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    International Journal of Hydrogen Energy 26 (2001) 265273

    www.elsevier.com/locate/ijhydene

    Eects of addition of electrolysis products on methane=airpremixed laminar combustion

    C. Uykura, P.F. Henshawb; , D.S.-K. Tinga, R.M. Barrona

    aMechanical Engineering, University of Windsor, 401 Sunset Avenue, Windsor, Ontario, Canada N9B 3P4bCivil and Environmental Engineering, University of Windsor, 401 Sunset Avenue, Windsor, Ontario, Canada N9B 3P4

    Abstract

    In this study, eects of the addition of small amounts of water electrolysis products on laminar premixed methane =air

    ames have been investigated using chemical kinetic simulation methods. The CHEMKIN kinetic simulation package was

    used with the GRI kinetic mechanism. Pollutant concentrations, ame speeds, temperature proles and lean ammability

    limits of methane=air, methane=hydrogen=air and methane=hydrogen=oxygen=air systems were compared at dierent addition

    percentages and equivalence ratios from 1.4 to the lean ammability limit. The addition of 10 20% hydrogen in the fuel

    was found to have a small eect in improving ame speed and lean ammability limit properties. However, the addition of

    oxygen and hydrogen in the same ratio as is found in water was shown to be benecial. Improvements in the ame speeds

    of methane=air mixtures by the addition of 10% hydrogen and its associated oxygen were equivalent to the improvements

    obtained by the addition of 20% hydrogen only. In near stoichiometric mixtures, the addition of oxygen substantially increased

    the NOx concentrations, but for lean mixtures no increase in NOx was predicted. CO emissions were reduced when hydrogen

    displaced carbon-containing fuels. ? 2001 International Association for Hydrogen Energy. Published by Elsevier Science

    Ltd. All rights reserved.

    Keywords: Water electrolysis products; Kinetic simulation; Hydrogen; Methane; Oxygen; CHEMKIN; GRI

    1. Introduction

    Natural gas, which is mainly composed of methane, oers

    signicant economic [1] and environmental [2,3] advantages

    over other fuels. Methane has lower emission levels com-

    pared with other fuels because of its chemical formula (lower

    carbon to hydrogen ratio) and utilizing it in leaner combus-tion can further reduce these levels. Leaner combustion of

    methane may result in higher thermal eciency and reduced

    emissions, especially of NOx . However, the low ignitibility

    and lower ame speed of methane, which cause combustion

    instabilities, excessive emissions and lower power output,

    are the major impediments to achieving satisfactory results

    with methane.

    Corresponding author. Tel.: +01-519-253-4232 ext 2588; fax:

    +01-519-971-3686.

    E-mail address: [email protected] (P.F. Henshaw).

    A practical solution to overcome the diculties with

    methane is addition of more reactive fuels such as hydrogen.

    There have been several investigations on the eects of the

    addition of hydrogen into methane. It has been shown both

    theoretically and experimentally that hydrogen addition

    results in substantial enhancement in the ignitibility and

    lean ammability limits of methane=air mixtures [417].Production of hydrogen by electrolysis of water may be

    preferred because of the safety and cost considerations of

    handling and storing hydrogen as a fuel additive [18,19].

    The oxygen by-product of electrolysis can also be added

    into the fuel=oxidizer mixture in order to improve combus-

    tion properties. Practical applications of the addition of elec-

    trolysis products into other fuels are already available in

    the market. Although investigations concerning the utiliza-

    tion of electrolysis products in practical devices such as IC

    engines were performed in several studies [20,21], some

    fundamental research is still needed to better understand

    combustion kinetics of these mixtures without the compli-cations of operating a practical combustion device.

    0360-3199/01/$ 20.00 ? 2001 International Association for Hydrogen Energy. Published by Elsevier Science Ltd. All rights reserved.

    PII: S 0 3 6 0 - 3 1 9 9 ( 0 0 ) 0 0 0 6 8 - 9

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    In this study, the eects of the addition of small amounts

    of hydrogen on methane=air combustion of premixed, lami-

    nar, freely propagating, planar ames has been theoretically

    investigated. In addition, since electrolysis of water may be

    the source of hydrogen, the addition of hydrogen and oxy-

    gen in the molar ratio H2 : O2 = 2 : 1 into a methane=airburner has been simulated.

