Subscriber access provided by Vanderbilt Libraries
Article
A novel concept of utilizing residual solids from enzymatic hydrolysis in biorefinery for lignosulfonates and fermentable sugars production Yalan Liu, Jinwu Wang, and Michael P. Wolcott ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.6b02328 • Publication Date (Web): 13 Oct 2016 Downloaded from http://pubs.acs.org on October 17, 2016
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.
ACS Sustainable Chemistry & Engineering 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 26
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
ACS Sustainable Chemistry & Engineering
1
A multi-step process to produce fermentable sugars and lignosulfonates from softwood
2
enzymolysis residues
3
Yalan Liua*, Jinwu Wangb, Michael P. Wolcotta
4
a
5
University, Pullman WA 99164-1806, United States
6
b
7
Flagstaff Road, Orono, ME 04469-5793, United States
8
*Corresponding to:
[email protected] (+1) 5093393158
9
Abstract:
Composite Materials & Engineering Center, 2001 East Grimes Way, Washington State
United State Department of Agriculture, Forest Service, Forest Products Laboratory, 35
10
The residual solids from enzymatic hydrolysis was usually burned to produce energy and have
11
been explored as a feedstock for various products including activated carbon and lignin based
12
polymers. These products require additional procedures unrelated to the existing biorefinery
13
equipment. In the current study, we proposed successive sulfite treatments to utilize the
14
enzymolysis residues for the producing fermentable sugars and lignosulfonates. Two sulfite
15
methods were compared as an initial pretreatment. It was found that the acid bisulfite treatment
16
achieved higher hemicellulose removal (90%), while neutral sulfite resulted in higher lignin
17
removal (50%) and a greater lignosulfonate yield (26.6 g from 100 g raw material). Overall, the
18
acid bisulfite treatment resulted in 66% glucan conversion by enzymatic hydrolysis, whereas
19
only 37% for the neutral sulfite method. In addition, the neutral sulfite pretreated wood reached
20
80% of the maximum sugar yield after 6 h of enzymatic hydrolysis, whereas 48 h for the acid
21
bisulfite pretreated wood. The multi-step treatment process achieved 84% total sugar conversion
22
and 58% lignin removal with 32.4 g lignosulfonates was produced from 100 g raw materials
ACS Paragon Plus Environment
1
ACS Sustainable Chemistry & Engineering
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 2 of 26
1
through this process. The results demonstrate that the multi-step treatment process has a potential
2
to maximize the yields of fermentable sugars and lignosulfonates.
3
Keywords:
4
Acid bisulfite treatment, Neutral sulfite treatment, Lignosulfonates, Sugars, Enzymatic
5
hydrolysis
6
1. Introduction
7
Pretreatment is a primary step to achieve adequate enzymatic hydrolysis yield of lignocellulosic
8
materials. Currently, there are a variety of pretreatment methods for lignocellulosic conversion,
9
such as mechanical, biological, and thermochemical methods1-2. Thermochemical methods are
10
widely used for pretreatment processes such as dilute acid for agricultural biomass and sulfite
11
pretreatment for woody biomass 3-5. Sulfite pulping has been used in pulp and paper industry
12
since the 1840s 6. It can be carried out under acid, neutral and alkaline conditions aiming at
13
hemicelluloses removal and/or lignin removal to obtain pulps with different characteristics.
14
Hemicellulose and lignin removal can decrease enzyme absorption to cellulose and increase the
15
accessibility of cellulose to the enzyme 7-8 resulting in increased enzymatic hydrolysis yield. In
16
addition, hemicelluloses can be hydrolyzed into monomeric sugars, and the lignin sulfonated
17
producing lignosulfonates, both of which are solubilized in the spent liquor. The acid bisulfite
18
method was found works efficiently on softwood pretreatment compared to other pretreatment
19
methods, such as dilution acid method4, 9-10. Neutral sulfite method was proved to achieve high
20
lignosulfonates yield in the spent liquor6, which increases the utilization of lignin in the
21
feedstock and reduced environmental issues.
22
Zhu et al. 4, 10-13 carried out extensive studies employing the SPORL (sulfite pretreatment to
23
overcome recalcitrance of lignocellulosic material) pretreatment process to achieve high sugar
ACS Paragon Plus Environment
2
Page 3 of 26
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
ACS Sustainable Chemistry & Engineering
1
recovery form woody biomass. Initially, a high temperature in the range of 180-220 oC was
2
adopted for SPORL treatments 14-16. However, the monomeric sugar degradation (such as
3
furfural and hydroxymethylfurfural) existed to a large extent at these high temperatures.
4
Therefore, a lower temperature (140 -165 oC) with long treatment time has also been explored.
