Journal Pre-proof Formation and nanoscale-characteristics of soot from pyrolysis of ethylene blended with ethanol/dimethyl ether Lijie Zhang, Kaixuan Yang, Rui Zhao, Yaoyao Ying, Dong Liu PII:
S1743-9671(19)30863-3
DOI:
https://doi.org/10.1016/j.joei.2019.11.012
Reference:
JOEI 668
To appear in:
Journal of the Energy Institute
Received Date: 27 June 2019 Revised Date:
21 November 2019
Accepted Date: 25 November 2019
Please cite this article as: L. Zhang, K. Yang, R. Zhao, Y. Ying, D. Liu, Formation and nanoscalecharacteristics of soot from pyrolysis of ethylene blended with ethanol/dimethyl ether, Journal of the Energy Institute, https://doi.org/10.1016/j.joei.2019.11.012. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2019 Published by Elsevier Ltd on behalf of Energy Institute.
1
Formation and nanoscale-characteristics of soot from
2
pyrolysis of ethylene blended with ethanol/dimethyl ether
3
Lijie Zhang1,2, Kaixuan Yang1,2, Rui Zhao1,2, Yaoyao Ying1,2*, Dong Liu1,2*
4 5
1 MIIT Key Laboratory of Thermal Control of Electronic Equipment, School of
6
Energy and Power Engineering, Nanjing University of Science and Technology,
7
Nanjing 210094, P. R. China.
8
2 Advanced Combustion Laboratory, School of Energy and Power Engineering,
9
Nanjing University of Science and Technology, Nanjing 210094, P. R. China.
10 11 12 13 14 15 16 17 18 19 20 21
*Corresponding Authors.
22
E-mail:
[email protected] (D. Liu),
[email protected] (Y.Y. Ying). 1
23
Abstract
24
Ethanol and dimethyl ether (DME) have been considered to be two of the most
25
potential additives for conventional hydrocarbon fuels. This paper focused on the
26
nanoscale characteristics of soot from ethylene pyrolysis with ethanol and DME
27
additions. The pyrolysis experiments were conducted in a α-alumina tube flow reactor
28
at 1273K, 1373K and 1473K, with the replacement of 0%, 50% and 100% (mole
29
fraction) ethylene by the two oxygenated fuels. The gas-phase kinetic modeling was
30
also performed to explore and understand the soot formation process. The main
31
pathways and some key soot precursors in the pyrolysis have been obtained. Soot
32
samples were characterized by high resolution transmission electron microscopy
33
(HRTEM), X-ray diffraction (XRD) and thermogravimetric analysis (TGA) to acquire
34
their internal structure and oxidation reactivity. Results showed that the mass of
35
collected soot diminished with the increase of the replacement of ethylene by
36
ethanol/DME. The effects of DME to inhibit the formation of soot were more obvious.
37
The least amount of soot was collected in the pyrolysis of pure DME. Peak mole
38
fraction of C2H2, C4H2, C4H4 and C5H5 also decreased with the increase of
39
replacement of ethylene by ethanol/DME, displaying the same tendency with the
40
variation trend of soot mass in the different pyrolysis conditions. According to TEM
41
and HRTEM results, the additions of ethanol and DME could decrease the growth rate
42
of soot contrasted with the pyrolysis of pure ethylene. Soot collected from the
43
pyrolysis of pure DME at 1273K and 1373K showed a typical amorphous structure
44
with short, highly-curved and turbulent fringe. With the reduction of the replacement 2
45
of ethylene by DME, mature soot with longer and more ordered fringe formed at
46
1373K and 1473K. The sequence of the mean fringe tortuosity of soot samples was
47
100% ethylene<50% DME<100% ethanol<50% ethanol< 100% DME. The order was
48
the same as the sequence of oxidation reactivity. Furthermore, with the increase of
49
temperature, the mass of soot increased. More mature soot with higher degree of
50
graphization, longer fringe length, smaller fringe tortuosity and lower oxidation
51
reactivity was obtained. High correlation between soot nanostructure and soot
52
oxidation reactivity was found.
53 54
Keyword: Soot; Pyrolysis; Ethanol; Dimethyl ether; Nanostructure; Reactivity
55
3
56
1. Introduction
57
Soot particles released from many combustion systems such as furnace and internal
58
engine have caused many environmental problems and could do great harm to human
59
health [1-4]. Facing to the increasingly harsh soot emission regulations, many
60
researchers began to focus on the investigations aiming to reduce soot production
61
including seeking for some alternatives to take the place of traditional fossil fuels.
62
Oxygenated biofuels such as alcohols, esters and ethers have attracted more and more
63
attentions as substitutes of conventional fuels due to their potential to reduce the
64
emission of soot and greenhouse gases [5-11].
65
Ethanol and dimethyl ether (DME) stand out prominently serving as the role of
66
substitutes of hydrocarbon fuels such as diesel and gasoline among the oxygenated
67
fuels [12-15]. Due to their different molecular structures, the two isomer oxygenated
68
fuels present various properties. More and more scholars have performed some
69
studies to obtain the combustion and pyrolysis features about the two fuels.
70
Research about the effects of ethanol or/and DME additions on the combustion and
71
pyrolysis fundamental characteristics, including intermediate species, reaction
72
pathways, gas products, ignition delay time and the flame speed, has been carried out
73
experimentally and numerically [16-23]. Barraza-botet et al. [16] performed the
74
ignition experiments of iso-octane and ethanol blends to acquire the ignition delay
75
time. Furthermore, speciation experiments were performed at 10 atm. Eight stable
76
intermediate species were measured by fast-gas sampling, gas chromatography and
77
mass spectrometry to depict the reaction pathway during the ignition. In the same year, 4
78
Hashemi et al. [17] studied the pyrolysis and oxidation experiments of ethanol in a
79
laminar flow reactor at the pressure of 50 bar and temperatures of 600-900 K. A
80
detailed chemical kinetic model was developed to predict ignition delay time and
81
flame speed of ethanol in literature. Geng et al. [18] studied the ignition delay time of
82
n-butanol/dimethyl ether mixtures in the shock tube. Wang et al. [19] focused on the
83
isomer influences on the composition of reaction intermediates in propene flames
84
with dimethyl ether or ethanol additions. The completed series of propene flames
85
blended with ethanol/DME were further analyzed by Frassoldati et al. [20] with a
86
kinetic model. Liu [21] performed the comparative study to get the chemical effects of
87
CO2 additions on ethanol/O2/Ar flame and DME/O2/Ar flame using a detailed
88
chemical mechanism. Paul et al. [22] illustrated the emission performance of a single
89
cylinder engine utilizing the blends of Diesel-DME(DEE) and Diesel-DME-ethanol.
