike. In all other cases, the pool is assumed to have an area that is predicted by the amount of liquid that enters the pool. Once a pool is formed, the liquid begins to evaporate from the surface. The vapor from the pool will combine with the vapor from the original flash and be dispersed downwind. This incident is treated by taking a "picture" of the release at a moment in time and then assuming it does not change. (See Figure D)
The airborne quantity for a liquid spill is determined by what happens to the liquid as it leaves the tank. If the liquid flashes to a high degree, then the airborne quantity is the discharge rate from the vessel. But if the liquid flash is low enough to allow pool formation, the airborne quantity is the gas flow resulting from the flash plus the airborne quantity that evaporates from the pool surface. Finally, as the tendency of the liquid to flash becomes small, the airborne quantity becomes the rate of evaporation from the pool surface. Figure 2 (page 10) provides a simplified flowchart for calculating airborne quantity. The equations are presented in both SI and US/British units.
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FIGURE 2 FLOWCHART FOR CALCULATING AIRBORNE QUANTITY
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ESTIMATING THE AIRBORNE QUANTITY FOR GAS RELEASES
The following equations, based on the sonic gas flow rate equation, are used to estimate the airborne quantity for a gas release,
SI Units
where Pa = absolute pressure = (Pg + 101.35) Pg = gauge pressure (kPa gauge) MW = molecular weight of the material T = temperature (C) D = diameter of the hole (millimeters)
{kg/sec}
(Equation 1A)
US/Brit Units
where Pa = absolute pressure = (Pg + 14.7) Pg = gauge pressure (psig) MW = molecular weight of the material T = temperature (F) D = diameter of the hole (inches)
{lb/min}
(Equation IB)
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ESTIMATING THE AIRBORNE QUANTITY FOR LIQUID RELEASES
The following steps describe a simplified procedure for estimating the airborne quantity for liquid releases.
Step 1: Determine the liquid flow rate being released.
The liquid release rate (L) is given by the following equations:
These equations assume that release from all scenarios will continue for at least five minutes before releases can be stopped. If a five minute release would exceed the total inventory, the release rate is calculated by dividing the total inventory by five minutes.
SI Units
where Pg = gauge pressure (kPa gauge)
(Note: for a tank open to the atmosphere Pg = 0) pj = density of the liquid at operating temperature (kg/m3) Ah = height of the liquid above the release point (meters) D = diameter of the hole (millimeters) US/Brit Units
where Pg = gauge pressure (psig)
(Note: for a tank open to the atmosphere Pg = 0) p] = density of the liquid at operating femperature (lb/ft3) Ah = height of the liquid above the release point (feet) D = diameter of the hole (inches)
{kg/sec]
(Equation 2A)
(lb/min)
(Equation 2B)
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12
Step 2: Determine the total liquid released.
The total amount of material contributing to the pool formation must be estimated in order to determine the pool size. If a release is large enough to empty a vessel in less than 15 minutes (including very large releases that occur in less than 5 minutes), the mass of liquid entering the pool is the total inventory of the vessel. For a longer duration continuous release (one lasting more than 15 minutes) the pool is assumed to reach a final size after 15 minutes. In this case, the mass determining the pool size is the release rate times 15 minutes (900 seconds).
The total liquid release (Wx) is the tank inventory (the tank is emptied in less than 15 minutes) or given by:
SI Units Wx = 900 L
{kg} (Equation 3A)
where
L = liquid flow rate (kg/sec) US/Brit Units
WT = 15L
{lb} (Equation 3B)
where
L = liquid flow rate (lb/min)
Compare the calculated Wj to the inventory of the system involved in the release. The total liquid assumed to be involved in the release is taken as the smaller of these two values.
Wj = smaller of calculated Wx or system inventory
Step 3: Calculate the fraction flashed.
Compare the operating temperature of the liquid to its normal boiling point. If the temperature is less than the normal boiling point, the flash fraction is zero. Go to Step 4, Equation 6. If the temperature is greater than the normal boiling point, calculate the fraction flashed (Fv).
The fraction of the liquid that will flash (Fv) when released is given by:
Fv=^(Ts-Tb) rlv
where
Tb = normal boiling point of the liquid Ts = operating temperature of the liquid Cp = average heat capacity of the liquid Hv = heat of vaporization of the liquid
SI
c c
J/kg/C
J/kg
(Equation 4)
US/Brit F F
BTU/lb/F BTU/lb
The CEI data table contains the ratio of heat capacities to latent heats of vaporization (Cp/Hv) for many chemicals. If a chemical is not listed and the needed information cannot be found, then a value of 0.0044 (SI) or 0.0024 (US/Brit) may be used for the ratio Cp/Hv.
As flashing occurs, some liquid will be entrained as droplets. Some of the droplets are quite small and travel with the vapor while the larger droplets fall to the ground and collect in a pool. As an approxima tion, the amount of material staying in the vapor is five times the quantity flashed. Therefore, if 20% of the material flashes, the entire stream becomes airborne and there is no pool formed.
The airborne quantity produced by the flash (AQf) is given by:
AQf = 5 (Fv) (L)
(kg/sec or lb/min}
(Equation 5)
where L = liquid flow rate (kg/sec or lb/min) If Fv > 0.2 then AQf = L and no pool is formed. Proceed to Step 6.
