Research of natural wood combustion and charring processes.
Maciulaitis, Romualdas ; Jefimovas, Andrejus ; Zdanevicius, Povilas 等
1. Introduction
Wood is a material used in many areas of engineering and
technology. It is used for manufacturing of building structures and
items, furniture and its parts, chipboards, plywood, flitch, paper,
cardboard and etc. In chemical industry, it is a suitable raw material
for production of a perfect absorbent charcoal as well as products of
its pyrolysis hydrocarbons, which are used to make gaseous fuel; and in
case of further processing, it can be used for synthesis of organic
solvents and even monomers. Wood is a fibrous material with a
directional structure of capillaries and pores clearly developed in the
vertical direction of the tree growth (anisotropy of properties), which
is fed with water and fertilizers (especially mineral salts) taken from
soil through tree roots, and which with the help of chlorophyll ensures
photosynthesis as well as uptake of nitrogen from air. Such is the
abstract summarised picture of wood synthesis (Jefimovas 2011).
Wood Characteristics
Wood is a unique anisotropic porous material of vegetable origin,
where the volume of pores takes 50-75% of the wood volume. It has a
number of advantages in comparison with other materials: it is solid and
may bear high loads. At the same time it is light, has low heat
conductivity, is easy to process and etc. However, there are some
important drawbacks of wood, such as absorption of large quantities of
water, decay, deformation under the influence of humidity, and most
importantly--flammability (Sniuolis 2004).
The main mass of completely dry wood (about 99%) consists of
organic substances. In addition to organic substances, wood contains
some minerals (salts), which turn to ash after wood is burnt.
Irrespective of tree species, completely dry wood has 49-50% of carbon,
43-44% of oxygen, about 6% of hydrogen and 0.1-0.3% of nitrogen. Carbon,
hydrogen and oxygen form complex organic substances--cellulose,
hemicellulose, lignin and the so-called extractive substances (resins,
gums, fat, tannides, pectins, etc.) (Jakimavicius 2003).
Peculiarities of Thermal Decomposition and Combustion of Wood
Depending on botanic origin, growing conditions, species and the
age of wood, the ratio of wood components is approximately as follows:
50% of cellulose, 25% of hemicellulose, 25% of lignin. Wood composing
substances have a varied structure and different thermal resistance
(Drysdale 1998).
Referring to the data of thermographic research obtained by various
authors, the thermal decomposition of wood components takes place at
different temperatures; however, different combustion media and wood
species are also used. As described by Roberts (1970), decomposition
(under vacuum conditions) takes place at the following temperatures:
hemicellulose--200-260[degrees]C; cellulose--240-350 [degrees]C;
lignin--280-500[degrees]C.
Hemicellulose and cellulose have a tendency of thermal
decomposition, whereas lignin is resistant to thermal decomposition and
its pyrolysis results in a char layer. Thermal decomposition of wood can
take place in case of free and partial supply of atmospheric oxygen. It
can also take place in case of oxygen shortage in the atmosphere.
Considering that a char layer results on the surface of wood, it should
be said that wood combustion is a particular process. During combustion,
this layer forms a tight shell, which impedes heat entrance into deeper
undecomposed layers of material and blocks free release of volatile
products into the atmosphere in the course of thermal decomposition.
Such behaviour at high temperatures restricts fire spreading for a
certain period of time. However, it is important that thermal
decomposition continues under the charred layer of wood, which may be
very dangerous as oxygen amounts to 43-44% in the chemical composition
of wood (Drysdale 1998). The products of thermal decomposition can
instigate smouldering. Shortly, formation of gas during smouldering can
cause the pressure to increase so high that char layer can break
resulting in flaming up (Jaskolowski 2001).
Usually, two methods to model pyrolysis of wood (biomass) are used
(Turner et al. 2010).
The first method is based on prediction taking into account
behaviour of wood, which depends on its main components according to the
equation
(Koufopanos et al. 1989): wood = % cellulose + % hemicellulose + %
lignin, where (%) is the amount of wood components.
The second method called the "Lumped Parameter Approach"
is based on classification of products that form during decomposition of
wood (biomass), having in mind that there is one homogenous element
consisting of dense products (resins), uncondensed products (gas) and
solid bodies (char). As a basis, the model uses three parallel initial
reactions when wood decomposes into char, resin and gas, however, there
are also secondary reactions taking place when resin decomposes into
char and gas (Turner et al. 2010). It should be emphasized that both
methods, in our opinion, only supplement each other without being
inconsistent.
Combustion as a phenomenon can take various forms, however in the
end they all come down to a chemical reaction between a flammable
substance and air. Proper use of this reaction results in numerous
benefits (power or heat sources), but if uncontrolled, it can cause both
serious material damage and human death (Drysdale 1998). Fire is a
complex phenomenon: its course and effects depend on many interrelated
factors. In case of fire, the most noticeable feature in wooden
buildings or buildings made of wooden structures is charring of wooden
items. This feature is important in identifying the cause of fire,
therefore, it is necessary to relate charring of wooden items and
structures with particular significant effects of fire, such as its
duration or temperature (Lipinskas 2006). Wood is a complex material;
its pyrolysis and combustion is influenced by various characteristics,
in addition to that, the dynamics of fire development is determined by
various factors, and all of the listed circumstances make it difficult
to determine combustion duration and temperature of wood.
