laccase biobleaching review - biorefinerybiorefinery.utk.edu/technical_reviews/laccasea.pdf · (x4)...
TRANSCRIPT
Laccase BioBleachingReview
Matyas KosaGeorgia Institute of TechnologySchool of Chemistry and Biochemistry
2
OUTLINE• Introduction• Occurrence in microbes, structure of laccase &
active site, enzyme activity• Active site – substrate oxidation• Mediator resources• CHEMISTRY; oxidative bleaching reactions
between Laccase Mediator System (LMS) &– Lignin– Model compounds
• Process parameters while laccase bleaching• Residual lignins
3
INTRODUCTION
• Laccase BioBleaching could be an environment friendly alternative to conventional methods
• No oxidative degradation on carbohydrates, more pulp more paper
• Laccase “size-problems”, unable to diffuse into pulp fibers
• Mediators (ABTS)Chakar, F. S. (2000) Holzforschung 54: 647-653Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352Bourbonnais, R. P. (1992) Applied Microbiology and Biotechnology 36: 823-827
4
NATURAL OCCURRENCE• Trees: polymerization• Fungi: degradation or “rot”• Ascomycetes: soft rot, stain fungi• Basidiomycetes: white rot, brown rot• Selective for hemicelluloses/lignin in middle
lamella and secondary cell wall using natural mediators
• Enzymes of delignification:– Laccase– Lignin peroxidase, Manganese peroxidase,
versatile peroxidase– (aryl-alcohol oxidase/dehydrogenase, quinone
reductase) Martinez, A. T. (2005) International Microbiology 8: 195-204
5
PEROXIDASES• Oxidants must be:
– Strong enough to attack nonphenolic lignin structures– Small enough to penetrate lignin– Extracellular systems to produce H2O2 (required for enzyme
oxidation)
• Lignin Peroxidase (LiP): degrades nonphenolic units up to 90%, uses veratryl alcohol as “mediator”, “real ligninase” => high E0 (>1.4 V*)
• Mn Peroxidase (MnP): generates Mn3+ as a diffusible oxidizer (chelated by organic acids), that in turn generates peroxide radicals (and others: phenoxi etc)
• Versatile Peroxidase (VP): uses both aboveHammel, E. K. (2008) Current Opininon in Plant Biology 11: 349-355Hofrichter, M. (2002) Enzyme and Microbial Technology 30: 454-466
Smith, A. T. (2009) Proceedings of the National Academy of Sciences 106: 16084-16089*
6
LACCASE• Laccase = benzenediol: oxygen oxidoreductase (or p-
diphenol: dioxygen oxidoreductase) EC 1.10.3.2.
• It catalyzes the reduction of O2 to H2O while oxidizes (typically) a p-dihydroxy phenol or e.g. polyphenols and methoxy substituted phenols like lignin, but NOTtyrosine
• Electrode potential not enough to oxidize nonphenolic lignin -> mediators– Low potential: <470 mV– Medium pot.: 470 mV – 730 mV– High Pot.: >730 mV
Baldrian, P. (2006) FEMS Microbiology Reviews 30: 215-242Martinez, A. T. (2005) International Microbiology 8: 195-204Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412
Bourbonnais, R. P. (1990) FEBS Letters 267: 99-102
Laccase oxidizing veratryl alcohol?
Through ABTS!
7
ENZYME PROPERTIES, ACTIVITY• Only catalyze thermodynamically favorable
reactions towards an equilibrium between substrates and products @ given conditions (T, pH, starting conc. etc.)
