Workshop at Indian Institute of Science 9-13 August, 2010 Bangalore India Fire Safety Engineering & Structures in Fire Organisers : CS Manohar and Ananth Ramaswamy Indian Institute of Science Speakers: Jose Torero, Asif Usmani and Martin Gillie The University of Edinburgh Funding and Fire Safety Engineering Methods Session JT10
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Workshop at Indian Institute of Science 9-13 August, 2010 Bangalore India Fire Safety Engineering & Structures in Fire Organisers:CS Manohar and Ananth.
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Workshop at Indian Institute of Science9-13 August, 2010BangaloreIndia
Fire Safety Engineering & Structures in Fire
Organisers: CS Manohar and Ananth RamaswamyIndian Institute of Science
Speakers: Jose Torero, Asif Usmani and Martin GillieThe University of Edinburgh
Funding and Sponsorship:
Fire Safety Engineering Methods
Session JT10
Suppression
Water Suppression
Should Active Suppression be Used? Should Active Suppression be Used?
Why can the decision of not using active suppression be made? Cost Environmental Concerns Damage of Property Incompatibility with the purpose of the building
Fire is a complex problem that requires a “cost/benefit” analysis
The Problem
Fire Control and Suppression
Combustion Products
Contaminated Water
Suppression Agents Fire Retardants
Contaminated Residues i.e. lead from paint
chars, tars, soil degradation
Fire Prevention
Early Detection Smoke Detectors, CO Detectors, IR Detectors,
UV Detectors, Motion Detectors Effective but not infallible
Proper Material Selection Low Flammability Materials - not always
possible to use – many times are not cost effective
Fuels – aircraft, cars, ships Plastics – everyday use Metals – flammable under extreme conditions –
i.e. turbine engines
Fire Retardants
Additives used to reduce the “flammability” of a material
Halogen-based retarded materials – i.e. PVC Inhibit gas phase combustion chemistry Produce contaminants during a fire Produce contaminants during recycling
Phosphorous based charring materials Formation of chars – reduces flow of fuel to flame Produce contaminants during fire Contaminate suppression water Lead to smolder fires – very difficult to detect and suppress
New environmentally friendly technologies Based on carbon fibers and nano-composites – still under
development
Fire Suppression
Water Sprinklers Water Mists Gaseous Agents Foams Dry Chemicals
Mechanisms of Flame Suppression
Thermal Sink Reduces the Mass Transfer number Reduces the flame temperature Reduces the Damköhler Number
Oxygen Displacement Reduces the Mass Transfer number Reduces the flame temperature Reduces the Damköhler Number
Chemical Inhibition Affects the Chemistry Reduces the Damköhler Number
Water Based Systems
Work on the basis of energy removal and oxygen displacement
Sprinkler Systems Simple systems, Low Maintenance, Low Cost Work by wetting the fuel surrounding the fire Not a suppression technique, more a control system Therefore: High Water discharge ~ 0.25 lt/m2s
Water Mists Water Discharge ~ 0.00025 lt/m2s High penetration due high momentum injection Everything else is more complex due to high pressure
Foams
Very limited applications liquid fuels protection of structures
Need to produce a film that spreads across the fuel lead to complex chemical composition generally based on Fluorine and Iodide
i.e AFFF Foams
C
F
F
C
F
F
C
F
F
C
F
F
C
F
F
C
F
F
C
F
F
C
F
F
F SO2N(CH2)3 N
CH3
CH3
CH3
+
I -
Dry Chemicals
Generally can only be discharged once
Reduced penetration Act as mostly as thermal sinks –
Less Efficient Chemical suppression only present if
dry chemical is “halogen” based Generally – highly corrosive
Gaseous Agents
High effectiveness Chemically active – i.e. Halons
Less effective Chemically inactive – extinction by reduction of
oxygen concentration or thermal sink
Advantages No clean-up necessary, easy storage, low
weight/volume ratio, high penetration (total flooding), electrically non-conductive, mostly non-corrosive, etc., etc., etc.
Mechanisms of Flame Suppression
Most effective is Chemical Inhibition
Halons are extremely effective at attacking “chain branching” reactions in combustion processes
Halons
Nomenclature
C F Cl Br I
Halon 13011 3 0 1 CF3Br
Halon 1011 1 0 1 1 CH2ClBr
Halon 2402 2 4 0 2 C2F4Br2
Why is Halon so Effective?