90
However, only quite limited references focusing on the sooting behavior and
91
characteristics of ethanol and DME in different lab-scale combustion configurations
92
could be found. Kang et al. [24] studied the effects of DME additions on the soot
93
formation characteristics in ethylene premixed burner-stabilized stagnation (BBS)
94
flame and found that the soot formation rate decreased with DME additions in the
95
BBS flame. The synergistic influence of DME additions on the soot formations was
96
not observed. Luo et al. [25] carried out the experimental research about the effects of
97
dimethyl ether addition on soot formation, evolution and characteristics in flame-wall
98
interactions. Moreover, few number of studies on the sooting behavior of ethanol and
99
DME during the laboratory pyrolysis have been performed. Esarte et al. [26-28] 5
100
conducted some investigations about the pyrolysis experiments with ethanol or/and
101
DME additions. Esarte et al. [26] carried out the experimental study about the
102
pyrolysis of acetylene-ethanol and acetylene-DME blends. Results showed that both
103
of the two oxygenated fuels could inhibit soot formation. The concentration of the rest
104
gas products in the outlet stream such as CO and CO2 had some relationship with the
105
various pathways during the pyrolysis process. But Esarte et al. focused on the
106
formation of soot and gas products like CO, CO2, CH4 and C6H6 and did not pay
107
attention to the soot characteristics. And there were no detailed discussions about the
108
relationships for the key species with soot formations. Furthermore, it has been
109
identified and validated that soot structure can affect its oxidation reactivity [11, 25,
110
28]. However, there are no available studies which are devoted to explore nanoscale
111
characteristics of soot in the flow reactor pyrolysis with the two different isomer
112
oxygenated fuels additions. Pyrolysis of the fuels is the first step in the whole
113
combustion process, which plays a pretty important role. It could have great effects on
114
formation of soot. The main aim of the present work was to study the effects of
115
ethanol and DME additions on nanostructure and oxidation reactivity of soot from
116
ethylene pyrolysis, and provide deep analyses about the pyrolysis performance of
117
these two isomer oxygenated fuels as fuel additives.
118
In this study, ethylene was chosen as the primary fuel because it was one of the
119
most important compositions among hydrocarbon fuels and has been widely used in
120
the research which concentrated on the soot formation. The pyrolysis experiments
121
with 0%, 50% and 100% replacement of ethylene by ethanol/DME at 1273K, 1373K 6
122
and 1473K were conducted. The three temperatures can reflect the three different
123
stages in the pyrolysis process, which was the starting point of soot production, the
124
lower soot production and the higher soot production. The gas-phase kinetic modeling
125
was performed to catch some key soot precursors. And main reaction pathways
126
analyses of ethylene, ethanol and DME during the different pyrolysis conditions were
127
also carried out to better comprehend soot formation process. To acquire nanoscale
128
characteristics of soot, high revolution transmission electron microscopy (HRTEM)
129
and X-ray diffraction (XRD) were utilized. A thermogravimetric analyzer (TGA) was
130
employed to get the soot oxidation reactivity.
131 132
2. Experimental and kinetic modeling
133
2.1 Experimental set up
134
The atmosphere pyrolysis of ethylene blended with ethanol/DME took place in a
135
α-alumina tube flow reactor at 1273K, 1373K and 1473K in Ar atmosphere, as shown
136
in Fig.1. Ethylene, Ar and DME were introduced to the mixing vessel from gas
137
cylinder by mass flow controllers (Sevenstar, CS200A). Liquid ethanol was delivered
138
to the evaporator by a Harvard PHD2000 syringe pump. All the pipelines were
139
wrapped with heating bands to prevent the gas ethanol liquefying. The α-alumina tube
140
with 700mm in length and 45mm internal diameter was placed inside an electric
141
furnace. Two furnace plugs were set in the entrance and exit of the tube separately to
142
avoid heat loss. The temperature profiles along the flow reactor were measured by
143
moving the K-type thermocouple, as shown in Fig.2. The step distance was 2 cm. 7
144
There existed a constant-temperature area from the location of 26cm to 34cm. C2H4 Ar
Exhaust Emissions
Mass Flow Controller
Particle Filter One-way Valve Mixing Vessel
145 146
Syringe Pump Evaporator
Tube Furnace
Fig.1. Schematic of the experimental set up.
147 148
Fig.2. Temperature profiles along the center of the α-alumina tube.
149 150
To study the effects of different carbon sources on soot formation and
151
characteristics, the mole amount of reacting carbon was kept the same in all the
152
pyrolysis conditions. Ar for carrying ethanol were kept 2% of the total gas in volume
153
fraction. Ar for dilution was introduced to obtain a total flow rate of 1000 ml/min
154
(STP, standard temperature and pressure),which leaded to the gas residence time
155
dependent on the reaction temperature, t(s)= 2605/T. C/O ratio is an important
156
parameter in this research. So two sets of the experiments were designed and 8
157
conducted. When C/O ratio equals 2, it means half-mole carbon in the C2H4 is
158
replaced by DME/ethanol. Pure DME/ethanol pyrolysis takes place when C/O ratio is
159
4. For any pyrolysis condition, experiments under three temperatures were performed.
160
Each experiment lasted for 1 hour. The detailed experimental conditions were shown
161
in Table 1. Table 1. Experimental conditions in the pyrolysis.
162 Pyrolysis
Flow rate (ml/min)
C/O
T(K)
conditions
Ethylene
Ethanol
DME
100% ethylene
20
0
0
/
50% ethanol
10
0.02623
0
4
1273
50% DME
10
0
9.8
4
1373
100% ethanol
0
0.05246
0
2
1473
100% DME
0
0
19.6
2
Dilution Ar
960
Carrier Ar
20
163 164
Soot was collected in the tail of the α-alumina tube by a piece of filtration
165
membrane. The filtration membrane with a diameter of 50 mm and aperture of 0.45
166
µm was put in front of the furnace plug. The quartz fiber cotton with a pore light of
167
lower than 5 µm was placed after the furnace plug in the end of the tube to prohibit
168
the uncollected soot blocking the back pipeline. The mass of the membrane was
169
weighed before the reaction and after the reaction separately by a high precision
170
balance in each pyrolysis condition. Soot mass was acquired by the difference. To
171
reduce measurement error, the operations of the measurements was conducted three
172
times.
173 174 175
2.2 Soot characterizations To get the morphology of the soot samples, an FEI Tecnai G2 F30 S-SWIN 9
176
transmission electron microscopy (TEM) was used. By magnifying the TEM pictures,
177
HRTEM pictures could be obtained to study the nanostructure of the soot particles.
178
The soot samples were firstly dispersed in ethanol ultrasonically for 90 min. Then,
179
three drops of the suspension were dropped to the carbon film (200 mesh) to do the
180
TEM and HRTEM tests. More than three locations of each grid were chosen to
181
guarantee the accuracy of the results. To make quantitative analysis, the homemade
182
MATLAB software [29-31] using the algorithms by Yehliu et al. [32, 33] was applied
183
to get the fringe parameters such as length and tortuosity.
184
A D8 Advance X-ray diffractometer with Cu Kα radiation was employed to analyze
185
the graphitization degree of soot samples. The scan range was 10°-100° and the scan
186
step size and speed were 0.05 and 0.2s/step respectively.
187
To obtain the oxidation reactivity of soot collected from different pyrolysis
188
conditions, an STA 449 F3 thermogravimetric analyzer was employed. Each soot
189
sample was weighed 5±0.3 mg at first and put into a quartz crucible. Soot sample was
190
heated in pure Ar atmosphere with a flow rate of 100 ml/min from 50℃ to 300℃ for
191
an hour to remove the volatile compounds. Afterwards, soot sample was heated from
192
300℃ to 500℃ continually. Then the temperature was kept to 500℃ for 150 minutes
193
in a mixture flow (78% Ar and 22% O2). The total flow rate was maintained to 100
194
ml/min in the whole process. The normalized oxidation reactivity curve of each soot
195
sample could be obtained through the calculation of the mass loss in the entire process.
196
The uncertainty of the experiments was ±4.7% error with 95% confidence [30].
