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QUANTITATIVE RISK ASSESSMENT REPORT FOR
LNG UNLOADING, STORAGE & RE-GASIFICATION PLANT AT
KRISHNAPATNAM PORT, ANDHRA PRADESH
Submitted to:
LNG BHARAT PRIVATE LIMITED
Andhra Pradesh
Submitted by:
Vimta Labs Ltd.
142 IDA, Phase-II, Cherlapally Hyderabad–500 051, Telangana State
[email protected], www.vimta.com (NABET & QCI Accredited, NABL Accredited and ISO 17025 Certified Laboratory,
Recognized by MoEF, New Delhi)
October 2015
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 2
1.0 INTRODUCTION
LNG Bharat Pvt. Ltd. (LNGBL), is a subsidiary company of KEI-RSOS Petroleum &
Energy (KRPEL) based in Rajahmundry, East Godavari, Andhra Pradesh. LNGBL
plans to set up India’s first floating storage LNG import terminal at
Krishnapatnam Port near Nellore in AP. The on-shore facilities will include a LNG
storage tanks, pumps, trailer filling stations, re-gasification system to supply
natural gas to pipeline. The facility will have a capacity of 5.0 MMTPA of LNG.
The LNGBL project is implemented by participation of INOX India limited, a
globally acclaimed company offering comprehensive solutions in cryogenic
storage, vaporization and distribution engineering. INOX India recently picked up
majority stake in Cryogenic Vessel Alternatives (CVA), a world leader in large
cryogenic transport tanks, oil and gas field pumping units, and mobile LIN storage
units. With this acquisition, INOX India has become the second largest player in
this business across the world.
The environmental impact assessment studies for the LNGBL project are being
carried out by Vimta Labs Limited, Hyderabad.
As per the Terms of Reference (ToR) issued by Expert Appraisal Committee,
Ministry of Environment & Forests, Government of India for this project, a tisk
assessment study is to be carried out in order to identify the hazards in the
facility and ensue that necessary protective measures are provided.
Accordingly, this quantitative risk assessment (QRA) study for the proposed LNG
import, storage and re-gasification facilities of LNG Bharatwas carried out by
QCI/NABET accredited Functional Area Expert (Risk & Hazard) of Vimta Labs in
consultation with team members from INOXCVA and LNGBL.
2.0 FACILITY DESCRIPTION
The system consists of LNG unloading, storage, transfer, vaporization & supply
of natural gas to users.
A floating storage unit (FSU) shall be parked on the jetty in KPT port which
shall store approx. 1,30,000 m3 of LNG. It shall deliver LNG at about 600
m3/hr. and at 5 barg at inlet of flexible hose connecting the FSU to jetty. The
FSU shall also deliver 2,00,000 Nm3/day of boil of gas at 1 barg and 5 deg. C
temperature at inlet of flexible hose connecting the FSU to jetty. The boil off
and LNG shall be brought to shore for storage and use.
Unloading arms shall be used to transfer LNG from FSU to ground valve unit.
The valve unit is connected by insulated pipe line to the land based storage
facility which is about 2500 metres away. The main LNG pipeline shall be 36”
NB size and shall be cold insulated. The BOG pipeline shall be 12”size. Other
pipelines such as LNG recirculation, nitrogen gas and fire water shall also be
configured.
The storage facility at KPT shall be configured in two phases. Phase 1 shall
consist of three horizontal vacuum insulated cryogenic storage tanks with total
gross capacity of 1050 m3. LNG unloaded from FSU shall be filled in these
storage tanks. When the FSU pumps are not operating, the long LNG pipeline
needs to be kept in cold condition. To achieve this, two separate pumps of
approx. 36 m3/hr each, located near the storage tank shall be provided. The
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 3
pumps shall circulate LNG in the long pipeline to keep in under cold condition. A
separate 3” or 4” recirculation line is provided for this purpose. The storage
facility has provision of 8 tanker filling bays. The LNG shall be filled from
storage tanks into trailers parked in these bays by pressure transfer. Provision
exists to fill trailers in case of emergency by using the re-circulation pumps
also. Each bay has a weigh bridge to measure and control the quantity of LNG
filled.
The FSU generates significant amount of BOG approx. 2,00,000 Nm3/day (8350
Nm3/hr). A separate BOG compressor shall be configured in the storage area to
further compress this BOG and deliver into user gas pipeline at 10 bar (g) and
2,00,000 Nm3/day flow rate. All the 3 gas lines meet in a common header from
where the natural gas shall be delivered to the 24” pipeline through metering
system. During the un-loading of ship BOG generated may reduce. To
compensate the same two additional pumps (max. 8000 Nm3/hr) are provided
which shall pump liquid from storage tanks (350 m3 X 3 Nos.) and add to the
gas flow in the main line. Ambient vaporizers shall be used to gasify this make-
up stream of LNG. The gas shall be supplied into 24” main gas line grid.
