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14-03-2019 | Issue 5/2019 Open Access

Fire Technology 5/2019

A Review of Design Values Adopted for Heat Release Rate Per Unit Area

Journal:
Fire Technology > Issue 5/2019
Authors:
Charlie Hopkin, Michael Spearpoint, Danny Hopkin
Important notes

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

1 Introduction

Heat release rate per unit area (HRRPUA) is commonly used as a design input for fire and smoke modelling. The heat release rate (HRR) of a fire may be calculated from the area of a fire using the following equation [ 1]:
$$ \dot{Q} = \dot{Q}''{\text{A}}_{fire} $$
(1)
where \( \dot{Q} \) is the total HRR (kW), \( \dot{Q}'' \) is the HRRPUA (kW/m 2) and \( {\text{A}}_{fire} \) is the area of fire involvement (m 2). This approach to determining HRR is typically adopted in circumstances where the fire is fuel bed controlled (i.e. controlled by the availability of fuel) and combustibles can burn freely without being limited due to a lack of ventilation. Using this approach assumes a HRRPUA value for a specific fuel type or fuel package (e.g. an item of furniture) and example values can be found in the literature, including standard text books such as Drysdale [ 2] and the SFPE Handbook of Fire Protection Engineering [ 3].
Alternatively, rather than using a specific fuel type or package, the HRR can be calculated as a function of the occupancy type for which a representative HRRPUA is applied and this value is then assumed for a specified area. The area may be taken to be a proportion of the enclosure floor area, to represent a designated fire footprint, or could be taken as the area of the entire enclosure. The fire footprint may represent the surface area of one or more fuel packages or could be related to an expected area of fire involvement, for example for a fire which has been limited by the actuation of a sprinkler system with an assumed sprinkler head spacing arrangement. With respect to this interpretation of area of fire involvement the Eurocode for actions on structures exposed to fire, EN 1991-1-2 [ 4], refers to \( {\text{A}}_{fire} \) as “the maximum area of the fire which is the fire compartment in case of uniformly distributed fire load but which may be smaller in case of a localised fire” [ 4]. Whilst EN 1991-1-2 is a code dedicated to structural response in fire, the content cited in Annex E relates to a generic description of enclosure fire development, giving guidance on fuel and ventilation-controlled regimes in terms of HRR and the relationship with time.
PD 7974-1:2003 [ 1] is a UK published document which provides guidance on the initiation and development of fire within the enclosure of origin and provides guideline values for various occupancies, reproduced in Table  1. The recommended HRRPUA values given in PD 7974-1:2003 reference NFPA 92B and the latest revision of UK guidance document CIBSE Guide E [ 5] also provides values consistent with those given in NFPA 92B. Thus, in its caveat of suggested HRRPUA values, PD 7974-1:2003 notes that “this information should be treated with care, as it is predominantly of US origin and therefore may not always be representative of UK occupancies”.
Table 1
PD 7974-1:2003 [ 1] suggested HRRPUA for fuel bed controlled fires
Occupancy
HRRPUA (kW/m 2)
Shops
550
Offices
290
Hotel rooms
250
Industrial excluding storage
90–620
Depending upon fuel and arrangement
The review herein results from discussions in the process of the revision of PD 7974-1 likely to be published in 2019, where uncertainty arose as to the origins and appropriate application of HRRPUA values given in the previous 2003 edition. This review is separated out into six main categories based on the building/occupancy type: industrial; shops and retail (mercantile); offices; hotel rooms; residential; and other types. These categories broadly align with those described in PD 7974-1:2003, given in Table  1.
Following a review of the history of HRRPUA values of the six occupancy categories, conclusions and recommendations are made on what may represent reasonable design values that can be incorporated into the revised edition of PD 7974-1, as well as discussion on what further work needs to be considered.