197 10
198
2.3 Kinetic modeling
199
To further supplement our study and qualitative acquire the additional information, we
200
performed the chemical kinetic modelling. A detailed chemical kinetic mechanism
201
(AramcoMech 3.0) was employed in the kinetic simulation for the pyrolysis of
202
ethylene blended with ethanol/DME. This mechanism containing 581 species and
203
3037 reactions has been widely utilized and validated against the experimental
204
measurements [34]. Considering to complexity of the multi-dimension, we simplified
205
the process and adopted Plug Flow Reactor (PFR) to carry out the modelling, which
206
was consistent with many pyrolysis model [38]. The measured temperature profile
207
was used as input temperature parameter to make the simulation keep consistent with
208
the experiments. The running step distance was 0.2 cm in the modeling. The mole
209
fraction of fuels and gas products at every specific position (every 0.2 cm) could be
210
acquired during the pyrolysis process.
211 212
3. Results and discussion
213
3.1 Soot formation analysis
214
3.1.1 Soot production and analysis
215
Fig.3 illustrated soot mass at different pyrolysis conditions. Soot amount decreased
216
with the increase of the replacement of ethylene by ethanol or DME at a certain
217
temperature. Moreover, it was obvious that less soot formed when replacing ethylene
218
with DME instead of ethanol at the same ethylene replacement (50% or 100%).
219
Contrasted to ethylene, ethanol and DME possessed lower C/H ratio. Furthermore, the
11
220
existence of O in ethanol and DME may lead to the oxidation reaction and could
221
affect soot formation reaction to some degree. This could give some reasons that soot
222
amount reduced when ethanol and DME were mixed into ethylene. It was found that
223
C-C bond may have some relationship with soot formation [26]. Compared with
224
ethanol, C-C bond was not found in DME. Instead, two C atoms connected with O
225
atom. Although they have the same chemical formula, different functional groups (-O-
226
and -OH) in DME and ethanol showed their various abilities to produce soot. No soot
227
can be collected from pyrolysis of pure DME at 1273K. When the blending ratios of
228
the oxygenated fuels were fixed, more soot produced as the temperature increased. It
229
implied that the soot formation process enhanced at high temperatures, which was
230
consistent with the previous pyrolysis studies [11, 17, 35].
231 232
Fig.3. Mass of soot from pyrolysis of ethylene blended with 0%/50%/100%
233
ethanol/DME at 1273/1373/1473K
234 235
Reaction pathway analysis at lower temperature (1273K) and higher temperature 12
236
(1473K) during the pyrolysis was performed separately in order to comprehend the
237
concrete chemical reactions and soot formation process. To choose proper locations to
238
carry out reaction pathway analysis, mole fraction profiles of ethylene, ethanol and
239
DME along the flow reactor at 1273K and 1473K were plotted, as shown in Fig.4.
240
With 50% ethanol additions, the mole fraction of ethylene increased to a peak at first
241
and then decreased to a certain value. The peak mole fraction of ethylene was
242
acquired when ethanol was entirely consumed, indicating that ethanol may produce
243
ethylene. Not all the ethylene was consumed at 1273K with 0% and 50%
244
ethanol/DME additions. When the temperature was 1473K, almost all the ethylene
245
was depleted. As shown in Fig.3, soot mass increased with the raise of temperature. It
246
could be inferred that at higher temperatures, the conversion of ethylene promoted
247
and more ethylene may take part in the reactions which were related to soot formation.
248
Ethanol and DME could be completely consumed at both 1273K and 1473K in a
249
pretty short distance no matter the ethylene replacement was 50% or 100%. Moreover,
250
it was apparent that ethanol and DME participate in the consumption reactions ahead
251
of ethylene. At 1473K, starting and ending points of ethylene, ethanol and DME
252
consumption moved forward compared with those at 1273K. This could result from
253
the different temperature profiles as shown in Fig.2.
254
Reaction pathway analysis was conducted at 1273K and 1473K by selecting proper
255
positions where around 70% fuel was consumed and most intermediates had high
256
mole fractions [36, 37]. The detailed related parameters were exhibited in Table 2.
257
Table 2. The related parameters of the fuels. 13
Temperature
Conditions
Distance
Ethylene
Ethanol
DME
(cm)
conversion
conversion
conversion
100% ethylene
38
68.8%
/
/
50% ethanol
38
60.3%
100%
/
50% DME
38
70.5%
/
100%
100% ethanol
21.4
/
77.8%
/
100% DME
21.4
/
/
65.4%
100% ethylene
24.8
73.9%
/
/
50% ethanol
24.8
68%
100%
/
(K)
1272K
1473K
50% DME
24.8
76.2%
/
100%
100% ethanol
18.8
/
77.2%
/
100% DME
18.8
/
/
63.8%
258
259 260
Fig.4. Mole fraction profiles of ethylene, ethanol and DME along the flow reactor for
261
different pyrolysis conditions. (a) (b) (c):1273K, (d) (e) (f):1473K. 14
262 263
Figs.5 and 6 exhibited the consumption pathways of ethylene at 1273K and 1473K
264
respectively with the replacement of ethylene by 0%/50% ethanol/DME. Through the
265
comparison of Figs.5 and 6, it could be easily found that the reaction pathways of
266
ethylene were simpler and the formation of soot precursors was more direct at 1473K.
267
The formation of soot precursors such as C2H2, C3H3 and C6H6 went through fewer
268
steps at 1473K. As shown in Figs.5 and 6, the most significant unimolecular
269
decomposition way of ethylene was the consumption pathway to produce C2H3 by the
270
attack of H radical both at 1273K and 1473K. The C2H3 radical could convert to C2H2
271
through R2 and R3. It was obvious that the contribution of the production of C2H3 and
272
C2H2 could be greater at 1473K. As seen from Fig.3, soot amount increased with the
273
raise of the temperature. It could be inferred that at higher temperature, the reactions
274
benefiting to the production of soot precursors were enhanced, which could result in
275
the promotion of soot production. C2H4+H=C2H3+H2
(R1)
C2H3(+M)=C2H2+H(+M)
(R2)
C2H3+H=C2H2+H2
(R3)
276
In Figs.5 and 6, C3H3 could be found after a series of intermediate reactions. C3H3
277
could contributed to the production of C6H6 and FULVENE through self-combination,
278
as shown in R4 and R5. Then C6H5 and FULVENE could convert to C6H6 through R6
279
and R7. C3H3+C3H3=C6H6 15
(R4)
C3H3+C3H3=FULVENE
(R5)
C6H5+H2=C6H6+H
(R6)
FULVENE+H=C6H6+H
(R7)
280
As one of the most important precursors of large monocyclic aromatic hydrocarbons
281
(MAHs) and polycyclic aromatic hydrocarbons (PAHs), C6H6 could take part in the
282
reactions related to the aromatics growth through hydrogen abstraction carbon
283
addition (HACA) and so on [38]. However, the reaction pathways of ethylene related
284
to the formation of C6H6 and its precursors in the pyrolysis pathways were similar
285
with the replacement of 50% ethylene by ethanol/DME. So it was hard to distinguish
286
the accurate chemical effects of ethanol and DME through Figs.5 and 6. To better
287
understand the soot formation process, the pathways of ethanol and DME at different
288
locations were depicted in Figs. 7 and 8 separately.
289 16
290
Fig.5. Reaction network of ethylene at 1273K at the location of 38cm. Percentages
291
given in parentheses are corresponding to the results of 100% ethylene. Percentages
292
given in square bracket are corresponding to the results of 50% ethanol. Percentages
293
given in angle bracket are corresponding to the results of 50% DME.