Thermographic Analysis
The thermographic analysis is used to study mechanism and kinetics
of thermal decomposition and combustion of natural wood unimpregnated
with fire retardants and its products (Fu et al. 2011). The results of
thermographic research carried out by other authors suggest that
decomposition of materials due to combustion is affected by substance
(tree) species (Bednarek et al. 2009) and the temperature rise rate
(Hagen et al. 2009; Otero et al. 2007; Yorulmaz, Atimtay 2009; Helsen et
al. 1999) as well as the environment (oxidizing, reducing gas), in which
the substance is being studied (Fu et al. 2011; Zhaosheng et al. 2009)
simulating conditions, which may occur during a fire.
Peculiarities of Charring
Under fire conditions, wood experiences pyrolysis (thermal
destruction) (Fig. 1). Pyrolytic gas typically flames up as soon as it
rises up to the surface of charred wood. Further combustion and
mechanical degradation of char finally destroys or splits off the outer
layer of char. The charring rate is in fact linearly dependent on time.
The temperature of char layer formation averages 300[degrees]C
(Lipinskas, Maciulaitis 2005).
During transformation of wood into char and combustible gas,
products of pyrolysis are substantially dependent on wood density.
Dependence of the charring rate on the unprotected wood density is also
emphasized in Eurocode 5 (LST EN 1995-1-2:2005). The standard assigns
the uniform charring rate for softwood with the density of [greater than
or equal to] 290 kg/[m.sup.3] and two ranges for hardwood with the
density of 290 kg/[m.sup.3] and [greater than or equal to] 450
kg/[m.sup.3].
Charring rate is influenced by wood moisture, surface orientation,
air movement, thermal load, gaps and etc. Heavy-timber or similar wood
that has no gaps or joints will char at similar rates to those found in
fire-resistance furnace tests--roughly 0.5-0.8 mm/min. Much higher
charring rates apply to floors and any other wood members where charring
is affected by the presence of gaps or joints. Laboratory tests show a
typical charring rate for floorboards of 1.5 mm/min, but under numerous
conditions the values are much larger. Even small gaps between boards,
if they are not blocked or otherwise protected, raise the charthrough
rate to 3-8 mm/min (Babrauskas 2005).
[FIGURE 1 OMITTED]
Charring of wood is closely related to the combustion
characteristics of wood components--hemicellulose, cellulose and
lignin--which influence formation of char. The majority of char is
formed during combustion of lignin (Drysdale 1998).
Charring of wood is also dependent on the heat load applied on the
structural surface and change in the value of heat load depending on the
length of thermal exposure (Taubkin 1999). In our opinion, based on the
data provided in Fig. 2, it can be interpreted that the uniform charring
depth may be obtained by exposing wood to different temperatures for
various periods of time. However, the uniform charring depth can also
result from wood exposure to different conditions of pyrolysis. It is
therefore not appropriate to estimate combustion duration, which is used
for identification of the fire source, only by charring depth. In
Lithuania, in order to determine the charring time of wooden structures,
the charring depth and electrical resistance of char are measured. The
charring time of wooden structures is calculated according to the
measured values of depth and electrical resistance and using the
dependencies (Lipinskas 2006) as well as taking into account the
thickness and moisture of the original wooden structure. According to
this time, the focus of fire is forecasted. However, this measuring
method is not widespread, as it requires special equipment.
[FIGURE 2 OMITTED]
The aim of the work is to investigate how the calorific value of
char resulting in wood of different species at different temperature
changes and what effect conditions of gaseous environment have on
peculiarities of wood combustion using the widespread method of a
calorimetric bomb.
2. Materials tested and testing methods
2.1. Tested materials and their characteristics
For experiments, softwood (pine, fir) and hardwood (aspen, oak) was
used. Before tests, wood was conditioned according to the requirements
of LST EN 13238:2010. The following average values of wood density were
determined: pine--545 kg/[m.sup.3], fir--513 kg/[m.sup.3], aspen--506
kg/[m.sup.3], oak--654 kg/[m.sup.3]. The moisture content in the samples
of oak was 12-15%, aspen--12-14%, fir--11-12%, pine--11-13%, the
moisture content was determined using a moister meter "HPM
2000".
2.2. The special one-side heating equipment
To identify charring peculiarities in wood of different species at
different temperatures, special one-side heating equipment was used
(Lukosius 2004; Lipinskas, Maciulaitis 2005). This equipment ensures the
simulated one-side heating of the test sample up to 950[degrees]C. The
equipment consists of one-side heating device, thermo-controller,
instrumentation and equipment for recording the readings (Fig. 3).
[FIGURE 3 OMITTED]
The principle of the experiment is to heat the sample on one side
based on dependency of temperature depending on time specified in and
regulated by LST EN 1363-1:2000.
For the purposes of testing, the above-described equipment ensured
the chosen heat load. The heat load on the structural surface and change
in the load value depending on the heating mode undoubtedly have an
influence on temperature distribution over the cross-section of the
structure.
The chosen basic heat load was regulated by the standard dependency
of temperature depending on time (Fig. 4), which simulated the
post-flashover stage. Fire resistance tests of structures were carried
out in various countries worldwide using the mentioned dependency (in
case of the chosen dependency between temperature and time, in the
beginning the temperature increases at about 100[degrees]C/min).
The mathematical expression of the standard temperature-time curve
(Fig. 4) is as follows (1):
T = 345lg(8t +1) + 20, (1)
where: T--average temperature in the heating chamber, [degrees]C;
t--test duration, min.
Different rate of the temperature change in the heating chamber is
important in several respects. The high temperature reached at high rate
simulates the environmental conditions, which are the most unfavourable
for the material being tested, when a continuous process of heat
propagation influencing physical and chemical transformations in the
material begins.
[FIGURE 4 OMITTED]
The height and width of the wood samples was 210 mm and 150 mm
respectively, the thickness varied from 47 mm to 59 mm (Fig. 5).
