Synergetic effect of co-pyrolysis of cellulose and ... - ACS Publications

Xue Junjie, Zhuo jiankun*, Liu Mi, Chi Yongchao, Zhang Dahu, Yao Qiang. 4. 5. Key Laboratory for Thermal Science and Power Engineering of Ministry of ...
1 downloads 0 Views 797KB Size
Subscriber access provided by UNIV LAVAL

Article

Synergetic effect of co-pyrolysis of cellulose and PP over an allsilica mesoporous catalyst MCM-41 using TG-FTIR and Py-GC-MS Junjie Xue, Jiankun Zhuo, Mi Liu, Yongchao Chi, Dahu Zhang, and Qiang Yao Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/acs.energyfuels.7b01651 • Publication Date (Web): 27 Jul 2017 Downloaded from http://pubs.acs.org on July 28, 2017

Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.

Energy & Fuels is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.

Page 1 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

1 2 3 4 5 6 7

Synergetic effect of co-pyrolysis of cellulose and PP over an all-silica mesoporous catalyst MCM-41 using TG-FTIR and Py-GC-MS Xue Junjie, Zhuo jiankun*, Liu Mi, Chi Yongchao, Zhang Dahu, Yao Qiang Key Laboratory for Thermal Science and Power Engineering of Ministry of Education, Department of Thermal Engineering, Tsinghua University, Beijing 100084, China

8 9 10 11

Abstract Biomass is one of the promising alternative materials to solve the energy and

12

environment crisis. Fast pyrolysis is one of the most economical and commercially

13

realizable technology to convert the biomass to useable fuels and chemicals. To

14

improve the liquid products, co-pyrolysis with propylene (PP) over a mesoporous

15

catalyst MCM-41 was studied in this paper. TG-FTIR and Py-GC-MS were used as

16

the main analysis methods to study the mass loss and the detailed products of the

17

co-pyrolysis. The mass loss, main functional groups and identified products of

18

pyrolysis of cellulose, PP and their mixture were analyzed and discussed. All the TG,

19

FTIR and Py-GC-MS data show there is no significant synergism between the

20

cellulose and PP when simply mixing them, though the C/H eff of the mixture

21

increases from 0 to 1.3. However, the addition of MCM-41 bring significant

22

synergism. The TG and DTG data show the co-pyrolysis with MCM-41 shifts the

23

decomposition of PP to lower temperature, which provides more overlap between

24

cellulose and PP in the range of 300-400°C. According to the FTIR spectra, there are

25

also CO, CO2 and carbonyl produced in the peak supposed for pyrolysis of PP for the

26

mixture together with MCM-41, which indicates the intermolecular synergetic

27

reaction. Furthermore, the results from Py-GC/MS show olefins (43.9%), oxygenated

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

28

compounds (24.8%, mainly alcohols) and aromatic (17.8%) are the main products of

29

co-pyrolysis of cellulose and PP in the presence of MCM-41, while the oxygenated

30

compounds (82.2%, mainly saccharides), olefins (4.7%) and aromatic (1.1%) will be

31

the main products without catalyst. The olefins and alcohols are much more than the

32

calculated value, which are the main result of synergism. The alcohols are mainly

33

produced from the radical from cracking of PP combines with the hydroxyl radical

34

produced from decomposition of cellulose. While the olefins are produced from

35

interaction reaction (carbenium ion reaction and β-scission) between the primary

36

products of the cellulose and hydrocarbon pool reaction of primary products of

37

cellulose and PP. The results of this study enhance the understanding of co-pyrolysis

38

of cellulose and PP in the presence of MCM-41 and provide the possible pathway of

39

modifying the special pyrolysis products in catalytic pyrolysis of biomass with

40

polymers.

41 42

Keywords: Co-pyrolysis, cellulose, PP, catalyst, synergism

43 44

ACS Paragon Plus Environment

Page 2 of 34

Page 3 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

45 46 47 48

1. Introduction Today, energy and environment problems have become one of the major problem

49

of the survival and development of human society.1 Biomass is an important part of

50

renewable energy, which can provide abundant carbon. What’s more, biomass will

51

trap and use the CO2 by photosynthesis when they grow up. These advantages make

52

biomass one of the promising alternative materials to solve the energy and

53

environment crisis. As a result, realizing the high efficiency of biomass conversion is

54

now an important development strategy of most country around the world.2

55

Pyrolysis is one of the effective ways to convert the biomass to liquid fuel and

56

chemicals. Fast pyrolysis is one of the most economical and commercially realizable

57

technology by rapid heating the biomass for bio-oil under no oxygen, which has few

58

limitation of raw material, high throughput and high reaction rate. 3-5 However, the

59

liquid fuel has high oxygen contents (10-40 wt%), low calorific value (16-19 MJ/kg,

60

about half that of crude oil ) and strong acidity (pH from 2 to 4). 6 As a result, the

61

liquid fuel cannot be used directly. 6 In 1986, Chen et al. put forward the concept of

62

effective hydrogen to carbon ratio (Eq. (1)) to estimate if the raw material is able to be

63

converted to hydrocarbon chemicals economically.

64 65

H − 2O Hൗ Ceff = C

(1)

The research indicates the raw material with a H/Ceff value of 1~2 can be

66

converted to petroleum products. While the raw material with a H/Ceff value lower

67

than 1 will produce more coke, which will deactivate the catalyst, and fail to produce

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

68

high quality liquid fuel.7 The H/Ceff value of lignocellulosic biomass is between 0~0.3,

69

which means lignocellulosic biomass is lack of hydrogen. 8 Some researchers studied

70

the co-pyrolysis of biomass with high H/Ceff value material like alcohols (methanol

71

and butanol). The results show co-pyrolysis increases the yield of petroleum

72

chemicals and decreases yield of the unwanted coke. 9-10

73

Waste plastics are much cheaper material with high H/Ceff value, like the two most

74

commonly used plastics polyethylene (PE) and polypropylene (PP) with very high

75

H/Ceff value being 2. Besides, waste plastics are abundant. The global production of

76

plastic has reached about 322 million tons in 2015 and has increased by 3.5% over

