Pretreatment of Corn Stover with Diluted Nitric Acid for the

Dec 5, 2017 - In this study, dilute nitric acid was selected as the catalyst to pretreat corn stover. The effects of nitric acid pretreatments on the ...
0 downloads 10 Views 1MB Size
Subscriber access provided by UNIV OF OREGON

Article

Pretreatment of corn stover with diluted nitric acid for enhancement of acidogenic fermentation Rui Zhang, Fengguo Liu, Hanqiao Liu, and Dianxin Zhang Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/acs.energyfuels.7b02596 • Publication Date (Web): 05 Dec 2017 Downloaded from http://pubs.acs.org on December 12, 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 27 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

Pretreatment of corn stover with diluted nitric acid for

2

enhancement of acidogenic fermentation

3 4

Rui Zhang*, Fengguo Liu, Hanqiao Liu, Dianxin Zhang

5

School of Energy and Safety Engineering, Tianjin Chengjian University, Tianjin 300384, China

6

*Corresponding author: Rui Zhang

7

E-mail: [email protected]

8

Telephone: +86 22 23085277

9 10 11 12 13 14 15 16 17 18 19 20 21 22

1

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

23

ABSTRACT: In this study, dilute nitric acid was selected as the catalyst

24

to pretreat corn stover. The effects of nitric acid pretreatments on the

25

efficiency of acidogenic fermentation and the acidogenic characteristic of

26

prehydrolysates were evaluated. The results showed that about 97%

27

hemicelluloses were recovered at the optimal condition (150 oC, 0.6%

28

HNO3, 2min). Acidogenic fermentation of prehydrolysate B (the highest

29

yield of total sugar) obtained at the optimal condition proved to be more

30

efficient, compared to prehydrolysate A (no inhibitor) and prehydrolysate

31

C (the highest yield of inhibitors), the VFAs concentration can reach the

32

highest level, and the distribution of VFAs exhibited butyric acid type

33

fermentation, this was more suitable for subsequent methanogenic

34

fermentation. This research provided an effective and suitable method for

35

accelerate biogas production from corn stover.

36

KEYWORDS: Pretreatment, Nitric acid, Corn stover, Acedogenic

37

fermentation

38 39

1. INTRODUCTION

40

Corn stover is the most abundant agricultural residues in china, and it

41

represents an ideally renewable, cheap, widely available feedstock for the

42

production of bioethanol, biogas, biohydrogen, and other chemicals.

43

Among all of the technologies, conversion of corn stover to biogas is one

44

of the most effective and cheapest methods, 1-3 which not only can supply 2

ACS Paragon Plus Environment

Page 2 of 27

Page 3 of 27 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

sustainable energy resources, but also can reduce the environmental

46

pollution. Besides, the Chinese government introduces a series of energy

47

structure adjustment policies currently, such as the project of changing

48

fuel from coal to natural gas, which makes the demand of natural gas

49

increasing quickly. Therefore, biogas production from corn stover is

50

promising. However, the main components of corn stover are

51

polysaccharide (cellulose and hemicellulose) and lignin, which form

52

complex three dimensional structures and are less available for

53

microorganisms under normal fermentation. Therefore, to achieve

54

efficient use of corn stover, pretreatment is the key point. Pretreatment

55

prior to anaerobic digestion has been proven to be one of simple and

56

effective methods to improve biodegradability of lignocellulosic

57

materials.4-6

58

A number of pretreatment methods have been investigated by former

59

researchers, including dilute acid pretreatment, alkali, inorganic salt,

60

liquid hot water, steam explosion, enzymatic pretreatment, and other

61

methods.7-12 Among all the methods, dilute acid pretreatment is the most

62

frequently studied process for corn stover, which can effectively convert

63

most of hemicellulose (about 80-90%) into fermentable sugars.13 Dilute

64

acid pretreatment has been considered as a suitable technology for

65

industrial scale biogas production.14-16 Sulfuric acid is commonly

66

employed as catalyst.17-19 As another strong acid, nitric acid has been 3

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

67

studied by a few researchers. Xiao et al. found that nitric acid could

68

accelerate the solubilization of ligin in the pretreatment of the newspaper

69

for bioconversion to methane.20 Rodriguez-chong et al. reported the effect

70

of nitric acid pretreatment of sugar cane bagasse, and confirmed that

71

nitric acid needed a shorter time to ensure high sugar concentration and

72

low concentration of inhibitors as compared with sulfuric acid and

73

hydrochloric acid.21In our previous study,22 nitric acid was also used to

74

pretreat corn stover, the results showed that 96% of the hemicelluloses

75

were hydrolyzed under the optimum condition. Thus, nitric acid has been

76

shown to be effective for hydrolysis of ligocellulosic materials.