294 295
Fig.6. Reaction network of ethylene at 1473K at the location of 24.8cm. Percentages
296
given in parentheses are corresponding to the results of 100% ethylene. Percentages
297
given in square bracket are corresponding to the results of 50% ethanol. Percentages
298
given in angle bracket are corresponding to the results of 50% DME.
299 300
Fig.7 showed the reaction network of C2H5OH with the replacement of 100%
301
ethylene by ethanol at 1273K/1473K at the location of 21.4cm/18.8cm where
302
77.8%/77.2% of the initial ethanol was exhausted respectively. As seen from Fig.7,
303
The consumption of ethanol primarily involved two pathways. One route was through
304
the dehydration reaction to produce ethylene. This was consistent with the previous
305
results in Fig.4. 17
C2H5OH=C2H4+H2O 306 307
308 309
(R8)
The other pathway was to form SC2H5OH by the attack of H, OH and CH3, contributing 49.1%/40.2% together at 1273K and 1473K individually. C2H5OH +H=SC2H4OH+H2
(R9)
C2H5OH +OH=SC2H4OH +H2O
(R10)
C2H5OH +CH3=SC2H4OH +CH4
(R11)
Great majority of SC2H5OH was consumed to bring about the formation of CH3CHO→CH3CO→CO through R12-R15. SC2H4OH=CH3CHO+H
(R12)
CH3CHO+H=CH3CO+H2
(R13)
CH3CHO+CH3=CH3CO+CH4
(R14)
CH3CO(+M)=CH3+CO(+M)
(R15)
310
As observed in Fig.4, ethanol could take part in the reactions ahead of ethylene.
311
When almost all the ethanol was consumed, ethylene just started to react. When 50%
312
or 100% ethanol was added to substitute ethylene at 1273K or 1473K, part of ethanol
313
could seize some radicals like H, OH and CH3 to take part in the formation of CO
314
rather than the yield of some vital soot precursors, resulting in the diminution of soot
315
production compared to pure pyrolysis of ethylene with the same mole amount, as
316
shown in Fig.3. Moreover, with the increase of the replacement of ethylene by ethanol
317
at a fixed temperature, more mole amount of C took part in the formation of CO,
318
which would could cause the reduction of soot amount.
319
Moreover, at 1473K, the consumption pathway of ethanol through the attack of H, 18
320
OH and CH3 to generate PC2H5OH could contribute 15.4% totally. Part of PC2H5OH
321
could convert to CO finally through the similar routes as R13-R15. However,
322
PC2H5OH could also participate in the reaction to produce ethylene at 1473K, which
323
gave the contribution of 71.3%. Then ethylene could join in the process to the
324
formation of soot through the pathway in Fig.6. So the effects of ethanol to suppress
325
soot production were much more obvious at 1273K. This was consistent with the
326
results shown in Fig.3. PC2H4OH=C2H4+OH
(R16)
327
328 329
Fig.7. Reaction network of C2H5OH when 100% ethanol was introduced at 1273K at
330
the location of 21.4cm. Percentages given in big parentheses are corresponding to the
331
results of 100% ethanol pyrolysis at 1473K at the location of 18.8cm.
332 19
333
Fig.8 presented the consumption pathway of DME when 100% DME was
334
introduced at 1273K/1473K at the location of 21.4cm/18.8cm where 65.4%/63.8% of
335
the initial DME was exhausted individually. The most vital unimolecular
336
decomposition of DME was the process to form CH3OCH2 by the attack of H,
337
contributing around 68% of DME consumption. Another reaction, which were the
338
production of CH3OCH2 and CH4 by the pelt of CH3, contributed 17.6%.
339
CH3OCH3+H=CH3OCH2+H2
(R17)
CH3OCH3+CH3=CH3OCH2+CH4
(R18)
Subsequently, CH3OCH2 could converted to CH3 and CH2O through R19. CH3OCH2=CH3+CH2O
(R19)
340
Moreover, another reaction, which was the formation of CH3 and CH3O through the
341
decomposition of CH3OCH3, could occur. CH3OCH3(+M)=CH3+CH3O(+M)
(R20)
342
Then, by the successive H abstraction, CO appeared through the pathway of
343
CH2O→HCO →CO.
344
Through Fig.8 as well as the reactions above, it was clear that DME was mainly
345
consumed to form CO, which indicated that this large part of C did not take part in the
346
formation of aromatics and soot. This could explain why soot production was lower
347
with the replacement of 50% or 100% ethylene by DME compared with soot amount
348
from co-pyrolysis of 50% ethylene and 50% ethanol, pure ethylene pyrolysis and pure
349
ethanol pyrolysis at the same temperature.
350
During the pyrolysis process, CH3 could take part in the formation of CH4 through 20
351
352
R21 and R22. CH3+H2=CH4+H
(R21)
CH2O+CH3=HCO+CH4
(R22)
Moreover, C2H6 could form through the recombination of CH3. CH3+CH3(+M)=C2H6(+M)
353
(R23)
C2H6 could convert to C2H4 through R24-R26. C2H6+H=C2H5+H2
(R24)
C2H6+CH3=C2H5+CH4
(R25)
C2H5(+M)=C2H4+H(+M)
(R26)
354
As shown in Figs.5 and 6, the pathways of C2H4 at lower and higher temperatures
355
were different. The abilities of C2H4 to form soot was stronger at 1473K. This could
356
give some evidence that more soot was collected at 1473K during the pyrolysis of
357
pure DME, although the consumption of DME at 1273K and 1473K followed the
358
similar pathway.
21
359 360
Fig.8. Reaction network of DME when 100% DME was introduced at 1273K at the
361
location of 21.4cm. Percentages given in big parentheses are corresponding to the
362
results of 100% DME at 1473K at the location of 18.8cm.
363
3.1.2 Relationship between soot amount and products involving soot formation
364
To get the relationship between soot amount and some species related to soot
365
formation, the simulated key mole fraction profiles of C2H2, C3H3, C4H2, C4H4, C5H5
366
and C6H6, which appeared in the previous pathways, were plotted during the pyrolysis
367
process at 1273K and 1473K separately, as presented in Figs.9 and 10.
368
It was clear to notice that the peak mole fraction of C2H2, C4H2, C4H4 and C5H5
369
decreased with the increase of the replacement of ethylene by ethanol or DME both at
370
1273K and 1473K. The peak mole fraction reduction of the four species was more
371
prominent with the replacement of ethylene by DME. For a fixed temperature, the
372
sequence of the peak mole fraction values of C2H2, C4H2, C4H4 or C5H5 kept the same,
373
which was 100% ethylene>50% ethanol>50% DME>100% ethanol>100% DME. 22
374
This was in the same tendency with the trend of soot amount. It could be deduced that
375
there existed a high correlation between soot amount and production of some
376
hydrocarbon species. During the pyrolysis of ethylene blended with ethanol/DME,
377
soot production had positive correlation with the peak mole fraction values of C2H2,
378
C4H2, C4H4 and C5H5.