77

2014.11 The polymeric wastes may take up to billions of years to degrade naturally

78

and result in environmental impact, which is concerned by the public.12-13 To recycle

79

the waste plastics and reuse them is of significance. In addition, biomass and plastics

80

are main components of municipal solid waste (MSW), like the package in food

81

industry, which are difficult to be separated.14 In conclusion, co-pyrolysis of biomass

82

and plastics is promising to effectively convert the biomass and waste plastics to

83

valuable liquid fuels and chemicals.15

84

Several researches concerning co-pyrolysis of biomass and plastics has been

85

reported.16-18 Some researchers found there is no noticeable cross reaction products

86

between pine and plastics or their decomposition products when co-pyrolysis without

87

catalyst.16 But other researchers reported the yield of bio-oil increased when

88

co-pyrolysis of pine and plastic. 15 And alcohol will increase in the bio-oil product if

89

co-pyrolysis of cellulose and PP. 19

ACS Paragon Plus Environment

Page 4 of 34

Page 5 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

90

Furthermore, the addition of proper catalyst is expected to reduce decomposition

91

temperature, to promote decomposition speed, and to modify the products. 20 The

92

mechanism for the improvements is the presence of the catalyst may change the

93

reaction path and the activation energy. 17-18, 21-23 For example, the addition of a

94

catalyst in polymer pyrolysis processes helps the hydrogen transfer reaction due to the

95

presence of acid active centers inside the catalyst.24 And there will be significant

96

synergism. The effective and most used catalyst is zeolite HZSM-5, with which the

97

yield of petrochemical product will be enhanced, and more aromatic compounds and

98

olefin will be produced.2, 17-18

99

However, due to the bulky nature of the polyolefin, especially the larger molecules

100

with branched structure like PP, the pore structure (pore size: 5.1 × 5.5 Å, internal

101

pore space: 6.4 Å) of the HZSM-5 is not big enough for the entrance and diffusion of

102

the reactant molecules, and the catalyst activity will be limited. 1, 13, 25 Besides, the

103

high acidity of the HZSM-5 leads to the excessive cracking of the cellulose and

104

plastics, which results in the carbon deposit and deactivation of the catalyst.26

105

Research found catalyst with bigger pore size will improve the diffusion limitation,

106

and the bigger plastic molecules can access the inner active site. 1 That means the

107

catalyst will be more effective only when its structure is accessible for the plastic

108

molecules. 24-25

109

MCM-41 is a silica catalyst with mesoporous pore size (2-50 nm), which is more

110

effective to catalyze reactions involving high volume molecules with non-ignorable

111

steric hindrance, and which will improve the limitation of the HZSM-5. 13, 24, 27

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

112

Besides, MCM-41 can also decrease the content of unwanted carboxylic acids and

113

carbonyl functionalities and increasing the quantity of desirable hydrocarbons, which

114

will upgrade the bio-oil. 27 It is promising to study the co-pyrolysis of cellulose and

115

polymer together with MCM-41, which may improve the products. However, there is

116

little knowledge about the co-pyrolysis of cellulose and PP in the presence of

117

MCM-41.

118

This study will focus on the synergetic effect of co-pyrolysis of cellulose and PP

119

over an all-silica MCM-41 catalyst, aiming at improving the products distribution and

120

giving more information about the mechanism of co-pyrolysis of cellulose and PP

121

over MCM-41 by analysis the pyrolytic kinetic data and the yield and distribution of

122

the pyrolysis products.

123 124 125 126 127 128

2. Material and methods 2.1 Cellulose, Polypropylene (PP) and MCM-41 The cellulose was bought from Alfa Aesar company, whose chemical formular is

129

[C6H10O5]n. The polypropylene (PP) was bought from Shanghai YangLi mechanical

130

and electrical technology company, whose chemical formular is [C3H6]n. The catalyst

131

MCM-41 was bought from the Catalyst Factory of Nankai University, which is made

132

from silicon. All of the sample and the catalyst are fine powder.

133 134 135 136 137

2.2 TG-FTIR Experiment To analyze the pyrolysis products and measure the weight change of the sample at the same time, the thermogravimetric analyzer (STA449F3, Netzsch, Germany) was

ACS Paragon Plus Environment

Page 6 of 34

Page 7 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

138

connected to a FTIR spectrometer (VERTEX70V, Bruker, Germany) using thermal

139

insulation pipeline, which was made from teflon. The temperature of the pipeline and

140

the FTIR sample chamber were kept at 200 oC. About 11 mg sample and

141

corresponding MCM-41 was put in the Al2O3 sample cup. The mass ratio of MCM-41

142

to sample is 10:1. Argon was used as protecting gas. And the gas flow is 60 ml/min.

143

The heating procedure started from room temperature and ended at 1000oC at the

144

heating rate of 20oC/min. For the FTIR experiment, the scanning was performed in

145

the range of 650~4000 cm-1 at the resolution of 4cm-1 and repeated for 16 times.

146 147 148

2.3 Py-GC/MS Experiment

149

To get more information of the primary reaction products, the fast pyrolyzer

150

(5200HP, CDS, USA) was connected to the gas chromatograph-mass spectrometer

151

(Clarus 560S, PerkinElmer, USA). Sample was put in the quartz tube, which can be

152

inserted in the pyrolyzer. About 0.1 mg sample (cellulose, PP, and their mixture (1:1

153

in weight)) was put in the center of the quartz tube first, then every 0.5 mg MCM-41

154

was put in the both ends of the quartz tube. At last, the silica wool was used at both

155

end of the quartz tube to avoid the solid powder being blew out of the tube. The

156

prepared tube was inserted in the pyrolyzer, which will heat from room temperature to

157

650 oC at 20 oC/ms and the temperature will be kept at 650 oC for 30 s. All the volatile

158

products were analyzed on-line using the GC-MS part. The TR-35 MS capillary

159

column (30m×0.25mm×0.25μm) was used. High purity (99.999%) Helium was

160

used as carrier gas, whose flow rate was 1mL/min. The split ratio was 1:80. The

161

heating procedure of the GC column was firstly kept at 40 oC for 4 min, then heated to