77

Furthermore, for methane production, nitric acid pretreatment was more

78

suitable than sulfuric acid, by reason that sulfate was converted to H2S,

79

which is a pollutant, while nitrate was converted to N2, which is

80

environmentally friendly in the anaerobic fermentation. Therefore, nitric

81

acid pretreatment is a favorable method for the conversion of corn stover

82

to methane.

83

In this study, diluted nitric acid was employed as a catalyst to hydrolyze

84

corn stover to transfer as many of the effective components (mainly

85

sugars) of the corn stover as possible into the liquid phase

86

(prehydrolysate), then the prehydrolysate was used to produce volatile

87

fatty acids (VFA). The prehydrolysate is primarily composed of small

88

molecule compounds that are more accessible to microorganisms. 4

ACS Paragon Plus Environment

Page 4 of 27

Page 5 of 27 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

89

Therefore, acidogenic fermentation of prehydrolysate could be efficient,

90

which will accelerate biogas production from corn stover. In addition, the

91

solid residue is also very valuable for containing cellulose and lignin, it

92

could be used to prepare carbonaceous solid acid, which showed excellent

93

catalytic hydrolysis performance for the lignocellulosic biomass.23-25

94

Therefore, the corn stover could be utilized efficiently.

95

However, the components of prehydrolysates obtained at different

96

pretreatment conditions were different, which influence the efficiency of

97

acidogenic fermentation greatly. So far, the comparison of acid

98

production capacity of different type of prehydrolysate obtained by nitric

99

acid pretreatment is relatively little. In this study, the contents of

100

prehydrolysates including sugars, acetic acid, and inhibitors (furfural and

101

HMF) were determined to evaluate the pretreatment effect. Then, three

102

types of prehydrolysates from nitric acid pretreatments were fermented to

103

produce volatile fatty acids (VFAs) and the acid production capacity of

104

sugar and inhibitors (furfural and HMF) in the prehydrolysate was

105

investigated.

106 107

2. MATERIAL AND METHODS

108

2.1. Raw materials

109

Corn stovers were harvested at a local farm and leaves were discarded.

110

The corn stover was air-dried, milled, screened to select the fraction of 5

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

111

particles with a size lower than 0.5 mm, and homogenized in a single lot

112

and stored until needed. The initial composition of corn stover was

113

(weight percent on dry basis): glucan, 36.2±0.62%; xylan, 19.0±0.36%;

114

araban, 2.9±0.43%; acetyl group, 4.4±0.59%; Klason lignin, 14±

115

0.28%; ash, 7.4±0.37%; and 16.1% others which are mainly protein,

116

extractives, and non-structural sugars. These values were in the range

117

reported by other researchers for corn stover.26-29

118

2.2. Nitric acid-catalyzed hydrothermal pretreatment

119

Pretreatment was performed in glass media bottles at 120 oC and in a

120

laboratory-scale pure titanium reactor with a total volume of 500 ml at

121

150 oC and 180 oC. The glass media bottles were heated to 120 oC with

122

autoclave. The pure titanium reactor was heated to 150 oC and 180 oC

123

with an electric heater. When the desired temperature inside the reactor

124

was reached, the treatment time was started to be counted. After the target

125

treatment time was reached, the reactors were cooled to below 50 oC with

126

room-temperature water. Then the pretreatment product was filtered by

127

vacuum pump, obtaining a solid phase and a liquid phase for further

128

analysis. Nitric acid concentrations were 0.1%, 0.6% (w/w). The

129

liquor/solid ratio was 9 g liquor/g solid corn stover in all experiments.

130

2.3. Anaerobic acidogenic fermentation

131

Three kinds of specific prehydrolysates under different experimental

132

conditions were selected for further anaerobic acidogenic fermentation. 6

ACS Paragon Plus Environment

Page 6 of 27

Page 7 of 27 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

133

The first kind of prehydrolysate (prehydrolysate A) is obtained when the

134

total sugars were relatively low, but the inhibitors (furfual and HMF)

135

were zero. The second kind of prehydrolysate (prehydrolysate B) is

136

obtained when the total sugars reached the maximum. The third kind of

137

prehydrolysate (prehydrolysate C) is obtained when the inhibitors (furfual

138

and HMF) reached the maximum.