2 Determination of HRRPUA

In the determination of HRRPUA from experimental data, the area of fire involvement \( ({\text{A}}_{fire} ) \) could be derived in multiple ways, such as by using the area of the fuel or the area of a burning enclosure, or by using less precise measures such as the direct visual observations or by inspecting images (video/still photographs) recorded during experiments. Experiments may include single or multiple burning items, and the HRR ( \( \dot{Q} \)) is typically determined either by oxygen calorimetry or an assessment of the mass of fuel consumed with respect to time, in the latter case by adopting a representative value for the heat of combustion of the fuel. The heat of combustion may be expressed either as a total or effective value, although in some work it is not always clear which of these has been adopted. Either approach produces a HRR curve where the HRR will typically fluctuate or change over time. The raw mass loss or heat release measurements from experiments may undergo some smoothing to reduce noise in the data, for example by applying the Savitzky–Golay smoothing filter, as illustrated by Staggs [ 6] for cone calorimeter mass data. Specific to HRR, Evans and Breden [ 7] note that such data can be made “more attractive by smoothing techniques”.
Values for HRRPUA are easily determined for fuels which burn in a relatively steady-state manner from:
$$ \dot{Q}'' = \frac{{\dot{Q}}}{{{\text{A}}_{fire} }} $$
(2)
However, in reality most fuels do not burn with a steady-state HRRPUA, even if the nominal area of burning remains constant. In such a case the HRRPUA can be determined by:
$$ \dot{Q}'' = \frac{{\overline{{\dot{Q}}} }}{{{\text{A}}_{fire} }} $$
(3)
where \( \overline{{\dot{Q}}} \) is the average HRR over a defined period of burning (where \( \dot{Q}'' \) is referred to herein as the ‘individual average HRRPUA’). The assumption of a fixed burning area is applied in NFPA 271 [ 8], for example. Fuels such as liquid hydrocarbons in pool configurations are often treated as though they burn at a steady-state, but in practice the turbulent flames results in a HRR that fluctuates around a mean value. Even this assumption may not account for the heat transfer effects to and from the fuel container or the initial (albeit rapid) growth period. Furthermore, most containers do not have perfectly flat bases. These combined factors result in the HRR not immediately reaching a maximum from zero or vice versa in the form of a step-function.
Fuel packages that may consist of several materials are unlikely to burn with a steady-state HRR but will typically involve growth and decay phases with an associated change in the area of burning. The piece-wise HRRPUA can be calculated at defined time-steps and the overall HRRPUA given by:
$$ \dot{Q}'' = \frac{{\mathop \sum \nolimits_{{t = t_{n} }}^{{t = t_{1} }} \left( {\frac{{\dot{Q}}}{{{\text{A}}_{fire} }}} \right)_{t} }}{n} $$
(4)
where \( \left( {\frac{{\dot{Q}}}{{{\text{A}}_{fire} }}} \right)_{t} \) is the HRRPUA at a given time-step t for the instantaneous HRR ( \( \dot{Q} \)) and instantaneous area ( \( {\text{A}}_{fire} \)), and \( n \) is the number of time-steps. The calculation can be carried out over the total duration ( \( t_{total} \)) of burning or some specified restricted timescale as appropriate. The determination of the total duration of burning is also subject to interpretation as in practice a fire experiment may be terminated before complete combustion has ceased. Within standard procedures, tests may be terminated under stated conditions, for example NFPA 271 [ 8], where specified durations have elapsed, or when the mass loss rate has dropped below a defined criterion.
Those fuel packages that exhibit growth and decay phases will result in a peak HRR. Experimentally the determination of a peak value will be affected by the sampling frequency of the instruments and whether any smoothing of data is carried out. Often the peak HRR is synonymous with the maximum HRR. However, Mowrer and Williamson [ 9] note that composite products and materials exhibit complex burning behaviour which may result in more than one peak in the HRR. The peak HRRPUA can be determined by:
$$ \dot{Q}''_{peak} = \left( {\frac{{\dot{Q}}}{{{\text{A}}_{fire} }}} \right)_{peak} $$
(5)
This paper defines the maximum ( \( \dot{Q}''_{max} \)) as the greatest HRRPUA for a given curve in circumstances where there may be more than one peak. Where a curve only has one peak, then the maximum and the peak are considered equivalent within the context of the discussion in this paper.
With respect to the above methods of determining HRRPUA, exemplar individual HRRPUA curves are shown in Fig.  1.
When data is available for two or more separate experiments (under the same experimental conditions) then a combined average HRRPUA ( \( \overline{{\dot{Q}''}} \)) can be calculated from the individual average HRRPUA values ( \( \dot{Q}'' \)). Similarly, a combined average maximum HRRPUA ( \( \overline{{\dot{Q}''}}_{max} \)) can be determined from individual maximum HRRPUA ( \( \dot{Q}''_{max} \)) values. Clearly care is required when interpreting reported HRRPUA values in terms of the calculation method and whether values are an individual or combined, average or maximum HRRPUA. Specific to this paper, PD 7974-1:2003 does not mention whether the HRRPUA values are intended to represent average or maximum values.
Finally, as discussed by Krasny et al. [ 10], when measuring the HRR of a burning item the presence of an enclosure can cause air vitiation effects, generate unsymmetrical air flow patterns and enhance the burning rate due to radiation feedback from the hot surfaces and upper gas layer. To overcome these enclosure effects, standard test methods for measuring HRR are operated in an open configuration, allowing an unrestricted flow of air to the combustion zone. Thus, it is possible that HRRPUA values cited in the literature do not include enclosure effects, although these effects may be relevant to a design application. The New Zealand verification method C/VM2 [ 11] includes an enhancement to the HRR at flashover to account for radiation from the upper gas layer in its design procedure.