[FIGURE 5 OMITTED]
Using the described equipment, the wood samples were exposed to
heating for a specific pre-set period of time t, min (5, 10, 20, 30 and
45). During this period, the average heating temperatures shown in Table
1 were reached, after this period the sample was removed from the
chamber followed by its extinguishing with a fire blanket.
[FIGURE 6 OMITTED]
After the sample cooled down, the charring depth H, mm of wood
under research was measured using sliding callipers. The measurements of
charring depth were taken as shown in Fig. 6. The depth was measured in
the surface part of the sample and the measurement result was the
average of at least 3 measurements. Three samples were heated for each
specified period of time. Once the charring depth was measured, the
charring rate of wood p, mm/min was calculated using the following Eq.
(2):
[beta] = H/[tau] (2)
where: [beta]--charring rate of wood, mm/min; [tau]--combustion
time, min, H--charring depth, mm.
The char formed during these tests was used for further research.
For that purpose, the layer of resulting char of up to 5 mm thick was
scraped off with a knife.
2.3. Calorimetric bomb method
Research of the resulting char was followed up by the test method
described in LST EN ISO 1716:2010 Reaction to fire tests for
products--Determination of the gross heat of combustion (calorific
value), which is applied to determine reaction to fire classes A1 and A2
according to LST EN 13501-1:2007. By performing this test, the gross
calorific value and net calorific value can be determined. The said
values are also known as the higher and lower heating values
respectively. The gross calorific value (or higher heating value) is
defined as the amount of heat released by combusting the product and the
entire water component is in liquid state at the end of combustion. The
net calorific value (or lower heating value) is defined as the amount of
heat released by combusting and the entire water component is in vapour
state at the end of combustion. During research the gross calorific
potential for char was determined, which hereinafter is referred to as
the calorific value and marked as PCS. The essence of this test is to
determine how much heat is released by completely burnt wood or
charcoal. For that purpose, special equipment (Fig. 7) was used. This
equipment consists of a stirrer, thermometer, calorimeter vessel, casing
and a combustion chamber (calorimetric bomb) (Fig. 8).
[FIGURE 7 OMITTED]
[FIGURE 8 OMITTED]
During testing, the mixer is rotated at a constant rate. In order
to avoid heat transfer from and to the calorimeter, the driving axle of
the mixer is equipped with a thermally insulated element located in the
gasket between the jacket and jacket cover. Magnetic mixing device can
also be used. When the temperature rise in the calorimeter vessel does
not exceed 0.01[degrees]C per 10 minutes, the sample is ignited and the
changes in temperature are recorded against the time scale. Standard
temperature changes against the time scale and the characteristic points
are shown in Fig. 9.
[FIGURE 9 OMITTED]
The course of research was as follows: any dirt was brushed off
from the sample of charred wood and up to 5 mm of the top char layer was
scraped with a knife from different points of the sample. Taken char was
ground with a pestle in the mortar. The ground char was placed into the
open vessel. The vessel with the char was conditioned to the constant
mass in a laboratory furnace at the temperature of approx. 60[degrees]C.
0.5-1.0 g of crushed charcoal--which was conditioned to the
constant mass--was placed to the glassy crucible (dimensions: diameter
of 25 mm, height of 19 mm, and wall thickness of 1.5 mm). Specimens were
weighed using a high accuracy weighing-scale to the precision of +/-
0.0001 g. The crucible was placed into the calorimeter bomb. A fuse wire
was attached to the calorimeter bomb electrodes (10 cm length, 0.0055 g
weight) in such manner that the coil formed in the centre of the bomb
contacted the specimen contained in the crucible. The calorimeter bomb
was placed in its steel body and screwed tightly. Then the calorimeter
bomb vessel was filled with pressurised oxygen (99.5% purity) until the
pressure of 3.0-3.5 MPa was reached. Simultaneously, the calorimeter
vessel was filled with distilled water until the weight of 3.4 kg. The
calorimeter bomb was placed into the water of stable temperature in such
manner that the top of the bomb was slightly submerged in the water.
Fuse cables were attached to the electrodes and the jacket cover was
closed. All testing equipment was controlled via the computer. Using a
software application, the necessary data are entered into the computer:
specimen weight, including fuse wire weight.
Once the test was completed, the jacket cover was opened, the
calorimeter bomb was removed and dried, and the test results and
temperature curve were recorded on the computer screen. The calorific
value was calculated by the software installed in the computer.
Three tests were performed with each sample of resulting char. Each
three samples were heated for the same period of time, therefore the
arithmetic average of nine samples was considered to be the calorific
value of char.
The calorific value of wood (oak, aspen, pine and fir) dried to the
constant mass in a laboratory drying chamber at the temperature of
60[degrees]C was also determined. In that case, the tests were conducted
with wood chip tablets and the calorific value was accounted for as the
arithmetic average of values obtained during three tests.
2.4. Termogravimetric analysis
The thermografic analysis was performed using the thermogravimetric
analyser "Linseis STA PT-1600". The analysis was carried out
under temperatures ranging from 25[degrees]C to 1000[degrees]C. The
temperature rise rate was 10[degrees]C/min. The analysis was performed
in gaseous environments of nitrogen and ambient air. The flow of
nitrogen and air was 0.15 l/min. Pieces of wood (oak and pine) weighing
9.36-10.17 mg were used for testing.
3. Research results and discussion
The results of charring research, which was carried out with
different species of wood using one-side heating chamber, are shown in
Figs 10 and 11.