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

162

180 oC at heating rate of 4 oC/min, afterwards, heated to 280 oC at 10 oC/min and kept

163

at 280 oC for 4 min. The temperature of all the connection line and the injection port

164

was kept at 280 oC to avoid condensation of the products. For the MS part, the

165

electron, whose energy is 70 eV, was used to activate the products and get the

166

expected ion. Qualitative analysis of the pyrolysis products was based on the NIST

167

library, Wiley library and publications. 19-20, 25, 34-35

168 169 170 171 172 173

3. Results and discussion 3.1 TG and DTG analysis Without catalyst MCM-41: The TG and DTG curves of pyrolysis of cellulose, PP

174

and their mixture under argon atmosphere are shown as Figure 1a and 1b. The

175

characteristic pyrolysis parameters of cellulose, PP and their mixture are shown as

176

Table 1. According to the results, the cellulose mainly decomposes in the range of

177

300-388 oC, and the max mass loss rate appears at 354 oC (Figure 1b). While the PP

178

mainly decomposes at higher temperature in the period of 411-501 oC, and the max

179

decomposing rate appears at 473 oC (Figure 1b). For the co-pyrolysis of cellulose and

180

PP, there are two pyrolysis stages according to the DTG curve (Figure 1b). The first

181

stage starts from 306oC and ends at 370 oC, and the weight loss ratio of this stage is

182

about 28.5 wt%. While the second stage took place in the period of 419-505 oC, and

183

the weight loss ratio in this range is 60.7 wt%. The weight loss ratio of the second

184

stage is 2.1 times of the first one. The max weight lose rate of these two stages appear

185

at 350 oC and 475 oC, respectively. According to the results of the pyrolysis

186

temperature period and max weight loss ratio of the mixture, they are very close to the

ACS Paragon Plus Environment

Page 8 of 34

Page 9 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

187

temperature when they decompose individually, which suggests there is no significant

188

synergistic effect between the co-pyrolysis of cellulose and PP. Similar results for the

189

TG behavior have been reported by other researchers. 18, 28-29

190 191

With MCM-41: Notably, the pyrolysis temperature of PP is reduced with the

192

appearance of MCM-41. According to the results, the pyrolysis temperature of PP is

193

reduced significantly from 411-501 oC to 277-491oC. However, the pyrolysis

194

temperature of cellulose is still in the similar range of 302-392oC (Table 1). That

195

means there will be a wider overlap region between their pyrolysis temperature

196

(Figure 1b), which is a great advantage for the synergistic reaction. The co-pyrolysis

197

results show the first pyrolysis stage is strengthened with a weight loss ratio being

198

36.0 wt%. And the weight loss ratio of second stage is 50.2 wt%. They are all

199

calculated by normalization, which is regardless of the catalyst weight. The weight

200

loss ratio of the second stage is 1.4 times of the first one. All these data show that

201

there is really significant synergistic reaction in the co-pyrolysis of cellulose and PP

202

when the MCM-41 is added, which strengthens the reaction in the lower temperature.

203

Marcilla et al. reported the maximum mass loss temperature decreased by 110 oC

204

when loaded 16 wt% of the MCM-41. And their data revealed a reduction in the

205

activation energy of the catalytic decomposition. 24 Other researchers have also

206

reported the consistent results of the synergism of the catalytic co-pyrolysis. 12, 24, 30

207

3.2 Products analysis by on-line FTIR

208

3.2.1 Products from pyrolysis of cellulose, PP and their mixture

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

209

Products with lower molecular weight, like CO2, CO and other oxygenated

210

chemicals, can be measured using mid-infrared (FTIR) spectrum. From the

211

information of the FTIR, possible reaction mechanism of the pyrolysis of cellulose,

212

PP, and their mixture can be speculated. 19, 28-29, 31-33 The wavenumber-to-compound

213

information are shown as Table 2.

214

Without MCM-41: The FTIR spectra of the products from the first mass loss peak

215

(mainly from cellulose pyrolysis) and second mass loss peak (mainly from PP

216

pyrolysis) are shown as Figure 2a and Figure 2b. According to Figure 2a, there are

217

obvious several peaks in the FTIR spectra, which are the information about CO2, CO

218

and other oxygenated chemicals (Table 1). The spectrum of the mixture (PP:

219

cellulose=1:1 wt%) from the first mass loss is almost the same as the pure cellulose.

220

Moreover, the products from the mixture of cellulose and PP is also almost the same

221

as the pure PP for the second mass loss peak. That means there is no significant

222

synergetic reaction between cellulose and PP without MCM-41 (Figure 2).

223

With MCM-41: For the first mass loss peak, which is mainly come from pyrolysis

224

of cellulose, the enhancement in the intensity of the bands in the cellulose together

225

with MCM-41 sample reflects all of the products increase apparently, except alcohols,

226

which means the MCM-41 promotes the further cracking of the cellulose (Figure 2).

227

For the cellulose and PP together with MCM-41, carboxyl compound (1179 cm-1) and

228

alcohols (1110 cm-1) disappear. Compared to the cellulose, the carbonyl (1742 cm-1),

229

furan (749 cm-1) and hydrocarbon compounds decrease apparently. While small

230

molecular like CO2 and CO increase significantly. Notably, there are two new peaks

ACS Paragon Plus Environment

Page 10 of 34

Page 11 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

231

(2183 cm-1 and 2113 cm-1) in both of the two samples with MCM-41 in the first mass

232

loss peak, which is attributed to the alkyne bond “C≡C” or conjugated dienes

233

“C=C-C=C”. For the second mass loss peak, the yield of alkanes and olefins decrease

234

slightly for both of the two samples when the MCM-41 added in (Figure 2b). Besides,

235

there is one more peak (2881 cm-1) in both of two samples with MCM-41 in the

236

second mass loss peak, which is attributed to the methyne bond “C-H”. The results

237

suggest the MCM-41 may promote the dehydrogenation and produce more

238

unsaturated products in the pyrolysis of cellulose or/and PP. Furthermore, MCM-41

239

will strengthen the deoxidized reaction (Figure 2) in the co-pyrolysis of cellulose and

240

PP, which results in the increase of CO2 and CO.