139

The acidogenic fermentation of the prehydrolysates took place in

140

anaerobic bottles which were first pruged by nitrogen to remove the air in

141

the headspace of bottles prio to the experiments, and then these bottles

142

were placed in a rotary shaker (150 rpm) and incubated at 37 oC (±1 oC).

143

The volume of each bottle was 250 ml, and the working volume was 200

144

ml. The seeding sludge was obtained from a municipal sewage treatment

145

plant located in Tianjin, china. Before acidogenic fermentation, the

146

prehydrolysate was diluted to meet the feed to microbes ratio (F/M ratio)

147

of 1.0 g of COD/g VSS.30,31 Assay with seed sludge alone was performed

148

as a control. VFAs produced from acidogenic fermentation of the

149

prehydrolysate were subtracted from the assay.

150

2.4. Combined severity factor

151

Combined severity factor (CSF) has been reported to evaluate the effect

152

of the hydrolysis conditions on the concentration of total sugars and

153

inhibitors, which combines catalyst concentration, reaction time, and

154

temperature into a single variable.32-35 The combined severity factor was 7

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 8 of 27

155

defined as,

156

  T − 100   CSF = log  t ⋅ exp    − pH  14.75   

157

Where t is the reaction time (min), T is the reaction temperature (oC), and

158

pH is the acidity of aqueous solution determined by the acid

159

concentration.

160

2.5. Analytical method

161

The chemical composition of corn stover was determined according to the

162

National Renewable Energy Laboratory analytical methods for biomass.36

163

Sugars and VFAs were determined using HPLC (LabAlliance, USA) with

164

a

165

5-hydroxymethyl-2-furfural (HMF)) with a UV detector by using a

166

column (BioRad Aminex HPX-87H, 300×7.8 mm) at 65 oC and 5 mM

167

H2SO4 as the mobile phase at a flow rate of 0.6 ml/min.

168

COD was determined with a standard method.37

169

3. RESULTS AND DISCUSSION

170

3.1. Optimization of pretreatment conditions on the contents of

171

prehydrolysates

172

Figure 1 shows the yields of xylose, glucose and arabinose obtained from

173

the prehydrolysates. Figure 1 showed that the yields of soluble xylose

174

increased with HNO3 concentration and reaction time at 120 oC, and the

175

xylose yield reached 88.9% at 120min and 0.6% HNO3.

176

As the temperature rose to 150 oC, as shown in Figure 1, the yield of

refractive

detector

and

inhibitors

8

ACS Paragon Plus Environment

(furfural

and

Page 9 of 27 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

177

soluble xylose increased all the time when the HNO3 concentration was

178

0.1%, while it decreased gradually with time when the HNO3

179

concentration was 0.6%, which can be attributed to the further

180

degradation of xylose. These results indicated that increasing acid

181

concentration can accelerate the degradation of xylan if the temperature is

182

high enough and prolonging the time results in the degradation of soluble

183

xylose.

184

As the temperature rose to 180 oC, the yields of xylose increased with a

185

narrow range in the first 10 min with 0.1% HNO3 and in the first 5 min

186

with 0.6% HNO3 and then decreased gradually. Meanwhile, the yield of

187

xylose obtained at 180 oC, 0.1% HNO3 was higher than that obtained at

188

150 oC, 0.1% HNO3, while the yield of xylose obtained at 180 oC, 0.6%

189

HNO3 was lower than that obtained at 150 oC, 0.6% HNO3, the results

190

implies that higher temperature can accelerate the degradation of xylan

191

when the acid concentration is low, but it can result in undesirable

192

decomposition of xylose when the acid concentration is high enough. The

193

lowest yield of xylose was 7.8% under harshest condition (180 oC, 0.6%

194

HNO3, 60min). The maximum soluble xylose yield in this study was

195

96.9% (150 oC, 0.6% HNO3, 2min), which is higher than that from

196

H2SO4-catalyzed hydrolysis reported by Liu et al (2004) (90.0%),38

197

Fe(NO3)3-catalyzed hydrolysis reported by Sun (2011) (91.8%)

198

dilute formic acid catalyzed hydrolysis reported by Xu (90.9%)40. The 9

ACS Paragon Plus Environment

39

and

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

199

higher xylose yield implies that HNO3 is a more efficient catalyst than

200

sulfuric acid, Fe(NO3)3 and fomic acid.