Step 4: Determine the pool size. The total mass of liquid entering the pool (Wp) is given by:
Wp = WT(l-5Fv)
(kg or lb)
(Equation 6)
where
Wj = total liquid released (kg or lb) Fv = fraction flashed
Please note that if none of the material flashes,
Wp = WT (kg or lb)
The size of the pool is approximated by assuming a pool depth of one centimeter. If the spill is in a diked area and of sufficient size, then the pool size is equal to the diked area.
The pool area (Ap) is given by:
SI Units W
Pool Area (AD) = 100--Pi
fm2}
(Equation 7A)
where
Wp = total mass entering the pool (kg) P] = density (kg/m2)
US/Brit Units W
Pool Area(AD) = 30.5--Pi
{ft2} (Equation 7B)
Wp = total mass entenng the pool (lb) p, = density (lb/ft3)
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14
If the liquid falls into a diked containment area, then the pool size may be equal to the diked area minus the area taken up by the tank. But, if the spill does not fill the diked area or occurs outside the diked area, use
Step 5: Determine the airborne quantity evaporated from the pool surface.
Airborne Quantity evaporated from the pool surface (AQp) is given by:
SI Units AQp = 9.0x10_4(ap0-95)^^---
{kg/scc}
(Equation 8A)
where
Ap = pool area (m2) MW = molecular weight Pv = vapor pressure of the liquid at the characteristic pool temperature (kPa) T =. characteristic pool temperature (C) (see Conditions 1 and 2)
US/Brit Units AQd = 0.154(ad 95)^W^~ p v p ' T +459
{lb/min}
(Equation 8B)
where
Ap = pool area (ft2) MW = molecular weight Pv = vapor pressure of the liquid at the characteristic pool temperature (psi) T = characteristic pool temperature (F) (see Conditions 1 and 2)
Condition 1 If the liquid is at or above ambient temperature but below its normal boiling point, the characteristic pool
temperature is equal to the operating temperature.
Condition 2 If the liquid is at or above its normal boiling point, the characteristic pool temperature is the normal boiling point of the liquid. The normal boiling point is the boiling point of the liquid at atmospheric pressure.
Step 6: Calculate the total airborne quantity. The total airborne quantity (AQ) is calculated by:
AQ = AQf + AQp
{kg/sec or lb/min} (Equation 9)
where
AQf = airborne quantity resulting from the flash (kg/sec or lb/min) AQp = airborne quantity evaporating from the pool surface (kg/scc or lb/min)
If the total Airborne Quantity (AQ) is greater than the liquid flow rate (L), set AQ = L.
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CEI AND HAZARD DISTANCE CALCULATION
Chemical Exposure Index
All CEI calculations assume a windspeed of 5 m/sec (11.2 miles/hour) and neutral weather conditions. The Chemical Exposure Index (CEI) is given by: SI Units
(Equation 10A)
where
AQ = airborne quantity (kg/sec) ERPG-2 = value (mg/m3)
US/Brit Units
(Equation 10B)
where
AQ - airborne quantity (lb/min) ERPG-2 = value (PPM) MW = molecular weight
If the CEI calculated value is greater than 1000, set CEI = 1000,
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16
Hazard Distance
The Hazard Distance (HD) is the distance to the ERPG-1, -2 or -3 concentration and is derived from the following equation:
SI Units
HD= 6551,1---- VERPG
{meters}
(Equation 11 A)
where
AQ = airborne quantity (kg/sec) ERPG = ERPG-1, ERPG-2 or ERPG-3 (mg/m 3)
US/Brits Units
HD = 9243 J---^-----\ ERPG(MW)
where
{feet}
(Equation 11B)
AQ = airborne quantity (lb/min) ERPG = ERPG-1, ERPG-2 or ERPG-3 (PPM) MW = molecular weight
If HD is greater than 10,000 meters (32,800 feet), set HD = 10,000 meters (32,800 feet).
DO CONF
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17
CEI
-CEI VS. AIRBORNE QUANTITY SI Units
o
d
w
w
>
00
0.000001
0.00001
0.0001
0.001
0.01
0.1
AQ (kg/sec) / ERPG-2 (mg/tn3)
1 10 100
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>
1000
*l-rHi
a a
w c*> 03
100
CEI
-CEI VS. AIRBORNE QUANTITY US/BRIT Units
10
1 0.00001
0.0001
0.001
0.01 0.1
1
AQ (Ib/min) / (ERPG-2 (PPM) * MW)
10
100 1000
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CHEMICAL EXPOSURE INDEX SUMMARY
PlantLocation Chemical______________________ _______________________ Total Quantity In Plant Largest Single Containment ___ _______________________________ ________________ Pressure Of Containment ___________ Temperature Of Containment _
1. Scenario Being Evaluated _____ 2. Airborne Release Rate from Scenario
3. Chemical Exposure Index
kg/sec lb/min
4.
Concentration
Hazard Distance
mg/m3
PPM
meters
feet
ERPG-l/EEPG-1 ERPG-2/EEPG-2 ERPG-3/EEPG-3
5. Distances to:
Public (generally considered Dow property line) Other in-company facility Non-company plant or business
meters _________ _________ ______
feet _________ _________ _________
6. The CEI and the Hazard Distance establish the level of review needed as determined in the Dow Process Risk. Management Guidelines for Facilities and Distribution.
7. If further review is required, complete Containment and Mitigation Checklist (Chemical Exposure Index Guide, 2nd Edition - Appendix 2, page 26) and prepare Review Package.
