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FECTORS I}IFLI'EDTCINC TBE RITE AND SEABII.TS OF TgE NNAEROBTC DTGESTIoIT PROCESS
A
thesi-s presentedin partial fulfilment of
the requirementsfor the
degreeof Dgctor of
philosophyin
BiotechnoloEy
at
MasseyUniversity
AI{DREI| TOEN I'BITSoII 1986
11
ABSERJACI
Three factors affecting the rate and stability of the methane
fermentation of a readily-hydrorysable feedstock vrere
investigated. The aim of this work was to d.everop improved.
processes and control- strategies to facilitate economic treatment of ind.ustrial wastes by anaerobic d.igestion
A comparison was made between the performance of a continuousry- fed digester and semi-continuous digesters srug fed every second
day. A semi-synthetic medium eri.th grucose as the major carbon
and energy source was used and seed materiar was transferred.
between the digesters, which were operated under similar loading conditions. The continuous digester repeated.ly failed even when
nnaral-oA .+ /l l
v..elsLes su *ilution and loading rates much lower than the maxi-mum values commonly reported. rn contrast, the semi-
continuous units provided satisfact,ory perfonnance and could be
easily and rapidly recovered from retard.ed. operation. Faj-Iure of the contj-nuous digesters rdas characterised by a steady farl in volatile suspended solids concent,ration forlowed by a rapid.
accumulation of acetate, and was attributed to a deficiency in the medium of one or more essential nutrients. These erere
l:roughi to be provided in t.he semi-continuous diqester bv lvsis of acidogenic bacteria or luxury uptake from the medium.
Degradation of acetic and propionic acids vras investigated. in batch culture. rncreasing the concentration of either acid. from lol l-evefs decreased the rate of utilisation of the acid, but the proposed inhibitory role of un-ionised acids r.ras not conclusively supported. rncreasing: the initiar acetate concentration above 1000 to 1500 mg.r-1 significantly red.uced the rate of degradation
^€ ^-^^l ^Jl^l ^! c^n
v! lvlvt,rvlrdus added at 500 mg.l-r. -- when acetate was add.ed aE
2000 mg.r-' the rate of i propionate utirisation was approximately half of that when ace!.ac.e was present at 500 rng.l-1 or l-ower.
11t
In batch culture experiments, addition of up to 3.2 nM cysteine- hydrochloride or sodium sulphide, or 4 .4. ml'[ sodj.um
thioglycollate did not inhibit total gas production from samples drawn from the continuous dig'ester. However the rate of methane production in effluent samples from a semi-continuous dig:ester was inhibited by 25 t to 30 t by addition of 3.2 mM cysteine or sulphide. rnhibition was attributed to tbe sulphide ion. Sodium thioglycollate did not inhibit methane production from acetate but propionate degradation was markedly reduced, wit,h increasingt inhibition noted with increasing incubation tirne.
The work adds to a considerable body of investigation into the factors influencing: anaerobic digestion and. the unresolved problem of process stability in long-term operation of conventional stirred t.ank digesters has again been highlighted.
Indicators and possible causes of process failure have been
suggested and further development of these should assist in the continuing increase in the rate of treatment while ensuring acceptable working rnargins of safety for the Process.
I\/
ACKNOIVIADGEIIEIIIS
I wish to acknowledge the following:
* Professor R.L. Earle, Dr V.F. Larsen and Dr G.J. Mandelsorr,
for their supervision and assist,ance.
* l'1r .Tohn Alger and Mr Derek Cou1ing, for their assistance in building and maintaining eguipment.
* Fellow staff members and post-graduate students of the Biotechnology Department,, for many useful discussions. I particularly wish t,o thank Dr Tony Paterson for his guidance on the use of various computer packages and his help with printing this thesis.
* The Department of Scientific and Industrial Research, for sponsoring this research.
* Nicky and Sa1ly, for proof-reading at a critical tfune.
* Brenda and Isaac, and other friends and farnily, for their support and encouragement,. this work is dedicated to them.