    2. The model

    The numerical simulation was performed in order to pre-

    dict adiabatic ame temperatures, pollutant concentrations

    and ame speeds of laminar, premixed, freely propagating,

    one-dimensional ames. The computational model used in

    this study consists of the following components: PREMIX

    [22], Sandias steady state, laminar, one-dimensional ame

    code; TWOPNT [22], a boundary value problem solver;

    a transport property preprocessor [22]; CHEMKIN-III [23],

    a gas-phase interpreter which processes the chemical re-

    action mechanism; and GRI 3.0 [24], a chemical reaction

    mechanism for methane combustion.

    PREMIX code which uses a hybrid time-integration=

    Newton iteration technique to solve the steady-state com-

    prehensive mass, species, and energy conservation equa-

    tions was set up to simulate a freely propagating ame

    with mixture-averaged formulas. An additional boundary

    condition for mass ow rate, which is necessary for this

    type of formulation, was obtained by xing the location of

    the ame by specifying the temperature at one point. The

    CHEMKIN package was modied to implement the GRImechanism by replacing its original reaction and transport

    library with the GRI les. In this study, the GRI mechanism

    version 3.0, which has 325 reactions and 53 species, was

    used without any modication. The mechanism is described

    extensively elsewhere [24].

    The problem environment was dened by setting the ini-

    tial and boundary conditions. The initial ow rate estimation

    of the fuel=oxidizer mixture was set equal to 0:04 (g=cm2 s)

    according to the published measurements of stoichiometric

    methane=air ame speeds [25]. The pressure and tempera-

    ture of the mixture were set at 1.0 atm and 298 K, respec-

    tively. The additional boundary condition required for theow solution was supplied by xing the temperature point

    for 400 K whose distance is calculated from the initial tem-

    perature prole estimation by the software. Since it was

    known from the previous studies [26] that the total reaction

    zone of the premixed, laminar, freely propagating, stoichio-

    metric methane=air ame is about 0.4 cm, the calculation

    domain was started 2 cm before the ame region and the

    total length of the calculation domain was chosen as 12 cm.

    The initial temperature prole estimation, which is required

    to start the iteration, was made according to the recent study

    of VanMaaren et al. [26]. Results of the rst simulation step

    were used as the temperature prole estimation for the next

    step.

    Table 1

    Unreacted fueloxidizer composition of methane=air mixtures at

    dierent equivalence ratios

    O2 N2 CH4

    1.5 0.1811 0.6831 0.13581.4 0.1827 0.6894 0.1279

    1.3 0.1844 0.6957 0.1199

    1.2 0.1861 0.7022 0.1117

    1.1 0.1879 0.7088 0.1033

    1 0.1896 0.7155 0.0948

    0.9 0.1915 0.7224 0.0862

    0.8 0.1933 0.7294 0.0773

    0.7 0.1952 0.7365 0.0683

    0.6 0.1971 0.7437 0.0591

    0.5 0.1991 0.7511 0.0498

    Table 2

    Unreacted fueloxidizer composition of methane=air mixture with

    the addition of 10% hydrogen by volume at dierent equivalence

    ratios

    O2 N2 CH4 H2

    1.5 0.1791 0.6757 0.1307 0.0145

    1.4 0.1808 0.6823 0.1232 0.0137

    1.3 0.1826 0.6890 0.1155 0.0128

    1.2 0.1844 0.6959 0.1077 0.0120

    1.1 0.1863 0.7029 0.0997 0.0111

    1 0.1882 0.7101 0.0916 0.0102

    0.9 0.1901 0.7174 0.0832 0.0092

    0.8 0.1921 0.7248 0.0748 0.0083

    0.7 0.1941 0.7324 0.0661 0.00730.6 0.1962 0.7402 0.0573 0.0064

    0.5 0.1983 0.7481 0.0482 0.0054

    Numerical solutions were obtained for the following

    mixtures: (1) pure methane=air, (2) 10% hydrogen + 90%

    methane+air, (3) 20% hydrogen + 80% methane + air, (4)

    10% hydrogen + oxygen (half as much as the hydrogen) +

    90% methane + air (the initial concentrations of these mix-

    tures can be found in Tables 14). Lean ammability

    limits, nal temperature proles, ame speeds and species

    concentration of these mixtures have been predicted fordierent equivalence ratios ().