8. List any sights, odors or sounds that might come from your facility and cause public concern or inquir ies (e.g., smoke, large relief valves, odors below hazardous levels such as mercaptans or amines, etc.)
Prepared by: __
Reviewed by:
_____________________ ___________
Date
Plant Superintendent or Manager
Site Review Representative
____________________________ ________________________________
Additional Management Review (if required)
____________ __
(471-00099) Rtv 9/*93
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TABLE 2A PHYSICAL PROPERTY TABLE FOR CEI (SI UNITS)
Chemical
Molecular Weight
Boiling Point
C
Vapor Pressure
kPa
Liquid Density @25 C @ BP
kg/m3 kg/m3
Gas Density @25 C kg/m3
Ratio of Cp/Hy 1/C
Acrolein Acrylic acid Acrylonitrile Allyl chloride Ammonia Benzene Bromine Butadiene Carbon disulfide Carbon monoxide Carbon tetrachloride Chlorine Chloroacetyl chloride Chloroform Chloropicrin Chlorotrifiuoroethylene Crotonaldehyde Dimethylamine Epichlorohydrin Ethyl chloride Ethylene dichloride Ethylene oxide Hydrogen bromide Hydrogen chloride Hydrogen cyanide Hydrogen fluoride Hydrogen sulfide Methacrylonitrile Methanol Methylamine Methyl chloride Methyl mercaptan Phenol Phosgene Propylene oxide Styrene Sulfuryl fluoride Sulfur dioxide Sulfur trioxidc Toluene diisocyanale Trimethylamine Vinyl acetate Vinyl chloride Vinylidene chloride
56.06 72.06 53.06 76.53 17.03 78.11 159.81 54.09 76.14 29.01 153.82 70.91 112.94 119.38 164.38 116.47 70.09 45.08 92.52 64.51 98.96 44.05 80.91 36.46 27.03 20.01 34.08 67.09 32.04 31.06 50.49 48.11 94.11 98.92 58.08 104.15 102.06 64.06 80.06 174.16 59.11 86.09 62.50 96.94
52.5 141.4 77.2 44.8 -33.4 80.1 58.7
-4.4 46.3 -191.5 76.8 -34.0 106.0 61.7 112.0 -28.2 102.4 6.9 116.4 12.3 83.5 10.5 -66.7 -85.0 25.7 19.6 -60.3 90.3 64.5 -6.3 -24.1 6.0 181.9 7.5 34.2 145.2 -55.2 -10.0 44.4 252.9 2.9 72.8 -13.8 31.7
35.866 0.539 13.900
48.480 1002.800
12.690 28.375 281.090 48.120 2807.000 15.162 778.340
3.330 26.175
3.356 641.260
4.787 205.460
2.279 159.950
10.590 174.010 2358.800 4773.100 98.780 122.740 2020.800
9.477 16.950 348.440 576.540 201.820 0.055 189.900 71.670 0.841 1747.100 392.850 35.688 0.002 221.160 15.280 395.140 79.517
834.4 1046.0 801.0 931.4 602.3 869.8 3105.0 614.9 1256.0
1585.0 1399.0 1412.0 1480.0 1648.0 1290.0 848.9 649.7 1175.0 892.1 1246.0 866.8 1762.0 805.2 679.6 981.5 767.3 794.9 786.0 655.2 915.7 858.6 1070.0 1360.0 823.2 901.6 1318.0 1353.0 1904.0 1211.0 624.8 924.7 902.1 1203.0
684.0
651.0
1562.0
1472.0 671.0 910.0 887.0 2199.0 1188.0 679.0 991.0 929.0
694.0 1014.0 884.0 1403.0
1702.0 1444.0
653.0 972.0
21
7.79 4.01E-03 6.69 5.92E-03
25.07
3.87E-03
35.13
3.96
4.40
3.25 95.46 113.0
1.14 1.15 34.30
7.98E-03
4.89E-03
4.31E-03
3.65E-03 5.66E-03 9.81E-03 2.83E-03 4.24E-03 5.26E-03
4.66 13.12 4.12
7.96
3.92E-03 4.19E-03 3.87E-03
4.32E-03
97.38 10.86
9.57E-03 3.91E-03
5.68 6.15E-03
10.90
3.88E-03
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TABLE 2B PHYSICAL PROPERTY TABLE FOR CEI (US/BRIT UNITS)
Chemical
Molecular Weight
Boiling Point
F
Vapor Pressure
psia
Liquid Density
@ 77 F @BP
lb/ft3
lb/ft3
Gas Density @ 77 F lb/ft3
Ratio of Cp/Hv 1/F
Acrolein Acrylic acid Acrylonitrile Allyl chloride Ammonia Benzene Bromine Butadiene Carbon disulfide Carbon monoxide Carbon tetrachloride Chlorine Chloroacetyl chloride Chloroform Chloropicrin Ch lorotrifi uoroethy lene Crotonaldehydc Dimethylamine Epichlorohydrin Ethyl chloride Ethylene dichloridc Ethylene oxide Hydrogen bromide Hydrogen chloride Hydrogen cyanide Hydrogen fluoride Hydrogen sulfide Methacrylonitrile Methanol Methylamine Methyl chloride Methyl mercaptan Phenol Phosgene Propylene oxide Styrene Sulfuryl fluoride Sulfur dioxide Sulfur trioxide Toluene diisocyanatc Trimcthylamine Vinyl acetate Vinyl chloride Vinylidcne chloride
56.06 72.06 53.06 76.53 17.03 78.11 159.81 54.09 76.14 29.01 153.82 70.91 112.94
119.38 164.38 116.47 70.09 45.08 92.52 64.51 98.96 44.05 80.91 36.46 27.03 20.01 34.08 67.09 32.04 31.06 50.49 48.11 94.11 98.92 58.08 104.15 102.06 64.06 80.06 174.16 59.11 86.09 62.50 96.94
126.5 286.5 171.0 112.6 -28.0 176.2 137.7
24.0 115.3 -312.7 170.2 -29.2 222.8 143.1 233.5 -18.8 216.3 44.4 241.5 54.1 182.3 50.9 -88.1 -121.1 78.3 67.3 -76.5 194.6 148.1 20.6 -11.4 42.7 359.4 45.5 93.6 293.4 -67.4 14.0 111.9 487.2 37.2 163.0
7.1 89.1
5.201 0.078 2.016 7.030 145.408 1.840 4.114 40.759 6.978 407.022 2.199 112.861 0.483 3.795 0.487 92.984 0.694 29.792 0.330 23.193 1.536 25.232 342.032 692.111 14.323 17.798 293.021 1.374 2.458 50.525 83.600 29.264 0.008 27.536 10.392 0.122 253.334 56.964 5.175 0.000 32.069 2.216 57.296 11.530
52.1 65.3 50.0 58.1 37.6 54.3 193.8 38.4 78.4