[FIGURE 10 OMITTED]
Fig. 10 reflects the thickness of char that forms during heating of
wood (oak, aspen, pine and fir) in a chamber for a different period of
time (the mean temperature values reached during this period of time are
presented in Table 1).
Irrespective of heating time, the smallest thickness of char
resulted in oak: in 5 minutes of heating, the char layer reached 1.0 mm
in thickness; while after 45 minutes--19.7 mm. Heating of oak resulted
in the thickness of char that was 1.7-2.8 times less than that of aspen
(after 5 min--1.7 mm, after 10 min--35.7 mm). The difference in the
resulting char thickness can be explained by different density of wood
as the average density of oak used for testing was 654 kg/[m.sup.3] and
that of aspen - 506 kg/[m.sup.3].
[FIGURE 11 OMITTED]
The values of the charring rate for the wood samples are presented
in Fig. 11. The lowest charring rate was characteristic to oak samples.
The exception was oak samples where after 10 minutes of heating the
charring rate was slightly lower than that after 5 minutes, which can be
explained by greater variation of density. If heated for 20 minutes, the
charring rate significantly increased and reached 0.35 mm/min. If heated
for 30 and 45 minutes, the difference in the charring rate was as little
as 0.1; after 30 min--0.43 mm/min and after 45 min 0.44 mm/min.
In comparison to oak, the charring rate of aspen samples as well as
those of pine and fir were higher. If heated for 5 minutes, the charring
rate of aspen and pine was 0.33 mm/min and that of fir was 0.27 mm/min.
After 10 minutes of heating, differently than in case of oak wood (0.17
mm/min), the charring rate of aspen (0.47 mm/min), fir (0.14 mm/min) and
pine (0.50 mm/min) wood increased evidently. If heated for 20, 30 and 45
minutes, the difference in the charring rates were not that big:
aspen--0.70-0.76-0.79 mm/min, pine--0.73-0.74-0.76 mm/min,
fir--0.67-0.72-0.77 mm/min, respectively.
The average charring rate of oak was 0.32 mm/min, fir--0.58 mm/min,
pine--0.60 mm/min, aspen--0.61 mm/min. The average charring rate of
aspen was 48% higher than that of oak.
After 45 minutes of heating, the charring rate of oak was 0.44
mm/min, aspen--0.79 mm/min, fir--0.77 mm/min, pine--0.76 mm/min. The
values of the charring rates for hardwood provided in Eurocode 5 (LST EN
1995-1-2:2005) were 0.50-0.55 mm/min, for soft wood--0.65-0.80 mm/min.
Thus, not all values of the charring rate obtained during tests matched
the ones provided in the Eurocode 5 (LST EN 1995-1-2:2005).
[FIGURE 12 OMITTED]
The regression analysis of the charring rate for different species
of wood was made, equations (3)-(6) were obtained, the predicted values
of the charring rate calculated using the equations (3)-(6) are
presented in Fig. 12. For derivation of equations, two parameters were
chosen - charring duration and charring rate. The equations were derived
using all experimental data of the charring process obtained for
different species of wood.
The regression analysis resulted in the highest value of the
correlation coefficient R = 0.9597, which was obtained in predicting the
charring rate of aspen, fir R = 0.9515, oak--R = 0.9424 and pine--R =
0.9240, which was the lowest value.
To predict the charring rate of different species of wood (oak,
aspen, pine and fir), the following equations (3)-(6) can be used:
Oak: [Y.sub.a] = (0.1458 + 0.0058X)* ([Y.sub.a] [less than or equal
to] 0.3174) + (0.3510 + 0.0021X)** ([Y.sub.a] > 0.3174); (3)
Aspen: [Y.sub.d] = (0.2000 + 0.0267X)* ([Y.sub.d] [less than or
equal to] 0.6097) + (0.6352 + 0.0036X)** ([Y.sub.d] > 0.6097); (4)
Pine: [Y.sub.p] = (0.1667 + 0.0333X)* ([Y.sub.p] [less than or
equal to] 0.6148) + (0.7092 + 0.0012X)** ([Y.sub.p] > 0.6148); (5)
Fir: [Y.sub.e] = (0.0667 + 0.04X)* ([Y.sub.e] [less than or equal
to] 0.5785) + (0.5908 + 0,0041X)** ([Y.sub.e] > 0.5785), (6)
where: *--the equation is applicable when the charring rate is
[less than or equal to] than the indicated specific value. From Fig. 12
it can be seen that this equation will be applicable when the charring
duration is 5-10 min; **--the equation is applicable when the charring
rate is > than the indicated specific value. From Fig. 12 it can be
seen that this equation will be applicable when the charring duration is
20-45 min.
Dependency of the calorific value of char resulting from different
species of wood depending on the heating time is provided in Fig. 13.
[FIGURE 13 OMITTED]
The calorific value of char resulting from oak wood reached 26.1
MJ/kg after 5 minutes of heating. After 10 minutes of heating, the
calorific value increased up to 29.5 MJ/kg; after 20, 30 and 45 minutes
of heating, the calorific values of char were more or less the same;
after 20 min--33.5 MJ/kg, after 30 min--33.9 MJ/kg, after 45 min--34.0
MJ/kg. The maximum calorific value of char was reached after 45 minutes
of heating. Even after 5 minutes of heating, the calorific value of char
was higher than the value of the wood itself, the determined calorific
value of dry oak was 18.9 MJ/kg.
The calorific value of char resulting from aspen wood was 25.3
MJ/kg after 5 minutes of heating; after 10 min--30.8 MJ/kg; after 20, 30
and 45 minutes of heating, the calorific values were similar--33.7
MJ/kg, 33.7 MJ/kg and 33.8 MJ/kg, respectively. The calorific value of
dry aspen wood was 18.7 MJ/kg.