5
Studies 9-10 confirm the pretreatment at 145 oC for 3 hour achieved over 80% total carbohydrates
6
conversion by enzymatic hydrolysis at a 4 - 6% (w/w) enzyme dosage based on the biomass. The
7
enzymolysis residues contains more lignin than softwood (15 to 35% lignin) and hardwood
8
(about 20% lignin), thus, it is a good resource for producing lignosulfonates 17. As lignin based
9
polymer was widely investigated in current researches18-24, lignosulfonates can be another
10
feasible product for utilizing lignin in the residues.
11
The lignosulfonates can be separated and purified from spent liquors 25-26 and then used in many
12
industries 27-28. Therefore, establishing lignosulfonates as a co-product can increase the
13
profitability of a biorefinery and more efficiently utilize the feedstock. Neutral sulfite treatment
14
has been found to produce high lignosulfonates yield with little degradation to the cellulose 6, 29.
15
Moreover, the lignosulfonate production with current types of equipment in the biorefinery can
16
be helpful for decreasing economic investment.
17
The objective of this study is to explore a feasible way to utilize the enzymolysis residues with
18
current equipment in biorefinery. Initially, we investigated the performance of two pretreatment
19
methods: acid bisulfite and neutral sulfite treatment in producing both monomeric sugars and
20
lignosulfonates. These two methods were first compared to delineate their performance and
21
function mechanism as a sole pretreatment method for biomass. Then, the enzymolysis residues
22
from the acid bisulfite pretreated wood was subjected to a neutral sulfite treatment. The spent
23
liquors from the sequential treatments were analyzed for monomeric sugars and lignosulfonates
ACS Paragon Plus Environment
3
ACS Sustainable Chemistry & Engineering
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
1
to characterize overall sugar and lignosulfonates production. The second step enzymatic
2
hydrolysis was carried out on neutral sulfite treated residues to investigate carbohydrates
3
accessibility after two treatments. As well, the yields of enzymatic hydrolysis were investigated
4
to optimize hydrolysis time. In all, the total mass balance of carbohydrates and lignin was
5
investigated.
6
2. Materials and Methods
7
2.1 Materials preparation
8
Douglas-fir (Pseudotsuga menziesii) micronized wood powders was prepared by an impact mill
9
(Zhenzhou Tianyuan Environmental Protection Machinery Co. Ltd, China) with 30 min milling
Page 4 of 26
10
of nominal 2-mm wood chips. The median particle size (D50) of this sample is 32 µm with a
11
standard deviation 1.2 µm measured by Malvern particle size analyzer (Mastersizer 3000 laser
12
diffraction).
13
The cooking liquor for acid bisulfite treatment has a 2.15% of calcium bisulfite and a 0.37% of
14
free sulfur dioxide. The sodium carbonate (J.T. Baker, ACS Reagent, Fisher Scientific) and
15
sodium sulfite (J.T. Baker, ACS Reagent, Fisher Scientific) were used for neutral sulfite
16
treatment. 96% Sulfuric acid (ACROS Organics, Fisher Scientific) was diluted into 72% with
17
distilled water for compositional analysis.
18
2.2 Acid bisulfite treatment (AbS)
19
The wood to chemical liquor ratio is 1:4 to obtain a 6.9% (w/w) equivalent sulfur dioxide
20
loading on wood at 145 °C and 2h. A Parr reactor (No. 4845, 100 ml) was employed for all the
21
treatments. It required approximately 30 min to reach 145 °C and 15 min to cool down to room
22
temperature. After treatment, the slurry was separated by vacuum filtration. The spent liquor was
ACS Paragon Plus Environment
4
Page 5 of 26
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
ACS Sustainable Chemistry & Engineering
1
collected for monomeric sugar and lignosulfonates (LS) analysis. The pretreated wood was
2
washed with distilled water and used for enzymatic hydrolysis.
3
2.3 Neutral sulfite treatment (NS)
4
A neutral sulfite liquor consisted of 6% (w/w) sodium carbonate and 16% (w/w) sodium sulfite
5
based on the oven dry wood weight. The solid to liquid ratio is 1:6 with a treatment temperature
6
160 oC and duration time 180 min as was outlined elsewhere 29. It required approximately 35 min
7
to heat up to 160 oC and 15 min to cool down. After treatment, the slurry was separated by
8
vacuum filtration and the solids were washed thoroughly. The same analysis was carried out for
9
the spent liquor and pretreated wood as described above.
10
2.4 Multi-step treatment process
11
The comparison results show acid bisulfite treatment is efficient in achieving high overall sugar
12
recovery whereas neutral sulfite performs well on lignin removal and shortening enzymatic
13
hydrolysis time to level-off. Therefore, we explored a sequential treatment by first applying the
14
AbS treatment on the micronized wood powder at145 oC for 2 h and then enzymatically
15
hydrolyzed the pretreated wood. The enzymolysis residues were subsequently treated with the
16
NS liquor at160 oC for 3 h to produce additional lignosulfonates. Lastly, the secondary residual
17
solids from the second-step treatment underwent additional enzymatic hydrolysis for subsequent
18
carbohydrate conversion. The solids from each step were analyzed on chemical compositions.