99.0 87.3 88.2 92.4 102.9 80.5 53.0 40.6 73.4 55.7 77.8 54.1 110.0 50.3 42.4 61.3 47.9 49.6 49.1 40.9 57.2 53.6 66.8 84.9 51.4 56.3 82.3 84.5 118.9 75.6 39.0 57.7 56.3 75.1
42.7
40.6
97.5
91.9 41.9 56.8 55.4 137.3 74.2 42.4 61.9 58.0
43.3 63.3 55.2 87.6
106.3 90.1
40.8 60.7
0.49 2.23E-03
0.42 3.29E-03
1.57 2.15E-03
2.19 4.43E-03 0.25 2.72E-03 0.27 2.40E-03 0.20 2.03E-03 5.96 3.14E-03 7.05 5.45E-03 0.07 1.57E-03 0.07 2.36E-03 2.14 2.92E-03
0.29 2.18E-03 0.82 2.33E-03 0.26 2.15E-03 0.50 2.40E-03
6.08 5.32E-03 0.68 2.17E-03
0.35 3.41E-03 0.68 2.16E-03
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APPENDIX 1 CHEMICAL EXPOSURE INDEX REVIEW PROCESS
The following is a recommended procedure for the CEI review process.
When a plant or facility requires a further review, they should notify the site Loss Prevention contact and agree to an appropriate review schedule.
The review process should have three elements: 1. A Pre-Review Working Session 2. The Chemical Exposure Index Review Package 3. The Formal Review
Pre-Review Working Session
A one to two hour working session at least two weeks prior to the formal review is strongly recommended.
Purpose: This preliminary working session would let the actual review focus on what can and will be done to eliminate, reduce and/or mitigate potential releases.
This working session should have the following suggested agenda:
1. --- 2.
X 3.
--A* 5. 6.
Review each chemical scenario, lines of defense, mitigation measures and plans for improvement with review team. Discuss any past releases of acutely toxic material. Interview an operator in the plant. This interview should focus on the operator's awareness of the Chemical Exposure Index scenarios, use of emergency procedures and specific personal concerns related to the potential release of toxic chemicals. Conduct a drill of a hypothetical CEI release scenario. This drill should be conducted by plant personnel with CEI review team members present and should be designed to evaluate the response to an emergency situation involving a major release of one of the chemicals with the largest CEI. Inspect equipment and piping related to each scenario with the largest CEI. This inspection will consider the condition of pipe and equipment, location of valves and mitigating devices, etc. Review documentation pertaining to each CEI scenario. The following documents are suggested as a minimum: Past hypothetical exercise reports Area monitoring system records Maintenance checklists Operating Discipline including: loading/unloading procedures, shutdown for releases, mitiga
tion procedures, spill reporting procedure, etc. Completeness and quality will be used as a criterion for evaluating the documentation.
' Written reports of the interview, drilfi' site inspection and documentation review should be prepared.
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23
Chemical Exposure Review Package
At least one week before the review, the following information should be sent to each member of the review team:
1. 2.
3.
4. 5.
6. 7. X 8.
, 7- 9.
10.
Chemical Exposure Index Summary sheets for all chemicals and scenarios calculated. A simplified process flowsheet for areas with chemicals having the largest CEls. Include: a) all vessels including description, designation, (i.e., storage tank VT-100) size and
normal contents. b) associated piping including size, approximate length between equipment and any
automated block valves. A description of the scenario for each chemical that results in the largest CEIs. Include: a) description of any major changes made to this system since the last audit.
b) description of the lines of defense or actions to be taken if each scenario occurs. c) description of any mitigation methods, including size of spill areas or dike areas. An area map showing three circles that represent the hazard distance for ERPG-1, -2 and -3 concentrations. A plot plan showing the location of gas monitors, spill detectors or other devices used to detect releases. Also include the type of device used to detect the release and the detection level for each type of device. A completed containment and compliance checklist. A list of the recommendations made in the previous review and the status of each recommendation. A written report for the hypothetical exercise based on one of the Chemical Exposure Index scenarios. Include a description of the hypothetical release, a chronological list of actions taken and any recommendations for improvement. Include time it took to isolate the release. Note: If the hypothetical exercise is to be done during the review, please include the written description of the exercise scenario in the package. Written results of the employee interview. A written report of the in-plant inspection of each Chemical Exposure Index scenario source site.