The BOG from semi-trailers & storage tanks shall be collected and feed to BOG
compressor located in storage area.
Phase 1A shall consist of a full containment type tank of 30,000 m3 to receive
and storage LNG. Submerged pumps inside the tank of suitable capacity shall
be provided to pump liquid out and required pressure 15 barg and flow rate
20,00,000 Nm3/day. Suitable re-gas arrangement shall be provided consisting
of ambient air vaporizers. Regulation and metering scheme shall be provided.
The gas shall be supplied into 24” main gas line grid.
Phase 2 shall consist of additional three full containment type tanks of 30,000
m3 capacity to receive and storage LNG. Submerged pumps inside the tank of
suitable capacity shall be provided to pump liquid out and required pressure 15
barg. Booster pumps will increase the pressure to about 70 barg. Suitable re-
gas arrangement shall be provided consisting of ambient air vaporizers.
Regulation and metering scheme shall be provided. Each of the three sets of
pumps, vaporizers and metering system will have capacity to supply 4
MMSCMD of gas at 65 barg pressure to the main gas line grid.
The facility shall also have liquid nitrogen (LN 2) storage system (approx. 10
kL) for supply of gaseous nitrogen (GN 2) as utility to ensure safety in
operation and maintenance of the LNG plant.
Following is a list of the equipment’s which form a part of the LNG Plant:
Phase – 1
1. Three horizontal vacuum insulated cryogenic storage tanks each with 350
m3 gross capacity (Model HL 35007 E)
2. Two Cryogenic liquid transfer pumps for recirculation and (or) trailer filling
3. Two Cryogenic liquid transfer pumps for grid line feed
4. Ambient air vaporizer for BOG generated from the storage tanks (AVC 3000
HP, 1 nos.)
5. Ambient air vaporizers for gas make-up to the grid line (AVC 2400 HP, there
shall be two banks of 4 vaporizers (one bank shall be working & another
stand-by)
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 4
6. Valve skid for filling of storage tanks and trailers
7. BOG compressor for BOG generated from storage tanks & FSU, trailers
8. Pressure regulation & metering (3 no & 1 no. respectively)
9. Valve skid for trailer filling & BOG
10. Skid for trailer depressurization
11. Drain vessel
12. Suction accumulator if required.
13. Valve skid on the jetty
14. Liquid nitrogen storage tank, ambient air vaporizer, pressure regulator for
GN2 supply
Phase – 1A
1. Flat bottom tank of full containment type, capacity 30000 m3 – 1 No.
2. Vaporizing skids (Capacity 2000000 Nm3/day, 83000 Nm3/Hr)
3. Pressure regulation & metering skid
4. BOG compressor for BOG generated from FBT
Phase – 2
1. Flat bottom tank of full containment type, capacity 30000 m3 – 3 Nos.
2. Tank pumps and high pressure (HP) pumps
3. Vaporizing skids (Capacity 4 MMSCMD)
4. Pressure regulation & metering skid
5. BOG compressor for BOG generated from FBT
Layout diagram of the proposed LNG Terminal at Krishnapatnam Port is shown
in Figure-1.
The arrangement for LNG supply from FSU is shown in Figure-2.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 5
FIGURE-1
LAYOUT OF LNG BHARAT TERMINAL AT KRISHNAPATNAM PORT
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 6
FIGURE-2
ARRANGEMENT FOR LNG SUPPLY FROM FSU
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 7
3.0 SCOPE, OBJECTIVE & METHODOLOGY
3.1. Scope
The scope of this QRA study covers the LNG storage and re-gasification plant of
LNG Bharat Private Limited including facilities under Phase 1, Phase 1A and
Phase-2 with 5 MMTPA capacity located in Krishnapatnam Port area.
3.2 Objective
The objectives of this study are as follows:
Identify major accident scenarios associated with the storage and handling of
hydrocarbons in the LNG terminal
Carry out consequence analysis for the significant accident scenarios
Carry out quantitative risk analysis,
Compare the risk values with specified risk tolerance criteria and
Identify measures for risk reduction wherever warranted.
3.3 Methodology
Risk arises from hazards. Risk is defined as the product of severity of
consequence and likelihood of occurrence. Risk may be to people, environment,
assets or business reputation. This study is specifically concerned with risk of
serious injury or fatality to people due to process hazards related to storage and
handling of LNG.
The following steps are involved in Quantitative Risk Assessment:
Study of the plant facilities and systems.
Identification of the hazards.
Enumeration of the failure incidents.
Estimation of the consequences for the selected failure incidents.
Risk analysis taking into account the failure frequency, extent of
consequences and exposure of people to the hazards.