19
2.5 Enzymatic hydrolysis
20
The pretreated wood from AbS and NS treatment were hydrolyzed with Cellic® CTec2 and
21
HTec2, which were complimentarily provided by Novozymes North America (Franklinton, NC).
22
The cellulase activity for CTec2 is 152.9 FPU /ml. The pretreated wood was hydrolyzed with a 4%
23
(w/w) CTec2 and 0.4% (w/w) HTec2 (based on oven-dry wood basis) enzyme dosage. The solid
ACS Paragon Plus Environment
5
ACS Sustainable Chemistry & Engineering
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
1
loadings were 2% (w/v) of a total 50 ml volume with 0.5 ml 2% (w/w) sodium azide added for
2
antibacterial function in hydrolysis slurry. A supernatant sample was collected after 0, 3, 6, 12,
3
24, 48, and 72 h hydrolysis and then diluted for analysis of monomeric sugars.
4
2.6 Fourier transform infrared (FTIR) analysis
5
The untreated, AbS, and NS treated samples used for FTIR analysis were prepared by drying in
6
the convection oven at 45 oC for 24 h. FTIR spectra were collected with a Thermo Nicolet
7
Avatar 370 spectrometer operating in the attenuated total reflection (ATR) mode (Smart
8
performance, ZnSe crystal performance, ZnSe crystal).
9
2.7 Spent liquor analysis
Page 6 of 26
10
Monomeric sugars in spent liquor can be measured according to the NREL standard 30 by ion
11
exchange chromatography (Dionex ICS-3000, CarboPac PA20 Guard column: 4 × 50 mm and
12
IonPac AS11-HC analytical column: 4 × 250 mm, ED40 electrochemical detector, AS40
13
autosampler, degassed E-pure water, 50mM and 200mM NaOH solution as eluent with a flow
14
rate 0.5 ml/min ).
15
The concentration of LS was measured by the UV-Visible spectrophotometer ( Perkin Elmer
16
Lambda 35, PerkinElmer, Inc. Waltham, MA) and calculated from the absorbance at wavelength
17
232.5 nm with an extinction coefficient of 24.5 31-32.
18
2.8 Compositional analysis
19
The samples for compositional analysis were prepared according to the NREL standard 33. Wet
20
pretreated wood was dried in a convection oven at 45 oC for 24 h. A two-step acid hydrolysis
21
was carried out based on the NREL standard 34. A 300 mg oven dried sample was hydrolyzed
22
with 3 ml 72% sulfuric acid for 1h at 30 oC. Then, 84 ml water was added into the mixture and
23
autoclaved for 1 h at 121 oC. Monomeric sugars were measured by Dionex ICS-3000, while acid
ACS Paragon Plus Environment
6
Page 7 of 26
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
ACS Sustainable Chemistry & Engineering
1
soluble lignin was measured by the UV-Visible spectrophotometer. Due to the co-elution of
2
xylose and mannose, the two sugars are reported as one value in this study as xylan/mannan or
3
xylose/mannose.
4
3. Results and discussion
5
3.1 Comparison of AbS and NS treatment
6
3.1.1 Treatment performance
7
The performances of the AbS and NS pretreatment methods were compared in terms of lignin
8
removal, hemicellulose removal, sugar recovery in spent liquor, as well as enzymatic hydrolysis
9
yield of pretreated wood. As shown in Table 1, AbS treatment achieved 90% hemicellulose
10
removal and 24% lignin removal, while NS treatment obtained 47% and 50%, respectively.
11
However, monomeric sugar was not detected in NS spent liquor whereas 67% hemicellulose
12
sugar was recovered in AbS spent liquor. The absence of free sugars in the NS spent liquor may
13
be attributed to the high treatment temperature and long duration time, which are favorable for
14
monomeric sugar degradation. Under this non-acidic conditions, the carbohydrate losses might
15
be mainly attributed to the endwise peeling degradation into carboxylic acids, and the chain
16
cleavage through hydrolysis with subsequent secondary peeling. Monomeric sugars are rapidly
17
degraded due to a low protection from other moieties 35-37 resulting in a low overall sugar
18
recovery by the NS treatment. But, the NS treatment resulted in 43% higher yield of LS and 26%
19
more lignin removal than AbS treatment.
20
When compared to the AbS and NS methods, the NS treatment performed better in lignin
21
removal, while AbS treatment achieved better hemicellulose removal and monomeric sugar
22
recovery in spent liquor. The mechanism for these two methods are hypothesized and diagramed
23
in Figure 138. In the AbS treatment, the primary reaction is hemicellulose hydrolysis, while lignin
ACS Paragon Plus Environment
7
ACS Sustainable Chemistry & Engineering
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 26
1
sulfonation is the primary reaction in NS treatment accompanied by the secondary reactions of
2
the edgewise peeling and hydrolysis with rapid degradation of monomeric sugars. AbS treatment
3
is carried out under acid condition, which is favorable for hemicellulose hydrolysis. Whereas the
4
SO32- in NS treatment under neutral condition is favorable for the breakage of lignin units6.