If a pre-review working session was not held, these last two items must be provided during the formal review.
Formal Review
The following four activities should be done prior to formal presentation if a pre-review working session was not held:
1. Hypothetical exercise 2. Employee interview 3. Site inspection of each scenario site 4. Documentation review
Suggested Review Agenda
1. Summarize the status of the recommendations made in the previous review. 2. Discuss incidents that have occurred involving chemicals being reviewed.
Include Spill History - incident reports and plant follow-up reports. 3. Summarize the results of CEI calculations. Include hazard distances for ERPG-1, -2, -3.
DO A 04bBb3 CONFIDENT TAl
24
4. Review the release scenarios for the largest CEIs. Include plot plan showing hazard distances. Address the following items for each scenario: a. Have there been any major changes or additions to this system since the last audit/assessment? b. Discuss your lines of defense that would prevent this scenario release from occurring. c. Discuss the mitigation procedures for each scenario.
5. Discuss results of hypothetical exercise held prior to audit. 6. Discuss results of employee interview held prior to audit. 7. Review results of site inspection of each CEI scenario sources site. 8. Discuss results of documentation review. 9. Discuss your plant's CEI related concerns generated from the audit/assessment preparation. 10. Discuss your plans for improving your operations from a CEI standpoint. 11. Are there any other specific concerns which should be addressed but were not identified in the CEI
review? A written response including action to be taken, person assigned, anticipated completion date should be reported to the Line Management and the Review Chairman within 45 days and maintained with your Chemical Exposure Index calculations.
DO A 046864 CONFIDENT! Al 25
APPENDIX 2 CONTAINMENT AND MITIGATION CHECKLIST
This checklist is a Process Hazard Analysis tool for evaluating a facility's mitigation features to prevent, detect or control potential releases of acute toxic substances.
The management of any plant or facility requiring review should complete this checklist as part of the preparation for a Chemical Exposure Index review. Please check those that are complete, operational or in compliance with known company rules, guidelines or requirements. Any item that cannot be checked should be marked with the percentage of completion. Be prepared to discuss plans for any item not completed.
Complete (v^)______Risk Reducing Factors________________
__________
1. All pressure vessel and relief device systems properly registered and inspection up to date and documentation complete. (No expansion joints or glass devices.)
__________
2. All hoses inspected and tested regularly.
__________
3. All operational controls and systems designed and routinelytested to "fail-safe."
____ ___ _
4. Critical Instrument Program up to date (e.g., redundant high level and temperature alarms, shutdowns, etc.)
__________
5. Operating Discipline complete and up to date.
__________
6. Vapor Detectors properly placed and tested regularly.
__________
7. Appropriate engineering specifications properly applied (e.g., lethal service, welded fittings, etc.)
__________
8. Are relief vents on toxic containers designed to minimize atmospheric emissions? (per Environmental Protection Guidelines for Operations) How? (circle) Scrubber, Flare or_________________________________
__________
9. Failure analysis and nondestructive testing carried out where needed (e.g., X-ray, vibration analysis or monitoring, acoustical emission, piping flexibility - hot and cold).
__________
10. Physical barriers in place (for traffic, cranes, etc.)
---------------
11. Designed for excess pressure, if needed (e.g., pipelines in certain areas, tank cars, trucks, etc.).
__________
12. All personnel properly trained to understand hazards and emergency responses.
---------------
13. Emergency Procedures (relating to this exposure potential) in place and annual drill held.
---------------
14. Safety Rules and Safety Standards regularly reviewed and enforced.
__ _15. Loss Prevention Principles and Minimum Requirements appropriately applied.
____ ____
16. Technology Center Guidelines appropriately incorporated.
__17. Reactive Chemical Review complete and up to date.
---------------
18. Loss Prevention Audit complete and up to date.
DC> A 04
--------------__________
19. Technology Center Audit complete and up to date. 20. All new operations and modifications underwent safety pre-startup audit.
________
21. Management of Change procedures written and utilized.
Completed by: Reviewed by:
Date: 26
APPENDIX 3
EXAMPLE CEI CALCULATIONS
CHLORINE VAPOR RELEASE
The 3/4 inch vapor connection on a 1 ton chlorine cylinder stored at ambient temperature (30 C or 86 F) has broken.
Needed information:
Pressure inside the cylinder, P5 Absolute Pressure, Pa Molecular Weight, MW Storage Temperature, T Diameter of Hole, D
SI 788.1 kPa gauge
889.5 kPa 70.91 30 C 19 mm
US/Brit 114.3 psig 129.0 psia
70.91 86 F 0.75 in
Determine Airborne Quantity.
SI Units (Equation 1A)
AQ = 4.751 xlO-6 D2Pa MW (T+273)
AQ = 4.751 x 10-6 (19)2 (889.5) 70.91 (30+273)
AQ = 0.74 kg / sec
US/Brit Units (Equation IB)
AQ = 3.751 D2 Pa MW (T+459)
AQ = 3.751 (,75)2 (129.0) 70.91 (86+459)
AQ = 98.21b/min
Calculate the CEI. SI Units (Equation 10A)
US/Brit Units (Equation 10B)
where ERPG-2 = 9 mg/m3
where ERPG-2 = 3 PPM
ICEI = 655.1 AQ ERPG-2 I0.74 CEI = 655.1
9.0 CEI = 188
ICEI = 281.8
AQ
(ERPG-2)(MW)
I 98.2
CEI = 281.8 (3.0X70.91)
CEI = 191
Differences in CEI values result from rounding the ERPG values when converting between PPM and mg/m3.