Combustion of Methane
HCOOHCO
OHHOH
COHHOHCH
OHOOH
MHCHMCH
2
2
223
2
34
BrOHOHHBr
HBrHBr
BrCFMBrCF
2
33
Halon 1301 + Heat
Why is Halon an Environmental Problem?
2
23
33
OBr2BrO2
OBrOOBr
BrCFUVBrCF
Consequences
The Montreal protocol banned the manufacturing and use of Halon 1301
No other alternative has proven to be as effective as Halon 1301
Fact Halon is present in 98% of commercial aircraft In 2000 there where 178 Halon discharges in
commercial aircraft It has been estimated that of those 178 discharges
more than 100 would have resulted in generalized fires that would have crashed-landed the aircraft
Conclusion
Is it justifiable to ban the use of Halon 1301 for fire applications?
Is environmental protection a sufficient “cost” to overwhelm the “benefits” of Halon 1301?
Fact The ozone depleting potential of all fire
related Halon 1301 deployments in a year is equivalent to that of the emissions of 132 cars!
Water Suppression-Sprinkler Systems
Water suppression is the most commonly used mechanism of active fire control in structures
Among the different water suppression systems, sprinklers are by far the most commonly used
Some design considerations will be presented
Effect of Sprinklers (I)
Effect of Sprinklers (II)
Increase the time to “Flash-Over” Decrease toxic product concentrations,
CO, HCN, etc. Decrease the room temperature Push the hot layer down slowing fire
growth Push the hot layer down slowing fire growth
Increase visibility “soot” dissolves in water
Effect of Sprinklers (III)
“sprinklers” are NOT designed to Extinguish the fire
“sprinklers” are designed to Increase the time available to extinguish the fire
Tg, ug
M, cp,
As
Fire Detector Activation
A first order analysis for predicting fire detector activation based on convective heating and a lumped capacity analysis
Principles of the DETAC Model
Background
1972 - Alpert - “Calculation of response time of ceiling-mounted fire detectors” - quasi-steady fires
1976 - Heskestad & Smith - Development of plunge test & RTI concepts
1984 - NFPA 72E App. C 1985 - Evans & Stroup - DETACT models 1987 - Heskestad & Bill - Conductance factor added 1998 - SFPE Task Group - Review bases of DETACT
Bases
Heat balance at detector
Convective heating only
Lumped capacity analysis
Negligible losses (basic model)
outinabs qqq
)( dgscin TTAhq
dt
dTmcq d
pabs
0outq
Predictive equation for temperature rise
Definition of detector time constant
Time constant not really constant
Solution
τ
TTTT
mc
Ah
dt
dT dgdg
p
scd)(
)(
sc
p
Ah
mcτ
Response Time Index
For cylinders in cross flow
Implications
Definition of RTI
Predictive equation
gc uh ~
guτ 1~ constuτ g
guτRTI
)( dg
gd TTRTI
u
dt
dT
RTI relationships
Lower RTI Faster response
Lower m or cp Lower RTI
Higher hc or As Lower RTI
In limit, as RTI 0, Td Tg
RTI determination (1)
Plunge test Tg = constant
ug = constant
Tact = known
Analytical solution
oτt
g
d eT
T /1Δ
Δ RTIut
g
act oacteT
T /1Δ
Δ
Plunge test
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
0 1 2 3 4 5
t/
T
d/
Tg τt
g
d eT
T /1Δ
Δ
DETACT formulation
Euler equation for Td
Substitute equation for dTd/dt
Evaluation requires RTI, Tg(t) and ug(t)
tdt
dTTT dtd
ttd Δ)()Δ(
tTTRTI
uTT t
dt
g
tgt
dtt
d Δ)()(
)(
)()Δ(
Detector activation
Fixed temperature devices
Rate-of-rise devices
Typical value of dTact/dt: 8.3ºC (15 ºF) /min
actactd tdt
dT
dt
dT
actactd tTT
Gas parameters - Tg, ug
Alpert correlation (unconfined ceiling jet)
Temperature Velocity
3/2,
,
3/5
3/2
,
)/(
32.0
9.16
HrT
T
H
QT
plg
cjg
plg
6/5,
,
3/1
,
)/(
2.0
95.0
Hru
u
H
Qu
plg
cjg
plg
General Information
Based on NFPA 13 – National Fire Protection Association Codes
Sprinkler selection is based on the rapidity with which the thermal sensor operates - RTI
Sprinkler System Design
The design of a sprinkler system consists of the following steps: Identification of the fuel load Identification of the use of the building Calculation of the sprinkler density Determination of sprinkler placement Definition of the different components of the system
Sprinklers Pipes Pumps Valves
Establishment of maintenance procedures
Procedures
Classification of occupancy or Classification of the fuel load
Determination of quantity of water needed
Determination of sprinkler type Water flow Activation temperature and RTI
Occupancy
Light risk
Moderate risk
High risk
Special Occupancy: I.e. Historic documents, film, art, nuclear power
plants, airports, etc.