TABLE OF coxEH|rs
ABSTRACT
ACKNOWLEDGEMENTS
TABLE OF CONTENTS
TABLE OF FIGURES TABLE OF TABLES ABBREVIATIONS CHAPTER ONE CHAPTER TWO
2.L Introduction 2.2 Microbiology fermentation
PREAMBLE
LITERATURE REVIEW
and biochenietry of the methane
2.2.1
Introduction2.2.2
The fermentative bacteria2.2.2.t
Hydrolysisof
biopolyuers2.2.2.2
Pnoduction andutillsatton
off ermentati.on lntermediates
2.2.3
The hydrogen-producing acetogenic bacterla2.2.4
Therole of
hydrogenln
regulating the fermentation2.2.5
The methanogenic bacteria2.3
Kinetic analysisof
the nethane ferrnentatlon2.3.t
Introduction2.3.2
CODflux in
the methane fermentation2.3.3
Reaction rate analysisof
the rate-1lnitlng2.3.4
Modelling stepof
nicrobial growthln
anaerobicdigestion
2.4
Anaerobic reactor designs2.4.L
fntroduction2.4.2
The conventional single tank process2.4.3
The anaerobic contact process2.4.4 .
The (UASBR}upflow anaerobic sludge blanket reactor2.4.5
The anaerobic upflowfilter
2.4.5
The downflow stationaryfixed-fllm
reactor( DSFFR )
2.t+.7 The attatched-fi1n fLuidised-bed reactor
(AFFBR) and the attatched-fllm expanded bed
reactor (AFEBR)
2.4.8
Novel anaerobic processesPage
1i
1v v
ix
xii
xv
1 3
13 14 3 4 4 7 7 8
35 36 36 L7 22 22 23 25 27 31 31 33 34 35
35
v1
2.5 Envlronmental factors affecting the rate and stability of the methane fernentatlon
2.5.1 Introduction 2.5.2 Temperature
2.5.3 pH and alkalinity
2.5.4 Oxi-dation-reduction potential (ORP) and
anaerobiosis
2.5.5 Retention time and organic loadlng rate (OLR) 2.5.6 Nutritional requirenents and toxic compounds
2.5.6.7 fntroductlon
2 .5.6.2 Ammonia
2.5.6.3 Sulphur conpounds
2.5.6.\ A1ka1i and alkaLi-earth netal cations
2 .5.6.5 Heavy metals
2.5.6.6 Other growth-promotlng factors 2.5.6.7 Other toxic compounds
2.5.7 Fermentation intermediates and end-products
2 .5.7 .L Introduction 2.5.7 .2 Carbon dioxide
2.5.7 .3 Volatile f atty acids (vFA)
2.6
SummaryCHAPTER THREE
Page 37 37 37 38 41 42 45 46 47 4B
5t
52 54 55 55 55 56 58
5t
63 63 63 63 63 64 56 65 66 67 67 nnII 72 73 75 77 79 79 79 B1 81 81 81 B3 B4 B4 B4 B4 B5 B5 86 B6 METHODS AND MATERIALS
3.1 Materlals
3. 1.1 Gener.al chenicals 3.1.2 Gases
3.1.3 Chromatography materlals 3.1.4 Microbial growth ne<lium 3.1.5 Glassware
3.2 Analytical proceduree
3.2 .1 lntroduction
3.2 .2 pH value
3.2.3 Volatile fatty aclds (vFA) by 3.2.\ Volatj-1e faEty acids by direct 3.2.5 Chemical oxygen demand (COD) 3.2.6 Biologlcal oxygen demand (BOD) 3.2.7 Solids compositlon
3.2.8 cas composition 3.2.9 Alkalinity
3.2.1O Ammonia nitrogen 3.2 11 Dissolved sulphide 3.2.L2 Glucose
3.2.L3 Oxidation-reduction potential 3.3 Continuous digestion experiments
3.3.1 Equipment and i.nstrumentation 3.3.2 Operating conditlons
3.4 Semi-continuous digestJ-on experiments
3.4.1 Equipnent and instrumentatlon '
"lJ2 i q Rafnh
3.4.1.1 Microferm dlgester 3.4.1,.2 Biogen digester Operating conditions digestion experiments
Equipment and instrumentation 3.5.1.1 Serum bottle cultures
chromatography
tltration
(ORP)
vil
3.5.1.2
Flask digesters3.5.2
Operating conditlons3.6 Statistical
analysisof
dataCHAPTER FOUR CONTINUOUS AND SEMI-CONTINUOUS DIGESTION EXPERIMENTS
4.1
Introduction4.2
Experi.mental method 4.2.t