3 Occupancy Types

3.1 Industrial

In 1977, Theobald [ 12] considered the growth and development of fire in industrial buildings. This work summarised a series of ten fire incidents and five experimental fires, reproduced in Table  2. These fire incidents and experimental fires were taken from previous research undertaken by Theobald [ 13] and Heselden et al. [ 14], respectively. The fire incidents included surveys of five storage buildings, one factory, two workshops and a hospital research unit, with enclosure areas ranging from 170 m 2 to over 10,000 m 2. Building contents of the fire incidents varied from packaged goods, cardboard, timber with three of the fire incidents including mixed combustibles (Table  2). Silcock [ 15] outlined the surveying method and fire reports, where several details were recorded by fire and rescue service personnel following the incident, including the location, spread and the extent of the fire.
Table 2
Data for fire incidents and experimental fires.
As summarised by Theobald [ 12]
Incident
Building contents
Compartment area
Estimated total wood equivalent of fuel
Fuel area
Fuel height
Estimated fuel consumed
Fire area
Estimated fire duration
Estimated burning rate per unit area of fire
m 2
kg
m 2
m
kg
m 2
min
kg/m 2/s
kW/m 2
1
Crated furniture
170
140,000
113
3.3
450
32.0
30.0
0.008
100
2
Vehicles, petrol, paint
260
145
6
0.8
36
6.0
5.0
0.020
260
3
Stacked sawn timber
170
4500
43
1.5
730
9.0
45.0
0.030
390
4
Books, furniture
460
44,000
18
3.0
11,000
418.0
60.0
0.007
93
5a
Stacked cardboard
90
16,500
55
1.8
5400
90.0
40.0
0.025
320
5b
Stacked chipboard
300
220,000
193
2.4
1800
300.0
15.0
0.007
86
6
Cartons, electrical goods
2200
116,000
273
2.0
28,600
250.0
80.0
0.024
310
7a
Cardboard cartons
1300
113,000
785
7.0
113,000
1300.0
30.0
0.048
620
7b
Cardboard reels
2500
2,540,000
624
7.0
510,000
2500.0
210.0
0.016
210
8
Packaged goods
10,200
7,200,000
4000
3.6
3,740,000
8360.0
180.0
0.041
540
9a
Wood cribs
28.5
218
8.65
0.1
218
28.5
19.0
0.007
88
9b
Wood cribs
28.5
436
8.65
0.2
436
28.5
20.0
0.013
165
9c
Wood cribs
28.5
872
8.65
0.4
872
28.5
22.0
0.023
300
9d
Wood cribs
28.5
1744
8.65
0.8
1744
28.5
28.0
0.036
480
9e
Carboard cartons
28.5
408
8.65
1.5
408
28.5
6.7
0.036
480
To calculate HRRPUA related to each incident, Theobald [ 12] considered the estimated mass of fuel consumed, and the estimated fire duration, relative to the recorded fire damage area. This provided an estimated burning rate in kg/m 2/s. To calculate the equivalent burning rate in kW/m 2, Theobald adopted a fixed heat of combustion value of 13 MJ/kg, equivalent to that of wood.
PD 7974-1:2003 [ 1] references Theobald’s work, recommending a HRRPUA of 90 kW/m 2 to 620 kW/m 2 for fires occurring in industrial occupancies. These values approximately equate to the minimum and maximum values for the fire incidents summarised by Theobald, and shown in Table  2. Thus, for industrial fires, the work of Theobald is based on fire incidents and experiments undertaken in the UK and the PD 7941-1:2003 caveat relating to the US origin of the information is inaccurate.
The first edition of NFPA 92B [ 16], published in 1991, recommends a HRRPUA of 260 kW/m 2 for industrial fires, referring to Theobald’s work. While NFPA 92B does not explicitly state why the 260 kW/m 2 value is recommended for industrial fires, it aligns with Incident 2 for the building containing vehicles, petrol and paint given in Table  2. This value has been adopted in subsequent revisions of NFPA 92B.