379
However, at 1273K and 1473K, the tendency of the peak mole fraction values of
380
C3H3 and C6H6 did not follow the same trend as 100% ethylene>50% ethanol>50%
381
DME>100% ethanol>100% DME. At 1273K, both of the peak mole fraction values of
382
C3H3 and C6H6 from pure DME pyrolysis were the smallest among the five pyrolysis
383
conditions. This was the same with the results of soot amount, which showed that the
384
least amount of soot was collected from pyrolysis of pure DME. The peak values of
385
C3H3 from pure ethanol pyrolysis, as well as co-pyrolysis of 50% ethylene and 50%
386
ethanol/DME were almost the same. With the elevation of ethylene replacement by
387
DME, the peak mole fraction of C6H6 decreased, which was coincident with the
388
results of soot amount. But compared with pure ethylene pyrolysis, the peak mole
389
fraction value of C6H6 was larger when 50% ethanol was added. As mentioned in
390
previous discussion, C3H3 has closely relationship with the formation of C6H6, as
391
showed in R4-R7. It could be found through the reaction pathways of ethylene and
392
ethanol that pyrolysis of ethanol was easier to produce C3. So the concentration of
393
C3H3 could increase slightly compared to pure ethylene pyrolysis. This phenomenon
394
was more obvious when the temperature was higher. The enhancement of
395
concentration of C3H3 could directly lead to the increase of the concentration of C6H6. 23
396
In Fig.3, higher amount of soot was collected in the pyrolysis of pure ethylene at a
397
fixed temperature. Soot mass decreased with the addition of 50% ethanol. The joint
398
influence of diverse soot precursors could cause such results. It could be clearly
399
noticed that the mole fraction of other important soot precursors reduced and the
400
reduction range was higher in comparison to C6H6. Therefore, it could be deduced
401
that soot formation was dominated by the co-contribution of the other various soot
402
precursors, which led to the reduction of soot amount. At 1473K, the smallest values
403
of the peak mole fraction of C3H3 and C6H6 were obtained from pure ethylene
404
pyrolysis because that much more C3H3 and C6H6 take part in the formation of PAHs
405
at higher temperatures. Moreover, as shown in Fig.6, when 50% oxygenated fuels
406
were added, the primary consumption of C2H2 caused the formation of
407
C3H4-P→C3H3→C6H6. During the pyrolysis of pure ethylene, the main deception of
408
C2H2 leaded to the production of C4H4 and C4H2, which may also result in the lower
409
values of the peak mole fraction of C3H3 and C6H6.
410
For a fixed ethylene replacement, the peak mole fraction of C2H2, C3H3, C4H2,
411
C4H4, C5H5 and C6H6 increased as the temperature increased. Positive correlation was
412
found between temperature and the peak mole fraction values of these species.
24
413 414
Fig.9. Simulated mole fraction information of C2H2, C3H3, C4H2, C4H4, C5H5, C6H6
415
during the pyrolysis process at 1273K. Mole fraction profiles: (A)C2H2, (B)C3H3,
416
(C)C4H2, (D)C4H4, (E)C5H5, (F)C6H6. Peak mole fraction with different replacement
417
of ethylene: (a)C2H2, (b)C3H3, (c)C4H2, (d)C4H4, (e)C5H5, (f)C6H6.
25
418 419
Fig.10. Simulated mole fraction information of C2H2, C3H3, C4H2, C4H4, C5H5, C6H6
420
during the whole pyrolysis process at 1473K. Mole fraction profiles: (A)C2H2,
421
(B)C3H3, (C)C4H2, (D)C4H4, (E)C5H5, (F)C6H6. Peak mole fraction with different
422
replacement of ethylene: (a)C2H2, (b)C3H3, (c)C4H2, (d)C4H4, (e)C5H5, (f)C6H6.
423 424
3.2 Soot characteristics analysis
425
3.2.1 Soot morphology and nanostructure analysis 26
426
Fig. 11 showed the typical TEM and HRTEM images of soot collected from
427
pyrolysis of ethylene blended with ethanol/DME at 1273K. As presented in Fig.
428
11(e)-(h), soot appeared to be liquid-like materials, which may result from the
429
chemical condensation of heavy PAHs at low temperature. These soot particles were
430
similar to young and nascent soot as presented in many previous research [29, 39, 40].
431
It was hard to obviously distinguish the independent individual particles and clarify
432
the borderline among particles because of the irregular shapes. However, a detailed
433
observation of soot particles could discover that particle-like protrusions or shaped
434
knobs formed under the cover of the film-like materials in Fig. 11(e)-(h). These
435
protrusions and knobs may develop from liquid-like materials [39]. No obvious soot
436
could be collected from pyrolysis of 100% DME at 1273K. The sections in the
437
specific yellow circles in Fig. 11(e)-(h) were magnified to acquire the HRTEM images
438
of soot, as described in Fig. 11(i)-(l). Fig. 11(m)-(p) were skeleton images extracted
439
from Fig. 11(i)-(l) for further inspections. These images showed short, highly-curved
440
and random fringe, presenting typical amorphous structures.
441
Fig. 12 gave the representative TEM and HRTEM images of soot collected from
442
pyrolysis of ethylene blended with ethanol/DME at 1373K. It was easy to perceive
443
many approximately rounded particles in the fashion of loosely chain-like way [17,
444
37], as presented in Fig. 12(f)-(i). More mature soot was found compared with soot in
445
Fig. 11. Fig. 12(j) exhibited morphology of soot from pyrolysis of 100% DME, which
446
was similar to young soot morphology mentioned in Fig. 11. The arrows in the yellow
447
circles marked the core structure which consisted of randomly arranged carbon fringe. 27
448
Outside the cores, planar carbon layer structures were found in Fig. 12(p)-(s). The
449
outer shell was comprised of some planar crystallites. Longer and relatively more
450
organized fringes could be seen obviously in parallel orientation. However, as 100%
451
DME took the place of 100% ethylene, soot sample showed contained mainly
452
turbostratic short and curve lattice fringes, as displayed in Fig. 12(t). It could be
453
inferred that soot collected from pyrolysis of 100% DME might be more reactive.
454
Fig. 13 offered the information of morphology and nanostructure of soot collected
455
from pyrolysis of ethylene blended with ethanol/DME at 1473K. The distribution way
456
of the aggregates in Fig. 13(f)-(j) was in common with that in Fig. 12(f)-(i). The
457
particles processed mainly round shape and it was clear to clarify the bounder line
458
among particles [41]. In Fig 13(k)-(o), typical core-shell structures could be observed.
459
The fringes were mainly parallel to each other and arranged in a concentric way,
460
representing the existence of graphitic structures [11, 42]. The irregular inner cores
461
with short fringes were encircled by the ordered long fringes. The outer layer was
462
arranged more neatly in Fig.13(p)-(r) compared with Fig.12, which implied that
463
higher temperature leaded to a more ordered arrangement of carbon layer. Multi-core
464
structure was noticed in Fig. 13(t). The inner cores were surrounded by many
465
paralleled long fringes. Compared to Fig. 13(p)-(s), Fig. 13(t) showed less ordered
466
and shorter fringes.
467
To better understand the morphology of the particles in different pyrolysis
468
conditions, Image J software was adopted to measure the diameter of the soot
469
particles in the TEM pictures. Figure 2.1 showed the mean values of the primary 28
470
particles.