241

3.2.2 Main change of the products along with pyrolysis temperature

242

Main products like furan compound (749 cm-1), alcohols (1110 cm-1), carboxyl

243

compound (1179 cm-1), carbonyl compound (1742 cm-1), CO (2352 cm-1), CO2 (2755

244

cm-1) and hydrocarbon compounds (2806 cm-1) are investigated here to study how the

245

products of cellulose, PP and their mixture change along with the increasing of the

246

pyrolysis temperature, which is one of the evidence of pyrolysis evolvement.

247

Products from Cellulose: According to Figure 3a, the main products of pyrolysis

248

of cellulose are carbonyl compounds, carboxylic compounds, alcohols, furans,

249

hydrocarbons, CO and CO2. The peak appears at 354oC, which is consistent with the

250

TGA result (3.1 TG and DTG analysis). The height of the peak of CO2 is half of that

251

of carbonyl compound. For the results of the cellulose with MCM-41, the catalyst

252

does not change the type of the products (Figure 3b). The yield of carboxylic

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

253

compounds is promoted in the main peak. Notably, there is still a lot of CO2 produced

254

in the higher temperature period (Figure 3b). It suggests the MCM-41 promotes the

255

decarboxylation and results in producing more carboxylic compounds and CO2 in a

256

very broad temperature range (300-700 oC).

257

Products from PP: The product of PP is much simpler than that of cellulose,

258

which has only one neat peak of hydrocarbon compounds at 2806 cm-1 (Figure 4).

259

The peak of the hydrocarbon compounds appear at 483 oC without MCM-41, and at

260

392 oC with MCM-41. The height of the latter one is higher. That means the MCM-41

261

catalyze the decomposition of PP at lower temperature and produce more hydrocarbon.

262

Elena et al. reported the FTIR spectra of pyrolysis of the PP under 315 oC, 360 oC and

263

465 oC. They also found the decomposition of the PP is prevailing at 465 oC. 29

264

Products from Mixture of cellulose and PP: The pyrolysis products of mixture of

265

cellulose and PP changing following the pyrolysis temperature are shown as Figure 5a

266

(without MCM-41) and Figure 5b (with MCM-41). According to Figure 5, there are

267

mainly two peaks for the mixture. The first peak, including carbonyls, carboxyls,

268

alcohols, furans, hydrocarbons, CO and CO2, is at 350 oC, which mainly come from

269

decomposition of cellulose. While the second peak happens at 479 oC, including

270

mainly hydrocarbon produced from pyrolysis of PP. Notably, there are also CO and

271

CO2 produced in the second peak, which is probably produced from the synergistic

272

reaction between cellulose and PP by decarboxylation and decarbonylation. In the

273

presence of MCM-41, the first peak is at 334 oC, which is a little lower than that of

274

without MCM-41. Less carbonyls and more CO2 are produced when adding PP to the

ACS Paragon Plus Environment

Page 12 of 34

Page 13 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

275

cellulose (Figure 5). The second peak is very low compared to the first peak, which is

276

at 456 oC. The yield of hydrocarbon decrease obviously in the second peak. The

277

results suggest the MCM-41 catalyst the decomposition of mixture of cellulose and

278

PP at lower temperature and enhance the yield of carbonyls, carboxyls, alcohols and

279

furans. Moreover, it also means the synergetic reaction between the cellulose and PP

280

decomposition that enhances the deoxygenation reaction will be strengthened when

281

providing MCM-41. More details of the production distribution will be discussed in

282

the following Py-GC-MS results analysis.

283

3.3 Products analysis by Py-GC/MS

284

The GC-MS curves of the cellulose, PP and their mixture decomposes at 650 oC

285

for 30s are shown as Figure 6 and Figure 7. According to related researches, 19-20, 25,

286

34-35

287

PP and their mixture is shown as Table 3 and Table 4. About one hundred compounds

288

were analyzed here. They were divided into alkenes, olefins, aromatics, oxygenated

289

groups first. Then the remaining compounds are put to the “else” group. More

290

information is in the supplementary data.

291

3.3.1 Cellulose, PP and their mixture without catalyst MCM-41

NIST and Wiley library, the main identified pyrolysis products of the cellulose,

292

The main pyrolysis product of cellulose is oxygenated chemicals, which takes up

293

90.4% of all the products (Table 3). Wherein, carbohydrate is the maximum product,

294

which accounts for 85.7% of all the products. The rest are ketones, alcohols, acids,

295

esters and epoxides, which takes up 2.0%, 1.5%, 0.42%, 0.70% and 0.07%,

296

respectively (Table 4). Furthermore, 1, 6-anhydro-Beta-D-glucopyranose is the main

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Page 14 of 34

297

monomer product of pyrolysis of cellulose, which accounts for 84.4% of all the

298

products (supplementary data). For the PP, olefins, aromatics and alkanes are the main

299

products, which account for 49.2%, 12.5% and 2.7%, respectively (Table 3). When

300

adding PP to the cellulose, though the C/H eff increases from 0 to be 1.3, the

301

oxygenated chemicals only decrease from 90.4% to 82.2%, which is much higher the

302

calculated value.

303 304 305 306 307

The calculated value is obtained from Eq. (2), Calculated value = 50%*Cellulose Value+ 50%*PP Value

(2)

In Eq. (2), Cellulose Value is the yield when using pure cellulose, and PP Value is the yield when using pure PP. Furthermore, according to the distribution of the oxygenated chemicals (Table 4),

308

the adding of the PP does not change the products significantly. It means the simple

309

mixing is not able to improve the products as expected. The FTIR data also show the

310

consistent results (3.2.1 Products from pyrolysis of cellulose, PP and their mixture).

311

Similar results have been reported by other researchers.19

312

3.3.2 Cellulose, PP and their mixture, with catalyst MCM-41

313 314

When put catalyst MCM-41 in the sample, the pyrolysis products of cellulose, PP and their mixture changed significantly.