3.2 Shops and Retail (Mercantile)

In 1979, Morgan [ 17] provided a design summary of smoke control methods in enclosed shopping complexes. In this document, Morgan discusses recommended design fire HRR for fires originating in shops and mentions that statistical information on shops is limited. However, Morgan specifies that for shops fitted with sprinkler systems, fewer than 5% resulting in sprinkler actuation become greater than 5 MW, subsequently stating that a 5 MW design fire “has become widely accepted as a maximum fire [size] for design purposes in view of its low probability of occurring”. Morgan equates this to a fire of base dimensions of 3 m by 3 m and a HRRPUA of 500 kW/m 2. Although the aforementioned 9 m 2 base would result in a HRRPUA of 555 kW/m 2 for a 5 MW fire, the specified dimensions are considered to broadly align with a 10 m 2 fire area with a 12 m perimeter [ 18, 19]. Morgan specifies that the selected HRRPUA is the ‘average’ of values obtained in experimental sprinklered fires, but does not comment on whether this represents a combined average ( \( \overline{{\dot{Q}''}} \)) or a combined average maximum ( \( \overline{{\dot{Q}''}}_{max} \)) across the experiments. Whilst Morgan does not specify how the fire area was determined, previous work by Hinkley [ 20] in 1971 on the control of smoke in enclosed shopping centres notes “in the absence of other information, it is suggested that a fire 3 m × 3 m should be taken”. While not explicitly stated, this appears to align with a typical spacing between sprinkler heads, with Hinkley [ 21] stating for a 3 m by 3 m fire—“this is considered reasonable if the fire is being controlled by sprinklers”. Hinkley [ 21] also refers to circumstances where a fire is limited by sprinklers “so that its heat output is about 5 MW” and later that “experiments… have shown that when sprinklers were operating its peak burning rate was about ½ MW/m 2”. The experiments involved the burning of 1.2 m wide by 2.4 m long by 1.8 m high storage rack that were loaded with approximately 100 kg of combustible materials, including polystyrene tiles, polyurethane foam, wood, wool and cardboard on wooden slats.
In reviewing the origins of the 5 MW retail design fire, Law [ 22] discusses the work of Hinkley. Law notes that in Hinkley’s experiments, an unsprinklered fire results in a maximum HRRPUA of approximately 1000 kW/m 2, a sprinklered shielded fire 300 kW/m 2 and a sprinklered unshielded fire 100 kW/m 2. The 5 MW fire is described as representative of a shielded sprinklered fire located in the ‘worst’ possible location, i.e. at the centre of a grid of four sprinkler heads spaced 3 m apart. This is described as a ‘typical’ sprinkler spacing, although Law notes that the maximum spacing could be up to 3.6 m by 3 m (10.8 m 2). Law suggests that the sprinklers are assumed to stop fire spread beyond the 3 m by 3 m area and remove half of the energy content by cooling the gases.
By referencing Morgan [ 17], NFPA 92B [ 16] in 1991 discussed an approximate HRRPUA of 50 Btu/s/ft 2 (568 kW/m 2) for mercantile occupancies, for a design fire size of approximately 5000 Btu/s (5275 kW). The 2012 edition of NFPA 92 [ 23] noted that this design fire size is based on a “statistical distribution of fire sizes in shops in the United Kingdom that include sprinkler protection”, where less than 5% of fires exceeded 5275 kW and geometrically this fire has been described as having an area of 3.1 m by 3.1 m (9.6 m 2). NFPA 92B’s 568 kW/m 2 was subsequently referenced and simplified in PD 7974-1:2003 [ 1] to 550 kW/m 2, more closely aligning with Morgan’s comments regarding a 5 MW design fire and 9 m 2 fire area. The precursor to PD 7974-1, Draft for Development DD 240-1:1997 [ 24], recommended 500 kW/m 2 for retail building use and similarly, Technical Memoranda TM19:1995 [ 25] recommended 500 kW/m 2 for shops.
Expanding on Morgan’s guidance published in 1979, Morgan and Gardner [ 26] authored BR 186 ‘Design principles for smoke ventilation in enclosed shopping centres’. This design guidance did not provide a recommended value for HRRPUA but refers to the 3 m by 3 m sprinkler-controlled fire which, as stated in BR 186, became “the accepted basis in the UK for a smoke ventilation system in a sprinklered shopping centre”. Likewise, BR 258 [ 18] ‘Design approaches for smoke control in atrium buildings’, published in 1994, refers to a 10 m 2 sprinklered retail fire but does not state the equivalent HRR or HRRPUA.
In the above works on the 5 MW design fire, it is not always explicitly stated whether the HRR and HRRPUA values given are referring to the total HRR or the convective portion only. However, it may be inferred from several sources that it is representative of the convective HRR only, where Morgan [ 17] refers to the “heat carried by the hot gases” when discussing fire size for the design of smoke control systems, Hansell and Morgan [ 18] states a “convective heat flux” for design fires associated with atria and Morgan and Gardner [ 26] adopt the “heat flow rate” when calculating the smoke temperature for a 5 MW fire. Therefore, the adoption of these values for the total HRR or HRRPUA would not directly align with the intent of the original works. Subsequent to this, BR 368 [ 19], Morgan et al.’s ‘Design methodologies for smoke and heat exhaust’, which builds upon both BR 186 and BR 258, recommends a HRRPUA of 625 kW/m 2 for steady-state retail design fires where sprinkler protection is provided, and 1200 kW/m 2 where there are no sprinklers. For the former, the commonly adopted 5 MW fire is considered explicitly representative of convective HRR at 75% of the total HRR, resulting in a total maximum HRR of 6250 kW for a fire area of 10 m 2. The latter 1200 kW/m 2 unsprinklered value broadly aligns with a 1000 kW/m 2 convective HRRPUA described by Law [ 22] for Hinkley’s original experiments.