201

A similar trend was found with arabinose, as shown in Figure 1. The

202

degradation of arabinan can be accelerated by increasing temperature and

203

HNO3 concentration. The maximum arabinose yield of 100% was

204

obtained at the condition of 120 oC, 0.6% HNO3, 120min, which was

205

higher than that of xylose, besides, the maximum arabinose yield was

206

obtained at a lower temperature than that of xylose. These results indicate

207

that it is much easier to obtain arabinose than xylose.

208

Figure 1 illustrates the effects of HNO3 concentration, temperature and

209

reaction time on the glucose yield. The trends in Figure 1 suggested that

210

the glucose yield increased first then decreased with temperature when

211

the HNO3 concentration was 0.1%. However, when the HNO3

212

concentration increased to 0.6%, the glucose yield increased quickly with

213

increasing temperature. These results show that the acid concentration is

214

very important for glucan hydrolysis. As shown in Figure 1, the reaction

215

time had little effect on glucose yields, prolonging time can result in

216

degradation of glucose to HMF when the temperature rose to 180 oC. The

217

maximum glucose yield was 18.6% obtained at 180 oC with 0.6% HNO3

218

after 10min reaction, which is lower than that of xylose and arabinose.

219

The result indicates that cellulose is more difficult to degrade as

220

compared to hemicellulose. 10

ACS Paragon Plus Environment

Page 10 of 27

Page 11 of 27 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

221 222 223

Figure 1. Effects of hydrolysis temperature and nitric acid concentration on sugar yield

224

Acetic acid was generated in the hydrolysis of acetyl groups of the

225

hemicelluloses. Figure 2 shows the variation of acetic acid concentration

226

for different temperature, acid concentration and response times. As

227

shown in Figure 2, the acetic acid concentration increased quickly with

228

temperature and time when HNO3 concentration was 0.1%. However,

229

when HNO3 concentration rose to 0.6%, the acetic acid concentration

230

increased quickly first while increasing temperature from 120 oC to 150

231

o

C, and then the rate of release was very slow but the acetic acid

232

concentration was not decreased, indicating that no decomposition

233

reaction took place. Acetic acid produced in the hydrolysis process not

234

only can promote further hydrolysis of corn stover, but can be used as a

235

good substrate in the methane production process.14

236 237

Figure 2. Effects of hydrolysis temperature and nitric acid concentration on the

238

concentration of acetic acid

239

Furfural was generated as a degradation product from xylose and

240

arabinose, HMF was the decomposition of glucose. Furfural and HMF are

241

furans compounds. Figure 3 shows the concentration variation of furfural

242

and HMF for different temperatures, HNO3 concentration and response

243

time. The result suggested that the concentrations of furfural and HMF 11

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

244

were both increased with the increased temperature, acid concentration

245

and reaction time. The decomposition reaction did not occur under

246

condition of 120 oC, 0.1% HNO3. However, when the temperature rose to

247

180 oC, the decomposition reactions were accelerated. The maximum

248

concentrations of furfural and HMF were 12.3 g/L and 7.9 g/L

249

respectively, which were obtained in the experiment performed with 0.6%

250

HNO3 at 180 oC with the reaction time of 60 min. This result implied that

251

most of the monosaccharide can be decomposed under the harshest

252

condition.

253 254 255

Figure 3. Effects of hydrolysis temperature and nitric acid concentration on the concentration of furfural and HMF

256

Both hexose and pentose can be used as substrates for methane

257

production by a mixture of microorganisms, but sugar degradation

258

compounds (furfural and HMF) are fermentation inhibitors. Therefore, to

259

evaluate the efficiency of hydrolysis conditions comprehensively, the

260

concentrations of sugars and furans (furfural and HMF) were compared at

261

various CSF (0.27-3.09). The results were shown in Figure 4, and it

262

indicated that the highest concentration (30.9 g/L) of total sugars was

263

obtained when CSF was fixed at about 0.73, corresponding to the

264

condition of 150 oC, 0.6% HNO3, and 2 min. The highest concentration

265

(20.2 g/L) of total furans when CSF was fixed at 3.09, corresponding to

266

the condition of 180 oC, 0.6% HNO3, and 60 min. 12

ACS Paragon Plus Environment

Page 12 of 27

Page 13 of 27 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

267 268

Figure 4. Concentration of total sugars and furans as a function of combined severity

269

factor (CSF)