• Enzyme activity => 1 U (unit): the amount of enzyme that catalyzes the conversion of 1 mol substrate /min (SI: 1 katal = 1 mol s-1)
• Kinetic parameters: kcat turnover number, KM Michaelis equilibrium const, kcat/KM; (Usually the larger kcat the better as well as for kcat/KM, however KM‘s value would need more discussion. Here the smaller the better…)
Fersht, A. (1999). Structure and mechanism in protein science. New York, W. H. Freeman and Company
8
LACCASE STRUCTURE
Garavaglia, S. C. (2004) Journal of Molecular Biology 342: 1519-1531Lyashenko, A. V. (2006) Acta Crystallographica Section F: Structural Biology and Crystallization CommunicationsF62: 954-957
3 domains all with -barrel topology.
9
FOLDS, ACTIVE-SITE POSITIONSURFACE OF LACCASE
binding pocket with 2,6-dimethoxyphenol
hydrophilic
hydrophobic
Active-site
Fold accommodate and enables connection between the binding site and the active site.
Active-site
binding pocket
Kallio, J. (2009) Journal of Molecular Biology 392: 895-909
Melanocarpus albomyces Laccase
10
SO FAR…
• Selective delignification by white rot fungi• Ligninolytic enzymes: laccase, peroxidase• Laccase:
– 3 domains provide accommodation for the binding/active sites, efficiency is important kcat
– Relatively low E0 (three categories) but large size, hence MEDIATORS are needed
• Can be utilized to bleach Kraft-pulp
11
BLEACHING CONSIDERATIONS I.
Kraft-pulp (washed)
Lignin: residual (native and Kraft)
Lignin model compounds
LaccaseLaccase Mediator System (LMS)
Changes in lignin (& carbohydrate)structures
+
LACCASE BIOBLEACHING
Bleached pulp
12
• Laccase active site mechanism(s)• Mediator types• Laccase efficiency [E0 (?), kcat, KM…]• Parameters affecting efficiency and substrate
specificity• Laccase-Mediator-Lignin “oxidation-line”
chemistry, step-by-step, direct-indirect• Laccase production, mediator resources• Environment for bleaching and its efficacy
BLEACHING CONSIDERATIONS II.
13
ACTIVE-SITE• Laccases are in the Multi Copper Oxidase
(MCO) family• All MCO’s contain four Cu ions in their active
sites:– 1 type 1 (T1) Cu, optic absorption @ 600 nm, causes
“blue” color in the enzyme solution, EPR active, substrate oxidation site
– 1 type 2 (T2) Cu, EPR active– 2 type 3 (T3) Cu, ions coupled through –OH bridge ->
diamagnetic, no EPR acivity, UV 330 nm detection• T2+(2)T3= trinuclear site of O2 reduction
to waterBaldrian, P. (2006) FEMS Microbiology Reviews 30: 215-242Quintanar, L. (2007) Accounts of Chemical Research 40: 445-452Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412
14
ACTIVE SITE STRUCTURE1. ENTRY or substrate
oxidation site w/ T1Cu, X is an axial ligand
2. His-Cys-His bridge that connects T1Cu to the trinuclear cluster ~13 Å
3. EXIT or O2 reduction site, T3Cu’s connected by –OH bridge ~4.3 Å
His
Cys
OH
HOH
e-
1.
2.
3. Baldrian, P. (2006) FEMS Microbiology Reviews 30: 215-242Quintanar, L. (2007) Accounts of Chemical Research 40: 445-452Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412
15
SUBSTRATE OXIDATION SITEPhe
Met
Planar-triagonal geometry: because of phenylalanine as axial ligand. When Met is absent Cys-Cu bond shows increased covalency (and ligand field strength).
Met-Cu -> long bond; Cys-Cu -> short bond => 4 coor-dinate (tetrahedral) T1 site.
3-coordinate T1 sites show substantially higher reduction potentials than 4-coordinate ones!
~0.7-0.8 V
~0.4-0.6 V
Substrate (S) + Cu++ => S. + Cu+
Quintanar, L. (2007) Accounts of Chemical Research 40: 445-452Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412
Site directed mutagenesis showed that the axial ligand of the T1 copper ion has no significant effect on redox potential of the T1 site of laccases! Then what does???