The calorific value of char resulting from pine wood was 26.5 MJ/kg
after 5 minutes of heating; after 10 min 30.9 MJ/kg; after 20, 30 and 45
minutes of heating, the calorific values were 34.1 MJ/kg, 34.1 MJ/kg and
34.0 MJ/kg, respectively. The calorific value of dry pine wood was 20.0
MJ/kg.
The calorific value of char resulting from pine wood was 20.5 MJ/kg
after 5 minutes of heating; and the value of dry fir wood amounted to
19.5 MJ/kg, with the difference of only 1.0 MJ/kg, while for some
species the difference in calorific values amounted to 6.5-7.2 MJ/kg.
After 10 minutes of heating, the calorific value of fir char was 29.8
MJ/kg; after 20 min--33.5 MJ/kg; after 30 min--33.6 MJ/kg; after 45
min--33.6 MJ/kg.
After 5 minutes of heating, the highest calorific value was of char
resulting from pine wood (26.5 MJ/kg), the lowest was that of fir (20.5
MJ/kg), with the difference between the highest and the lowest values
amounting to 6 MJ/kg. After 10, 20, 30 and 45 minutes of heating, the
differences between the lowest and the highest values were small: after
10 min--1.4 MJ/kg, after 20 min--0.6 MJ/kg, after 30 min--0.5 MJ/kg, and
after 45 min--0.4 MJ/kg.
The calorific value of char resulting from different species of
wood after they were heated for 20 minutes and longer (the average
heating temperature reaching [greater than or equal to] 780[degrees]C)
were within the range of 33.5 MJ/kg and 34.1 MJ/kg. This small change in
the calorific values at the temperature higher than 780[degrees]C can be
explained by the data obtained by another author (Demirbas 2001).
According to Demirbas (2001), when carbonising fir wood to the
temperature of 777[degrees]C, the resulting char residue in the
elemental composition is 91.2% of carbon, 1.5% of hydrogen, 4.0% of
oxygen, 0.1% of nitrogen, and 3.1% of ash; and if heated to the
temperature of 877[degrees]C--92.1% of carbon, 1.2% of hydrogen, 3.3% of
oxygen, 0.1% of nitrogen, and 3.3% of ash. The composition of fir wood
before tests was: 51.9% of carbon, 6.1% of hydrogen, 40.9% of oxygen,
0.3% of nitrogen. If wood is heated at the temperature above
780[degrees]C, changes in the elemental composition of the resulting
char residue are slight, therefore the differences between the calorific
values are small and the calorific value depends namely on the amount of
carbon, hydrogen and oxygen in the material. The theoretical calorific
value of lignocellulosic materials is calculated according to the
formula (7) (Demirbas et al. 1997):
HHV = 0.335(C) +1.423(H) - 0.154(0), (7)
where: HHV--calorific value (MJ/kg); C, H, O--amount of elements
(carbon, hydrogen, oxygen) in the material (%).
The ratio of the calorific values for char resulting from different
species of wood and dry wood are provided in Fig. 14. The ratio was
calculated by dividing the calorific value of char resulting from wood
after heating it for a definite period of time by the determined
calorific value of the same species of dry wood.
[FIGURE 14 OMITTED]
The smallest ratio of the calorific values is between char
resulting from fir wood after heating it for 5 minutes and dry fir wood,
namely--1.05. The ratio between the calorific values of char resulting
from other species of wood after heating for 5 minutes and dry wood is
1.331.38. The smallest ratio of the calorific values is between char
resulting from wood after heating it for 10 minutes as well as that of
fir wood--1.53. The ratio between the calorific values of char resulting
from other species of wood after heating for 10 minutes and dry wood is
1.55-1.64.
If wood is heated for 20 minutes and longer, similarities between
fir and pine as well as between oak and aspen, that is, between softwood
and hardwood, emerge. The values of the calorific value ratios for fir
char and wood become practically equal to the ratio values for pine. The
same situation is between oak and aspen. The values of the calorific
value ratios for hardwood char and wood are higher than that of
softwood.
Using a calorimetric bomb method, it is possible to determine the
amount of heat released by the completely burnt material. However, the
amount of this heat is different from the heat, which would be emitted
during a fire (Heskestad 2006; Heskestad, Delichatsios 1989). There are
two wood burning mechanisms: 1) pyrolysing combustible vapours, which
burn in the gaseous phase and 2) burning as a solid, at the surface
(char burning); therefore during the burning process, different amount
of heat is emitted during different stages. This can be confirmed by
results obtained from the test on a 17 mm sample of the Western red
cedar. It is clear that the effective heat of combustion is not a
constant; it is roughly 12 MJ/kg for the first part of the test, but
increases to around 30 MJ/kg during the charring period at the end of
the test (Babrauskas 2008).
[FIGURE 15 OMITTED]
For pine (Fig. 15 a and b) and oak (Fig. 15 c and d),
thermogravimetric research was carried out. Thermogravimetric research
was conducted in different gaseous media: nitrogen (Fig. 15 a and c) and
air (Fig. 15 b and d).
Pyrolysis of pine took place in stages in the nitrogen environment
(Fig. 15 a). The endo-effect in the DTA curve (min 85.4[degrees]C) can
be interpreted by elimination of moisture (water) present in wood. Here,
the loss of mass was 5.6%. The exo-effect becomes apparent in the first
stage at a temperature of 85-230[degrees]C (max ~170[degrees]C). Then,
reactions of hemicellulose pyrolysis and oxidation take place. The loss
of mass at this stage was ~7%.