270

In order to evaluate the pretreatment of corn stover with nitric acid

271

completely, a simple economical analysis was made. The cost of the nitric

272

acid pretreatment mainly depends on the dosage and price of catalyst

273

according to our analysis. Hence, the cost of nitric acid pretreatment was

274

calculated according to HNO3. The optimum condition was taken for

275

example. At this condition, the HNO3 concentration is 0.6% (w/w), which

276

was prepared by 65% (w/w) HNO3, thereby, 0.083g 65% (w/w) HNO3

277

was needed when 1g corn stover was pretreated. The price of 65% (w/w)

278

HNO3 was $166 per ton according to market price. Therefore, the cost of

279

the nitric acid pretreatment is $ 0.014/Kg corn stover. Although the price

280

of HNO3 is higher than H2SO4 and HCl, the negative influence of HNO3

281

on anerobic fermentation is lower than H2SO4 and HCl, therefore, HNO3

282

has advantage. A new and high efficient method was needed to reduce its

283

pretreatment cost, which could increase its competitiveness as a catalyst.

284

3.2. Effect of prehydrolysate to the amount and composition of VFAs

285

Three kinds of prehydrolysate were chosen to be the substrate for

286

anaerobic acidogenic fermentation. The compositions of prehydrolysate A,

287

prehydrolysate B and prehydrolysate C are shown in Table 1.

288

Prehydrolysate A was obtained when nitric acid concentration was low, 13

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 27

289

total sugar concentration was almost equal to that of prehydrolysate C,

290

and

291

Prehydrolysate B was obtained when total sugar concentration reached

292

the maximum, prehydrolysate C was obtained when the total furans

293

concentration reached the maximum. The three kinds of prehydrolysates

294

were selected to compare the effect of different concentration of sugar

295

and furan on the acidogenic fermentation process.

the

furans

(furfural

and

HMF)

concentration

was

zero.

296 297

Table 1 Pretreatment condition of three kinds of prehydrolysates and their

298

compositions

299 300

Figure 5 shows the variation of VFAs concentration in prehydrolysate A,

301

prehydrolysate B and prehydrolysate C fermentations. As shown in

302

Figure 5, VFAs concentration in prehydrolysate B fermentation was

303

higher than that in prehydrolysate A and prehydrolysate C at any time in

304

the whole process. The maximum VFAs concentration in prehydrolysate

305

A, B and C digestions were 1110.8 mg COD/ L, 2513.4 mg COD/ L, and

306

1095.4 mg COD/ L, respectively. This result implies that sugar was easier

307

to be utilized by bacteria than furfural and HMF. In addition, VFAs

308

concentration in prehydrolysate A fermentation was higher than that of

309

prehydrolysate C after 10h. Although the initial COD was the same, total

310

sugar was almost equal, while the inhibitor (furfural and HMF) 14

ACS Paragon Plus Environment

Page 15 of 27 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

311

concentration in prehydrolysate C was higher than that in prehydrolysate

312

A. This indicated that furfural and HMF were harder to be utilized by

313

acid-producing bacteria than sugar.

314 315

Figure 5. Variation of VFAs concentration during the acidogenic fermentation with

316

different prehydrolysates as substarte

317

Figure 6-8 show the VFAs distribution patterns with the addition of

318

different prehydrolysates. As shown in Figure 6, acetic acid and propionic

319

acid accounted for 67-98% of the VFAs from 2 to 72 h. Then the

320

proportion of propionic acid decreased to zero while the proportion of

321

acetic acid increased. The acids were only acetic acid and valeric acid

322

from 96 to120 h. The results indicated that the fermentation of

323

prehydrolysate A exhibited

324

fermentation before 72 h, which can result in low efficiency of

325

methanogenic phase due to the low acetogenic rate of propionic acid.

326

However, the final acid products of prehydrolysate A were suitable for

327

subsequent acidogenic fermentation. As shown in Figure 7, acetic acid

328

and propinic acid accounted for most of the VFAs before 48h, and then

329

butyric acid exceeded propionic acid. Furthermore, the proportion of the

330

sum of acetic acid and butyric acid was about 80% during 48 to 120h in

331

prehydrolysate B, exhibiting the feature of butyric acid fermentation type,

332

which was proved to be favorable to the subsequent biogas production.

the feature of propionic acid-type

15

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

333

As shown in Figure 8, the proportion of the sum of acetic acid and

334

propionic acid were 65-90% in prehydrolysate C during the acidogenic

335

fermentation process, and propionic acid accounted for most of VFAs,

336

exhibiting propionic acid fermentation type.