Equipment4.2
.2
Experimental progra.nme4.2.3
Growth mediun4.2.4
Inoculun sources and preparation4.2.5
Start-up procedure4.2.6
Sanpling4.2.6.I
Continuous digestion experinents4.2.6.2
Serni-continuous digestlon experinents4.2.7
Analytical procedures4.3
Results and discuseion4.3.1
Continuous digestion4.3.1.1
Run 1 (Conr)4 .3.t
.z
Run 2 ( cDR2 )4.3.1.3
Run 3 (con3)4.3.2
Semi-continuous dlgestion4 .3 .2
.L
Run 1 ( SCDR1 )4.3.2.2
Run 2 (SCDR2)4.3.3
Evaluati-onof
thenutritional
gtatusof
the standard growth medium4.3.4 Effect of
nedlun addltlons on batchdigestion of
contlnuoue dlgester liquor4.4
Overall discussion4.5
ConclusionsCHAPTER FIVE DEGRADATION OF VOLATILE FATTY ACIDS THE METHANE FERMENTATION
5.7 Introductlon
5.2 Experimental method
5.2.7 Equipment
5.2.2 Inoculum sources and preparation 5.2.3 Culture conditions and preparation 5.2.4 Saropling and analytical procedures 5.2.5 Analysis of results
5.3 Results
5.3.1 Experiment 1
5.3.1.1 Effect of acetate on utllisation of propionlc acid
5.3.1.2 Effect of pnopionate on utllisation of acetic acid
5.3.2 Experlment 2
5.3.2.7 Effect of acetate on utilisation of propionic acid
5.3.2.2 Effect of propionate on utilisation of acetic acid
rN
Page 87 B7 87 88
B8 88 88 88 90 90 90
9t
9L 91 92 92 92 92 94 105
t07 r07
TL2 118 124 L26 135
t37
137
t37
L37 138 138 139 L39 140 140 141 r47 150 150 755
5.3.3
Estimation5.4
Discussion5.5
ConclusionsCHAPTER SIX
APPENDIX THREE
APPENDTX FOUR
APPENDTX FIVE
vili
page
of
the ps;fprrm specific growthrate
L6t151 158 EFFECT OF SULPHUR.CONTAINTNG REDUCING
AGENTS ON THE METHANE FERI{ENTATION
170
t70t7t
77L L73 174 L74 190 194 796 204 224
6.7
Introduction6.2
Experinental method6.2.!
Equiprnent and general procedure6.2.2
fnoculum source and media preparation6.2.3
Sanpllng and analysis 6.3 Results6.4 Discussion 6.5 Conclusions
CHAPTER SEVEN REFERENCES
APPENDIX ONE
FINAL DISCUSSTON AND CONCLUSIONS
PROCEDURE USED TO CALCULATE THE
TOTAL VOLATTLE FATTY ACID (TVFA}
CONCENTMTTON
APPENDTX TWO ADDITIONAL EXPERTUENTAL DATA PERTAINING 226 TO THE CONTINUOUS AND SEMI-CONTTNUOUS
DIGESTION EXPERTMENTS
EXPERIMENTAL DATA FOR BATCH DIGESTTON EXPERIMENTS INVESTTGATTNG DEGNADATION
OF VOLATTLE FATTY ACIDS
229
SAMPLE GENSTAT PROGRAI'! USED TO FIT THE 234 LOGTSTTC EQUATION TO EXPERTI{ENTAL DATA
FROM STUDTES ON DEGRADATION OF VOLI\TILE FATTY ACIDS
EXPERTMENTAL DATA FOR BATCH DIGESTTON EXPERIMENTS INVESTIGATING THE EFFECT OF SULPHUR-CONTAINING REDUCTNG AGENTS ON
THE METHANE FERI'IENTATTON
239
1x
TABLE OF FIGUNES;
page
2.I Outline of the majon netabolic ptocesses involved in 5
the nethane fermentation
2.2 Major pathways fon anaerobic uti.llsation of pynuvate 10 2.3 COD flux in the nethane fernentation of complex waste 24 2.4 Proposed COD flux in the methane fernentation of 26
carbohydrate waste
2.5
Configurationsfor
the major anaerobic reactor designs3.1
Experimental set-upfor
the contlnuouadigestlon
82experiments
3.2
Experimental set-upfor
the senl-continuousdigestion
85experiments
4.1
Performanceof
the continuous dlgegter, run1
errcl.*(CDR1), from inoculatlon
to
day 1034.2
Perfomanceof
the continuous digester, run2
(CDR2) encl.4.3 Specific r
"ate data for CDR2 encl.