16
E0 & REACTIVITY• Factors, such as solvent accessibility, dipole orientation
and H-bonding will contribute to the tuning of E0!• Does E0 affect reactivity? NO. It specifies the type of
substrates that a given enzyme can oxidize (E0 has to be lower). Then what determines reactivity?
• Parameters associated with reactivity, efficiency (kcat):– Side-chains present in the binding site that enhance:
laccase-substrate complex formation, orientation of this complex for appropriate electron transfer (ET) towards T1
– More solvent exposed T1 site, easier access by substrate
– Changes in His-ligand distances to T1CuQuintanar, L. (2007) Accounts of Chemical Research 40: 445-452Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412
17
MECHANISM• Solvent exposed N: of His
and another Glu or Asp residue H-bond to the substrate
• The cleft otherwise is hydrophobic
• H+ is withdrawn by the acid
• e- is withdrawn by T1Cu through His and forwarded to the trinuclear center
Garzillo, A. M. (2001) Journal of Protein Chemistry 20: 191-201Garavaglia, S. C. (2004) Journal of Molecular Biology 342: 1519-1531Kallio, J. (2009) Journal of Molecular Biology 392: 895-909
2,6-DMP
Asp or GluActive-site Binding-site
18
BRIDGE• Bridge is formed by a His-
Cys-His bridge• According to modeling
pathways after knowing the crystal structure:– e- goes through Cys-S,
Cys-C=O, H-bond, His-N’s then to the trinuclear cluster
• Electrons are used to reduce O2 to H2O
Garavaglia, S. C. (2004) Journal of Molecular Biology 342: 1519-1531Baldrian, P. (2006) FEMS Microbiology Reviews 30: 215-242Shleev, S. (2008) Angewandte Chemie International Edition 47: 7270-7274
19
WHOLE ACTIVE SITE
O2 reductive cleavage, structure of radical containing active site intermediates. Discovered by EPR, Quantum and molecular mechanical studies.
Shin, W. (1996) Journal of the American Chemical Society 118: 3202-3215Palmer, A. E. (2001) Journal of the American Chemical Society 123: 6591-6599Solomon, E. I. (2001) Angewandte Chemie International Edition 40: 4570-4590Lee, S.-K. (2002) Journal of the American Chemical Society 124: 6180-6193Solomon, E. I. (2004) Chemical Reviews 104: 419-458Rulisek, L. (2005) Inorganic Chemistry 44: 5612-5628Quintanar, L. (2007) Accounts of Chemical Research 40: 445-452
Research Groups
Shleev, S. (2006) Biochimie 88: 1275-1285Morozova, O. V. (2007) Biochemistry (Moscow) 72: 1396-1412Shleev, S. (2008) Angewandte Chemie International Edition 47: 7270-7274
20
PREDICTED “MECHANISM”0: oxidized resting state1: fully reduced enzyme2: peroxide intermediate3: native intermediate 14: native intermediate 2
Shleev, S. (2006) Biochimie 88: 1275-1285Rulisek, L. (2005) Inorganic Chemistry 44: 5612-5628
0
1 2
34 Not fully understood, states 0-2 are observed + in 4 all Cu is 2+
1-4: 02 + 4e- + 4H+ = 2H2O
21
EFFECTS OF pH• Non-phenolic substrates
loose only electron, however as pH increases HO- will bind to the trinuclear cluster decreasing activity: linear dependence on pH
• Phenolics release H+, as the pH increases more phenoxy compounds -> higher activity. Then as pH increases more the above effect kicks in:Bell shapedpH profile
Non-phenolic substrate e.g. ABTS
Phenolic substrate e.g. 2,6-DMP
22
ACTIVE-SITE SUMMARY
Entry site: substrate is oxidized while T1 site is reduced (x4)
T1Cu: catalytic activity depends on multiple factors but not E0
H-C-H:e- are transported from T1 to trinuclear cl.