337 338 339 340 341

Figure 6. VFAs distribution patterns during the acidogenic fermentation with prehydrolysate A as substrate Figure 7. VFAs distribution patterns during the acidogenic fermentation with prehydrolysate B as substrate

342

Figure 8. VFAs distribution patterns during the acidogenic fermentation with

343

prehydrolysate C as substrate

344

4. CONCLUSION

345

In this study, pretreatment of corn stover by dilute nitric acid and

346

acidogenic fermentation with different prehydrolysates were investigated.

347

The results show that nitric acid hydrolysis can be efficient. The VFAs

348

produced by prehydrolysate B was higher than that of prehydrolysate A

349

and C all the time during the acidogenic fermentation process, and the

350

maximum VFAs produced by prehydrolysate B was twice as much as that

351

of prehydrolysate A and C. In addition, the distribution of VFAs produced

352

by prehydrolysate B is more suitable for subsequent methanogenic

353

fermentation. Therefore, prehydrolysate B obtained at the condition of

354

150 oC, 0.6% HNO3 and 2 min, can be used as good substrates for the

355

acidogenic fermentation process.

356

AUTHOR INFORMATION 16

ACS Paragon Plus Environment

Page 16 of 27

Page 17 of 27 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

357

Corresponding Author

358

*E-mail: [email protected]

359

Notes

360

The authors declare no competing financial interest.

361

ACKNOWLEDGEMENT

362

This research was funded by National Key Technology R&D Program

363

(Grant NO. 2007BAD75B07), Doctoral Scientific Research Foundation

364

of Tianjin Chengjian University (Grant NO. 60-1302), and The Basic

365

Scientific Research Sponsored Project of Universities in Tianjin (Grant

366

NO. 2016CJ05).

367

REFERENCES

368

(1) Ji, J.L.; Zhang, J.Y.; Yang, L.T.Y.; et al. Environ. Technol. 2017, 38,

369

1465-1473.

370

(2) Croce, S.; Wei, Q.; D'Imporzano, G.; et al. Biotechnol. Adv. 2016, 34,

371

1289-1304.

372

(3) Hassan, M.; Ding, W.M.; Umar, M.; et al. Energ. Fuel. 2016, 30,

373

9463-9470.

374

(4) Zheng, M. X.; Li, X. J.; Li L. Q. Bioresour. Technol. 2009, 100,

375

5140-5145.

376

(5) Qing, Q.; Zhou L. L.; Guo Q.; et al. Bioresour. Technol. 2017, 233,

377

284-290.

378

(6) Wang, F.; Zhang, D.L.; Wu, H.K.; et al. Bioresour. Technol. 2016, 218, 17

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

379

731-736.

380

(7) Amnuaycheewa, P.; Hengaroonprasan, R.; Rattanaporn, K.; et al. Ind.

381

Crop. Prod. 2016, 87, 247-254.

382

(8) Xu, H.F.; Li, B.; Mu, X.D. Ind. Eng. Chem. Res. 2016, 55, 8691-8705.

383

(9) Baral, N.R.; Shah, A. Bioresour. Technol. 2017, 232, 331-343.

384

(10) Zhi, Z.H.; Li, N.; Qiao, Y.N.; et al. Ind. Crop. Prod. 2015, 76,

385

672-680.

386

(11) He, L.L.; Huang, H.; Zhang, Z.Y. Curr. Org. Chem. 2015, 19,

387

437-446.

388

(12) Hu, Y.; Pang, Y.Z.; Yuan, H.R.; et al. Bioresour. Technol. 2015, 175,

389

167-173.

390

(13) Ruiz, E.; Romero, I.; Moya, M.; et al. Bioresour. Technol. 2013, 140,

391

292-298.

392

(14) Zhao, X.; Wang, L.J.; Lu, X.B.; et al. Bioresour. Technol. 2014, 158,

393

12-18.

394

(15) Zhang, R.; Lu, X.B.; Liu, Y.; et al. Chem. Eng. Technol. 2011, 34,

395

409-414.

396

(16) Marzialetti, T.; Olarte, M.B.V,; Sievers, C.; et al. Ind. Eng. Chem.

397

Res. 2008, 47, 7131-7140.

398

(17) And, C.L.; Wyman, C.E. Ind. Eng. Chem. Res. 2004, 43, 2781-2788.