    3. Results and discussion

    The solution algorithm was rst tested for accuracy by

    comparing the ame speed at dierent equivalence ratios of

    pure methane=air mixtures to published values. The ame

    speed is dened as the speed, relative to and normal to the

    ame front, with which unburned gas moves into the front

    and is transformed to products under laminar ow condi-

    tions [29]. In our study it was simply the velocity of gas

    ow at the adiabatic boundary of the ame (ow velocity

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    Table 3

    Unreacted fueloxidizer composition of methane=air mixture with

    the addition of 20% hydrogen by volume at dierent equivalence

    ratios

    O2 N2 CH4 H2

    1.5 0.1768 0.6672 0.1248 0.0312

    1.4 0.1787 0.6742 0.1177 0.0294

    1.3 0.1806 0.6813 0.1105 0.0276

    1.2 0.1825 0.6886 0.1031 0.0258

    1.1 0.1845 0.6961 0.0955 0.0239

    1 0.1865 0.7038 0.0878 0.0219

    0.95 0.1876 0.7076 0.0838 0.0210

    0.9 0.1886 0.7116 0.0799 0.0200

    0.85 0.1896 0.7155 0.0759 0.0190

    0.8 0.1907 0.7195 0.0718 0.0179

    0.7 0.1929 0.7277 0.0635 0.0159

    0.6 0.1951 0.7361 0.0551 0.0138

    0.5 0.1974 0.7446 0.0464 0.0116

    Table 4

    Unreacted fueloxidizer composition with addition of water elec-

    trolysis products addition (10%) at dierent equivalence ratios

    O2 N2 CH4 H2

    1.5 0.1824 0.6696 0.1331 0.0147

    1.4 0.1842 0.6763 0.1254 0.0139

    1.3 0.1860 0.6831 0.1176 0.0130

    1.2 0.1879 0.6900 0.1097 0.0121

    1.1 0.1899 0.6971 0.1016 0.0112

    1 0.1918 0.7043 0.0933 0.0103

    0.9 0.1938 0.7117 0.0848 0.00940.8 0.1959 0.7193 0.0762 0.0084

    0.7 0.1980 0.7270 0.0674 0.0074

    0.6 0.2001 0.7348 0.0584 0.0064

    0.5 0.2023 0.7429 0.0492 0.0054

    at 0 distance). Values of laminar ame speed S0u , reported

    in the literature have been characterized by substantial scat-

    ter [25]. This scatter has been attributed to the fact that no

    experiments can directly generate an ideal one-dimensional,

    planar, adiabatic, steady, unstrained, laminar ame for which

    S

    0

    u is dened. However, three recent and promising resultshave been chosen for comparison [26 28]. Fig. 1 illustrates

    that the ame speed simulated by GRI is equal to or higher

    than the measured results. This may be a consequence of

    tuning the GRI mechanism using the experimental results

    from earlier publications where the ame speed was mea-

    sured to be higher [28]. However, as shown in Fig. 1, sim-

    ulated results are in good agreement with Gu et al.s results

    [28] in the lean side (up to equivalence ratio = 1:0). This

    measurement set is approximately 10% lower than simula-

    tion on the rich side of the curve. However, the rich side

    simulations are in good agreement with Van Maarens data

    [27], which gives lower than the simulated values for the

    lean side. This can be explained by the stretch levels of dif-

    Fig. 1. Simulated and measured [2628] laminar ame speeds of

    methane=air mixtures.

    Fig. 2. Eects of the hydrogen (10 and 20%) and hydrogen=oxygen

    (10%) addition on laminar ame speeds at dierent equivalence

    ratio methane=air mixtures.

    ferent measuring methods and the strong relation between

    the level of stretch and ame velocity for low Lewis number

    mixtures. Lean methane mixtures are more stoichiometric at

    the ame, leading to enhanced burning intensity [31].

    The leanest combustible 1 methane=air mixture has been

    predicted to be =0:55 with this solution method. This value

    is also in good agreement with Zebatakiss [32] measured

    value of = 0:54.

    Flame speed predictions for methane=air combustion with

    H2 and H2 + O2 addition can be seen in Fig. 2. Although

    hydrogen has a ame speed seven times higher than

    methane, adding 10% hydrogen increases the ame speed

    of the mixture by only 8% at = 1:0. Adding 20% H2increases the ame speed by a maximum of 15% at the

    stoichiometric condition, whereas a 13% higher levels

    in ame speed were predicted with the addition of 10%

    H2 + O2. The percentage increase in ame speed due to

    1 Although the ammability limit is dened as the leanest fuel

    oxidizer mixture ratio beyond which no ame will propagate [30],

    in this study it is predicted as the leanest mixture that results in

    temperature increase.