5
3.1.2 Enzymatic hydrolysis
6
Figure 2 compares the enzymatic digestibility of pretreated wood by the two treatment methods.
7
Figure 2(a) shows the AbS resulted in 30% higher glucan yield than the NS pretreated wood at a
8
4.4% enzyme dosage. Increasing of enzyme dosage to 8.8% did not increase glucan yield
9
significantly for the NS pretreated wood. Since the AbS treatment hydrolyzed 13% glucan into
10
the spent liquor, the total glucan conversion into monomeric sugars at 0 hour is set at this value
11
in Figure 2(a). It is apparent that the NS treatment is more effective at lignin removal while
12
hemicellulose conversion is more greatly facilitated by AbS treatment. As is shown in Figure 1,
13
the combined lignin and hemicellulose complex provides protection to the cellulose fibrils,
14
thereby imparting the recalcitrance to enzymatic conversion which is commonly found38.
15
Therefore, from the results presented here, we can conclude that for softwoods, partial removal
16
of both the lignin and hemicellulose are an important factor for affecting glucan yields. In
17
addition, the acid hydrolysis of the hemicellulose, that occurs in the AbS method improves the
18
overall sugar yield by liberating these C6 varieties during the pretreatment stage.
19
Figure 2(b) shows the AbS method resulted in 40% higher xylan/mannan conversion compared
20
to the NS method. The NS pretreated wood had 20% xylan/mannan conversion compared to 6%
21
of AbS pretreated wood by enzymatic hydrolysis. Sixty-one percent of xylan/mannan have been
22
hydrolyzed into the AbS spent liquor, while the NS method did not generate any free sugars in
23
the spent liquor. However, the NS treated solid reached a plateau of sugar conversion (24 h for
ACS Paragon Plus Environment
8
Page 9 of 26
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
ACS Sustainable Chemistry & Engineering
1
glucan and 12 h for xylan/mannan) sooner than the AbS pretreated wood. This may indicate that
2
high lignin removal can reduce enzymatic hydrolysis time compared to hemicellulose removal.
3
This behavior may result from the cellulase absorption on lignin that has been observed by
4
others7-8.
5
3.1.3 FTIR analysis
6
Figure 3 shows band intensity changes for AbS and NS pretreated wood. The peak at 1731 cm-1
7
for the untreated sample is attributed to ester linkages from hemicelluloses and lignin 39. The
8
spectrum becomes flat at 1731 cm-1 for the NS pretreated wood but a small broad peak,
9
indicating the higher percentage of ester linkage removal from the NS than the AbS treatment.
10
The band 1508 cm-1 represent aromatic skeleton vibration from lignin 18, 40. The NS pretreated
11
wood displayed a lower intensity of this band, indicating higher lignin removal. Bands 1158,
12
1105, and 1055 cm-1 are assigned to C-O-C vibration and C-O vibration in cellulose and
13
hemicellulose 41-42. After the hemicellulose removal by the treatments, the peaks of these two
14
bands become more obvious for the two pretreated wood compared to those for the untreated
15
sample. The AbS pretreated wood displayed higher intensity for these two bands compared to the
16
NS pretreated wood indicating cellulose structure becomes more accessible due to high
17
hemicellulose removal. This may account for the high glucan yield of AbS pretreated wood.
18
3.2 Multi-step treatment process
19
3.2.1 Sugar conversion and lignin removal
20
Table 2 shows carbohydrate conversion and lignin removal in each step. This process achieved
21
83.9% total sugar conversion and 58.3% lignin removal. The first two steps obtained
22
approximately 69.5% sugar conversion, which is the major source of sugar conversion. The NS
23
treatment step removed 35% lignin, which is 13% higher than AbS step. The final enzymatic
ACS Paragon Plus Environment
9
ACS Sustainable Chemistry & Engineering
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 10 of 26
1
hydrolysis step resulted in 15% additional sugar conversion. Considering the small amount of
2
carbohydrates remained in the residual solids after two treatments, the second enzymatic
3
hydrolysis may not prove cost-effective.
4
3.2.2 Enzymatic hydrolysis
5
The kinetics of enzymatic hydrolysis was also investigated. Figure 4 shows similar glucan and
6
xylan/mannan yields were achieved at 72 h for the 1st and 2nd enzymatic hydrolysis. However, it
7
took at least 48 h to achieve 80% of maximum yield in the first hydrolysis, whereas it only took
8
6 h in the second hydrolysis as shown in Figure 4. Therefore, the second hydrolysis may be
9
carried in a small amount of time, such as 6 h. This can save time occupancy of an equipment in
10
a biorefinery resulting in saving energy and investments.