DO A C.ONFT OF NT 1 A' 27
Calculate Hazard Distances.
SI Units (Equation 11A) For ERPG-2 = 9 mg/m3
US/Brit Units (Equation 11B) For ERPG-2 = 3 PPM
HD = 6551 AQ ERPG
AQ HD = 9243
ERPG (MW)
10.74
VHD = 6551 9 HD = 1,878 meters For ERPG-1 = 3 mg/m3 HD = 6551 HD = 3,254 meters For ERPG-3 = 58 mg/m3
i 98.2
HD = 9243 '3(70.91)
HD = 6,280 feet For ERPG-1 = 1 PPM
98.2 HD = 9243.
1(70.91) HD = 10,878 feet For ERPG-3 = 20 PPM
HD = 6551 V 58
HD = 740 meters
HD = 9243 ) 98n2 V 20(70.91)
HD = 2,432 feet
Differences in HD values result from rounding the ERPG values when converting between PPM and mgAn3.
00 A 046867 f ONFTDFNTT AL
28
AMMONIA LIQUID RELEASE
Ammonia is stored in a 12 ft diameter by 72 ft long horizontal vessel under its own vapor pressure at ambient temperature (30 C or 86 F). The largest liquid line out of the vessel is 2 inch diameter (50.8 mm).
Needed information:
Pressure inside vessel, Pg Temperature inside vessel, T Normal boiling point Liquid density in vessel, pi Ratio Cp/Hv Height of liquid in tank, Ah Diameter of hole, D Molecular weight, MW
SI 1064 kPa gauge
30 C -33.4 C 594.5 kg/m 3 4.01 E-03 3.66 m 50.8 mm
17.03
US/Brit 154.5 psig
86 F -28 F 37.1 lb/ft3
2.23 E-03 12ft 2.0 in 17.03
Estimate liquid released.
SI Units (Equation 2A)
US/Brit Units (Equation 2B)
1000Pg
L = 9.44xlO~7D2 p,
+ 9.8 Ah
Pi
|244Pg
L = 2.234Dzp,.
+ Ah
Pi
L - 9.44 x 10-7(50.8)2(594.5)J10,,a064) + 9.8 (3.66) 594.5
L = 61.9 kg/sec
L = 2.234(2.0)2(37.1) J144(154-5) +12.0 37.1
L = 8,200 lb / min
Estimate flash fraction. SI Units (Equation 4A)
USIBrit Units (Equation 4B)
Fv=^E-(Ts-Tb) Hv
FV=^(TS-Tb) Hv
Fv= 0.00401(30-(-33.4))
Fv = 0.00223(86--(-28))
Fv =0.254
Fv = 0.254
Since Fv > 0.2 AQ = L AQ = 61.9kg/scc
Since Fv > 0.2 AQ = L AQ = 8,200 lb/min
29
Calculate CEI,
SI Units (Equation 10A)
where ERPG-2 = 139 mg/m3
JCEI = 655.1 --Q \ ERPG-2
m , /61.9
VCEI -655.1.1 139 CEI = 437
Calculate the Hazard Distances.
SI Units (Equation 11A) For ERPG-2 = 139 mg/m3
--HD = 6551 j A VERPG
HD = 6551 J--
V 139 HD = 4,372 meters
=ForERPG-1 17 mg/m3 = J--VHD 6551
17
=HD 12,500 meters =For ERPG-3 696 mg/m3
= I--HD 6551 V 696
=HD 1,953 meters
US/Brit Units (Equation I OB) where ERPG-2 = 200 PPM CEI - 281.8^(ERpa2)(MW)
JCE. = 281.8 8200 \ 200(17.03) CEI =437
US/Brit Units (Equation 1 IB) For ERPG-2 = 200 PPM
HD = -9243, - - --- - y ERPG(MW)
\HD = 9243 ------ 200(17.03) HD = 14,342 feet
ForERPG-1 = 25 PPM
= VHD 9243 j 8200 25(17.03)
=HD 40,564 feet
For ERPG-3 = 1000 PPM
= - - --- -HD 9243 y1 1000(17.03) =HD 6,414 feet
00 A 0A6869 C.ONf7 T OFNl ' A'.
30
STYRENE LIQUID RELEASE
Styrene is stored in a 40 ft x 40 ft API tank at ambient temperature (25 C or 77 F). The tank has a closed vent system but is essentially at ambient pressure. The outlet is a 6-inch Schedule 40 nozzle.
Needed information:
Pressure inside the tank, Pg Temperature inside the tank, T Normal boiling point Vapor pressure, ambient temperature Liquid density, pi Height of liquid. Ah Molecular weight, MW
SI 0.0 kPa 25 C 145.2 C 0.841 kPa 901.6 kg/m3 12.2 m 104.15
US/Brit 0.0 psig
77 F 293.4 F 0.122 psi 56.3 lb/ft3
40.0 ft . 104.15
Scenario selection -- For greater than 4-inch diameter, use 20% of the cross sectional area (CSA).