471
Measuring the diameters of the particles was a little hard because the particles were
472
bundled together and it was difficult to identify the clear boundary. So probably the
473
results overestimated the mean diameter of the particles, as mentioned in [29]. For
474
100% DME pyrolysis at 1373K, few particle could be found because that soot just
475
evolve from the liquid-like materials. So the particle sizes at this condition were not
476
performed. It could be found that with the increase of temperature from 1373K to
477
1473K, the mean particles size decreased except 100% ethanol pyrolysis. During this
478
period, the crack between particles took the lead, which resulted in the decrease of the
479
mean diameter of the particles. Moreover, it was interesting that the mean particle
480
diameter decreased with the addition of ethanol/DME at 1373K. However, at 1473K,
481
with the injection of ethanol/50% DME, the average particle size increased. It could
482
be deduced that there presented a suitable temperature range best for soot growth
483
between the low and high temperatures [11]. Different fuel mixtures processed the
484
various temperature range which was most proper for soot growth. At first, film-like
485
substance produced at lower temperature, and then tiny particles emerged and
486
agglomerated with the raise of temperature. The average size of the particles grew
487
bigger. However, at higher temperature, the larger particles broken into smaller ones
488
and made the particles size smaller, limiting the further growth of soot. For 100%
489
ethanol pyrolysis, soot may go through the growth stage from 1373K to 1473K.
490
However, for 50% DME/ethanol pyrolysis, soot may pass the crack and collision
491
process and the mean diameter got smaller from 1373K to 1473K. 29
492
Overall, temperature and fuel mixtures had a great influence in soot morphology
493
and nanostructure as shown in Fig.11-13. As observed in previous research [21],
494
emission of soot may go through different phases in the flame——gas-phase
495
chemistry to produce PAH molecules; inception of PAHs to form primary soot
496
particles; soot mass growth; coagulation and aggregation between particles;
497
carbonization and then oxidation of soot particles. As for pyrolysis processes in
498
present work, although violent oxidation reactions like combustion may not happen,
499
the growth and aggregation of soot were similar. Moreover, with the increase of
500
temperature, from 1273K to 1473K, morphology and nanostructure of soot collected
501
in the outlet of the flow reactor varied. Furthermore, fuel type and composition such
502
as the blended ratio of ethanol/DME could affect the growth rate of soot, the main
503
reaction pathway and the nanostructure of soot [21, 42].
30
504 505
Fig.11. TEM, HRTEM and extracted skeleton images of soot particles collected in
506
different pyrolysis conditions at 1273K.
507
31
508 509
Fig.12. TEM, HRTEM and extracted skeleton images of soot collected in different
510
pyrolysis conditions at 1373K.
32
511 512
Fig.13. TEM, HRTEM and extracted skeleton images of soot particles collected in
513
different pyrolysis conditions at 1473K.
33
514 515
Fig.14. Average sizes of the particles at different pyrolysis conditions.
516
To better understand the nanostructure characteristic of soot collected from
517
pyrolysis of ethylene blended with ethanol/DME, the detailed quantitative analysis
518
was carried out by processing the skeleton images in Fig.11-13. The results were
519
depicted in Fig.14. Fig.15 (a)-(e) conveyed the fringe length information. Fig.15 (f)-(j)
520
described the fringe tortuosity distribution. Visual comparison could clarify that with
521
the increase of temperature, the percentage of fringes whose length was larger than
522
1.5nm was clearly higher. Fringe length less than 1.0 nm had a less proportion. Fringe
523
tortuosity showed the opposite tendency. The percentage of fringe whose tortuosity
524
was bigger than 1.2 was lower as temperature raised. It was obvious that mean fringe
525
length had connections with mean fringe tortuosity. Larger fringe length was
526
correlated with smaller fringe tortuosity. At a fixed temperature, 1373K or 1473K, the
527
mean values of fringe length exhibited the ranking of 100% ethylene>50% DME>100%
528
ethanol>50% ethanol>100% DME. The sequence of mean fringe tortuosity showed
529
the opposite order. Soot with shorter fringe length had the higher reactivity because
530
carbon in the edge sites was more reactive than the basal plane carbon atoms [43]. It 34
531
could be deduced that soot collected from pyrolysis of 100% DME with the shortest
532
fringe length could have the highest reactivity at the fixed temperature.
533 534
Fig.15. Fringe length and tortuosity distribution of soot in different pyrolysis 35
535
conditions at various temperatures.
536 537
3.2.2 XRD analysis for soot
538
XRD patterns of soot collected from various pyrolysis conditions were presented in
539
Fig.16 to get the chemical structure of soot samples [44]. Soot samples collected at
540
1273K were not enough to perform XRD tests and the following TGA examinations,
541
so only the XRD results of soot sampled at 1373K and 1473K were shown here.
542
It was clear to notice that the diffraction peaks were close to the angles of 25° in
543
Fig.16. The existence of 002 band represented the emergence of crystalline graphitic
544
carbon and could assess the graphization degree of soot samples [45, 46]. The peak
545
diffraction angles of soot from different pyrolysis conditions were extracted from
546
Fig.16, as presented in Table 3. The diffraction peak of soot collected from 1373K
547
shifted to the left compared with that at 1473K although at the same ethylene
548
replacement. It showed that the raise of temperature could promote the graphization
549
degree of soot. The distinct differences of soot diffraction angles could be observed
550
when oxygenated fuels was introduced at 1373K or 1473K. With the additions of
551
oxygenated fuels, the graphization degree of soot declined. The results were
552
consistent with previous analysis of TEM and HRTEM results.
553
36
554 555
Fig.16.XRD spectra of soot collected from different pyrolysis conditions: (a) 1373K, (b) 1473K.
556 557 558
Table 3. Peak diffraction angles of soot from different pyrolysis conditions. Pyrolysis condition
1373K
1473K
2θ (degree)
100% ethylene
23.78
50% ethanol
23.43
50% DME
23.60
100% ethylene
24.78
50% ethanol
23.95
100% ethanol
24.41
50% DME
24.60
100% DME
23.81
559 560
3.2.3 Soot oxidation reactivity analysis
561
The oxidation reactivity of soot samples collected from different pyrolysis
562
conditions at 1373K and 1473K was presented in Fig.17. The normalized mass loss
563
curves were acquired from the output results by TGA. With the increase of
564
temperature, the oxidation reactivity of soot was lower. Soot collected at 1273K with
565
the disordered structure owned the higher oxidation reactivity since the disordered
566
carbon was easier to react with oxygen. Soot formed at 1473K with the higher 37
567
graphitization had the lower oxidation reactivity.
From Fig 17(b), it was clear that
568
the curve with the biggest slope belonged to 100% DME pyrolysis, which showed that
569
the oxidation reactivity of soot collected from pyrolysis of 100% DME was the
570
highest at 1473K. The normalized mass curves showed a sequence of oxidation
571
reactivity as 100% ethylene<50% DME<100% ethanol<50% ethanol< 100% DME
572
both at 1373K and 1473K. It fitted well with the sequence of fringe length and
573
tortuosity as well as the XRD results discussed above. With the blending of
574
oxygenated fuels, soot exhibited shorter fringe length, bigger fringe tortuosity, lower
575
graphization degree and lower oxidation reactivity. High relationship between soot
576
nanostructure and soot oxidation reactivity was explored. Soot collected with 50%
577
ethanol addition was more reactive toward O2 than that with 100% ethanol addition
578
because of the less ordered fringe length arrangement, which was in line with the
579
results by Esarte et al. [28]. Although DME has the same formula with ethanol, their
580
sooting characteristic varied.
581
oxidation reactivity than that with 100% DME addition, which was in agreement with
582
the previous HRTEM and XRD results.
583
ethanol, 50% DME or 100% ethanol, the main soot production way was still the
584
decomposition of ethylene, which was similar to the pure ethylene pyrolysis. This
585
may cause the similar oxidation reactivity of the collected soot.