Exit site: Trinuclear cluster, O2molecule binds in and through the peroxide and native states gets reduced to 2 water molecules with 4 e- transported from substrates
Reaction with 2,6-DMPfungi E0 [mV] kcat [1/s]
T.t. 790 109
T.p. 742 24000
P.o. 740 120100
R.l. 730 7400
Other substrate -> different activities!
T and pH optimum!
23
LACCASE SIZE PROBLEMS
Archibald, F. S. (1997) Journal of Biotechnology 53: 215-236
24
ACTIVITY PROPERTIES• Activity really depends on the following factors:
– Side-chains present in the binding site that enhance: laccase-substrate complex formation, orientation of this complex for appropriate electron transfer (ET) towards T1
– More solvent exposed T1 site, easier access by substrate– Changes in His- distances to T1Cu
• Laccase cannot reach lignin in cell-walls
Can it be that laccase evolve(-d) to oxidize “small” molecules (mediators) by increasing its active site E0 and specifically changes its binding/active site structures for enhanced electron transfer?! “Host-range” mutation, where range is not lignin but the most abundant relatively high E0 mediator…
25
BLEACHING CONSIDERATIONS III
• Lignin model compounds• Mediators• Native lignin in pulp• Kraft lignin• Residual lignin• In bleaching: mediator(s) and
residual lignin after Kraft cycle
SUBSTRATE OXIDATION:
Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
26
LACCASE OR LMS• Using lignin from totally different sources
with different kind of mediators and laccase preparations, and combining these in basically every possible way, the results show:
• IF ONLY LACCASE IS USED THE LIGNIN WILL POLYMERIZE
• IF LACCASE MEDIATOR SYSTEM (LMS) IS USED THEN THE LIGNIN WILL DEPOLYMERIZE
Shleev, S. (2006) Enzyme and Microbial Technology 39: 841-847
27
NATURAL MEDIATORS
• Secreted extracellularly by fungi• Present in situ as common secondary plant
metabolites• Released in large amounts during the
microbial degradation of lignocellulose
acetosyringone syringaldehyde acetovanillone
E0 [mV] vs. SCE*
*Standard Calomel Electrode
534 542
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629
28
SYNTHETIC MEDIATORS
• These compounds are target substrates of laccases
• They can mediate lignin or veratryl alcohol (VA) oxidation only after being oxidised bylaccase or an electrode
E0 [mV] vs. SCE*
*Standard Calomel ElectrodeGonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629
2,2’-azino-bis(3-ethyl-benzothiazoline-6-sulphonic acid) ABTS
1-hydroxybenzotriazoleHBT
Violuric acidVLA
663441
29
ELECTROCHEMISTRY• Cyclic voltammetry: with
0.2 mM ABTS in pH=4 buffer the potential of the electrochemical cell is continuously increased by 20 mV/s until 1000 mV is reached vs AG/AgCl electrode
• Then E is decreased with same rate
• Current is monitoredE (413 mV) -> large & ic/ia ~ 1 shows stabile intermediates!
ABTS ABTS+.
ABTS2+
ABTS+.ABTS
ABTS2+ic
ia
Ea = anodic-oxidation potential
Ec
Ea
Current [A]
Potential [mV]
(Ec + Ea)/2=E0 vs St.El.
Ea
Ec = cathodic-reduction potential
ic
Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
30
ABTS-VA
ia ~2x ia(ABTS)
ia(ABTS)
ia(ABTS+VA)
* Homogeneous redox catalysis (HRC): 1. electrochemical generation of a chemically stable molecular oxidant-> 2. diffuse into solution able to oxidize the substrate in place of the electrode. It is usually possible to carry out oxidation with a smaller overpotential than required directly
Reaction is driven by the irreversible two electron oxidation of VA to V-aldehyde. Regenerates cation radical.