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    Fig. 3. Temperature prole of freely propagating premixed laminar

    ames of dierent stoichiometric fuel mixtures.

    Fig. 4. The eects of dierent additives on nal ame temperature

    of freely propagating premixed laminar ame on dierent equiva-

    lence ratios.

    H2 or H2 + O2 addition is independent of the equivalence

    ratio. The leanest ammable mixture for a freely prop-

    agating laminar methane=air ame was predicted to be

    = 0:55. This was improved to = 0:54 with the ad-

    dition of 10% hydrogen. The addition of 20% hydrogen

    produced no further improvement in lean ammability limit

    ( = 0:54). Results from the addition of 10% hydrogenwith accompanying oxygen into methane=air combustion

    systems improved the lean ammability limit to = 0 :52.

    The reason that the addition of oxygen leads to a further

    increase in ame speed and lean ammability limit may be

    explained by the increase in the oxygen and methane mole

    fraction in the unburnt mixture compared with methane or

    methane=hydrogen mixtures of the same equivalence ratio.

    Temperature proles of dierent mixtures for the whole

    ame area are illustrated in Fig. 3. Although all mixtures

    appear to have similar temperature proles, the nal tem-

    peratures (temperatures at the end of the computational

    domain) vary for dierent mixtures as seen in Fig. 4.

    Although hydrogen has a higher ame temperature com-

    Fig. 5. The eects of dierent additives on nal carbon monoxide

    concentrations.

    Fig. 6. The eects of dierent additives on nal NO concentrations.

    pared with methane, the ame temperature of the mix-

    ture was increased by less than 1% even with the ad-

    dition of 20% H2. The addition of oxygen into these

    mixtures resulted in a further increase in nal ame

    temperature of 1%. These increases are partially due

    to the fact that the added oxygen resulted in less air

    being added to maintain the same stoichiometry. The use

    of oxygen instead of air at the same stoichiometry means

    that less inert nitrogen is available to absorb heat in the

    reaction, resulting in a higher temperature.

    The carbon monoxide concentrations have been compared

    for dierent mixtures in Fig. 5. The addition of hydrogencauses the overall carbon to hydrogen ratio of the mixture

    to decrease (a pure hydrogen ame produces no CO). As a

    result, CO concentrations for the hydrogen added mixtures

    decreased. The decrease in CO as compared to methane was

    not as great when oxygen was added to the unburnt mixture

    due to the higher methane mole fraction. Dierences in CO

    concentrations for all lean mixtures were negligibly small,

    due to the low CO concentrations found at these equivalence

    ratios.

    The eects of hydrogen and oxygen addition on NO

    concentrations for dierent equivalence ratio methane=air

    mixtures are shown in Fig. 6. High temperatures and high

    oxygen concentrations result in high NO formation rates

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    Fig. 7. The eects of temperature and oxygen concentration on NO production rate for stoichiometric mixtures ( = 1) (a)

    methane=air + hydrogen (b) methane=air + hydrogen + oxygen.

    [29]. With hydrogen=methane mixtures, the slight increase in

    temperature due to addition of H2 is compensated by the

    decrease in oxygen concentration, leading to lower NO

    concentrations in lean mixtures. The addition of oxygen

    causes the mixture to have both an increase in oxygen con-centration and an increase in adiabatic ame temperature

    leading to higher NO concentrations for those mixtures

    near stoichiometry. However, for lean mixtures, dierences

    in NO emissions are very small.

    Figs. 7 and 8 illustrate the reasons for dierent emission

    behaviors in dierent mixtures. In stoichiometric mixtures

    ( = 1), which have maximum total NO levels, an increase

    in NO starts with an increase in temperature (0.05 cm)

    but in the region that has higher oxygen levels (0.05 0.07

    cm) no signicant NO production was observed because

    the temperature was low. In Fig. 7, dNO=dt for hydro-

    gen and hydrogen=oxygen added mixtures start to increase

    as the temperatures are increased (0.07 cm). However,

    dierences in NO production take place near the highest

    temperature region (0.10 cm). Dierences in NO produc-

    tion rate diverge, as the temperature levels are dierent. In

    contrast, for lean mixtures (Fig. 8) NO production begins to

    dier in the region that has relatively high oxygen concentra-tion dierences and relatively small temperature dierences

    (0.7 cm). However, the NO production rates are similar in

    regions where the temperature prole is dierent, such as

    at 0.2 cm.