Risk assessment to compare the calculated risk level with risk tolerability
criteria and review of the risk management system to ensure that the risk is
“As Low As Reasonably Practicable” (ALARP)
The process of QRA is shown in the following block diagram in Figure 3.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 8
FIGURE-3
FLOW DIAGRAM OF QUANTITATIVE RISK ASSESSMENT (QRA)
3.3.1 Consequence Analysis
Consequence analysis for the selected failure scenarios is carried out using DNV
Phast software which provides results for selected failure scenarios such as the
following:
Dispersion of toxic clouds to defined concentrations
Heat radiation intensity due to pool fire and jet fire
Explosion overpressure
Phast stands for ‘Process Hazard Analysis Software Tool’. It uses Unified
Dispersion Modeling (UDM) to calculate the results of the release of material into
the atmosphere.
Phast has extensive material database and provides for definition of mixtures.
Phast software is well validated and extensively used internationally for
consequence and risk analysis.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 9
3.3.2 Quantitative Risk Analysis (QRA)
The Quantitative Risk Analysis (QRA) is carried out using the renowned DNV
software Phast Risk Micro (previously known as SAFETI Micro) version 6.6.
The following input data are required for the risk calculation:
Process data for release scenarios (material, inventory, pressure,
temperature, type of release, leak size, location, etc.)
Estimated frequency of each failure case
Distribution of wind speed and direction (wind rose data).
Distribution of personnel/ population in the plant/ adjoining area during
the day and night time.
Ignition sources
Failure frequencies are estimated using generic failure databases published by
organizations such as International Association of Oil & Gas Producers (OGP).
RISK ANALYSIS
The results of Quantitative Risk Analysis are commonly represented by the
following parameters:
Individual Risk
Societal Risk
Individual risk is the risk that an individual remaining at a particular spot would
face from the plant facility. The calculation of individual risk at a geographical
location in and around a plant assumes that the contributions of all incident
outcome cases are additive. Thus, the total individual risk at each point is equal
to the sum of the individual risks, at that point, of all incident outcome cases
associated with the plant.
The individual risk value is a frequency of fatality, usually chances per million per
year, and it is displayed as a two-dimensional plot over a locality plan as contours
of equal risk in the form of iso-risk contours as shown in the following Figure-4.
FIGURE-4
ISO-RISK CONTOURS ON SITE PLAN (TYPICAL)
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 10
3.3.3 Risk Tolerability Criteria
For the purpose of effective risk assessment, it is necessary to have established
criteria for tolerable risk. The risk tolerability criteria defined by UK Health &
Safety Executive (UK-HSE) are normally used for risk assessment in the absence
of specific guidelines by Indian authorities.
UK-HSE has, in the publications “Reducing Risk and Protecting People” and
“Guidance on ALARP decisions in control of major accident hazards (COMAH)”
enunciated the tolerability criteria for individual risk .
Indian Standard IS 15656:2006 provides guidelines for hazard identification and
risk analysis.
The risk tolerability criteria are as follows-
An individual risk of death of one in a million (1 x 10-6) per annum for
both workers and the public corresponds to a very low level of risk and should
be used as a guideline for the boundary between the broadly acceptable and
tolerable regions.
An individual risk of death of one in a thousand (1 x 10-3) per annum
should on its own represent the dividing line between what could be just
tolerable for any substantial category of workers for any large part of a
working life, and what is unacceptable.
For members of the public who have a risk imposed on them ‘in the wider
interest of society’ this limit is judged to be an order of magnitude lower, at 1
in 10,000 (1 x 10-4) per annum.
The upper limit of tolerable risk to public, 1 x 10-4 per year, is in the range of risk
due to transport accidents. The upper limit of broadly acceptable risk, 1 x 10-6 per
year, is in the range of risk due to natural hazard such as lightning. The
tolerability criteria for individual risk are shown in Figure 5.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 11
Intolerable Risk
Risk Tolerable If ALARP
Broadly Acceptable
10-3 per year
10-6 per year
10-4 per year
10-6 per year
Risk to Personnel Risk to Public
FIGURE-5
INDIVIDUAL RISK CRITERIA
3.3.4 Societal Risk (or Group Risk) Criteria
Societal Risk parameter considers the number of people who might be affected by
hazardous incidents. Societal risk is represented as an F-N (frequency-number)
curve, which is a logarithmic plot of cumulative frequency (F) at which events
with N or more fatalities may occur, against N.
Societal risk criteria indicate reduced tolerance to events involving multiple
fatalities. For example a hazard may have an acceptable level of risk for one
fatality, but may be at an unacceptable level for 10 fatalities. The tolerability
criteria for societal risk as defined by UK-HSE are shown in the following Figure-
6.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 12
FIGURE-6
SOCIETAL RISK CRITERIA
3.3.5 Risk Assessment
Based on the results of QRA, necessary measures to reduce the risk to ALARP are
to be formulated. For this purpose the information regarding top risk contributors
provided by Phast Risk software is useful.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 13
4.0 QUANTITATIVE RISK ANALYSIS
4.1 Input Data for Risk Analysis
The details of storage tanks are provided in Table-1.