For 6-inch Schedule 40, CSA = 28.89 in2
0.20(28.89) = 5.78 in2
D = ^--A =^--5.78 = 2.71 in or 68.9mm
Estimate liquid released. SI Units (Equation 2A)
7 7 |1000P,, L = 9.44xl0"7D2pJ---------L + 9.8 Ah
V Pi L = 9.44 x 10~?(68.9)2(901.6) .100Q(0) + 9.8 (12.2)
V 901.6 L = 44.2 kg / sec Compare operating temperature to normal boiling point:
25 C< 145 C Therefore, Flash Fraction = 0 Estimate pool size. SI Units (Equation 3A) WT=900(L) WT = 39,800 kg = Wp
31
US/Brit Units (Equation 2B) 7 (144 P,,
L = 2.234 D2 p, J------- &. + Ah V Pi
L = 2.234(2.7 l)2t56.3)^^^- + 40.0
L = 5,842 lb/min
77 F< 293.4 F
US/Brit Units (Equation 3B) WT = 15(L) WT =87,600 lb = Wp DO A 046870 00NFTDFNTTA1
SI Units (Equation 7A) wp
AD = 100-- P Pi
Ap =!00 39800 p 901.6
Ap =4,410m2
Assume no dike. SI Units (Equation 8A)
AQp-9.0*10^(Ap095)<"W>1''' p x p ' T+273
Characteristic pool temperature equals ambient AOp=9.0X,0-(4410-)1M,'5(784,) p ' ' 25+273 AQp =0.767 kg/sec
SI Units (Equation 9A) AQ = AQf + AQp
AQ = 0 + 0.767 AQ = 0.729 kg / see Calculate CEI. SI Units (Equation 10A) where ERPG-2 = 1065 mg/m3
CEI = 655.1 / AQ \ ERPG-2
VCEI = 655.1 1065 CEI = 18
US/Brit Units (Equation 7B) Ad =30.5--wp2P) . 87600 A,, =30.5-------- p 56.3 Ap =47,460 ft2
US/Brit Units (Equation 8B) AQp = 0..54(A-)m
AQp .0,54(47460*)Mp)
AQp = 101 Ib/min USIBrit Units (Equation 9B)
AQ = AQf + AQp AQ = 0 +101 AQ = 101 lb/min
US/Brit Units (Equation 10B) where ERPG-2 = 250 PPM CEI = 281.8 --------- ----------\ (ERPG-2)(MW) CEI = 281.8 ------ -------V 250(104.15) CEI = 18
DO A 046871 C0NFTDFNTTA1
32
Calculate the Hazard Distances.
SI Units (Equation 11A) For ERPG-2 = 1065 mg/m3
HD=655,iife
VHD = 655 1065 HD = 176 meters
For ERPG-1 = 213mg/m3 HD = 655.5TM
V 213
HD = 393 meters
For ERPG-3 = 4259 mg/m3 HD = 6551 IQTM! V 4259 HD = 87.9 meters
USfBrit Units (Equation 11B) For ERPG-2 = 250 PPM
HD 9243^ERPG(MW)
HD=9243iSn
HD = 576 feet For ERPG-1 = 50 PPM
HD=92436sii
HD = 1,287 feet For ERPG-3 = 1000 PPM
HD = 9243jl000(104.15)
HD = 288 feet
DO A 04687 C.ONFTDFNTTA
33
CHLORINE LIQUID RELEASE
Chlorine is stored in a sphere at 5 C (41 F). A 2-inch nozzle fails on the bottom of the vessel allowing liquid to escape.
Needed information:
Pressure inside the cylinder, Pg Molecular weight, MW Storage temperature, T liquid density, pi Height of liquid in the sphere, Ah Diameter of hole, D Capacity of sphere
SI 332 kPa gauge
70.91 5 C 1458 kg/m3
6m 50.8 mm 1.134 x 106 kg
US/Brits 48.2 psig
70.91 41 F 91.01 lb/ft2
19.7 ft 2 in
2.5 x 106 ib
Estimate liquid released.
SI Units (Equation 2A)
7 7 [TooopI
L = 9.44 x 10~7D2 Pj J---------fi- + 9.8 Ah
Y Pi
L = 9.44 x 10-7(50.8)2(1458)+ 9.8 (6) V 1458
L = 60.1 kg/sec
US/Brit Units (Equation 2B)
2 l144P " L = 2.234DZ pi J------- + Ah
V Pi
L = 2.234(2)2 91.01 P44-48--+ 19.7 V 91.01
L = 7,967 lb/min
Determine the total liquid released.
For 15 minutes (900 seconds), the total liquid leaving the tank is:
WT = 900(60.1) = 54,090 kg
WT = 15(7,967) a 119,505 lb
The capacity of the tank when full is 1.134 x 106 kg. Since Ly = 54090 kg is less than the capacity of the tank.
WT= 54,090 kg
WT =119,505 lb
Calculate the flash fraction.
Needed information:
Normal boiling point temperature = -34 C
Normal boiling point temperature = -29.2 F
Heat of vaporization = 275,030 J/kg
Heat capacity of liquid (at average temperature) = 943.8 J/kg/C
oo a 04A873 CONFTnFNTTAl
34
A technically correct solution for evaluating the flash fraction requires the heat capacity (Cp) to be evaluated at the average temperature (storage and boiling point) and the heat of vaporization at the boiling point. For example:
Cp (@ -15 C or 5 F) = 943.8 J/kg/C = 0.2254 BTU/lb/F
and HV(BP) = 285,457 J/kg = 122.72 BTU/lb
SI Units (Equation 4A)
US/Brit Units (Equation 4B)
Fv=^L(Ts-Tb) Hv
Fv =~"(TS-Tb) Hv
Fv = 9418 (5-(-34.0)) 285,457
Fv =0.129
0.2254(41 (-29.2)) v 122.72
Fv =0.129
Calculate vapor source strength from the flash.