The second exothermal effect during pyrolysis became apparent at
the temperature of 230-361[degrees]C (max ~300[degrees]C). At this
stage, the mass is lost suddenly and the total loss amounts to ~49% (DTG
curve). This means that the largest amount of volatile gas forms here,
and decomposition and combustion of cellulose prevails.
The third exothermal effect--and at the same time the stage of
pyrolysis--took place when the temperature exceeded 361.2[degrees]C and
was over at approximately 710[degrees]C. Its maximum was at
~430[degrees]C. The process progressed at a lower speed compared to the
second stage and here gasification and oxidation reactions of lignin
prevailed. The total loss in this stage amounted to ~20%.
Later, two more exo-effects became apparent with maximums at
~810[degrees]C and ~930[degrees]C. This could be interpreted by
combustion of char itself and its monoxide. The loss in these stages was
~7%. The total loss of mass amounted to ~89%.
It must be pointed out that all combustion reactions took place due
to oxygen present in the chemical composition of wood and its
capillaries because the research was carried out in the nitrogen
environment.
Gasification and combustion of pine in the air environment also
took place in stages (Fig. 15 b). The endoeffect in the DTA curve (min
84[degrees]C) can be interpreted by elimination of moisture present in
wood. The loss of mass amounted to ~5%. The first exothermal effect
during pyrolysis and oxidation of hemicellulose became apparent at the
temperature of 84-405[degrees]C (max ~330.6[degrees]C). It should be
emphasized that in fact the course of the DTA curve was also different
at the first stage compared to the one in the nitrogen medium. The total
loss of mass at this stage was ~65% of the total mass of the sample.
That was the most intense loss of mass, which significantly differed
from the results of the tests in nitrogen gas.
The second exothermal effect during pyrolysis and combustion of
cellulose became apparent at the temperature of 405-470[degrees]C (max
-456.9[degrees]C). Mass was lost rather quickly (DTG curve) and the
total loss of mass amounted to ~18%.
The third exothermal effect during decomposition and combustion
reactions of lignin became apparent at the temperature of
470-500[degrees]C (max -473.9[degrees]C). The total loss of mass at this
stage amounted to ~6%.
The character of curves for the latter two stages differed
significantly from the ones in nitrogen medium. Moreover, the results
showed that in the temperature range, practically no processes took
place. The total loss of mass amounted to ~94%.
Gasification and combustion of oak in the nitrogen environment also
takes place in stages (Fig. 15 c). The endo-effect in the DTA curve (min
105.2[degrees]C) can be interpreted by elimination of moisture present
in wood, which makes 1.0% of the total mass. The exo-effect in the first
stage became apparent at the temperature of 105.2-232.8[degrees]C (max
-180[degrees]C). Pyrolysis and oxidation reactions of hemicelluloses
also took place at this stage. The total loss of mass at this stage
amounted to ~1.5%.
The second stage of pyrolysis took place at the temperature of
232.8-343.8[degrees]C. Its maximum was ~300[degrees]C. At this stage,
mass was lost at high speed and its loss amounted to ~44%. The largest
amount of volatile gas formed at this stage, and decomposition of
cellulose and combustion of its pyrolysis products prevailed.
The third exothermal effect during pyrolysis and oxidation became
apparent at the temperature of 232.8-695 [degrees]C (max
~420[degrees]C). The total loss of mass at this stage amounted to ~25%.
Reactions of lignin decomposition and combustion of its products
prevailed.
Later, two more exo-effects became apparent with maximums at
~827[degrees]C and ~928[degrees]C. This could be interpreted by
combustion of char itself and its monoxide. The loss in these stages was
~4%. The total loss of mass amounted to ~75%.
Decomposition of oak in the air environment also took place in
stages (Fig. 15 d). The endo-effect in the DTA curve (min 96[degrees]C)
can also be interpreted by elimination of moisture present in wood. The
loss of mass amounted to ~5%. The exo-effect in the first stage became
apparent at the temperature of ~96-100[degrees]C (max ~330.9[degrees]C).
Pyrolysis and oxidation reactions of hemicelluloses also took place at
this stage. Mass was lost at a very high speed at this stage and its
total loss amounted to -44%.
The second stage of pyrolysis of cellulose and oxidation of its
products took place at the temperature of ~400-190[degrees]C . The
maximum of the exo-effect was 486.7[degrees]C. The total loss of mass in
this stage amounted to ~23%.
The third stage of pyrolysis took place at the temperature of
490-505[degrees]C. The maximum of the exo-effect was 493.3[degrees]C.
The total loss of mass at this stage amounted to -23%. Reactions of
lignin destruction and combustion prevailed.
The total loss of mass amounted to -95%. Moreover, the results
showed that in the temperature range of 505-1000[degrees]C, practically
no processes took place.
As it can be seen from the thermograms presented in Fig. 15, the
results of thermogravimetric analysis in different environment for oak
and pine are essentially different but in terms of nature, they are
similar when research is carried out in the same gas medium.
Pyrolysis and oxidation of wood in nitrogen environment starts and
is more intense at lower temperatures. These processes take place due to
presence of oxygen in wood.
When tests were performed in air environment, pyrolysis and
oxidation of individual components of wood started and were more intense
at higher temperatures.
4. Conclusions
1. The charring rates of wood increase as the heating time
increases, with the exception of oak wood, the charring rate of which
after 10 minutes of heating is smaller that after 5 minutes of heating.
From among the tested species of wood (fir, pine, oak and aspen) the
smallest charring rate was for oak, the largest--after 10 and 20 minutes
of heating--for pine, after 30 and 45 minutes--for aspen, after 5
minutes of heating the charring rate for pine and aspen was the same.