11
3.3 Total mass balance analysis
12
Figure 5 shows the total mass balance of carbohydrates and lignin in the multi-step treatment
13
process. We can tell that the acid bisulfite pretreatment hydrolyzed a majority of hemicelluloses
14
while producing 18.7 g LS. In the first enzymatic hydrolysis, 64% glucan and 69%
15
xylan/mannan were converted from the AbS pretreated wood. Meanwhile, the neutral sulfite
16
treatment removed 46% lignin from first enzymolysis residues and produced 13.7 g LS. Sixty-six
17
percent glucan and 70% xylan/mannan from the NS treated residual solids were converted in the
18
second hydrolysis. At last, the final residual solids comprised of 18% carbohydrates and 72%
19
lignin. The majority of the final residual solids is lignin, it can be simply reused for lignin based
20
polymers, activate carbon, or worked as binder in pellet production. In total, this process
21
achieved 84% total sugar conversion and 32.4 g lignosulfonates production from 100 g raw
22
materials. The AbS treatment and 1st enzymatic hydrolysis was aimed at maximizing
23
carbohydrate conversion, while the NS treatment was in pursuit of maximizing lignosulfonates.
ACS Paragon Plus Environment
10
Page 11 of 26
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
ACS Sustainable Chemistry & Engineering
1
By conducting the AbS treatment first, the rapid monomeric sugar degradation under neutral or
2
alkaline sulfite conditions was avoided. Also, the second hydrolysis was completed in a short
3
time period such as 6-12 h due to monomeric sugar yield plateau after 24 h.
4 5
Acknowledgements
6
The chemical liquor in this study was kindly provided and analyzed by Weyerhaeuser with help
7
from Dr. Jonhway Gao. The authors gratefully acknowledge the Northwest Advanced
8
Renewables Alliance (NARA), supported by the Agriculture and Food Research Initiative
9
Competitive Grant no. 2011-68005-30416 from the USDA National Institute of Food and
10
Agriculture, and the China Scholarship Council funding.
11
ACS Paragon Plus Environment
11
ACS Sustainable Chemistry & Engineering
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
1
References
2
1.
3
lignocellulosic biomass. Bioresource Technol 2009, 100 (1), 10-18.
4
2.
5
Lignocellulosic Biomass for Efficient Hydrolysis and Biofuel Production. Ind Eng Chem Res
6
2009, 48 (8), 3713-3729.
7
3.
8
production and enzymatic hydrolysis of dilute acid-pretreated mixed softwood. Bioresource
9
Technol 2013, 140, 306-311.
Page 12 of 26
Hendriks, A. T. W. M.; Zeeman, G., Pretreatments to enhance the digestibility of
Kumar, P.; Barrett, D. M.; Delwiche, M. J.; Stroeve, P., Methods for Pretreatment of
Lim, W. S.; Lee, J. W., Influence of pretreatment condition on the fermentable sugar
10
4.
Shuai, L.; Yang, Q.; Zhu, J. Y.; Lu, F. C.; Weimer, P. J.; Ralph, J.; Pan, X. J.,
11
Comparative study of SPORL and dilute-acid pretreatments of spruce for cellulosic ethanol
12
production. Bioresource Technol 2010, 101 (9), 3106-3114.
13
5.
14
M., Effect of sulfuric acid addition on the yield and composition of lignin derived oligomers
15
obtained by the auger and fast pyrolysis of Douglas-fir wood. Fuel 2013, 103, 512-523.
16
6.
17
New York, N. Y.: 1993; Vol. 2nd Edition.
18
7.
19
stover. Bioresource Technol 2006, 97 (4), 583-591.
20
8.
21
on enzymatic hydrolysis of steam pretreated corn stover. Bioresource Technol 2007, 98 (13),
22
2503-2510.
Zhou, S.; Osman, N. B.; Li, H.; McDonald, A. G.; Mourant, D.; Li, C. Z.; Garcia-Perez,
Sjoestrom, E., Wood Chemistry: Fundamentals and Applications. 2nd ed.; Academic,
Kim, S.; Holtzapple, M. T., Effect of structural features on enzyme digestibility of corn
Öhgren, K.; Bura, R.; Saddler, J.; Zacchi, G., Effect of hemicellulose and lignin removal
ACS Paragon Plus Environment
12
Page 13 of 26
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
ACS Sustainable Chemistry & Engineering
1
9.
Gao, J.; Anderson, D.; Levie, B., Saccharification of recalcitrant biomass and integration
2
options for lignocellulosic sugars from Catchlight Energy's sugar process (CLE Sugar).
3
Biotechnol Biofuels 2013, 6, 10.
4
10.
5
J.; Anderson, D., Using sulfite chemistry for robust bioconversion of Douglas-fir forest residue
6
to bioethanol at high titer and lignosulfonate: A pilot-scale evaluation. Bioresource Technol 2015,
7
179, 390-397.
8
11.