TABLE-1
DETAILS OF STORAGE TANKS
S.no. Description Nos. Pressure Temp. (c) Type Capacity (each)
Phase-1
1. LNG Tanks
(T101/102/103)
3 3.2 barg Horizontal;
Vacuum insulated
350 M3
Phase-1A
2. LNG Tank (ST1001) 1 138 mbarg (-)162 Full containment 30,000 MT
Phase-2
4. LNG Tanks (ST1001A; ST1001B; ST1001C)
3 138 mbarg (-)162 Full containment 30,000 MT
4.2 Weather Data
The weather data for the site required for dispersion analysis and QRA are
provided in Table-2.
TABLE-2
CLIMATOLOGICAL DATA
Month Temperature (0C) Rainfall (mm)
Max. Min. Monthly Total
January 28.2 20.4 4
February 30.6 20.8 0
March 39.6 22.8 0
April 38.4 24.2 0
May 41.7 24.7 18
June 40.0 22.0 174
July 38.0 22.0 38
August 37.0 23.0 160
September 39.7 25.2 192
October 35.4 24.2 257
November 34.8 22.6 158
December 28.7 21.5 159
Wind rose diagrams for the site showing the distribution of wind direction and
wind speed during a year are shown in the Figure-7.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 14
FIGURE -7
WIND ROSE DIAGRAM
Annual
8.30 hr
Annual
17.30 hr
SPEED CALM
1151
SCALE
19 >19 Km/hr
5%
4.0%
SW
10.5% N
W
5.7
% S
9.8% W C-16.2%
SE 7.0%
E 1.1%
NE 2.
6%
N 1
.4%
4.4
% N
NW
NNE 1
.1%
3.1
% S
SW
SSE 9
.3%
9.9% WSW
11.0% WNW
ESE 1.7%
ENE 1.2%
2.0%
SW
2.0% N
W
0.4
% S
7.1% W C-3.9%
SE 12.3%
E 11.0%
NE 13
.3%
N 0
.5%
1.0
% N
NW
NNE 3
.7%
0.5
% S
SW
SSE 2
.9%
5.1% WSW
4.6% WNW
ESE 17.5%
ENE 12.2%
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 15
4.3 Hazards in LNG Installation
LNG is liquefies natural gas. It is mostly methane with some ethane and propane
depending on the source.
The properties of LNG significant for this study are as follows.
Molecular weight 16-17 (approx.)
Normal boiling point (-) 162 C
Liquid density at boiling point 430 kg/m3
Vapour density at 20 C 0.7 kg/m3
Lower flammable limit (LFL) 5 % (vol)
Upper flammable limit (UFL) 15 % (vol)
Reactivity classification for explosion Low
Accidental release of LNG can result in the following hazards.
Pool fire due to burning of liquid LNG causing burn injury and structural
damage by thermal radiation
Jet fire due to burning of gas leaking from pressurized equipment or piping
Flash fire due to ignition of flammable gas cloud causing burn injury
Vapour cloud explosion due to ignition of large flammable gas cloud under
conditions of confinement or congestion
Explosion effect due to rapid phase transformation (RPT) by evaporation of
large quantity of LNG released into water
Roll over phenomenon in storage tank due to sudden vaporization of large
quantity of LNG under abnormal conditions
Asphyxiation hazard due to dispersion of large quantity of gas reducing
oxygen concentration in the vicinity
Cold burns due to contact with cryogenic liquid
Pool Fire, Jet Fire & Flash Fire
The main hazard of LNG spill is fire and primary focus is on pool fire caused by
ignition of vapour formed on a pool of liquid formed by the spill. LNG being mainly
methane, burns with a luminous non-smoky flame and the pool fire has high
radiation intensity than heavier hydrocarbons. A large LNG pool fire is shown
below. (Ref: LNG Risk Based Safety – Modeling and Consequence Analysis by
Woodward & Pitblado).
Jet fire is caused by release by leak from pressurized vessel or piping, such as
natural gas system after vaporizer. The heat radiation from jet fire is localized
and likely to cause damage of structures and equipment if prolonged.
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 16
When LNG spills on water or land, gas evaporating from the pool will mix with air
and form a vapour cloud which will then be driven by the wind. If any point of the
vapour cloud with dimensions defined to flammable concentrations (above lower
flammable limit) reaches an ignition source and ignites, there will be a flash fire.
The flash fire will be transient, with exposure lasting only for fraction of a second.