2. The largest value of the correlation coefficient (R = 0.9597)
was obtained when predicting the charring rate for aspen and the
smallest value (R = 0.9240) was obtained when predicting the charring
rate for pine. The values of the obtained correlation coefficients in
the experimental equations are 0.9240-0.9597, which means that there is
an obviously close interdependence of parameters.
3. The calorific values of char residue, irrespective of the time
of wood heating, are higher than those of wood from which char residue
has been obtained. The calorific value of dry wood is 18.7-20.0 MJ/kg
and the calorific value of char residue after 5 minutes of heating is
20.5-26.5 MJ/kg.
4. The calorific values of resulting char residue increase rapidly
until 20 minutes of heating. After 5 minutes of heating the calorific
value reaches 20.5-26.5 MJ/kg and after 20 minutes--33.5-34.1 MJ/kg.
Later, after 30 and 45 minutes of heating, the calorific values change
insignificantly. Then the difference between the largest and the
smallest value is about 0.6 MJ/kg
5. The results of the thermogravimetric analysis in different
environment for oak and pine are essentially different. However, in
terms of nature they are rather similar when research is carried out in
the same gas medium.
6. In nitrogen environment pyrolysis and oxidation of individual
species of wood due oxygen present in wood starts and is more intense in
lower temperature range, and for three components it continues even to
the temperature of ~700[degrees]C. Later, two more exo-effects become
apparent with maximums at ~810-827[degrees]C and ~928-930[degrees]C.
This could be interpreted by combustion of char itself and its monoxide,
which is confirmed by large residue: 11% in case of pine and 25% in case
of oak.
7. In air environment, pyrolysis and oxidation of individual
components of wood starts and is more intense in the range of higher
temperatures, however ends having in fact reached ~500[degrees]C and
later on no processes take place. Amount of residue is small: 6% in case
of pine and 5% in case of oak.
doi:10.3846/13923730.2012.720935
References
Babrauskas, V. 2005. Charring rate of wood as a tool for fire
investigations, Fire Safety Journal 40(6): 528-554.
http://dx.doi.org/10.1016/j.firesaf.2005.05.006
Babrauskas, V. 2008. Heat Release Rates. The SFPE Handbook of Fire
Protection Engineering. 4th Ed. National Fire Protection Assotiation,
Quincy, MA. 628 p.
Bednarek, Z.; Griskevicius, M.; Sauciuvenas, G. 2009. Tensile,
compressive and flexural strength reduction of timber in fire,
Engineering Structures and Technologies 1(3): 148-156.
http://dx.doi.org/10.3846/skt.2009.18
Demirbas, A. 2001. Carbonization ranking of selected biomass for
charcoal, liquid and gaseous products, Energy Conversion and Management
42(10): 1229--1238. http://dx.doi.org/10.1016/S0196-8904(00)00110-2
Demirbas, A; Gullu, D.; Caglar, A.; Akdeniz, F. 1997. Estimation of
calorific values of fuels from lignocellulosics, Energy Sources 19(8):
765-770. http://dx.doi.org/10.1080/00908319708908888
Drysdale, D. 1998. An introduction to Fire Dynamics. 2nd ed. John
Willey and Sons. 447 p.
Hagen, M.; Hereid, J.; Delichatsios, M. A.; Zhang, J.; Bakirtzis,
D. 2009. Flammability assessment of fire-retarded Nordic Spruce wood
using thermogravimetric analyses and conecalorimetry, Fire Safety
Journal 44(8): 1053-1066.
http://dx.doi.org/10.1016/j.firesaf.2009.07.004
Helsen, L.; Van den Bulck, E.; Mullens, S.; Mullens, J. 1999.
Low-temperature pyrolysis of CCA-treated wood: thermogravimetric
analysis, Journal of Analytical and Applied Pyrolysis 52(1): 65-86.
http://dx.doi.org/10.1016/S0165-2370(99)00034-0
Heskestad, G. 2006. Heat of combustion in spreading wood crib fires
with application to ceiling jets, Fire Safety Journal 41(5): 343-348.
http://dx.doi.org/10.1016/j.firesaf.2006.01.008
Heskestad, G.; Delichatsios, M. A. 1989. Update: The initial
convective flow in fire, Fire Safety Journal 15(6): 471475.
http://dx.doi.org/10.1016/0379-7112(89)90017-9
Jakimavicius, C. 2003. Medienotyra [Timber study]. Kaunas:
Technologija. 271 p.
Jaskolowski, W. 2001. Szybkosc zweglania i generacji ciepla podczas
spalania drewna zabezpieczonego przeciwogniowo [Rate of heat generation
and formation of char on the samples surface during burning wood which
is protected from fire]. Poznan, Poland. 87 p.
Jefimovas, A. 2011. Medienos degimo ir anglejimo ypatumai
[Peculiarities of timber combustion and charring], in 14-oji Lietuvos
jaunijii mokslininkii konferencija "Mokslas -- Lietuvos
ateitis", sekcija "Statyba" [14th Conference of
Lithuanian young scientists "Science--Future of Lithuania, Section
"Construction], Vilnius, Lithuania, 2011. 5 p.
Koufopanos, C. A.; Lucchesi, A.; Mashio, G. 1989. Kinetic modelling
of the pyrolisis of biomass and biomass component, The Canadian Journal
of Chemical Engineering 67(1): 75-84.
http://dx.doi.org/10.1002/cjce.5450670111
Lipinskas, D. 2006. Gaisro kilimo vietos nustatymas pagal mediniii
konstrukciji apanglejimq [Prediction of fire origin location to wood
materials sharring]. PhD Thesis. Vilnius: Vilnius Gediminas Technical
University. 128 p.