9
and yields from subsequent enzymatic saccharification of pretreated lodgepole pine. Bioresource
Zhu, J. Y.; Chandra, M. S.; Gu, F.; Gleisner, R.; Reiner, R.; Sessions, J.; Marrs, G.; Gao,
Zhu, W.; Zhu, J. Y.; Gleisner, R.; Pan, X. J., On energy consumption for size-reduction
10
Technol 2010, 101 (8), 2782-2792.
11
12.
12
production from SPORL-pretreated lodgepole pine: preliminary evaluation of mass balance and
13
process energy efficiency. Appl Microbiol Biot 2010, 86 (5), 1355-1365.
14
13.
15
production from beetle-killed lodgepole pine using SPORL technology and Saccharomyces
16
cerevisiae without detoxification. Tappi Journal 2011, 10 (5), 9-18.
17
14.
18
and Dilute Acid Pretreatment on Substrate Morphology, Cell Physical and Chemical Wall
19
Structures, and Subsequent Enzymatic Hydrolysis of Lodgepole Pine. Appl Biochem Biotech
20
2012, 168 (6), 1556-1567.
21
15.
22
on lignocellulose conversion--a review. Appl Biochem Biotechnol 2011, 164 (8), 1405-1421.
Zhu, J. Y.; Zhu, W. Y.; OBryan, P.; Dien, B. S.; Tian, S.; Gleisner, R.; Pan, X. J., Ethanol
Zhu, J. Y.; Luo, X. L.; Tian, S.; Gleisner, R.; Negron, J.; Horn, E., Efficient ethanol
Li, X. P.; Luo, X. L.; Li, K. C.; Zhu, J. Y.; Fougere, J. D.; Clarke, K., Effects of SPORL
Vidal, B. C., Jr.; Dien, B. S.; Ting, K. C.; Singh, V., Influence of feedstock particle size
ACS Paragon Plus Environment
13
ACS Sustainable Chemistry & Engineering
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
1
16.
2
yield in pretreatment of softwood for ethanol production. Bioresource Technol 2009, 100 (24),
3
6312-6316.
4
17.
Ek, M., Wood chemistry and wood biotechnology. Walter de Gruyter: 2009; Vol. 1.
5
18.
Li, H.; McDonald, A. G., Fractionation and characterization of industrial lignins. Ind
6
Crop Prod 2014, 62, 67-76.
7
19.
8
shape memory copolymeric elastomers derived from lignin and glycerol-adipic acid based
9
hyperbranched prepolymer. Ind Crop Prod 2015, 67, 143-154.
Page 14 of 26
Monavari, S.; Galbe, M.; Zacchi, G., Impact of impregnation time and chip size on sugar
Li, H.; Sivasankarapillai, G.; McDonald, A. G., Highly biobased thermally-stimulated
10
20.
Li, H.; Sivasankarapillai, G.; McDonald, A. G., Lignin Valorization by Forming
11
Toughened Thermally Stimulated Shape Memory Copolymeric Elastomers: Evaluation of
12
Different Fractionated Industrial Lignins. J Appl Polym Sci 2015, 132 (5), 1505-1517.
13
21.
14
Thermally Stimulated Shape Memory Copolymeric Elastomers-Partially Crystalline
15
Hyperbranched Polymer as Crosslinks. J Appl Polym Sci 2014, 131 (22), 12050-12060.
16
22.
17
Polymers. Biomacromolecules 2015, 16 (9), 2735-2742.
18
23.
19
toughened lignin-co-polymers: Development of hyperbranched prepolymers for cross-linking.
20
Biomass Bioenerg 2012, 47, 99-108.
21
24.
22
McDonald, A.; Wolcott, M., Thermal pretreatment of a high lignin SSF digester residue to
23
increase its softening point. J Anal Appl Pyrol 2016.
Li, H.; Sivasankarapillai, G.; McDonald, A. G., Lignin Valorization by Forming
Sivasankarapillai, G.; Li, H.; McDonald, A. G., Lignin-Based Triple Shape Memory
Sivasankarapillai, G.; McDonald, A. G.; Li, H., Lignin valorization by forming
Howe, D.; Garcia-Perez, M.; Taasevigen, D.; Rainbolt, J.; Albrecht, K.; Li, H.; Wei, L.;
ACS Paragon Plus Environment
14
Page 15 of 26
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
ACS Sustainable Chemistry & Engineering
1
25.
Chakrabarty, K.; Krishna, K. V.; Saha, P.; Ghoshal, A. K., Extraction and recovery of
2
lignosulfonate from its aqueous solution using bulk liquid membrane. Journal of Membrane
3
Science 2009, 330 (1-2), 135-144.
4
26.
5
amine extraction and ultrafiltration: A comparative study. Holzforschung 2005, 59 (4), 405-412.
6
27.
7
utilization of lignosulfonates. Surfactants from Renewable Resources 2010, 269-283.