Soot collected with 50% ethanol addition had lower
As shown in Fig. 5-7, when adding 50%
586
38
587 588
Fig.17. TGA curves of soot collected from different pyrolysis conditions: (a)1373K,
589
(b) 1473K.
590
4. Conclusion
591
This pyrolysis experiments have been carried out with the replacement of 0%, 50%
592
and 100% (mole fraction) ethylene of ethylene by ethanol/DME at 1273K, 1373K and
593
1473K respectively to get the effects of these two isomer oxygenated fuels on soot
594
nanostructure and soot oxidation reactivity as substitutes of ethylene. The gas-phase
595
kinetic modeling was also performed to understand the soot formation process. The
596
main conclusions were summarized as follows:
597
(1) With the increase of the replacement of ethylene by ethanol or DME, the mass of
598
soot diminished obviously because of the reduction of C/H ratio and C/O ratio.
599
Moreover, compared with ethanol, DME has stronger potential to reduce soot
600
formation.
601
(2)The peak mole fraction of C2H2, C4H2, C4H4 and C5H5 showed the same tendency
602
with soot mass in the different pyrolysis conditions, which was 100% ethylene>50%
603
ethanol>50% DME>100% ethanol>100% DME. Positive correlation between soot
604
mass and the peak mole fraction of C2H2, C4H2, C4H4 or C5H5 was found. 39
605
(3)Fuel types could affect the growth rate of soot, soot nanostructure and soot
606
oxidation reactivity greatly. The additions of ethanol and DME could decrease the
607
growth rate of soot. The sequence of oxidation reactivity was 100% ethylene<50%
608
DME<100% ethanol<50% ethanol< 100% DME. This order was the same as the
609
ranking of fringe length and peak diffraction angles of soot samples.
610
(4)With the increase of temperature, the mass of soot increased. And positive
611
correlation between temperature and the peak mole fraction of C2H2, C4H2, C4H4 or
612
C5H5 was observed. At higher temperature, more mature soot with higher degree of
613
graphization, longer fringe length, smaller fringe tortuosity and lower soot oxidation
614
reactivity was obtained. At low temperature, soot showed typical amorphous structure
615
and higher oxidation reactivity.
616
(5)The results from HRTEM, XRD and TGA had high correlations. Soot particles
617
with longer fringe length and smaller fringe tortuosity showed more ordered and
618
arranged nanostructure, higher graphitization degree and lower oxidation reactivity.
619 620 621 622
Acknowledgement This work was supported by the National Natural Science Foundation of China (51822605).
623 624
Reference
625
[1] I.M. Kennedy, The health effects of combustion-generated aerosols, Proceedings
40
626
of the Combustion Institute, 31 (2007) 2757-2770.
627
[2] N.E. Sánchez, A. Callejas, A. Millera, R. Bilbao, M.U. Alzueta, Formation of
628
PAH and soot during acetylene pyrolysis at different gas residence times and
629
reaction temperatures, Energy, 43 (2012) 30-36.
630
[3] A.K. Virtanen, J.M. Ristimäki, K.M. Vaaraslahti, J. Keskinen, Effect of engine
631
load on diesel soot particles, Environmental science & technology, 38 (2004)
632
2551-2556.
633
[4] T.W. Hesterberg, C.M. Long, W.B. Bunn, C.A. Lapin, R.O. McClellan, P.A.
634
Valberg, Health effects research and regulation of diesel exhaust: an historical
635
overview focused on lung cancer risk, Inhalation toxicology, 24 (2012) 1-45.
636
[5] J.C. Escobar, E.S. Lora, O.J. Venturini, E.E. Yáñez, E.F. Castillo, O. Almazan,
637
Biofuels: Environment, technology and food security, Renewable and Sustainable
638
Energy Reviews, 13 (2009) 1275-1287.
639
[6] A.K. Agarwal, Biofuels (alcohols and biodiesel) applications as fuels for internal
640
combustion engines, Progress in Energy and Combustion Science, 33 (2007)
641
233-271.
642
[7] A. Zare, T.A. Bodisco, M.N. Nabi, F.M. Hossain, M.M. Rahman, Z.D. Ristovski,
643
R.J. Brown, The influence of oxygenated fuels on transient and steady-state
644
engine emissions, Energy, 121 (2017) 841-853.
645
[8] A.C. Hansen, M. Gratton, W. Yuan, Diesel engine performance and NOx
646
emissions from oxygenated biofuels and blends with diesel fuel, Transactions of
647
the ASABE, 49 (2006) 589-595. 41
648
[9] H. Liu, X. Bi, M. Huo, C.-f.F. Lee, M. Yao, Soot emissions of various oxygenated
649
biofuels in conventional diesel combustion and low-temperature combustion
650
conditions, Energy & Fuels, 26 (2012) 1900-1911.
651
[10] C. Esarte, M. Abián, Á. Millera, R. Bilbao, M.U. Alzueta, Gas and soot products
652
formed in the pyrolysis of acetylene mixed with methanol, ethanol, isopropanol
653
or n-butanol, Energy, 43 (2012) 37-46.
654
[11] D. Liu, W. Wang, Y. Ying, M. Luo, Nanostructure and reactivity of carbon
655
particles from co-pyrolysis of biodiesel surrogate methyl octanoate blended with
656
n-butanol, Fullerenes, Nanotubes and Carbon Nanostructures, 26 (2018) 278-290.
657
[12] A.E. Farrell, R.J. Plevin, B.T. Turner, A.D. Jones, M. O'hare, D.M. Kammen,
658
Ethanol can contribute to energy and environmental goals, Science, 311 (2006)
659
506-508.
660 661 662 663
[13] J. Goldemberg, Ethanol for a sustainable energy future, science, 315 (2007) 808-810. [14] T.A. Semelsberger, R.L. Borup, H.L. Greene, Dimethyl ether (DME) as an alternative fuel, Journal of Power Sources, 156 (2006) 497-511.
664
[15] C. Arcoumanis, C. Bae, R. Crookes, E. Kinoshita, The potential of di-methyl
665
ether (DME) as an alternative fuel for compression-ignition engines: A review,
666
Fuel, 87 (2008) 1014-1030.
667
[16] C.L.
Barraza-Botet,
M.S.
Wooldridge,
Combustion
chemistry
of
668
iso-octane/ethanol blends: Effects on ignition and reaction pathways, Combustion
669
and Flame, 188 (2018) 324-336. 42
670 671
[17] H. Hashemi, J.M. Christensen, P. Glarborg, High-pressure pyrolysis and oxidation of ethanol, Fuel, 218 (2018) 247-257.
672
[18] Z. Geng, L. Xu, H. Li, J. Wang, Z. Huang, X. Lu, Shock tube measurements and
673
modeling study on the ignition delay times of n-butanol/dimethyl ether mixtures,
674
Energy & Fuels, 28 (2014) 4206-4215.
675
[19] J. Wang, U. Struckmeier, B. Yang, T.A. Cool, P. Osswald, K. Kohse-Höinghaus,
676
T. Kasper, N. Hansen, P.R. Westmoreland, Isomer-specific influences on the
677
composition
678
ethanol/propene flame, The Journal of Physical Chemistry A, 112 (2008)
679
9255-9265.
of
reaction
intermediates
in
dimethyl
ether/propene
and
680
[20] A. Frassoldati, T. Faravelli, E. Ranzi, K. Kohse-Höinghaus, P.R. Westmoreland,
681
Kinetic modeling study of ethanol and dimethyl ether addition to premixed
682
low-pressure propene–oxygen–argon flames, Combustion and Flame, 158 (2011)
683
1264-1276.