AQf = 5(FV)(L) = 5(0.129)(60.1) = 38.8 kg /sec
(SI)
AQf = 5 (Fv) (L) = 5 (0.129X7967) = 5,139 lb / min
(US/Brit)
Calculate the total liquid entering the pool. Wp = WT (1--5FV) = 54,090(1 - (5)(0.129)) = 19,202 kg
(SI)
Wp = WT(1-5FV) = 119,505(1 - (5) (0.129)) = 42,424 lb
(US/Brits)
Liquid density of chlorine at its boiling point = 1,562 kg/m3
SI Units (Equation 7A)
US/Brit Units (Equation 7B)
Wp A,, = 100--^
Pi
Ap =i0019202 p 1562
W Ap =30.5--E-
Pi
. 42424 A0 =30.5---------
p 97.5
Ap = 1,229 m2
Ap =13,271 ft2
DU A 046874 fONFTDFNTT A!
35
Calculate the vapor flow rate from the pool.
Since chlorine is boiling in the pool, Pv = 101.3 kPa = 14.70 psi Molecular weight of chlorine = 70.91
SI Units (Equation 8A)
US/Brit Units (Equation 8B)
aqp=9.o*io^(ap0.)<M^
AQp = 0..54(Ap)<^
AQp = 9.0 x 10^ (l 229-95) 7-1 (1 --3) Vp v ' (-34.0)+273
AQp =23.3 kg/sec
AQp=0.154(1327.'>")70-91<,4-70o)
pv
1 (-29.2)+459
AQp =3,083 lb/min
Calculate source strength of release. SI Units (Equation 9A)
AQ = AQf + AQp
US!Bril Units (Equation 9B) AQ = AQf + AQp
AQ = 38.8+ 23.3
AQ = 5139+ 3083
AQ = 62.1kg/sec
AQ = 8,222 lb /min
Compare to the liquid release: 62.1 kg/sec is greater than 60.1 kg/sec and 8,222 Ib/min is greater than 7,967 lb/min:
AQ = 60.1 kg / sec
AQ = 7,967 lb/min
Calculate the CEI. SI Units (Equation 10A)
where ERPG-2 = 9 mg/m3
US/Brit Units (Equation 10B) where ERPG-2 = 3 PPM
CEI = 655.1 /- A-- \ ERPG-2
CEI = 281.8,/--------- ----------\(ERPG-2)(MW)
CEI = 655.1^TM-
CEI = 1,963 This is greater than 1000; thus
CEI = 1.000
CEI = 281.8 / 7967... \ 3(70.91)
CEI = 1,725
This is greater than 1000; thus CEI = 1,000
DO A 046875 (': 0 N T 7 D F N T T A l
36
Calculate the Hazard Distances.
SI Units (Equation 11A) For ERPG-2 = 9 mg/m3
HD = 6551J AQ V ERPG
HD = 6551^---
HD = 16,929 meters HD is greater than 10,000 meters, thus HD = 10,000 meters ForERPG-1 = 3 mg/m3 HD = 6551^~i
HD = 29,321 meters HD is greater than 10,000 meters, thus HD = 10,000 meters ForERPG-3 = 58 mg/m3
HD = 6551 V 58
HD = 6,668 meters
US/Brit Units (Equation 11B) For ERPG-2 = 3 PPM
hd=9243i|erpg?mw,
HD = 9243 1 7967-- \ 3(70.91)
HD = 56,525 feet HD is greater than 32,800 feet, thus HD = 32,800 feet For ERPG-1 = 1 PPM HD = 9243 J 7967
V 1(70.91) HD = 97,973 feet HD is greater than 32,800 feet, thus HD = 32,800 feet ForERPG-3 = 20 PPM HD = 9243 1 7967
\ 20(70.91) HD = 21,907 feet
DO A 046876 C.ONf T DFNT T A!
37
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CORPORATE SAFETY, LOSS PREVENTION, AND SECURITY PUBLICATIONS
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June 1989
Guidelines Guidelines for A Contractor Safety, Loss Prev,, & Security Program, 2nd Edition Guidelines for Safety, Loss Prevention and Security Audits, 3rd Edition Guidelines for Office Safety, Loss Prevention and Security, 2nd Edition Guidelines for Emergency Planning Guidelines for A Motor Vehicle Accident Prevention Program, 3rd Edition Guidelines for Safety on Non-Dow Premises (Reprinted Oct. 1988) Guidelines for S/LP/S Reporting, 5th Edition Guidelines for Root Cause Incident Investigation Fire and Explosion Index Hazard Classification Guide, 6th Edition Guidelines for Public Warehouse Rating & Risk Analysis Distribution Emergency Response Process2 Air Travel - Policy and Guidelines (Reprinted Jan. 1989) Guidelines for Safe Sample Shipping, 3rd Edition Guidelines for A Reactive Chemicals Program, 2nd Edition Guidelines for Handling Dow Proprietary Information, 2nd Edition Guidelines for Personal Safety & Security at Hotels/Motels
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