3.3 Offices

Law [ 27] discussed fire and smoke hazards in air-supported structures as part of a paper first published in 1980. Within this, Law further summarised fire incidents in industrial premises previously discussed by Theobald [ 12]. Law proposed that values of 0.02 kg/m 2/s and 290 kW/m 2 for the mass burning rate per unit area and HRRPUA, respectively, may be adopted when considering furniture fires in offices and residential accommodation. While not explicitly stating how these values were derived, they approximately equate to the combined average mass burning rate per unit area and HRRPUA values from Theobald’s industrial fire incidents (i.e. Incidents 1 to 8 in Table  2). The 290 kW/m 2 HRRPUA recommendation was subsequently referenced and adopted in NFPA 92B [ 16] when considering HRRPUA for use in smoke management design of offices. PD 7974-1:2003 references NFPA 92B for its 290 kW/m 2 recommended design value for offices with the inaccurate caveat relating to the information being of US origin.
Separate to Law’s paper, Morgan and Hansell [ 28] considered the implications of fire sizes and sprinkler effectiveness in offices. When proposing a method for determining a HRR for office design fires, a HRRPUA of 260 kW/m 2 was used. This value was again derived from Theobald [ 12] and applying a fixed fire load per unit area of 57 kg/m 2. Morgan and Hansell stated that this fixed fuel load was adopted from unpublished surveys carried out by Melinek from 1965 to 1967, where it was determined that office fuel load was less than 57 kg/m 2 in approximately 95% of cases. This fuel load per unit area corresponded to mass burning rate per unit area of 0.0144 kg/m 2/s for the ‘wood crib’ curve shown in Fig.  2 (reproduced from Theobald [ 12]). However, instead of using the wood-equivalent 13 MJ/kg heat of combustion adopted by Theobald, Morgan and Hansell applied an alternative value of 18 MJ/kg. Morgan and Hansell [ 28] also note that the resulting HRRPUA is “close to the heat release rate per unit area of 290 kW/m 2 for offices quoted by Law”.
In their following work on calculating smoke flows in atria, Morgan and Hansell [ 29] discussed problems arising from their previous interpretation of Theobald [ 12], where they assumed that a ‘wood crib’ curve (Fig.  2) would be representative of fuel loads found in offices, expressing these values as ‘equivalent wood loads’. In their previous calculation, Morgan and Hansell applied Theobald’s data for the mass burning rate of fuel per unit area (or the burning rate per unit area of fire). However, as noted by Law in her comments on the paper [ 30], the fuel area of the wood crib experiments was one-third of the enclosure area and therefore was not representative of the burning rate per unit area of the entire enclosure. In response, Morgan and Hansell discussed uncertainties in the fire incidents as to how the fuel was distributed within the space [ 31]. Theobald’s industrial fires data was therefore replotted to consider the burning rate per unit area of available fuel within the enclosure instead of the burning rate per unit area of fire damage (per Table  2), to produce the new relationships shown in Fig.  3. Adopting a heat of combustion of 13 MJ/kg for wood instead of the previously used 18 MJ/kg, again for a design fire load of 57 kg/m 2, Morgan and Hansell proposed a revised HRRPUA of 230 kW/m 2 for offices, with an equivalent mass burning rate of 0.0177 kg/m 2/s. In comparison, if Morgan and Hansell’s original 18 MJ/kg heat of combustion value was instead adopted, this would produce a HRRPUA of approximately 320 kW/m 2.
BR 368 [ 19] recommends a HRRPUA of 255 kW/m 2 for open-plan offices and also refers to a value of 270 kW/m 2 for cellular offices. The 255 kW/m 2 value aligns closely with the 230 kW/m 2 to 260 kW/m 2 values calculated by Morgan and Hansell. The latter 270 kW/m 2 value relates to experiments undertaken by Ghosh [ 32] and others, where the total HRR of the fire was measured in a calorimeter with a 6 m by 6 m hood. The area of the fire was estimated from visual observations and photographs. Ghosh noted that, following sprinkler actuation, the HRRPUA reduced to 190 kW/m 2 and also stated that in the experiments, the maximum HRRPUA varied from 150 kW/m 2 to 650 kW/m 2.
BS 7346-4:2003 [ 33], a British Standard and code of practice on the ‘Functional recommendations and calculation methods for smoke and heat exhaust ventilation systems, employing steady-state design fires’ almost universally adopts the same HRRPUA values as those given in BR 368 for all building types and circumstances. However, there is a single exception where BS 7346-4 recommends a HRRPUA of 225 kW/m 2 for an office fire with standard response sprinklers, contrary to BR 368 which recommends 255 kW/m 2 irrespective of whether sprinklers are included or not. It is suspected by the authors of this paper that the 225 kW/m 2 value given in BS 7346-4:2003 may have been the result of a typing error (i.e. from 255 kW/m 2 to 225 kW/m 2).
Previously DD 240-1:1997 [ 24] and TM19:1995 [ 25] suggested a HRRPUA for offices of 250 kW/m 2 and this value is currently adopted in EN 1991-1-2 [ 4]. These all likely relate back to Morgan and Hansell’s 260 kW/m 2 value.
Yuen and Chow [ 34] revisited Morgan and Hansell’s work on offices to propose a new method of selecting design fires. To capture uncertainty associated with HRRPUA, a uniform distribution was proposed which ranged from 90 kW/m 2 to 360 kW/m 2. To obtain these upper and lower bounds, the work of Theobald [ 12] was again referenced. The same method of Morgan and Hansell was applied, with an assumed fire load per unit area of 57 kg/m 2, instead proposing limits from the ‘normal’ and ‘high’ ratios of fuel surface to fuel mass (shown in Fig.  2).
In separate work, Hietaniemi and Mikkola [ 35] collated information on a series of office workstation experiments by Madrzykowski [ 36], Madrzykowski and Watson [ 37], Kakegawa et al. [ 38], Ohlemiller et al. [ 39], where it was summarised that the maximum HRRPUA for these experiments ranged from 820 kW/m 2 to 1799 kW/m 2 with an average maximum ( \( \overline{{\dot{Q}''}}_{max} \)) of 1156 kW/m 2. In some instances, the HRRPUA represented a value averaged across the area of an entire burning enclosure (for example a 6.3 m by 6.3 m room for Kakegawa et al. [ 38].), and in others it related to the burning area of a single cubicle, or to the burning area of single items only. Given the different experimental conditions of the sources of data, the range of HRRPUA values for these fires is not necessarily representative of the same calculation methods and application (e.g. a single item versus an enclosure), resulting in potential inconsistencies across the dataset.