315

According to Figure 8, oxygenated chemicals are still the main products of

316

pyrolysis of cellulose together with MCM-41, which account for 57.2% of all the

317

products. However, the distribution of the oxygenated chemicals changes significantly.

318

First, the saccharides decrease sharply from 85.7% to 10.1%. Besides, remarkable

ACS Paragon Plus Environment

Page 15 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

319

amount (34.9%) of furans are produced. It suggests the MCM-41 promotes the

320

opening ring reaction of the saccharides, which also results in the increase of other

321

oxygenated chemicals like alcohol, acid, esters, ketone and epoxides (Table 4). In

322

addition, compared to the pure cellulose, other products of high value like aromatics,

323

olefins and alkanes also increase significantly, which take up 15.7%, 4.9%, and 0.52%

324

of all the products, respectively. This result is also consistent with the front FTIR

325

result, where C=C increases significantly.

326

As for the PP and MCM-41, the olefins and aromatics are the main products,

327

which accounts for 36.2% and 34.0% of all the products. Compared to the pure PP,

328

more aromatics and less olefins are produced, which means the MCM-41 motivates

329

the cyclization of the olefins or other product to form aromatics.

330

When mixing PP with cellulose together with MCM-41, the pyrolysis products

331

change significantly. The oxygenated chemicals reduce significantly from 57.2% to

332

23.7%, while the olefins increase from 4.9% to 43.9%. And the yield of aromatic

333

hydrocarbons and alkanes are 17.8% and 2.4%. Compared to the calculated value, the

334

mixture of cellulose and PP co-pyrolysis with MCM-41 strengthens the conversion of

335

oxygenated chemicals to olefins, which notes a very significant synergism. Besides,

336

the yield of “else” group reduces significantly to be half of the calculated value,

337

which means the reactions are directed positively in some extent with the presence of

338

MCM-41. Y.-H. Lin also found the MCM-41 helps to produce more olefinic products.

339

20

340

lot (Table 4 and Figure 9). First, the saccharides continue decreasing from 10.1% to

In addition, the distribution of the produced oxygenated chemicals also improve a

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

341

4.9%. Second, the furan reduces from 34.9% to 3.5%, while the alcohol increases

342

from 7.5% to 49.3%. Third, the esters, which will improve the stability of the oil, also

343

increase from 9.5% to 17.5%. It suggests the addition of PP promotes the reactions,

344

which produce non-cyclic chemicals like alcohols, aldehydes and esters instead of

345

cyclic chemicals like furans, epoxide and phenol. Deepak, et al (2015) also reported

346

the alcohol was one of the cellulose-PP interaction product, which is involving

347

hydroxyl radical abstraction from cellulose, chain fission, β-scission and

348

intramolecular hydrogen abstraction from PP. 19 The other synthesis pathway is

349

involved by the hydrocarbon pool mechanism, where the furans will be consumed and

350

olefins will be produced. 8-9

351

3.3.3 Proposed reaction pathway

352

As shown as Figure 10, after taking all the results of TG-FTIR and GC-MS into

353

consideration, the possible reaction pathway of the co-pyrolysis of cellulose and PP

354

together with MCM-41 is summarized. The products are formed through series of

355

complicated reactions, which can be classified into three types, including

356

decomposition of cellulose, decomposition of PP, and intermolecular reactions

357

between cellulose, PP and their intermediate products. The well-known reaction

358

mechanisms, such as radical reaction mechanism, hydrocarbon pool, carbenium ion

359

reaction, β-scission and Diels-Alder reaction, 9-10, 36-37 will be involved during the

360

catalytic pyrolysis process with MCM-41.

361

The main product of pyrolysis of cellulose is oxygenated chemicals, where

362

saccharides occupied 85.6% of all identified oxygenated products (Table 4), which

ACS Paragon Plus Environment

Page 16 of 34

Page 17 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

363

was marked as path 1 in Figure 1016. While olefins, aromatics and alkanes are the

364

main products of decomposition of PP (path 6, 7, 8). 17, 25, 36 When simply mixing the

365

cellulose and PP without catalysts, there is no significant synergism between the

366

pyrolysis, which still mainly produces saccharides, olefins, aromatics and alkanes.

367

However, the adding of MCM-41 change the products significantly. Pyrolysis of

368

cellulose together with MCM-41 produces olefins, aromatics and alkanes, apart from

369

oxygenated chemicals (path 9 and path 11). 35-36 Furthermore, the furans are the major

370

products of oxygenated chemicals. It suggests the path 1 is restrained while the path 2

371

is strengthened. For the PP together with MCM-41, the catalyst strengthen the

372

reaction to form more aromatics (path 8).

373

Notably, olefins will be the major product of co-pyrolysis of cellulose and PP

374

together with MCM-41. At the same time, alcohols become the main product of the

375

oxygenated chemicals. It shows the path 3, 4, 5, 9 and 10 are strengthened, which are

376

mainly the synergetic reactions between cellulose and PP. Path 3, 4 and 5 describe the

377

radical from cracking of PP combines with the hydroxyl radical produced from

378

decomposition of cellulose (Figure 10). 19, 36 Path 9 is the cross reaction (carbenium

379

ion reaction and β-scission) between the intermediate products of the cellulose.17 And

380

Path 10 is the cross reaction of intermediate product of cellulose and PP based on the

381

hydrocarbon pool mechanism. 1-2, 8-9, 17, 36

382

However, different from the HZSM-5, the yield of aromatic compounds is less

383

than the calculated value. Shantanu Kelkar(2015) also reported mesoporous catalyst,

384

which lacks of microporous and macroporous structure, will reduce the yield of

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

385

aromatic compounds. 35 It also suggests the mechanism of the co-pyrolysis in presence

386

of MCM-41 is different from that with HZSM-5. It is believed that all-silica MCM-41

387

catalyst has no acidic sites, while HZSM-5 has both weak acid site and strong acid

388

site, which can promote the yield of aromatic compounds. In this study, all-silica

389

MCM-41 shows large surface area (756 m2/g) because of mesoporous structures, and

390

the average pore size was 3.2 nm, which partly compensates its weaker acid property.