    As can be seen in Fig. 9, the history of NO levels and

    NO production rates are dierent for dierent equivalence

    ratios. NO levels for lean mixtures increase up to a

    maximum level within a certain distance but remain nearly

    constant over the rest of the computational domain. But for

    stoichiometric mixtures, increases in NO continue down-

    stream till the end of the computational domain. To explain

    the dierences in NO production, Fig. 10 is helpful. The

    major reactions for NO production have been determined by

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    Fig. 8. The eects of temperature and oxygen concentration on NO production rate for lean mixtures ( = 0:6) (a) methane=air + hydrogen

    (b) methane=air + hydrogen + oxygen.

    reaction rate parameters and instantaneous concentrations

    of reactants for all NO producing reactions. Not surpris-

    ingly, the three most common reactions are the well-known

    Zeldovich mechanism [29]:

    O + N2 NO + N ; (1)

    N + O2 NO + O ; (2)

    N + OH NO + H : (3)

    In dierent mixtures and at dierent equivalence ratios,

    reactions responsible for the major NO production vary. For

    lean mixtures (c and d), rates of all three reactions are sim-

    ilar and reaction (2) has the maximum rate. This might be

    the reason for oxygen concentration dependence of NO rates

    for lean mixtures. For hydrogen added stoichiometric mix-

    tures (a), reaction (3) has the maximum rate starting with the

    maximum temperature and up to the end of the ame front.

    However, for oxygen=hydrogen added stoichiometric mix-

    tures (b), all three reactions have their maximum value at

    dierent positions on the ame and have a similar non-zero

    value downstream of the reacting front.Although NOx emissions are the total of NO and NO2,

    as illustrated in Fig. 11, the nal NO2 concentrations for

    all mixtures and all equivalence ratios were predicted to

    be less than 1% of the nal NO concentrations. Also, NO2concentrations show similar trends as NO concentrations in

    terms of H2 eects (cf. Fig. 11 with Fig. 6).

    4. Conclusions

    Hydrogen and oxygen have been proposed as additives

    to methane-fueled combustion systems in order to improve

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    Fig. 9. NO concentrations and NO production rates of lean and stoichiometric mixtures of methane=hydrogen=air andmethane=hydrogen=oxygen=air with respect to the ame distance.

    pollutant emissions and thermal eciency. However, some

    theoretical studies about kinetic behavior of these sys-

    tems are essential to predict the possible benets and

    to reduce drawbacks. In this study, the kinetics of hy-

    drogen and oxygen addition eects on basic combustion

    properties of methane laminar premixed ames were

    investigated.

    It has been found that the addition of 10 or 20% hydro-

    gen to methane=air laminar premixed ames did not signi-

    cantly improve the lean ammability limits. The maximum

    increase in lean ammability limit was 2% which occurred

    with 20% H2 addition. On the other hand, the addition of

    10% hydrogen with oxygen in a H2 : O2 ratio of 2 : 1 resulted

    in a 5% increase in lean ammability limit. The tempera-

    ture proles and concentrations of pollutant species (NO,

    NO2, and CO) for methane=air with 10 or 20% H2 mixtures

    were predicted to be similar to the proles for methane =air

    mixtures.

    The addition of 10% H2 + O2 resulted in as much im-

    provement in ame speed as the addition of 20% H2.

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    Fig. 10. The eects of the dierent reactions on NO production for lean and stoichiometric mixtures.

    Temperature proles of oxygen added mixtures were

    predicted to be higher at all equivalence ratios. Car-

    bon monoxide and NOx concentrations of oxygen

    added mixtures are also higher than the 10 or 20% H2mixtures.

    In summary, the addition of hydrogen and oxygen was

    predicted to be more benecial than the addition of pure

    hydrogen in terms of ame speed, temperature, lean

    ammability limit, and CO concentrations. Increases in

    NO concentrations were predicted to be higher with the

    addition of hydrogen and oxygen. But it was shown

    that these eects could be compensated by the exten-

    sion in lean ammability limit. It is also clear that uti-

    lizing hydrogen and oxygen as additives in practical

    combustion systems may result in higher power outputs

    because of the increase in fuel concentration in the mix-

    ture compared with methane=air or methane=air + H2

    mixtures.

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    Fig. 11. The eects of dierent additives on nal NO2 concentra-

    tions.

    Acknowledgements

    This project was partially sponsored by the Natural

    Sciences and Engineering Research Council of Canada

    (NSERC).

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