399

(18) Cai, B.Y.; Ge, J.P.; Ling, H.Z.; et al. Biomass Bioenergy 2012, 36,

400

250-257. 18

ACS Paragon Plus Environment

Page 18 of 27

Page 19 of 27 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

401

(19) Feher, A.; Feher, C.; Rozbach, M.; et al. Chem. Biochem. Eng. Q.

402

2017, 31, 77-87.

403

(20) Xiao, W.P.; Clarkson, W.W. Biodegradation. 1997, 8, 61-66.

404

(21) Rodr´ıguez-Chong, A.; Ram´ırez, J.A.; Garrote, G.; et al. J. Food

405

Eng. 2004, 61, 143-152.

406

(22) Zhang, R.; Lu, X. B.; Sun, Y. S.; et al. J. Chem. Technol. Bio. 2011,

407

86, 306-314.

408

(23) Chen, G.; Fang, B.S.; Bioresour. Technol. 2011, 102, 2635-2640.

409

(24) Jiang, Y.J.; Li, X.T.; Wang, X.C.; et al. Green Chem. 2012, 14,

410

2162-2167.

411

(25) Victor, A.; Pulidindi, I.N.; Kim, T.H.; et al. RSC Adv. 2016, 6, 31-38.

412

(26) Walsum G.P.; Shi H.L.. Bioresour. Technol. 2004, 93, 217-226.

413

(27) Wyman C.E.; Dale B.E.; Elander R.T.; et al. Bioresour. Technol.

414

2005, 96, 2026-2032.

415

(28) Kim T.H.; Lee Y.Y. Bioresour. Technol. 2006, 97, 224-232.

416

(29) Li Y.Q.; Zhang R.H.; Chen C.; et al. Bioresour. Technol. 2013, 149,

417

406-412.

418

(30) Lin, C. Y.; Wu, C. C.; Wu, J. H.; et al. Biomass Bioenergy 2008, 32,

419

1109-1115.

420

(31) Wang, X. Y.; Zhang, S.T.; Wang, J.; et al. Bioresources 2012, 7,

421

1111-1122.

422

(32) Silverstein, R. A.; Chen, Y.; Sharmashivappa, R. R.; et al. Bioresour. 19

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 20 of 27

423

Technol. 2007, 98, 3000-3011.

424

(33) Liu, L.; Sun, J. S.; Cai, C. Y.; et al. Bioresour. Technol. 2009, 100,

425

5865-5871.

426

(34) Zhou, N.; Zhang, Y.M.; Wu, X.B.; et al. Bioresour. Technol. 2011,

427

102, 10158-10161.

428

(35) Baral, N. R.; Shah, A. Bioresour. Technol. 2017, 232, 331-343.

429

(36) Sluiter A, Hames B, Ruiz R, Scarlata C, Sluiter J, Templeton D.

430

Determination of sugars, byproducts, and degradation products in liquid

431

fraction process samples, Biomass Analysis Technology Team Laboratory

432

Analytical Procedures, Technical Report NREL/TP-510-42623; National

433

Renewable

434

http://www.mrel.gov/docs/gen/fy08/42623.pdf.

435

(37) Standard methods for the examination of water and wastewater, 4th

436

ed.; China EPA, National Environment Protection Agency: Beijing,

437

People's Republic of China, 2002.

438

(38) Liu, C. G.; Wyman, C. E. Ind. Eng. Chem. Res. 2004, 43, 2781-2788.

439

(39) Sun, Y. S.; Lu, X.B.; Zhang, R.; et al. Appl. Biochem. Biotech. 2011,

440

164, 918-928.

441

(40) Xu, J.; Wang, L. J.; Zhi, Z. H.; et al. Energ. Fuel. 2015, 29,

442

8157-8161.

Energy

Laboratory:Golden,

443 444 20

ACS Paragon Plus Environment

CO,

USA,

2008;

Page 21 of 27 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

445

A List of Tables

446

Table 1 Pretreatment condition of three kinds of prehydrolysates and their

447

compositions

448 449

Table 1. Pretreatment condition of three kinds of prehydrolysates and their

450

compositions Nitric acid Prehydrolysate

Reacn

Treatment

Total sugars

Total furans

temp(oC)

time(min)

concn (g/L)

concn (g/L)

concn (%(w/w))