8
28.
9
68-73.
Ringena, O.; Saake, B.; Lehnen, R., Isolation and fractionation of lignosulfonates by
Lauten, R. A.; Myrvold, B. O.; Gundersen, S. A., New developments in the commercial
Pearl, I. A., Utilization of by-products of the pulp and paper industry. Tappi 1982, 65 (5),
10
29.
Sjöde, A.; Frölander, A.; Lersch, M.; RØDSRUD, G. Lignocellulosic biomass conversion
11
by sulfite pretreatment. 2013.
12
30.
13
Sugars byproducts and degradation products in liquid fraction process samples. In Laboratory
14
Analytical Procedure from the National Renewable Energy Laboratory Biomass Analysis
15
Technology (NREL BAT) Team, 2006.
16
31.
17
hardwood chips in a pulping process for sugar production. J Biotechnol 2012, 162 (4), 422-429.
18
32.
19
composition of spent liquors from acidic magnesium-based sulphite pulping of Eucalyptus
20
globulus. J Wood Chem Technol 2009, 29, 322–336.
21
33.
22
Samples for Biomass Compositional Analysis. In Laboratory Analytical Procedure from the
23
National Renewable Energy Laboratory Biomass Analysis Technology (NREL BAT) Team, 2008.
Sluiter, A.; Hames, B.; Ruiz, R.; Scarlata, C.; Sluiter, J.; Templeton, D., Determination of
Llano, T.; Rueda, C.; Quijorna, N.; Blanco, A.; Coz, A., Study of the delignification of
Marqués, A. P.; Evtuguin, D. V.; Magina, S.; Amado, F. M. L.; Prates, A., Chemical
Hames, B.; Ruiz, R.; Scarlata, C.; Sluiter, A.; Sluiter, J.; Templeton, D., Preparation of
ACS Paragon Plus Environment
15
ACS Sustainable Chemistry & Engineering
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 16 of 26
1
34.
Sluiter, A.; Hames, B.; Ruiz, R.; Scarlata, C.; Sluiter, J.; Templeton, D.; Crocker, D.,
2
Determination of Structural Carbonhydrates and lignin in biomass. In Laboratory Analytical
3
Procedure from the National Renewable Energy Laboratory Biomass Analysis Technology
4
(NREL BAT) Team, 2011.
5
35.
6
catalyzed hemicellulose hydrolysis in sweet sorghum bagasse for xylose production. Ind Crop
7
Prod 2012, 38, 81-86.
8
36.
9
hydrolysis of corn stover in a dilute acid cycle spray flow-through reactor at moderate conditions.
Liu, X.; Lu, M.; Ai, N.; Yu, F.; Ji, J., Kinetic model analysis of dilute sulfuric acid-
Jin, Q.; Zhang, H.; Yan, L.; Qu, L.; Huang, H., Kinetic characterization for hemicellulose
10
Biomass Bioenerg 2011, 35 (10), 4158-4164.
11
37.
12
Rates of dissolution of lignin and hemicellulose. Sven Papperstidn 1973, 76 (15), 561-568.
13
38.
14
315–319.
15
39.
16
cellulose obtained from steam-exploded wheat straw. Carbohyd Res 2005, 340 (1), 97-106.
17
40.
18
characterization of lignins solubilized during alkaline peroxide treatment of barley straw. Eur
19
Polym J 2002, 38 (7), 1399-1407.
20
41.
21
and histochemical characterisation of wood and lignin of five tropical timber wood species of the
22
family of Dipterocarpaceae. Wood Sci Technol 2010, 44 (2), 225-242.
Hagberg, B.; Schöön, N.-H., Kinetics aspects of the acid sulfite cooking process: Part 1.
Hsu, T. A.; Ladisch, M. R.; Tsao, G. T., Alcohol from cellulose. ChemTech 1980, 10 (5),
Sun, X. F.; Xu, F.; Sun, R. C.; Fowler, P.; Baird, M. S., Characteristics of degraded
Sun, R. C.; Sun, X. F.; Fowler, P.; Tomkinson, J., Structural and physico-chemical
Rana, R.; Langenfeld-Heyser, R.; Finkeldey, R.; Polle, A., FTIR spectroscopy, chemical
ACS Paragon Plus Environment
16
Page 17 of 26
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
ACS Sustainable Chemistry & Engineering
1
42.
Windeisen, E.; Strobel, C.; Wegener, G., Chemical changes during the production of
2
thermo-treated beech wood. Wood Sci Technol 2007, 41 (6), 523-536.
3
4
ACS Paragon Plus Environment
17
ACS Sustainable Chemistry & Engineering
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 18 of 26
Table Captions Table1. Comparison of acid bisulfite and neutral sulfite treatment method. Table 2. Total Sugar conversion and lignin removal in multi-step treatment process.