Lipinskas, D.; Maciulaitis, R. 2005. Further opportunities for
development of the method for fire origin prognosis, Journal of Civil
Engineering and Management 11(4): 299-307.
http://dx.doi.org/10.1080/13923730.2005.9636361
LST EN ISO 1716:2010 Gaminiii reakcijos { ugn{ bandymai. Degimo
silumos (silumingumo) nustatymas [Reaction to fire tests for
products--Determination of the gross heat of combustion (calorific
value)]. European committee for standardization, Brussels. 42 p.
LST EN 1363-1:2000 Atsparumo ugniai bandymai. 1 dalis. Bendrieji
reikalavimai [Fire resistance tests--Part 1: General requirements].
European committee for standardization, Brussels. 29 p.
LST EN 13501-1:2007 Statybos gaminiii ir statinio elementii
Uasifkavimas pagal atsparumq ugniai. 1 dalis. Klasifikavimas pagal
atsako { ugn{ bandymii duomenis [Fire classification of construction
products and building elements - Part 1: Classification using data from
reaction to fire tests]. European committee for standardization,
Brussels. 53 p.
LST EN 13238:2010 Statybiniii gaminiii reakcijos { ugn{ bandymai.
Kondicionavimo proceduros ir bendrosios pagrindii atrankos taisykles
[Reaction to fire tests for building products--Conditioning procedures
and general rules for selection of substrates]. European committee for
standardization, Brussels. 11 p.
LST EN 1995-1-2:2005 Eurokodas 5. Mediniii konstrukciji
projektavimas. 1-2 dalis. Bendrosios nuostatos. Konstrukciji elgsenos
ugnyje skaiciavimas. [Eurocode 5: Design of timber structures--Part 1-2:
General--Structural fire design]. European committee for
standardization, Brussels. 73 p.
Lukosius, K. 2004. Naujas vienpusis konstrukciji kaitinimo metodas
ir jo taikymas prognozuojant atitvarinii konstrukciji atsparumq ugniai
[New one side heating method for structures and its application for
prediction of fire resistance of structures with separation function].
PhD Thesis. Vilnius: Vilnius Gediminas Technical University. 100 p.
Otero, M.; Gomez, X.; Garcia, A. I.; Moran, A. 2007. Effects of
sewage sludge blending on the coal combustion: A thermogravimetric
assessment, Chemosphere 69(11): 1740-1750.
http://dx.doi.org/10.1016/j.chemosphere.2007.05.077
Roberts, A. F. 1970. A review of kinetic data for the pyrolysis of
wood and related substances, Combustion and Flame 14(2): 261-272.
http://dx.doi.org/10.1016/S0010-2180(70)80037-2
Sniuolis, R. 2004. Inzinerines medziagos [Engineering Materials].
Siauliai: Lucilijus. 255 p.
Tan, F. T.; Ma, X. Q.; Feng, C. 2011. Investigation on combustion
of fire retardant board under different N2-O2 mixture gas atmospheres by
using thermogravimetric analysis, Construction and Building Materials
25(4): 2076-2084. http://dx.doi.org/10.1016/j.conbuildmat.2010.11.036
Taubkin, S. I. 1999. Pozhar i vzryv, osobennosti ikh ekspertizy.
Moskva: VNIIPO. 600 s.
Turner, I.; Rousset, P.; Remond, R.; Perre, P. 2010. An
experimental and theoretical investigation of the thermal treatment of
wood (Fagus sylvatica L.) in the range 200-260 [degrees]C, International
Journal of Heat and Mass Transfer 53(4): 715-725.
http://dx.doi.org/10.1016Zj.ijheatmasstransfer.2009.10.020
Yorulmaz, S. Y.; Atimtay, A. T. 2009. Investigation of combustion
kinetics of treated and untreated waste wood samples with
thermogravimetric analysis, Fuel Processing Technology 90(7): 939-946.
http://dx.doi.org/10.1016/j.fuproc.2009.02.010
Zhaosheng, Y.; Xiaoqian, M.; Ao, L. 2009. Thermogravimetric
analysis of rice and wheat straw catalytic combustion in air- and
oxygen-enriched atmospheres, Energy Conversion and Management 50(3):
561-566. http://dx.doi.org/10.1016/j.enconman.2008.10.022
Romualdas Maciulaitis (1), Andrejus Jefimovas (2), Povilas
Zdanevicius (3)
Department of Building Materials, Vilnius Gediminas Technical
University, Sauletekio al. 11, LT-10223 Vilnius, Lithuania E-mails: (1)
romualdas.maciulaitis@vgtu.lt; (2) andrejus.jefimovas@dok.vgtu.lt
(corresponding author); (3) povilas.zdanevicius@vgtu.lt
Received 04 Jan. 2012; accepted 20 Jun. 2012
Romualdas MACIULAITIS. Prof., Dr Habil of Technological Sciences at
the Department of Building Materials, Vilnius Gediminas Technical
University (VGTU). Research interests: development of building materials
and analysis of their characteristics.
Andrejus JEFIMOVAS. A PhD student at the Department of Building
Materials, Vilnius Gediminas Technical University (VGTU). Research
interests: research of timber charring.
Povilas ZDANEVICIUS. A PG student at the Department of Building
Materials, Vilnius Gediminas Technical University (VGTU). Research
interests: research of timber charring.
Table 1. The average reached temperature in the heating
chamber depending on time
Heating time, Reached average heating temperature,
min [degrees]C
5 580
10 680
20 780
30 840
45 900