It will cause serious burn injury to people only inside the fire zone. The flash fire
will quickly burn back to the source and, in this case, result in a pool fire.
Vapour Cloud Explosion
Ignition of the vapour cloud having large quantity of fuel gas mixed with air to
flammable concentration (above LFL) may also result in vapour cloud explosion
(VCE) under conditions of partial confinement or congestion. A pressure wave is
formed by the flame front and the resultant overpressure may cause damage to
people and structures. The extent of explosion overpressure depends on the
flame speed. Natural gas has low reactivity of explosion. Therefore, vapour cloud
explosion is not likely in case of LNG release in open area.
Rapid Phase Transformation (RPT)
RPT explosion is a physical explosion due to sudden boiling from liquid to vapour
that occurs when LNG is spilled into water such that LNG penetrates into and
mixes well with water. No injuries have occurred from RPT of LNG but equipment
damage may occur.
Roll Over in LNG Tank
Liquid in LNG tank kept stagnant for long period can stratify. Liquid density in
upper layer will increase over time due to methane boiling off thus increasing the
percentage of heavier components. When at some point the layers invert, the
lower layer will rise to the surface and a fraction of it immediately flash. Since
one volume of liquid will expand to 600 volumes of vapour, there will be sudden
increase in tank pressure that may exceed relief capacity. This phenomenon is
known as Roll Over. It is a hazard to operating personnel. Preventive measures
for roll over include provision of multiple temperature indicators to monitor
temperatures in different zones of the tank and recirculation of tank contents to
avoid stagnation.
Asphyxiation
When vapour from leaking LNG mix with air, oxygen concentration in air
(normally 21 %) will be reduced. Atmosphere with less than 19.5% oxygen is
designated as oxygen deficient. Breathing air with oxygen concentration below
15% will impair behaviour, below 10% will cause nausea and vomiting and below
6% will cause fatality. Such asphyxiation effect will only very close to the LNG
spill and thus not expected to affect the public.
Cold Burn
Accidental contact with leaking LNG at (-) 162 C will cause severe cold (frost)
burn injury. There was one incident in 1977 during ship loading when a large
valve made of wrong grade of aluminium ruptured spraying LNG on the worker
nearby. This hazard is likely to occur close to the leak. Preventive measures
include use of proper materials for equipment, leak check procedure and use of
appropriate clothing and PPE.
4.4 LNG Incidents
LNG industry has maintained high standards of safety over the past six decades.
Safety record of all LNG facilities worldwide demonstrate safety of the primary
LNG Bharat Pvt. Ltd.
Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
Revision: A2 Oct 2015
VIMTA Labs Limited, Hyderabad 17
containment of LNG tank because the secondary spill containment systems
installed around all the tanks have never been required to hold liquid.
A few significant incidents in LNG installations available in technical publications
are as follows.
Cleveland, Ohio (1944)
A large LNG tank failed shortly after it was placed in service. Ignition of the
dispersing vapour cloud resulted in 128 fatalities in nearby residential area. The
tank failure was due to compromise in the material of construction on account of
war time shortage of alloy steel. This is the only incident of LNG tank failure.
Italy (1971)
This was one incident of roll over while unloading into LNG tank. The tank
pressure increased suddenly and roof was slightly damaged. There was no
ignition.
Maryland (1979)
Explosion occurred in the electrical substation of LNG terminal due to leakage
through inadequately tightened electrical penetration seal of LNG pump. The
explosion caused one fatality, injury to another and considerable property
damage. Necessary changes were made in design codes to prevent such
incidents.
Indonesia (1993)
LNG leaked from an open run-down line in the LNG liquefaction facility during
pipeline modification project and entered the concrete storm water system. It
caused rapid vapor expansion which overpressurized and ruptured the sewer
lines.
Ship Incidents
There were a few incidents of LNG release due to valve leakage and two incidents
of overfilling which resulted in cracking of deck plates. In one case of valve
failure, there was spillage of LNG on the worker.
There were a few cases on stranding/ grounding of vessel resulting in damage of
ballast tanks and vessel bottom, and listing of vessel. However, there were no
instances of LNG release.
There was one case of mooring breakage during loading resulting in hull and deck
fractures. However, there was no LNG release.
There was one case of collision of LNG carrier in ballast condition with US nuclear
powered submarine. The ship suffered leakage of sea water into double bottom
dry tank area.
Damage of LNG tank in ship can occur only when the hulls are breached by high
energy collisions. This is not likely in the area around LNG berth in a port where
the carrier movement is carried out under controlled conditions using velocity
meters and other devices. Regular maintenance of shipping channel and control
of ship movement in port is required to prevent occurrences of collision or
grounding.
4.5 References
The following publications are used for reference in this study.