Ele
ctro
de s
urfa
ce
(E0=1175 mV)
Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390Andrieux C. P. (1986) Journal of Electroanalytical Chemistry 205: 43-58
31
HBT-VA
hydrogen atom transfer
ia/ic large: way more than 1, because HBT is instabile or because of a different reduction -> like HAT. There are evidence for both reasoning.
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
32
MEDIATOR CATALYTIC EFFICIENCY (CE)• ia(ABTS+VA)= ik anodic
peak current (catalytic current) of the compound acting as catalyst in the presence of substrate
• ia(ABTS)= ic is the diffusion controlled peak current of the catalyst
• k will be proportional to ik/ic and it describes CE
ia(ABTS)
ia(ABTS+VA)
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
33
MEDIATOR vs. ENHANCER• Most compounds described as
laccase-mediators are not strictly redox mediators, since their oxidized intermediates are electrochemically unstable
• Consequently, only a small number of redox cycles occur during their catalytic oxidation
• These compounds have to be continually replenished in the media hence the term ‘laccase enhancer’ is more precise
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629
HBT: enhancer, continuous presence of potential is required!
Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
34
MEDIATOR (ABTS)-LACCASE
• Laccase efficiently oxidizes ABTS mainly to ABTS+.
• There is oxidation of VA @ laccase E (585 mV), however it is really slow
Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
35
CE ON VA AND KL• Both groups
measured the catalytic efficiency (CE) of the given mediators and enhancers on both the model compound VA and on Klason lignin (KL) as well
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629Bourbonnais, R. (1998) Biochimica et Biophysica Acta 1379: 381-390
36
“BEST” MEDIATORS• Electrodes were used and higher potentials than
laccase could produce!• HOWEVER: The redox potential of the
mediators seems to play a negligible role in the catalytic efficiency of lignin oxidation; their effectiveness is likely to depend on the chemical reactivity of the radical formed after their initial step of oxidation.
• Oxidation of the different components of lignin activate cascade reactions between phenolic and non-phenolic compounds!=>further oxidation
Gonzalez Arzola, K. (2009) Electrochimica Acta 54: 2621-2629
37
A DIFFERENT APPROACH• Between 1984 and 1988 Higuchi and his group
conducted oxidation-degradation experiments on lignin model compounds with fungal extracellular media
• They used mass-spectrometry to analyze reaction products
• Different models (synthesized with 18O @ different positions) were used in H2
18O and H2O to figure out cleavage mechanisms
• Later they began to use mediators as well, but stayed with the same analytical logic/methods
Umezawa, T. (1984) Agricultural Biological Chemistry 48: 1917-1921Kawai, S. (1985) Agricultural Biological Chemistry 49(8): 2325-2330Kawai, S. (1988)Archives of Biochemistry and Biophysics 262: 99-110
Kawai, S. (1988) FEBS Letters 236: 309-311
38
OXIDATION MECHANISM 1. Formation of radicals
I. 1,3-dihydroxy-2-(2,6-dimethoxyphenoxy)-1-(4-ethoxy-3-methoxyphenyl) propane
I.
II. 2-(2,6-dimethoxyphenoxy)-1-(4-ethoxy-3-methoxyphenyl)-3-hydroxypropanonepropane
II.
III. 1-(4-ethoxy-3-methoxyphenyl)-3-hydroxypropanonepropane
III.a b c
Aryl cation radicalBenzylic radical
Kawai, S. (2002) Enzyme and Microbial Technology 30: 482-489
39
OXIDATION MECHANISM 2. C-C cleavage
d
IV. 2,6-DMP
IV.
V. 4-ethoxy-3-methoxybenzoic acid
V.
Kawai, S. (2002) Enzyme and Microbial Technology 30: 482-489
“generating” a mediator
NON-PHENOLIC IN ALL CASES!
40
OXIDATION MECHANISM 3. -ether cleavage
b c
VI. 1-(4-ethoxy-3-methoxyphenyl)-1,2,3-trihydroxypropane
VI.