684
[21] D. Liu, Chemical effects of carbon dioxide addition on dimethyl ether and
685
ethanol flames: a comparative study, Energy & Fuels, 29 (2015) 3385-3393.
686
[22] A. Paul, P.K. Bose, R. Panua, D. Debroy, Study of performance and emission
687
characteristics of a single cylinder CI engine using diethyl ether and ethanol
688
blends, Journal of the Energy Institute, 88 (2015) 1-10.
689
[23] L. Shi, C. Ji, S. Wang, X. Cong, T. Su, D. Wang, Combustion and emissions
690
characteristics of a S.I. engine fueled with gasoline-DME blends under different
691
spark timings, Fuel, 211 (2018) 11-17. 43
692
[24] Y. Kang, Y. Sun, X. Lu, X. Gou, S. Sun, J. Yan, Y. Song, P. Zhang, Q. Wang, X. Ji,
693
Soot formation characteristics of ethylene premixed burner-stabilized stagnation
694
flame with dimethyl ether addition, Energy, 150 (2018) 709-721.
695 696
[25] M. Luo, D. Liu, Effects of dimethyl ether addition on soot formation, evolution and characteristics in flame-wall interactions, Energy, 164 (2018) 642-654.
697
[26] C. Esarte, A. Millera, R. Bilbao, M.a.U. Alzueta, Effect of ethanol, dimethylether,
698
and oxygen, when mixed with acetylene, on the formation of soot and gas
699
products, Industrial & Engineering Chemistry Research, 49 (2010) 6772-6779.
700
[27] C. Esarte, M. Peg, M.P. Ruiz, A. Millera, R. Bilbao, M.U. Alzueta, Pyrolysis of
701
ethanol: gas and soot products formed, Industrial & Engineering Chemistry
702
Research, 50 (2011) 4412-4419.
703
[28] C. Esarte, A. Callejas, Á. Millera, R. Bilbao, M.U. Alzueta, Characterization and
704
reactivity with NO/O2 of the soot formed in the pyrolysis of acetylene–ethanol
705
mixtures, Journal of analytical and applied pyrolysis, 94 (2012) 68-74.
706
[29] Y. Ying, D. Liu, Effects of butanol isomers additions on soot nanostructure and
707
reactivity in normal and inverse ethylene diffusion flames, Fuel, 205 (2017)
708
109-129.
709
[30] Y. Ying, D. Liu, Nanostructure evolution and reactivity of nascent soot from
710
inverse diffusion flames in CO2, N2, and He atmospheres, Carbon, 139 (2018)
711
172-180.
712 713
[31] Y. Ying, D. Liu, Effects of water addition on soot properties in ethylene inverse diffusion flames, Fuel, 247 (2019) 187-197. 44
714
[32] K. Yehliu, R.L. Vander Wal, A.L. Boehman, Development of an HRTEM image
715
analysis method to quantify carbon nanostructure, Combustion and Flame, 158
716
(2011) 1837-1851.
717
[33] K. Yehliu, R.L. Vander Wal, A.L. Boehman, A comparison of soot nanostructure
718
obtained using two high resolution transmission electron microscopy image
719
analysis algorithms, Carbon, 49 (2011) 4256-4268.
720
[34] C.-W. Zhou, Y. Li, U. Burke, C. Banyon, K.P. Somers, S. Ding, S. Khan, J.W.
721
Hargis, T. Sikes, O. Mathieu, E.L. Petersen, M. AlAbbad, A. Farooq, Y. Pan, Y.
722
Zhang, Z. Huang, J. Lopez, Z. Loparo, S.S. Vasu, H.J. Curran, An experimental
723
and chemical kinetic modeling study of 1,3-butadiene combustion: Ignition delay
724
time and laminar flame speed measurements, Combustion and Flame, 197 (2018)
725
423-438.
726
[35] M.P. Ruiz, A. Callejas, A. Millera, M.U. Alzueta, R. Bilbao, Soot formation from
727
C2H2 and C2H4 pyrolysis at different temperatures, Journal of Analytical and
728
Applied Pyrolysis, 79 (2007) 244-251.
729
[36] D. Liu, J. Santner, C. Togbé, D. Felsmann, J. Koppmann, A. Lackner, X. Yang, X.
730
Shen, Y. Ju, K. Kohse-Höinghaus, Flame structure and kinetic studies of carbon
731
dioxide-diluted dimethyl ether flames at reduced and elevated pressures,
732
Combustion and Flame, 160 (2013) 2654-2668.
733
[37] M. Luo, D. Liu, Combustion characteristics of primary reference fuels with
734
hydrogen addition, International Journal of Hydrogen Energy, 41 (2016)
735
11471-11480. 45
736
[38] Z. Cheng, L. Xing, M. Zeng, W. Dong, F. Zhang, F. Qi, Y. Li, Experimental and
737
kinetic modeling study of 2,5-dimethylfuran pyrolysis at various pressures,
738
Combustion and Flame, 161 (2014) 2496-2511.
739
[39] M. Alfè, B. Apicella, R. Barbella, J.N. Rouzaud, A. Tregrossi, A. Ciajolo,
740
Structure–property relationship in nanostructures of young and mature soot in
741
premixed flames, Proceedings of the Combustion Institute, 32 (2009) 697-704.
742
[40] L.G. Blevins, R.A. Fletcher, B.A. Benner, E.B. Steel, G.W. Mulholland, The
743
existence of young soot in the exhaust of inverse diffusion flames, Proceedings of
744
the Combustion Institute, 29 (2002) 2325-2333.
745
[41] R.L. Vander Wal, A. Yezerets, N.W. Currier, D.H. Kim, C.M. Wang, HRTEM
746
Study of diesel soot collected from diesel particulate filters, Carbon, 45 (2007)
747
70-77.
748 749 750 751
[42] R.L. Vander Wal, A.J. Tomasek, Soot nanostructure: dependence upon synthesis conditions, Combustion and Flame, 136 (2004) 129-140. [43] R.L. Vander Wal, A.J. Tomasek, Soot oxidation: dependence upon initial nanostructure, Combustion and Flame, 134 (2003) 1-9.
752
[44] G.N. Okolo, H.W.J.P. Neomagus, R.C. Everson, M.J. Roberts, J.R. Bunt, R.
753
Sakurovs, J.P. Mathews, Chemical–structural properties of South African
754
bituminous coals: Insights from wide angle XRD–carbon fraction analysis, ATR–
755
FTIR, solid state 13C NMR, and HRTEM techniques, Fuel, 158 (2015) 779-792.
756
[45] L. Dobiášová, V. Starý, P. Glogar, V. Valvoda, Analysis of carbon fibers and
757
carbon composites by asymmetric X-ray diffraction technique, Carbon, 37 (1999) 46
758
421-425.
759
[46] P. Jia, Y. Ying, M. Luo, B. Jiang, D. Liu, Effects of swirling combustion on soot
760
characteristics in 2,5-dimethylfuran/n-heptane diffusion flames, Applied Thermal
761
Engineering, 139 (2018) 11-24.
47
Highlights: Ranking of soot mass is 100% ethylene>50% ethanol>50% DME>100% ethanol>100% DME. Soot mass is positively correlated with mole fraction of C2H2, C4H2, C4H4 and C5H5. Sequence of reactivity is 100% ethylene<50% DME<100% ethanol<50% ethanol<100% DME. Soot with longer fringe length shows lower oxidation reactivity.