391

12, 30

392

products to produce more olefinic products. Besides, the MCM-41 may help cellulose

393

produce more free radical and motivate the chain end scission of PP to produce more

394

olefin.

395

4. Conclusion

The MCM-41 may strengthens the β-scission of cellulose, PP and their primary

396

The co-pyrolysis of cellulose and PP in the presence of MCM-41 was studied

397

using TG-FTIR and Py-GC/MS in this paper. All the TG, FTIR and Py-GC-MS data

398

show there is no significant synergism between the cellulose and PP when simply

399

mixing them, though the C/H eff of the mixture increases to be 1.3. However, the

400

adding of MCM-41 bring significant synergism. The TG and DTG data show the

401

co-pyrolysis with MCM-41 shifts the decomposition of PP to lower temperature,

402

which provides more overlap between cellulose and PP. According to the FTIR

403

spectra, there are also CO, CO2 and carbonyl produced in the second peak (mainly

404

from PP) for the mixture together with MCM-41, which indicates the intermolecular

405

synergetic reaction. Furthermore, the results from Py-GC/MS show olefins, aromatic

406

and oxygenated compounds (mainly alcohols) are the main products of co-pyrolysis

ACS Paragon Plus Environment

Page 18 of 34

Page 19 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

407

of cellulose and PP in the presence of MCM-41. The olefins and alcohols are much

408

more than the calculated value, which are the main result of synergism. The alcohols

409

are mainly produced from the radical from cracking of PP combines with the hydroxyl

410

radical produced from decomposition of cellulose. While the olefins are produced

411

from interaction reaction (carbenium ion reaction and β-scission) between the primary

412

products of the cellulose and hydrocarbon pool reaction of primary products of

413

cellulose and PP.

414

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

415

Page 20 of 34

Table 1 Characteristic pyrolysis parameters of cellulose, PP and their mixture Decomposition

Weight loss ratio

Max mass loss

temperature range/°C

/ wt%

temperature/°C

Cell

300-388

80.7

354

Cell-MCM-41

302-392

52.2

347

PP

411 -501

95.9

473

PP-MCM-41

277-491

100.0

387

Cell-PP

306-370, 419-505

28.5, 60.7

350, 475

Cell-PP-MCM-41

302-387, 407-506

36.0, 50.2

347, 456

Feedstock

416 417

Table 2 Wavenumber to compounds of the pyrolysis products of cellulose, PP and

418

their mixture Wavenumber/cm-1

Compounds

3350~4000, 1260~2059

H2 O

2275~2390

CO2

2048~2143~2238

CO

1625~1858

Carbonyls

2666~3060

hydrocarbon

1067~1110

alcohols

1184

Carboxyl

747

furans

2848,2881,2918,2963,1375,1462

alkane

891,968,1648,3081

alkene

419 420

ACS Paragon Plus Environment

Page 21 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

421 422

Table 3 Main products from pyrolysis of cellulose, PP and their mixture at 650 oC for

423

30s (GC-MS)

424

Feedstock /% Cell Cell-MCM-41 Cell/PP Cell/PP-MCM-41 PP PP-MCM-41

H/C eff 0 0 1.3 1.3 2.0 2.0

Oxygenated 90.4 57.2 82.2 24.8 0 0

Olefins 0 4.9 4.7 43.9 49.2 36.2

Aromatics 0 15.7 1.1 17.8 12.5 34.0

Alkanes 0 0.52 0 2.4 2.7 5.4

Else 9.6 21.7 12.0 11.1 35.6 24.5

425 426

Table 4 Oxygenated chemicals of products from pyrolysis of cellulose, PP and their

427

mixture at 650 oC for 30s (GC-MS)

428

Feedstock /% H/C eff Alcohol Furans Acids Esters Saccharides Ketone Phenol Epoxide

Cell 0 1.5 0 0.42 0.70 85.7 2.0 0 0.07

Cell-MCM-41 0 7.5 34.9 5.8 9.5 10.1 17.9 4.1 10.0

Cell/PP 1.3 0.87 0 0.04 0.15 80.6 0.45 0.08 0.01

429 430

ACS Paragon Plus Environment

Cell/PP-MCM-41 1.3 49.3 3.5 6.2 17.5 4.9 13.9 0 0

Energy & Fuels

100

80

TG/%

60

40

Cell Cell/MCM-41 PP PP/MCM-41 Cell-PP Cell/PP/MCM-41

20

0 200

400

431

T/

432

(a)

600

0

DTG(%/min)

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Page 22 of 34

-20

-40

Cell Cell/MCM-41 PP PP/MCM-41 Cell-PP Cell/PP/MCM--41

-60 200

400

433

T/

434

(b)

600

435

Figure 1 TG (a) and DTG (b) curve of pyrolysis of Cellulose, PP and their mixture

436

(mass ratio= 1:1) with MCM-41 (MCM-41 to sample mass ratio=10:1)

ACS Paragon Plus Environment

Page 23 of 34

0.5

Cell Cell/MCM-41 Cel/PP Cel/PP/MCM-41

A/a.u.

0.4

0.3

0.2

0.1

500

1000

1500

2000

2500

3000

3500

4000

3500

4000

Wavenumber/cm-1

437 438

(a) First mass loss peak PP PP/MCM-41 PP/Cell PP/Cel/MCM-41

2.0

1.5

A/a.u.

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

1.0

0.5

0.0

500

1000

1500

2000

2500

3000

Wavenumber/cm-1

439 440

(b) Second mass loss peak

441

Figure 2 FTIR spectra of the first (a) and second (b) mass loss peak of pyrolysis of

442

cellulose, cellulose/MCM-41 (1:10), PP, PP/MCM-41 (1:10), cellulose/PP (1:1) and

443

cellulose/PP/MCM-41 (0.5:0.5:10),herein the absorbance value of mixture is adjusted

444

using pure cellulose or PP.

ACS Paragon Plus Environment

Energy & Fuels

0.10

furans alcohols carboxyls carbonyls CO CO2

Absorbtion /a.u.