3.4 Hotel Rooms

Alongside their work on fires in offices, Hansell and Morgan [ 40] proposed fire characteristics for hotel bedrooms, with a recommended HRRPUA of 249 kW/m 2. This was determined from a survey of fire loads in three bedrooms for a hotel near Heathrow Airport, referenced as a private communication, in combination with work by Pettersson et al. [ 41] on the magnitude of fuel loads in hotels. To determine the HRRPUA, Hansell and Morgan adopted a fuel load density of 357 MJ/m 2 for the worst-case of the three surveyed hotel bedrooms, considered equivalent to 19.2 kg/m 2 for wood load fuel density assuming a heat of combustion of 18.6 MJ/kg. This fuel load density aligned with the 85 th percentile of fuel loads observed by Pettersson et al. The time for the fuel to burn was derived from the work of Thomas and Theobald [ 42] on the burning rates and durations of fires, in an appendix to Theobald’s work on industrial fires [ 12], where it was proposed that the following equation be adopted:
$$ t = 590 f^{0.3} $$
(6)
where \( t \)(s) is the total duration of burning and \( f \) is the fuel load density (kg/m 2). This relationship, reproduced in Fig.  4, was derived from the ten industrial fire incidents discussed by Theobald. Using this relationship, a fuel load density of 19.2 kg/m 2 results in a predicted burning duration of 1432 s (23.9 min), producing a HRRPUA of 249 kW/m 2 for 357 MJ/m 2. Although not discussed by Hansell and Morgan, applying the same method for the given hotel bedroom with the lowest fuel load density (10.2 kg/m 2, 190 MJ/m 2) results in a HRRPUA of 160 kW/m 2. In their subsequent revisiting of their work, discussed previously for HRRPUA values of offices, Morgan and Hansell proposed an adjusted HRRPUA for hotel bedrooms of 80 kW/m 2 to be applied across the entire floor area of the enclosure of fire origin [ 29].
In the above Thomas and Theobald method, fire duration is correlated with fire load density, not total fire load. As such, the correlation is independent of the enclosure size. The fire incidents considered by Theobald had enclosure areas which ranged from 90 m 2 to 10,200 m 2, with fuel areas ranging from 6 m 2 to 4000 m 2. For larger enclosures, the total fire duration will be heavily influenced by the time taken for the fire to spread to involve all fuel within the space. It is also improbable that all fuel burned near simultaneously, i.e. a fire that develops to flashover. Stern-Gottfried and Rein [ 43] note in their literature review of travelling fires that characteristic burning time (i.e. burning time per m 2 of fuel) can be in the region of 19 min to 30 min, a time period much less than many of the fire durations documented by Theobald and given in Fig.  4 (up to 210 min). It may be that, in the context of the fires observed by Theobald, the total burning duration across the floor area was extended due to the occurrence of travelling fires. There are therefore limitations in adopting the relationship given by Thomas and Theobald outside of the context of the original industrial fire incidents.
Hansell and Morgan’s value of 249 kW/m 2 is referenced in NFPA 92B [ 16] and the most recent 2018 edition of NFPA 92 [ 44] for a recommended HRRPUA for hotel rooms. This value was subsequently referenced and adopted in PD 7974-1:2003 [ 1], with a recommended HRRPUA of 250 kW/m 2, again making the inaccurate caveat relating to the information being of US origin.
BR 368 [ 19] recommends a HRRPUA of 250 kW/m 2 for hotel bedrooms where sprinkler protection is provided and the fire area is limited to 2 m 2, or alternatively 100 kW/m 2 where there are no sprinklers and the fire area is assumed as the entire bedroom enclosure. Although the exact origin of the 100 kW/m 2 value is not specified, it appears to broadly align with both Morgan and Hansell’s adjusted 80 kW/m 2 value and a design fire load of 81.6 MJ/m 2 described by Pettersson et al. [ 41], recommended to be applied to the total room floor area. Applying the same method described by Morgan and Hansell [ 40] above for the Pettersson et al. 81.6 MJ/m 2 fuel results in an equivalent wood fuel load fuel density of 4.4 kg/m 2. Assuming an 18.6 MJ/kg heat of combustion previously adopted by Hansell and Morgan in turn produces a HRRPUA of 88 kW/m 2.