“LNG Risk Based Safety – Modeling and Consequence Analysis” by Wodward &
Pitblado, American Institute of Chemical Engineers
“LNG Safety and Security” by Center for Energy Economics, Texas
“NFPA 59A: Standard for the Production, Storage and Handling of Liquefied
Natural Gas – 2013 Edition”
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Quantitative Risk Assessment (QRA) for LNG Storage & Re-Gasification Terminal at Krishnapatnam Port,
Andhra Pradesh
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VIMTA Labs Limited, Hyderabad 18
“EN 1473:2007 – Installation and equipment for liquefied natural gas – Design
of onshore installations”
“ EN 14620:2006 - Design and manufacture of site built, vertical, cylindrical,
flat-bottomed steel tanks for storage of refirigated liquefied gases with
operating temperature between 0C and -165C” (This standard replaces BS
7777)
“Risk-Based LNG Facility Siting and Safety Analysis in the U.S. – Recent
Developments” by American Gas Association
4.6 Consequence Analysis
In case of leaks from the LNG tanks, pumps, vaporizers etc. the hazards are
mainly pool fire, jet fire, flash fire and/or vapour cloud explosion.
Pool/ jet fire heat radiation
The effects of heat radiation from pool fire are shown in the following Table-3.
TABLE-3
EFFECTS OF HEAT RADIATION
Heat Radiation Level
(kW/m2) Observed Effect
1.2 Average solar radiation received at noon in summer
4 Sufficient to cause pain to personnel if unable to reach cover within 20 seconds; however blistering of the skin (second-degree burn) is likely; 0% lethality.
12.5 Minimum energy required for piloted ignition of wood, melting of plastic tubing.
Significant chance of fatality for medium duration exposure
37.5 Sufficient to cause damage to process equipment. Significant chance of fatality if exposed even for very short duration.
Vapour Cloud Explosion (VCE)
When a large quantity of flammable vapour or gas is released, mixes with air to
produce sufficient mass in the flammable range and is ignited, the result is a
vapour cloud explosion (VCE). The damage effect of VCE is due to overpressure,
The effects of overpressure due to VCE are shown in the following Table-4.
TABLE-4
EFFECTS OF OVERPRESSURE
Over-pressure
Observed Effect bar(g) psig
0.021 0.3 “Safe distance” (no serious damage below this value);
some damage to house ceilings; 10% of window glass
broken.
0.069 1 Repairable damage; partial demolition of houses, made
uninhabitable; steel frame of clad building slightly
distorted.
0.138 2 Partial collapse of walls of houses.
0.207 3 Heavy machines (3000 lb) in industrial buildings
suffered little damage; steel frame building distorted
and pulled away from foundations.
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Flash fire is represented by presence of flammable gas mixture above LFL
concentration.
Consequence analysis has been carried out for selected scenarios in the LNG
Terminal using DNV Phast software.
Results of consequence analysis for the above scenarios are shown in the Table-
5.
TABLE-5
CONSEQUENCE ANALYSIS RESULTS
Description Downwind Effect
Distances (Metres)
Wind speed & Atm. Stability Class 3 m/s; D 6 m/s; D
1. LNG Vaporizer Inlet - 25mm Leak (Liquid)
Pool fire heat radiation intensity
4 kW/m2 117 117
12.5 KW/m2 73 74
37.5 kW/m2 43 45
Vapour cloud explosion overpressure
0.021 bar (0.3 psi) 151 140
0.069 bar (1 psi) 109 97
0.207 bar (3psi) 94 78
Flash fire envelope
LFL concentration (4.4%) 85 70
2. LNG Vaporizer Outlet - 25mm Leak (Gas)
Jet fire heat radiation intensity
4 kW/m2 39 39
12.5 KW/m2 31 32
37.5 kW/m2 25 26
Vapour cloud explosion overpressure
0.021 bar (0.3 psi) 56 48
0.069 bar (1 psi) 35 29
0.207 bar (3psi) 28 24
Flash fire envelope
LFL concentration (4.4%) 21 19
3. FSU Discharge Connection Hose Leak
Pool fire heat radiation intensity
4 kW/m2 67 68
12.5 KW/m2 42 44
37.5 kW/m2 24 26
Vapour cloud explosion overpressure
0.021 bar (0.3 psi) 124 92
0.069 bar (1 psi) 80 55
0.207 bar (3psi) 64 42
Flash fire envelope
LFL concentration (4.4%) 52 39
4. Ship to Ship Transfer Hose Leak
Pool fire heat radiation intensity
4 kW/m2 92 94
12.5 KW/m2 58 60
37.5 kW/m2 33 36
Vapour cloud explosion overpressure
0.021 bar (0.3 psi) 135 103
0.069 bar (1 psi) 85 65
0.207 bar (3psi) 67 52
Flash fire envelope
LFL concentration (4.4%) 60 48
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The LNG bullets to be installed in Phase – I are double wall type with vacuum insulation
in the annular space. This type of vessel is not susceptible to BLEVE/ fire ball hazard.