A

0.1

120

120

8.90

0

B

0.6

150

2

30.88

0.83

C

0.6

180

60

8.60

20.15

451 452 453 454 455 456 457 458 459 460 21

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

461

A List of Figures

462

Figure 1. Effects of hydrolysis temperature and nitric acid concentration

463

on sugar yield

464

Figure 2. Effects of hydrolysis temperature and nitric acid concentration

465

on the concentration of acetic acid

466

Figure 3. Effects of hydrolysis temperature and nitric acid concentration

467

on the concentration of furfural and HMF

468

Figure 4. Concentration of total sugars and furans as a function of

469

combined severity factor (CSF)

470

Figure 5. Variation of VFAs concentration during the acidogenic

471

fermentation with different prehydrolysates as substarte

472

Figure 6. VFAs distribution patterns during the acidogenic fermentation

473

with prehydrolysate A as substrate

474

Figure 7. VFAs distribution patterns during the acidogenic fermentation

475

with prehydrolysate B as substrate

476

Figure 8. VFAs distribution patterns during the acidogenic fermentation

477

with prehydrolysate C as substrate

478

22

ACS Paragon Plus Environment

Page 22 of 27

Page 23 of 27 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

479 480

Figure 1. Effects of hydrolysis temperature and nitric acid concentration on sugar

481

yield

482

(Xy 1: Xylose-120 oC, 0.1% HNO3; Xy 2: Xylose-120 oC, 0.6% HNO3; Xy 3: Xylose-150 oC,

483

0.1% HNO3; Xy 4: Xylose-150 oC, 0.6% HNO3; Xy 5: Xylose-180 oC, 0.1% HNO3; Xy 6:

484

Xylose-180 oC, 0.6% HNO3; Gl 1: Glucose-120 oC, 0.1% HNO3; Gl 2: Glucose -120 oC, 0.6%

485

HNO3; Gl 3: Glucose-150 oC, 0.1% HNO3; Gl 4: Glucose-150 oC, 0.6% HNO3; Gl 5: Glucose

486

-180 oC, 0.1% HNO3; Gl 6: Glucose-180 oC, 0.6% HNO3; Ar 1: Arabinose-120 oC, 0.1% HNO3;

487

Ar 2: Arabinose-120 oC, 0.6% HNO3; Ar 3: Arabinose-150 oC, 0.1% HNO3; Ar 4: Arabinose-150

488

o

C, 0.6% HNO3; Ar 5: Arabinose-180 oC, 0.1% HNO3; Ar 6: Arabinose-180 oC, 0.6% HNO3)

489

23

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

490 491

Figure 2. Effects of hydrolysis temperature and nitric acid concentration on the

492

concentration of acetic acid

493 494

Figure 3. Effects of hydrolysis temperature and nitric acid concentration on the

495

concentration of furfural and HMF

496

(Fur 1: Furfural-120 oC, 0.1% HNO3; Fur 2: Furfural -120 oC, 0.6% HNO3; Fur 3: Furfural -150 24

ACS Paragon Plus Environment

Page 24 of 27

Page 25 of 27 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

497

o

C, 0.1% HNO3; Fur 4: Furfural -150 oC, 0.6% HNO3; Fur 5: Furfural -180 oC, 0.1% HNO3; Fur 6:

498

Furfural -180 oC, 0.6% HNO3; HMF 1: HMF -120 oC, 0.1% HNO3; HMF 2: HMF -120 oC, 0.6%

499

HNO3; HMF 3: HMF -150 oC, 0.1% HNO3; HMF 4: HMF -150 oC, 0.6% HNO3; HMF 5: HMF

500

-180 oC, 0.1% HNO3; HMF 6: HMF -180 oC, 0.6% HNO3)

501

502 503

Figure 4. Concentration of total sugar and furans as a function of combined severity

504

factor (CSF)

505

(PHA: Prehydrolysate A, PHB:Prehydrolysate B, PHC:Prehydrolysate C)

506

25

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

507 508

Figure 5. Variation of VFAs concentration during the acidogenic fermentation with

509

different prehydrolysates as substarte

510 511

Figure 6. VFAs distribution patterns during the acidogenic fermentation with

512

prehydrolysate A as substrate

513 26

ACS Paragon Plus Environment

Page 26 of 27

Page 27 of 27 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

514 515

Figure 7. VFAs distribution patterns during the acidogenic fermentation with

516

prehydrolysate B as substrate

517 518

Figure 8. VFAs distribution patterns during the acidogenic fermentation with

519

prehydrolysate C as substrate

27

ACS Paragon Plus Environment