4.4
Effectof
additi-onof
sulphur-containingreducing
100agents
to
CDR2; five-day avet:age data4.5
ORP and TVFA datafor
CDR2 durlng the onsetof
LOz retarded digestion\.6
Perforrnanceof
the continuous dlgester, run 3 (cDR3) encl.*4.7 Specific rate daEa for CDR3 encl.*
4.8
Avenage tirne courseof total
gas productionfron
111SCDRl
4.9
Performanceof
the seml-continuous Blogendigester,
enc1. *( SCDR2 )
4.10 Average
tine
courseof total
gas pnoductionfrorn
I75SCDR2
4.11 Acetate degradation
in
batch dlgesterssupplenented
t25 with trace metals and 1ysed. ce11s. :jj
* Iarge tl iagram enclosed inside back coven . ,--,'. i
. ':l
.i;
32
page
4.I2 Data from Hansson and Molin (1981a) showing methane 133 producti.on from acetate in continuous-culture under
a N, atmosphere
5.1 Propionate utilisation in selected runs with 142 propionate added at 500 mg/I, experinent 1
5.2 Proplonate uti.llsation ln duplicate runs with 143 propionate added at 500 mg/I, experinent 1
5.3 Observed and predicted propi-onate concentfatlons 145
for gelected runs, experiment 1
5.4 Volumetric rate of proplonate utilisatlon in selected t46 runs wi-th proplonate added at 500 mg/\ , experiment 1-
5.5 Acetate utilisation in selected runs with 148 propionate added at 500 mg/I, experiment 1
5.6 Observed and predicted potential acetate pool I49 concentrations for selected runs, expe::iment 1
5.7 Propionate utllisati-on in selected runs with 757 acetate added at 500 mg/\, experiment 2
5.8 Propionate utilisatj.on 1n duplicate runs with 153
propionate added at 500 mg/I, experirnent 2
5.9 Observed and predicted propionate concentrati-ons L54 for selected runs, expefiment 2
!.10 Acetate utilisation in seLected runs with tS6 propionate added at 500 mg/I, experinent 2
!.11 Acetate utilisation in dupJ-icate runs with I57 propionate added at 500 mg/l , experi-ment 2
5.12 Observed and predicted potential acetate pool 158
concentrations for selected runs, experinent 2
5.13 Acetate utilisation in selected runs with acetate 59
added at 2000 mg/\, experlment 2
5.14 Acetate utilisation ln dupllcate runs with acetate 150
added at 2000 mg/a, experiment 2
6.7 Total gas production in batch digesters, experiment 1 775
6.2 Total gas production in batch digesters, experiment 2 L76
6.3 Methane productlon for batch digesters in experinent 3 t78 6.4 Methane production for batch digesters in experiment 3 L79 6.5 Methane productlon in batch digesters, experiment 4 183
r1
6.6 Methane
6.7 Methane
6.8 Methane
6,9 Methane
production production production production
dlgesters, dlgesters, digesters, dlgesters,
experinent experiment experlnent experinent in batch
in batch in batch in batch
5 6
7 8
Page 184 185 185 188
xil
TABLB OF TABI,E'S
page
2.7
Stoi-chiometny and changein
free energy valuesfor
15propionate and butyrate degradatlon reactione
2.2
Stoichiometry and changein
free enetgy valuesfor
LTpyruvate degradation reactlons
2.3
Stoichionetry and changein
free energy valuesfor
Lg the major nethane fornation reactions2.4
Kinetic parameters describing the methanefernentatl-on
302.5
Conparisonof typical
organlc loadLng ratesand
45treatment efflciencies
for
various anaerobic reactor designs3.1
Conpositionof
the growth nedium used,in contlnuous
d5and seml-continuous dlgestlon experlments
3.2
Compositionof
the vitamin solution usedto
66supplenent the standard growth rnedium
3.3
Conpositionof
thevolatile fatty
acldstandard
69solutions
3.4
Estinationof
the precislonof volatile fatty acid
TOconcentration neasurement
3.5
Eetimationof
the accuracyof
the volatiLefatty
7!acid rneasurement by gas chronatography
3.6
Performance characterlsticsfor
chemlcaloxygen
,U demand measurement3.7
Estimatj-onof
the precisionof
biologicaloxygen
7jdemand measurement
3.8
Estinationof
the pnecisionof
solidsconpositlon
TT!oeasurement
3.9
Performance characteristicsof
gascompostion
80 measurement4.1
Overviewof
experimental programmefor continuous