The large LNG tanks to be installed in Phase – IA and Phase – II are full containment
type with pre-stressed outer wall and RCC roof which are designed to contain the liquid
and vapour without any limitation. Therefore, pool fire and gas dispersion due to failure
of primary containment (inner steel tank are not considered for these tanks.
Graphical results of consequence analysis plotted on pipeline route map are provided in
the Figure-8 to Figure-19.
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FIGURE-8
LNG VAPORIZER 1 INLET LIQUID LEAK
(Pool Fire Intensity Ellipse-3 m/s; D)
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FIGURE-9
LNG VAPORIZER 1 LIQUID LEAK
(Flash Fire Envelope - 3 m/s; D)
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FIGURE-10
LNG VAPORIZER 1 LIQUID LEAK
(Vapour Cloud Explosion Overpressure Radii -3 m/s; D)
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FIGURE-11
LNG VAPORIZER 2A INLET LIQUID LEAK
(Pool Fire Intensity Ellipse-3 m/s; D)
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FIGURE-12
LNG VAPORIZER 2A INLET LIQUID LEAK
(Flash Fire Envelope-3 m/s; D)
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FIGURE-13
LNG VAPORIZER 2A INLET LIQUID LEAK
(Vapour Cloud Explosion Overpressure Radii -3 m/s; D)
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FIGURE-14
FSU DISCHARGE HOSE LEAK
Pool Fire Intensity Ellipse - 3 m/s; D
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FIGURE-15
FSU Discharge Hose Leak
Flash Fire Envelope- 3 m/s; D
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FIGURE-16
FSU DISCHARGE HOSE LEAK
Vapour Cloud Explosion Overpressure Radii-3 m/s; D
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FIGURE-17
LNG SHIP TO SHIP TRANSFER HOSE LEAK
Pool Fire Intensity Ellipse -3 m/s; D
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FIGURE-18
LNG SHIP TO SHIP TRANSFER HOSE LEAK
Flash Fire Envelope- 3 m/s; D
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FIGURE-19
LNG SHIP TO SHIP TRANSFER HOSE LEAK
(Vapour Cloud Explosion Overpressure Radii-3 m/s; D)
Review of Consequence Analysis Results
The following observations are made based on review of the results of
consequence analysis for the selected failure scenarios.
High pressure LNG liquid and vapour leak from Vaporizer
The fire radiation and gas dispersion effects fall well within the facility boundary.
FSU discharge hose leak
The pool fire radiation, gas dispersion and vapour cloud explosion overpressure
effects fall within the safety exclusion circle (200 m radius) indicated in the layout
plan.
It is noted that FSU will not be required after implementation of Phase-II. In the
subsequent system for transfer directly from LNG carrier, it is recommended to
provide unloading arms.
Ship to ship transfer hose leak
The pool fire radiation, gas dispersion and vapour cloud explosion overpressure
effects fall within the safety exclusion circle (200 m radius) indicated in the layout
plan.
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4.7 Input Data for QRA
The input data for all failure scenarios considered for QRA are listed in Table-6.
TABLE-6
FAILURE SCENARIOS AND THE RELEVANT INPUT DATA
Item Description Dyke Size Failure
Scenario
Failure Rate for
Each Equipment (per year)
LNG Tanks (Vacuum Insulated) –
350 M3 Capacity
(T101/102/103)
5 mm Leak 1.0E-03
25 mm Leak 4.0E-04
100 mm Leak 1.0E-04
LNG Tank (Full Containment
Type) – 30,000 M3 Capacity
(ST1001; ST1001A; ST1001B;
ST1001C)
120 x 120
x 2.5 m
Catastrophic
failure
1.0E-08
Outlet Pipe
Failure
1.0E-05
LNG Vaporizer Unit E1301A/1302A;
E1301B/1302B; E1301C/1302C)
5 mm Leak 7.0E-04
25 mm Leak 2.5E-04
100 mm Leak 1.0E-04
LNG Trasfer System to/from FSU
Hose/ flange connections
5 mm Leak 2.0E-05
25 mm Leak 5.0E-06
100 mm Leak 6.0E-07
4.8 Population Data
The distribution of people in the LNG Terminal and surrounding area is as follows.
Total number of people within the port area after the completion of all phases of
the port operation will be around 4000.
The number of persons within the LNGBL is estimated to be about 130 including
the contractor persons
4.9 Ignition Source Data
The LNG terminal and adjacent POL storage area are to be maintained free of
ignition sources and provided with flame-proof electrical equipment.
The whole port area outside the LNG terminal and POL storage has been
considered for potential ignition sources.