Figure Captions Figure 1. Proposed reaction mechanism of AbS and NS treatment (adapted from Hsu, 1980). Figure 2. The enzymatic hydrolysis of acid bisulfite and neutral sulfite pretreated wood: (a) glucan and (b)xylan/mannan. Figure 3. FTIR-ATR analysis of untreated, AbS, and NS pretreated wood. Figure 4. Enzymatic hydrolysis kinetics in the multi-step treatment process based on treated material. Figure 5. Total mass balance of carbohydrates and lignin of the multi-step treatment process.
ACS Paragon Plus Environment
18
Page 19 of 26
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
ACS Sustainable Chemistry & Engineering
Table 1 Acid bisulfite treatment Component
Untreated (g)
Spent liquor (g)
Treated Solid (g)
Glucan
38.1
4.3
Xylan/Mannan
13.0
Arabinan
Neutral sulfite treatment
Removal (%)
Spent liquor (g)
Treated Solid (g)
Removal (%)
33.4
12.3
0
34.2
10.2
8.6
1.7
86.9
0
8.0
38.5
1.2
0.5
0
100
0
0.4
66.7
Galactan
3.0
2.5
0
100
0
0.7
76.7
Hemicellulosea
17.2
11.6
1.7
90.1
0
9.1
47.1
AILb
29.1
─
23.5
19.2
─
13.4
53.8
ASLc
4.9
─
2.3
53.1
─
3.6
26.5
Total Lignind
34.0
─
25.8
24.1
─
17.0
50.0
Lignosulfonates
─
18.7
─
─
26.6
a. b. c. d.
─
─
Hemicellulose includes xylan / mannan, arabinan, and galactan AIL short for acid soluble lignin ASL short for acid insoluble lignin Total lignin includes AIL and ASL
ACS Paragon Plus Environment
19
ACS Sustainable Chemistry & Engineering
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 26
Table 2 Component
Acid bisulfite
1st Enzymatic hydrolysis
Neutral sulfite
2nd Enzymatic hydrolysis
Total (%)
Sugar conversion
28.6%
40.9%
0
14.3%
83.9
ASL removal
51.1%
0
17.3%
0
68.4
AIL removal
18.0%
0
37.4%
0
55.4
Total lignin removal
22.7%
0
35.6%
0
58.3
ACS Paragon Plus Environment
20
Page 21 of 26
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
ACS Sustainable Chemistry & Engineering
Figure 1
Lignin
Cellulose
Amorphous Region Crystalline Region
Hemicellulose
ACS Paragon Plus Environment
21
ACS Sustainable Chemistry & Engineering
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 26
Figure 2
\
ACS Paragon Plus Environment
22
Page 23 of 26
1055 1031
1158 1158
Untreated
897
1105
1262
1328
1371
1455 1421
1508
1639 1607
1031
Figure 3
1731
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
ACS Sustainable Chemistry & Engineering
NS treated
AbS treated
1800
1600
1400
1200
Wavenumbers (cm
800
1000
-
1
ACS Paragon Plus Environment
23
ACS Sustainable Chemistry & Engineering
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 26
Figure 4
ACS Paragon Plus Environment
24
Page 25 of 26
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
ACS Sustainable Chemistry & Engineering
Figure 5
Raw material:100g Glucan: 38.1g Xyl/mann: 13.0g Arabinan: 1.2g Galactan: 3.0g ASL: 4.9g AIL: 29.1g
Solids: 41.3g Glucan: 12.0g Xyl/mann: 0.6g ASL: 2.4g AIL: 23.9g
Solids: 63.9g Glucan: 33.4g Xyl/mann: 1.7g ASL: 2.4g AIL: 23.9g AbS treatment o 145 C and 2h
Spent liquor Glucan: 4.3g Xyl/mann: 8.6g Arabinan: 0.5g Galactan: 2.5g LS: 18.7g
st
Solids: 27.5g Glucan: 11.6g Xyl/mann: 0.4g ASL: 1.2g AIL: 13.0g nd
1 Enzymatic hydrolysis
NS treatment o 160 C and 3h
2 Enzymatic hydrolysis
1st hydrolysate: Glucan: 21.5g Xyl/mann: 1.2g
Spent liquor: Sugar: N.D. LS: 13.7g
2nd hydrolysate: Glucan: 7.6g Xyl/mann: 0.3g
ACS Paragon Plus Environment
Solids: 19.6g Glucan: 3.5g Xyl/mann: 0.1g ASL: 1.2g AIL: 13.0g
25
ACS Sustainable Chemistry & Engineering
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
Table of Content ; Title: A multi-step process to produce fermentable sugars and lignosulfonates from softwood enzymolysis residues; Authors: Yalan Liu, Jinwu Wang, Michael P. Wolcott ; Synopsis:Utilizing softwood enzymolysis residues with multi-step treatment process targeting at boost lignosulfonates and fermentable sugar production 338x190mm (300 x 300 DPI)
ACS Paragon Plus Environment
Page 26 of 26