0.08

0.06

hydrocarbon 0.04

0.02

0.00 200

400

600

800

o

Temperature / C

445 446

(a) Cellulose furans alcohols carboxyls carbonyls CO CO2

0.02

Absorbtion /a.u.

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Page 24 of 34

hydrocarbon

0.01

0.00

200 447 448

400

600

800

o

Temperature / C (b) m(Cellulose)/m(MCM-41) =1:10

449

Figure 3 FTIR spectra of the main products (furans, alcohols, carboxyls, carbonyls,

450

CO, CO2 and hydrocarbon) of cellulose (a) and cellulose/MCM-41 (b) along with

451

increasing of the pyrolysis temperature

ACS Paragon Plus Environment

Page 25 of 34

0.20 0.15

PP/MCM-41 PP

0.10

A/a.u.

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

0.05 0.00 -0.05 -0.10 200

400

600

800

Temperature/

452 453

Figure 4 FTIR spectra of the products (hydrocarbon compounds) of PP along with

454

increasing of the pyrolysis temperature

ACS Paragon Plus Environment

Energy & Fuels

0.10

Absorbtion /a.u.

0.08 0.06 0.04

furans alcohols carboxyls carbonyls CO CO2 hydrocarbon

0.02 0.00 -0.02 200

400

600

800

o

455

Temperature / C

456

(a) m(cellulose)/m(PP)=1:1

0.0100 furans alcohols carboxyls carbonyls CO CO2

0.0075

Absorbtion /a.u.

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Page 26 of 34

0.0050

hydrocarbon

0.0025

0.0000

200

600

800

o

Temperature / C

457 458

400

(b) m(cellulose)/m(PP)/m(MCM-41) =0.5:0.5:10

459

Figure 5 FTIR spectra of the main products (furans, alcohols, carboxyls, carbonyls,

460

CO, CO2 and hydrocarbon) of the mixture (cellulose and PP) along with increasing of

461

the pyrolysis temperature

ACS Paragon Plus Environment

Page 27 of 34

9

1.4x10

Relative Abundance

cellulose

9

1.2x10

9

1.0x10

8

8.0x10

8

6.0x10

8

4.0x10

8

2.0x10

0.0 5

10

15

25

30

35

Time (min)

462 463

20

Figure 6 GC-MS data of products from pyrolysis of cellulose at 650 oC for 30s 9

4.70x10

9

3.76x10

9

2.82x10

9

1.88x10

8

Relative Abundance

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

9.40x10

c b a 5

464

10

15

20

25

30

35

Time (min)

465

Figure 7 GC-MS data of products from pyrolysis of (a) cellulose/MCM-41(mass

466

ratio= 1:10), (b) PP/MCM-41(mass ratio= 1:10) and (c) Cellulose/PP/MCM-41 (mass

467

ratio= 1:1:20) at 650 oC for 30s

468

ACS Paragon Plus Environment

Energy & Fuels

60

cellulose/MCM-41 PP/MCM-41 cellulose/PP/MCM-41 calculated value

Area (%)

50 40 30 20 10 0 469

alkanes

olefins

aromatics oxygenated

else

470

Figure 8 Distribution of the products pyrolysis from cellulose/MCM-41, PP/MCM-41

471

and Cellulose/PP/MCM-41, herein calculated value is equal to 50% of the cellulose

472

value plus 50% of the PP value 50

cellulose/MCM-41 cellulose/PP/MCM-41

40

Selection (%)

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Page 28 of 34

30

20

10

0

e 473

x id po

e

s l l e s es rs ide an no ids ster on ho d r r t e c e y o a u e h a f h e k ph eh et alc cc ald sa

474

Figure 9 Distribution of the oxygenated chemicals from cellulose/MCM-41 and

475

Cellulose/PP/MCM-41

ACS Paragon Plus Environment

Page 29 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

476 477

Figure 10 Reaction pathway of co-pyrolysis of cellulose and PP together with

478

MCM-41

479

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

480 481 482

Acknowledgments

483

The authors gratefully acknowledge the funding support by the National Natural

484

Science Foundation of China (No.51576111),and the National Key Research Program

485

(No. 2016YFE0102500).

486

ACS Paragon Plus Environment

Page 30 of 34

Page 31 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

487 488 489

References

490

[1] Beom, S. K.; Young, M. K.; Hyung, W. L.; Jungho, J.; Do, H. K.; Sang, C. J.;

491

Chui, C. W.; Young, K. P. ACS Sustainable Chem. Eng. 2016, 4, 1354-1363.

492

[2] Li, X. Y.; Li, J.; Zhou, G. Q.; Feng, Y.; Wang, Y. J.; Yu, G.; Deng, S. B.; Huang,

493

J.; Wang, Bin. Appl. Catal. A: Gen. 2014, 481, 173-182.

494

[3] Dinesh, M.; Charles, U. P.; Philip, H. S. Energy Fuels 2006, 20, 848-889.

495

[4] Yu, Y.; Chua, Y. W.; Wu, H. W. Energy Fuels 2016, 30, 4145-4149.

496

[5] Tian, Y. Y.; Qiao, Y. Y. Sino-global Energy 2014, 19, 19-24.

497

[6] Mortensen, P. M.; Grunwaldt, J. D.; Jensen, P. A.; Knudsen, K. G.; Jensen, A. D.

498

Appl. Catal. A: Gen. 2011, 407, 1-19.

499

[7] Chen, N. Y.; Degnan, T. F.; Koenig, L. R. Chem. Tech. 1986, 16 (8), 506-511.

500

[8] Zhang, H. Y.; Cheng, Y. T.; Vispute, T. P.; Xiao, R.; Huber, G. W. Energy

501

Environ. Sci. 2011, 4 (6), 2297-2307.

502

[9] Zhang, H. Y.; Carlson, T. R.; Xiao, R ; Huber, G. W. Green Chem. 2012, 14 (1),

503

98-110.

504

[10] Faisal A.; Wan, M. D. Energy Convers. Manage. 2014, 87, 71-85.