Kawai, S. (2002) Enzyme and Microbial Technology 30: 482-489
41
OXIDATION MECHANISM 4. aromatic ring (phenolic)
Kawai, S. (1988) FEBS Letters 236: 309-311
4,6-di(tert-butyl)guaiacol
muconic acid methyl ester (MAME)
muconolactone
Can be found in lot of literature on lignin degradation with laccase.
NO AROMATICS-> NO QUINONES (CHROMOPHORES)-> NO COLOR
42
OXIDATION MECHANISM 5. aromatic ring (non-phenolic)
a
b
VII. 1-(4-ethoxy-3-methoxyphenyl)-1,2,3-trihydroxypropane-2,3-cyclic carbonateVIII. 1-(4-ethoxy-3-methoxyphenyl)-1,2,3-trihydroxypropane-1,2-cyclic carbonate
VII.
VIII.
Kawai, S. (2002) Enzyme and Microbial Technology 30: 482-489 Umezawa, T. (1987) FEBS Letters 218: 255-260
NO AROMATICS-> NO QUINONES (CHROMOPHORES)-> NO COLOR
43
LMS BLEACHING OPERATION• Laccase Mediator System (LMS) bleaching
stage is assigned: LA• Alkali extraction stage, usually NaOH: E• Bleaching efficiency is measured with: KAPPA-
number (), brightness (b), delignification % (d%) pulp & paper physical properties (e.g. tear index)
• Influencing parameters: T, pH, time (t), pulp source, laccase conc., mediator conc., O2pressure (pO2) and number of consecutive stages
44
BOURBONNAIS-PAICE-ABTS
• Observations of Bourbonnais and Paice, with the following conditions: 10% washed Kraft-pulp consistency, 2h, pH 5, 300 kPa (~3 Atm) O2, 1% ABTS and 5U enzyme per g pulp
• Physical properties -> minimal change, except slight 2% decrease in tear index
starting ~17% (SW) decreases 25% after LA-E and by 55% if stages are repeated!Sulfite-pulp it is 50% after only LA-E!
Bourbonnais, R. (1996) TAPPI Journal 79: 199-204
45
BOURBONNAIS-PAICE-ABTS
Bourbonnais, R. (1996) TAPPI Journal 79: 199-204
t[0.5, 1, 2, 4 h] pH [3-6] T
[22-80°C]Laccase
[1-25 U/g]ABTS
[0.1-2.5%]
LA ~ 2% decrease from
17->15optimum @ 5 optimum @ 60 optimum around
5the higher the better: 2.5
LA-E ~ 2% decrease from 14->12
optimum @ 5 optimum @ 50 optimum around
1the higher the better: 2.5
bLA only slight increase
~0.5%
LA-E ~2% increase
d%LA 1.7->10.5 continuous
LA-E 16->27 continuous
With pO2 the experience is it doesn’t really effect above 100 kPa so there’s no reason to go higher.
All seems really good except that ABTS is pretty expensive. How about other mediators?
46
OTHER SYNTHETIC MEDIATORS
• Delignification with laccase-HBT LMS can remove 20-30% more lignin than ABTS LMS
• LA-E with NHA, HBT and VLA removed 19, 20 and 37 % of lignin from the starting pulp respectively
• VLA reacts with C5-condensed phenolicunits as well!
N-acetyl-N-phenylhydroxylamine (NHA)
HBT
VLA
Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352
47
NATURAL MEDIATORS• LA-E with PCA actually
increased , while SA and AS decreased it with ~1.5 % however they both underperformed HBT (~4%)
• Brightness increased ~15%, but still under HBT (25%)
acetosyringone AS
syringaldehydeSA
p-coumaric acidPCA
Camarero, S. (2007) Enzyme and Microbial Technology 40: 1264-1271
48
E-STAGE EFFECTThe alkaline (E) stage isn’t just an extraction stage, it enhances brightness by reacting with quinones as well.BAR = benzylic acid rearrangement.