Fuel Load
Class I: Non combustible materials stocked on “wood pallets” or in single thickness cardboard boxes covered with a plastic film cover.
Class II: Non combustible materials stocked on “wood pallets” or in multiple thickness cardboard boxes covered with a plastic film cover.
Class III: Wood products, paper, natural fibers, C-Type plastics.
Class IV: A Type Plastics (between 5-15% of the weight) and plastics of types B or C for the rest.
Class II Liquid: 37.8 oC<Tf< 60 oC Class II A: 60 oC<Tf<93 oC Class II B: Tf>93 oC
Te=Boiling temperature
Plastics
Type A: ie. Polyethylene, polystyrene, polypropylene, PVC, etc.
Type B: ie. Fluoroplastics, natural rubber, nylon, silicone
Type C: ie. Melamine, fenolites, urea
Water Density (Qd)
Flow Through a Sprinkler: “K” Factor
PKQi Factor-K Nominal
gpm/(psi)1/2
Factor-K Range
gpm/(psi)1/2
Factor-K Range
dm3/min/ (kPa)1/2
%Over Nominal
Discharge with K-5.6
Thread
1.4 1.3-1.5 1.9-2.2 25 1/2 in. NPT 1.9 1.8-2.0 2.6-2.9 33.3 1/2 in. NPT 2.8 2.6-2.9 3.8-4.2 50 1/2 in. NPT 4.2 4.0-4.4 5.9-6.4 75 1/2 in. NPT 5.6 5.3-5.8 7.6-8.4 100 1/2 in. NPT 8.0 7.4-8.2 10.7-11.8 140 1/2 in. NPT or
3/4 in. NPT 11.2 11.0-11.5 15.9-16.6 200 3/4 in. NPT 14.0 13.5-14.5 19.5-20.9 250 3/4 in. NPT 16.8 16.0-17.6 23.1-25.4 300 3/4 in. NPT 19.6 18.6-20.6 27.2-30.1 350 1 in. NPT 22.4 21.3-23.5 31.1-34.3 400 1 in. NPT 25.2 23.9-26.5 34.9-38.7 450 1 in. NPT 28.0 26.6-29.4 38.9-43.0 500 1 in. NPT
Sprinkler Density
Sprinklers per m2 : “n”
Total number of sprinklers: “N”
N=n.A
i
d
Q
Qn
Activation Temperature
The decision is based on the fuel load/occupancy
Activation Temperature (oC)
Classification ColourCode
38 Ordinary No-Colour 66 Intermediate White
107 High Blue 149 Extra-High Red 191 Very-Extra-High Green 246 Ultra High Orange 329 Ultra High Orange
Distribution and Installation
Sprinklers are distributed through the protected space homogeneously
The water pressure will be established by the code and the sprinkler density Water pumps are many times necessary
The total flow is established on the basis of the number of sprinklers
Installation Details
NFPA 13 gives details on how to place sprinkler heads
ST-AST
SA
SS
SP
SC
SC
Special Sprinkler Types
Regular Sprinklers: Direct 40-60% of the water towards the fire
ESFR-Early suppression fast response Extended Coverage Large Drop Sprinkler Open Sprinklers (no actuator) Quick Response (QR) Quick Response Early Suppression (QRES) Residential Sprinklers (fast response sprinklers
rated for residential use), etc., etc., etc.,
Installation Types
Wet Pipe System-Standard, water filled pipes with sensor at the sprinkler head
Circulating-Closed Loop System-combined wet pipe sprinkler system with HVAC system
Dry Pipe System-Pressurized air/nitrogen, its release opens the water valve-for non-heated environments
Combined-Dry Pipe Pre-reaction System-thermal sensor + fire detection system, for fast or screened response
Deluge System-Dry pipes with a fire sensor, no thermal sensor (open sprinklers)
Limitations of this approach
Effectiveness of the system is base on empirical data for a reduced number of configurations
No quantitative estimate of the “probability of success” can be stated
No quantitative estimate of the potential “outcome” can be specified
This approach is being phased-out by performance design….