3.5 Residential

For residential design, EN 1991-1-2 [ 4] recommends a HRRPUA of 250 kW/m 2, as did TM19:1995  [ 25]. In proposing a HRRPUA of 290 kW/m 2 for offices, Law [ 27] also noted that this value may be applied for residential occupancies. The adoption of such values is illustrated by Holborn et al. [ 45] who analysed fire sizes and fire growth rates using data from fire investigations, using a value of 250 kW/m 2 for residential fires, referencing both NFPA 92B [ 16] and DD 240-1:1997 [ 24].
Fang and Breese [ 46] undertook sixteen burnout experiments to investigate fires in residential occupancies. These were performed in two rooms of 3.3 m wide, 3.3 m long and 2.4 m high, and 3.3 m wide, 4.9 m long and 2.4 m high, respectively. Included in the rooms were household furniture, linings and interior finishes described as “typical of actual occupancies”. Using the maximum HRR in the enclosure combined with the total enclosure floor area, the maximum HRRPUA ranged from 320 kW/m 2 to 570 kW/m 2 for the experiments. This work is referenced in Klote and Milke’s ‘Principles of Smoke Management’ [ 47], where they note that Fang and Breese determined a similar average maximum HRRPUA for residential occupancies as Morgan’s 500 kW/m 2 value for retail occupancies. However, the latter was determined across a limited floor area while the former was representative across the complete enclosure floor area.
Hietaniemi and Mikkola [ 35] simulated a series of residential fires, adopting statistical distributions for mass and the heat of combustion of furniture items located in hypothetical residential room layouts. Furniture items included sofas, armchairs, coffee tables, televisions, etc. Using the results of the simulations, Gumbel distributions were proposed which differed depending on the room of fire origin. The distribution parameters (α, β) for these distributions, as well as the average fire load density and equivalent HRRPUA, are given in Table  3.
Table 3
Fire load density and HRRPUA for different residential room types.
From Hietaniemi and Mikkola [ 35]
Room
Fire load density
HRRPUA
Living room
α = 405 MJ/m 2
α = 565 kW/m 2
 
β = 96 MJ/m 2
β = 134 kW/m 2
 
Average = 460 MJ/m 2
Average = 642 kW/m 2
Bedroom
α = 522 MJ/m 2
α = 805 kW/m 2
 
β = 233 MJ/m 2
β = 191 kW/m 2
 
Average = 656 MJ/m 2
Average = 805 kW/m 2
Kitchen
α = 613 MJ/m 2
α = 816 kW/m 2
 
β = 89 MJ/m 2
β = 194 kW/m 2
 
Average = 665 MJ/m 2
Average = 928 kW/m 2
Whole apartment
α = 467 MJ/m 2
α = 624 kW/m 2
 