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4.10 QRA Results
Individual risk
Iso-risk contours for individual risk due to LNG Terminal Phase 2 are shown in
Figure-20. An enlarged diagram is shown in Figure-21.
FIGURE-20
ISO-RISK CONTOURS FOR INDIVIDUAL RISK (PHASE 2)
1E-06 per year
1E-07 per year
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FIGURE-21
ISO-RISK CONTOURS (PHASE 2) – ENLARGED VIEW
1E-06 per year
1E-07 per year
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The maximum individual risk contour observed in the LNG Terminal is 1E-06 per
year. The maximum individual risk is found to be 2.4E-05 per year. This will be
the location-specific individual risk (LSIR) applicable to a person standing at the
site all the time in the year. However, any individual person working in the LNG
Terminal is present at the site for an average period of about 8 hours of work
during the day.
Therefore the individual-specific individual risk (ISIR) a person working in the LNG
Terminal is estimated as follows:
ISIR = LSIR x (fraction of time in the year when exposed to risk)
= (9.0E-06) x (8/24) = 3E-06 per year.
The estimated maximum ISIR value of 3E-06 per year is in the lower part of ALARP
region close to Acceptable level.
Risk contours of 1.1E-06 per year are within the LNG Terminal. Therefore the
individual risk to members of the public due to the LNG Terminal is less than 1.1E-
06 per year and in Acceptable region
The vales of individual risk to plant personnel and general public in comparison
with the specified risk criteria are shown in Figure 22.
FIGURE-22
INDIVIDUAL RISK DUE TO LNG TERMINAL
Intolerable Risk
10-3 per year
10-4 per year
Risk to Personnel
Risk to Public
Risk Tolerable if ALARP
Max. Individual Risk to
Plant Personnel: 3 x 10-6 per
year Max. Individual Risk to
Public: 1 x 10-7 per year
10-6 per year 10-6 per year
Broadly Acceptable
Risk
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Societal Risk
The FN Curves for societal risk due to the LNG Terminal during Phase 2 with 5 MM
TPA capacity is shown in Figure-23.
FIGURE-23
SOCIETAL RISK DUE TO LNG TERMINAL
It is seen that the societal risk due to the LNG Terminal is well within the
Acceptable region.
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5.0 CONCLUSIONS & RECOMMENDATIONS
5.1 Conclusions
The results of this QRA study for the LNG Terminal at Krishnapatnam Port lead to
the following conclusions.
Individual risk to members of the public is less than 1 x 10-6 per year and
therefore in the Acceptable level.
Individual risk to personnel working in the Terminal is 3 x 10-6 per year which
is in the lower part of ALARP region very close to Acceptable level.
Societal risk is well within the Acceptable level.
Consequence analysis for LNG release shows that for the maximum credible
scenarios such as 25 mm leak in high pressure LNG system, the effect distances
for pool/ jet fire, flash fire and VCE are within the Terminal boundary.
LNG tanks are of full containment type which ensures high degree of safety for
the LNG storage system.
The reaction time considered for closure of valves is 10 sec. The leak scenario is
for the volume of LNG contained between the valves (4 hoses). The QRA/Risk
contours are drawn accordingly for various wind directions and the envelope is
found within the 200m radius from LNGBL berth. The fire water pump house is
located outside this zone. It should be ensured that necessary safety systems
are provided to close the shutdown valves for transfer hose/ unloading arm within
10 seconds.
Based on worldwide experience over 70 years, LNG industry including on-shore
installations and marine LNG carriers has established exemplary safety record.
The above results indicate that the LNG Terminal at Krishnapatnam Port conform
well to the risk criteria. LNGBL are expected to ensure the best practices for
safety management system, engineering, construction, operation and
maintenance for the LNG Terminal.
The installation design and construction conform to relevant Indian/ international
codes and standards including OISD and PNGRB guidelines.
In case of any LNG liquid or gas leakage in the Terminal, it is necessary to isolate
the supply with minimum delay. For this purpose effective leak detection system
with alarm and automatic arrangements for isolation and/ or mitigation is to be
established. Besides the conventional systems for gas leak detection, imaging
systems are also found to be very effective for monitoring LNG transfer
equipment over large area.
Safety Measures to be adopted
Following are some of the important project specific information to be enlisted:
1) Leak detection and valve closing time is limited to 10 sec.
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2) For Hoses at ship to ship transfer a leakage scenario of 3 m3 between valves
(volume contained in 4 hoses) is considered.
3) For ship to shore transfer of LNG regular unloading arms are proposed for
improved safety against rupture/leaks as against normal hoses.
4) Double wall buffer tanks in Phase-1 and full containment tanks in Phase-1A
and Phase-2 are proposed for improved safety against tank failures.
5) Existing port DMP is being updated with project specific emergency
preparedness and risk management measures.
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