505

[11] Association of Plastic Manufacturers Europe. An analysis of European plastics

506

production, demand and waste data. Belgium: European Association of Plastics

507

Recycling and Recovery Organisations, 2016, 1-38.

508

[12] Liu, M.; Zhuo, J. K.; Xiong, S. J.; Yao, Q. Energy Fuels 2014, 28, 6038-6045.

509

[13] Aguado, J.; Sotelo, J. L.; Serrano, D. P.; Calles, J. A.; Escola, J. M. Energy Fuels

510

1997, 11(6), 1225-1231.

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

511

[14] Zhou, H.; Meng, A. H.; Long, Y. Q.; Li, Q. H.; Zhang, Y. G. Renew. Sust. Energ.

512

Rev. 2014, 36, 107-122.

513

[15] Mihai, B.; Suat U.; Cornelia, V.; Jale, Y. Fuel 2010, 89, 1911-1918.

514

[16] Bhattacharya, P.; Steele, P. H.; Hassan, E. B. M.; Mitchell, B.; Ingram, L.;

515

Pittman, C. U. Fuel 2009, 88, 1251-1260.

516

[17] Dorado, C.; Mullen, C. A.; Boateng, A. A. ACS Sustainable Chem. Eng. 2014, 2

517

(2), 301-311.

518

[18] Li, X. Y.; Zhang, H. F.; Li, J.; Su, L.; Zuo, J. N.; Komarnenic, S.; Wang, Y. J.

519

Appl. Catal. A: Gen. 2013, 455, 114-121.

520

[19] Deepak, K. O.; Vinu, R. RSC Adv. 2015, 5, 66861-66870.

521

[20] Lin, Y. H.; Yen, H. Y. Polym. Degrad. Stabil. 2005, 89, 101-108.

522

[21] Sharypov, V. I.; Beregovtsova, N. G.; Kuznetsov, B. N.; Baryshnikov, S. V.;

523

Cebolla, V. L.; Weber, J. V.; Collura, S.; Finqueneisel, G.; Zimny, T. J. Anal. Appl.

524

Pyrolysis 2006, 76, 265-270.

525

[22] Rutkowski, P. J. Anal. Appl. Pyrolysis 2012, 95, 38-47.

526

[23] Zhang, H. Y.; Nie, J. L.; Xiao, R.; Jin, B. S.; Dong, C. Q.; Xiao, G. M. Energy

527

Fuels, 2014, 28 (3), 1940-1947.

528

[24] Marcilla, A.; Gomez, A.; Reyes, J. A.; Giner, A. Polym. Degrad. Stabil. 2003, 80,

529

233-240.

530

[25] Serrano, D. P.; Aguado, J.; Escola, J. M. ACS Catal. 2012, 2, 1924-1941.

531

[26] Ibá˜nez, M.; Artetxe, M.; Lopez, G.; Elordi, G.; Bilbao, J.; Olazar, M.; Casta˜no,

532

P. Appl. Catal. B: Environ. 2014, 148-149, 436-445.

ACS Paragon Plus Environment

Page 32 of 34

Page 33 of 34

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

Energy & Fuels

533

[27] Melligan, F.; Hayes, M. H.; Kwapinski, W.; Leahy, J. J. Energy Fuels 2012, 26,

534

6080-6090.

535

[28] Zhu. X. L. Molecular spectroscopy analytical technology combined with

536

chemometrics and its application. Chemical Industry Press: Beijing, 2011; pp

537

160-195.

538

[29] Elena, P.; Manuela, T. N.; Maria, C. P.; Cornelia, V. Polym. Degrad. Stabil.

539

2014, 109, 13-20.

540

[30] Aguado, J.; Serrano, D.P.; Miguel, G. S.; Escola, J.M.; Rodrıguez, J.M. J. Anal.

541

Appl. Pyrolysis 2007, 78, 153-161.

542

[31] Du, Y. Y.; Jiang, X. G.; Lv, G. J.; Li, X. D.; Chi, Y.; Yan, J. H.; Liu, X. D.;

543

Alfons, B. J. Therm. Anal. Calorim. 2014, 117, 343-353.

544

[32] Wang, S. R.; Lin, H. Z.; Zhang, L.; Dai, G. X.; Zhao, Y.; Wang, X. L.; Ru, B.

545

Energy Fuels 2016, 30, 5721-5728.

546

[33] Zhang, H. Y.; Shao, S. S.; Xiao, R.; Shen, D. K.; Zeng, J. M. Energy Fuels 2014,

547

28, 52-57.

548

[34] Yang, Y.; Luo, Z. Y.; Chen, W.; Li, G. X.; Lu, K. Y.; Zhang, H. L. Energy

549

Procedia 2014, 61, 2093-2096.

550

[35] Shantanu, K.; Christopher, M. S.; Kevin, A.; Li, Z. L.; Ambareesh, M.; Dennis, J.

551

M.; Thomas, J. P.; Robert, M. K. Appl. Catal. B: Environ. 2015, 174-175, 85-95.

552

[36] Zhang, X. S.; Lei, H. W.; Chen, S. L.; Wu, J. Green Chem. 2016, 18, 4145-4169.

553

[37] Juan, D. M.; Alberto, V.; Ana, M. M.; Ramón, M.; Maria, V. N.; Neus, P.; Anna,

554

A.; Jordi, B.; Tomás, G. Fuel Processing Technol. 2014, 119, 263-271.

ACS Paragon Plus Environment

Energy & Fuels

1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60

555 556 557 558 559 560 561 562 563

Supporting Information: 1. Table S1 Main identified products from pyrolysis of cellulose at 650 oC for 30s (GC-MS) 2. Table S2 Main identified products from pyrolysis of cellulose, PP and their mixture together with catalyst at 650 oC for 30s (GC-MS) 3. Table S3 All the peaks from pyrolysis of cellulose, PP and Cellulose/PP at 650 oC for 30s (GC-MS) 4. Table S4 All the peaks from pyrolysis of cellulose/MCM-41, PP/MCM-41 and Cellulose/PP/MCM-41 at 650 oC for 30s (GC-MS)

ACS Paragon Plus Environment

Page 34 of 34