β = 72 MJ/m 2
β = 148 kW/m 2
 
Average = 509 MJ/m 2
Average = 710 kW/m 2

3.6 Other Types

Early work by Klote and Milke [ 48] on the design of smoke management systems does not provide specific advice for HRRPUA. Subsequently Klote et al. [ 49] refer to BR 368 in the context of retail, office and library spaces, although they recommend that a value of 230 kW/m 2 be used for any space “where the major fuels would be transient fuels” and 650 kW/m 2 be considered for spaces with furniture or other combustible materials but with no further substantiation. Thus, spaces with furniture could potentially refer to both office and residential type occupancies. Klote et al. note that this approach is “rough” and that more detailed analysis can result in different design fires.
Fleischmann [ 50] provided ‘general’ recommended values for HRRPUA for use in fire safety design. To determine these values, Fleischmann considered average and maximum HRRPUA values recorded for polyurethane foam-fabric composites commonly found in upholstered furniture, from experiments undertaken by Denize [ 51]. For these fires, the average HRRPUA ( \( \overline{{\dot{Q}''}} \)) ranged from 165 kW/m 2 to 441 kW/m 2, with the maximum HRRPUA ranging from 262 kW/m 2 to 470 kW/m 2. Also discussed were much larger HRRPUA values determined for large-scale pool fires (maximum ranging from 498 kW/m 2 to 4505 kW/m 2) and stacked commodities (245 kW/m 2 to 3118 kW/m 2). The latter was determined from a summary by Babrauskas [ 52] provided in the second edition of the SFPE Handbook of Fire Protection Engineering, in turn taken from work by Alpert and Ward [ 53] and Delichatsios [ 54].
Alpert and Ward [ 53] summarised a series of stacked commodity experiments with the HRRPUA ranging from 35 Btu/ft 2/s to 1500 Btu/ft 2/s (400 kW/m 2 to 17,000 kW/m 2), although it was not explicitly stated whether these represent average or maximum values. Similarly, Delichatsios [ 54] discussed ‘small-scale’ experiments of different palletised commodities, with each experiment covering a floor area of approximately 6.3 m 2. The maximum HRR from these experiments ranged from 1.09 × 10 6 Btu/min to 7.06 × 10 6 Btu/min, resulting in HRRPUA values ranging from 3000 kW/m 2 to 20,000 kW/m 2. The ‘Valorisation Project: Natural Fire Safety Concept’ [ 55] recommends a HRRPUA of 1250 kW/m 2 to 6000 kW/m 2 for stacked commodities, depending on the stacked height and content.
A series of trial building cases were simulated by Fleischmann [ 50] to consider the sensitivity of varying HRRPUA in computational fluid dynamics software Fire Dynamics Simulator (FDS). Using the context of experimental values and FDS simulations, Fleischmann concluded with a recommended range of HRRPUA from 500 kW/m 2 to 1000 kW/m 2 for non-storage occupancies and 1000 kW/m 2 to 2500 kW/m 2 for storage occupancies. These recommended ranges were adopted in C/VM2 [ 11], specifying that “a range is provided… to accommodate different HRR and mesh sizes”.

4 Conclusions and Recommendations

This review has highlighted how many of the design values in provided UK guidance for HRRPUA are ultimately derived from a small number of fire incidents and experiments described by Theobald [ 12, 13] in the 1970s. These fire incidents occurred in storage buildings, factories, workshops and a hospital research unit and were considered in combination with experimental data for wood cribs. The data was however subsequently adapted in various forms to consider shops and retail buildings, offices, hotel rooms and residential buildings. Variations in recommended values have occurred over time due to adjustments or differences in interpretation from various authors, including Law [ 27] and Morgan and Hansell [ 28, 29, 40]. Following this, proposed values were adopted in PD 7974-1:2003 [ 1], BS 7346-4:2003 [ 33], NFPA 92B [ 16] (and subsequent revisions [ 23, 44]), BR 368 [ 19] and CIBSE Guide E [ 5].
The review has attempted to highlight additional data available which relates specifically to the discussed occupancies and building types, although in certain instances they may still relate back to the work of Theobald. In the absence of further information, it is proposed that the ranges given in Table  4 may be adopted. These characterise the HRRPUA for either a specified average or maximum HRR for a representative fire footprint, and the selection of an applicable HRRPUA within these bounds will be dependent on the arrangement and quantity of anticipated fuel load. It is intended that these values will be incorporated into the revised edition of PD 7974-1. It is acknowledged that providing a range of values is less convenient than the single fixed values given currently in PD 7974-1:2003, in that fixed values can be more easily adopted and require limited consideration. Therefore, in adopting the revised values, designers will need to take greater care in considering the relevant source material in the context of the design problem and fire safety objectives.
Table 4
Identified HRRPUA ranges available from literature
Occupancy
HRRPUA (kW/m 2)
References
Shops
270–1200 (maximum)
Ghosh [ 32], Hinkley [ 20], Law [ 30] and Morgan et al. [ 19]
Offices
150–650 (maximum)
Ghosh [ 32]
Hotel rooms
250 (average)
Hansell and Morgan [ 40]
Residential
320–570 (maximum)
Fang and Breese [ 46]
Industrial
90–620 (average)
Theobald [ 12]
Storage/stacked commodities
400–20,000 (maximum)
Alpert and Ward [ 53] and Delichatsios [ 54]
The range of values given in Table  4 provides an opportunity for HRRPUA to be considered probabilistically, but distributions for such values would require further research intended to be undertaken by the authors of this paper. In addition, it would be beneficial for the recommended HRRPUA design values to be revisited in the context of modern building environments and their associated fuel loads.

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