Moldes et al tested what happens if the E stage is replaced by a peroxide (P) stage. The result: decrease is less than half compared to E, but the brightness increased by 16% (12% in E).
Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352Moldes, D. (2008) Bioresource Technology 99: 8565-8570
NO QUINONES (CHROMOPHORES)-> NO COLOR
49
RESIDUAL LIGNIN
• Isolation procedure: 4.15 w/V% solids (pulp) in solution of 9:1 p-dioxane:water, 2 h of boiling then double filtration, pH neutral with NaHCO3 -> evaporation under reduced pressure to ~10% of solution. Water addition and 1N HCl to pH 2.5, then filtration and wash.
• Analysis by NMR or Pyrolysis GC-MSSealey, J. (1998) Enzyme and Microbial Technology 23: 422-426Chakar, F. S. (2000) Holzforschung 54: 647-653Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352
50
RESIDUAL STRUCTURES-1. before LMS: between 70-100 (10-14%) after LMS: down to around 40-50 (6-7%)
• LA-E with ABTS then 13C-NMR, Sealey et al:
-COOHC-3,4 ofsubstituted G
units
C-3,4 of G anddemethylated G
units
-O-aryl C MeO-
Change ~13% growth, see BAR @ E stage ~20% decrease ~37% decrease Slight
Increase~10%
decrease
Even better if an O2 (O) stage is included after pulping!Sealey, J. (1998) Enzyme and Microbial Technology 23: 422-426Chakar, F. S. (2000) Holzforschung 54: 647-653Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352
51
RESIDUAL STRUCTURES-2.• Chakar et al (2000), 31P-NMR:
– If E, P, O stages are used w/ HBT brightness is really enhanced (~6-7%)
– ~50% increase in –COOH vs brownstock (BS), ~7.5% increase vs only E-stage applied
– Phenolic –OH in C5-noncondensed: 2.5 times the decrease in E-P-O vs E an overall 42%
– Phenolic –OH in C5-condensed: 4.5 times the decrease in E-P-O vs E an overall 37%
– Aliphatic –OH slight increase
Chakar, F. S. (2000) Holzforschung 54: 647-653
52
RESIDUAL STRUCTURES-3.• Chakar et al (2004), 31P-NMR:
– LA-E with HBT and VLA– -COOH: 40% (HBT) 70% (VLA) increase vs
BS– Noncondensed C5: HBT 11%, VLA 41%
decrease vs BS– Condensed C5: HBT 2.5%, VLA 15%
decrease vs BS– Aliphatic: HBT 6%, VLA 12% decrease vs BS-O-aryl: HBT 1-2%, VLA 10% increase vs BS
– Methoxyl: HBT 7%, VLA 6% decrease vs BSChakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352
53
SUMMARY ON RESIDUAL LIGNIN• All results will strongly depend on what stages are
included either before (O) or after (E, P, O) the LA stage as well as the type of mediator used! Repeating stages will increase efficiency as well!
• -COOH content will considerably increase, see E-stage chemistry
• The use of LA-E-P-O or VLA as mediator will significantly increase the removal of C5 condensed units
• Significant decrease in noncondensed C5 units, less significant decrease in methoxyl and aliphatic-OH groups
• Slight increase in -O-aryl structures• Around 30% increase in S/G ratio with both natural
(SA) and synthetic (HBT) mediatorsCamarero, S. (2007) Enzyme and Microbial Technology 40: 1264-1271Moldes, D. (2008) Bioresource Technology 99: 8565-8570Bourbonnais, R. (1996) TAPPI Journal 79: 199-204
Sealey, J. (1998) Enzyme and Microbial Technology 23: 422-426Chakar, F. S. (2000) Holzforschung 54: 647-653Chakar, F. S. (2004) Canadian Journal of Chemistry 82: 344-352