89and semj--continuous digestion experinentg
4.2
Comparisonof
speciflc rate datafor continuous
104digestion, run
2
(CDR2) ana other studies using glucose-based mediax1L1
page
4.3 Summary of steady-state data for the senl-continuous 109 Microferm d.j.gester (SCDR1)
4.4 Summary of steady-state data for the semj.-continuous 113 Biogen digester ( SCDR2 )
4.5 Major performance characteristics for SCDR2 at Lt6 steady state and for CDR3 from day 7O to day 96
4.6 Conparison of the composition of yeast extracts from LzO various manufacturers
4.7 Comparlson of the standard growth mediun L22
supplemented with cysteine-HC1 and other nedia used
in studies of the methane fermentation
5.1 Experinental conditions for batch dlgestion 138a experlnents
5.2 Coefflclents of the logistic equation for acid 144 utilisation in exoerinent 1
5.3 Coefficients of the Loglstlc equation for acid I52 utilisation in exoeriment 2
6.I Batch digester protocol showing component volumes t|t 6.2 Experimental conditions fon the batch digestion I72
experiment s
6.3 Actual and theoretical yields of nethane fron batch 180 digesters in experiments 3 to B
6.4 Residual volatile fatty acids ln batch digester with 181
added thioglycollate; experiment 3, tun5
6.5 Residual volatile fatty acj-ds in batch dlgester with L87
added thioglycollate; expeniment 8, run3
6.6 Residual dlssolved sulphide concentrations in 189 selected batch digesters
A2.1 Gas production from SCDR1 at varying tines fron feed 226 addition
A2.2 Gas production from SCDR2 at varying tines fron feed 227 addition
A2.3 Acid concentratlons in batch digesters supplemented 228
with trace metals or lysed cell-s
Al.1 Data for experiment 1 229
A3.2 Predicted volumetric rates of proplonate degradation 23O for batch digester, experiment 1
xtv
AJ. J Data for
45. 1 Data for
AJ.2 Data for 45.3 Data for 45.4 Data for 45.5 Data for 45.6 Data for 45.7 Data
for
A5.8 Data for
experiment experinent experiment experiment experinent experinent expeninent expeniment experi_rnent
2 1
2 3
4
5 5 I
8
Page
23t
239 239 240 240 24L 24L 242 242
EBEREMTATTONS
Abbreviations of volatile fatty acid names:
Ac acetic aci-d
Pr propionic acid iBu iso-butyric acid Bu butyric acid iVa iso-valeri-c acid Va valeric acid
Acids will be reffered t,o by the suffLxes r-ate' and '-ic acidtr interchangeably.
A subscript "i' denotes the intlal acid concentration.
Abbreviation of units:
atm
atmospheres'
gramnehr
hourkcal
kilocalorieI litre
mg:
milligrarunemin
minutemI nilli1itre nm
millimetremM
milU:noles perlitre
mo1
molemv ni-llivolt
r.p.m.
revolutions per minutepf
microlitrexvf-
other abbreviations:
a coefficient, of the logistic equation (dirnensionless) ATP adenosine triphosphate
b coefficient of the logistic eguation (day-l) BOD' five-d.ay biological oxygen demand (*g.f-l) CDR1 continuous digestion, run L
CDR2 cont.inuous digestion, run 2 CDR3 continuous digestion, run 3
COD chemical oxygen denand (*S.f-1)
CODr chemical oxygen dernand removed (mg.1-1)
CODR' specific rate of chenical oxygen demand removal (9 coDr.g vss-1.d"y-l)
cyst cysteine-hydrochloride
E" electrode potential relative to the saturated calomel
electrode (mV)
Eh electrode potential relative to the standard hydrogen
electrode (mv)
HRT hydraulic retention time (days) i.d. internal diameter
K coefficient of the logistic equation (g.1-1) K" half-saturation constant for sustrate utilisation
(n. ,_r )
NAD nicotinamide adenine dinucleotide
NADH reduced nicotinamide adenine dinucleotide
oLRs specific organic loading' rate (9 COD.g VSS-1.d.y-l) OLR' volumetric organic loading rate (g COD.t-1.aay-1)
ORP oxidation-reduction potential
pCOZ carbon dioxide partial pressure (bar)
rs rate of substrate utilisation (g substrate.l-1.hr-1) rsrmax maximum rate of subst,Eate utilisation
f,x race of biomass growth (g biomass.l-1.d"y-1) s substrate concentration (n.t-t)
S total sulphur concentration (mM or ng.t-l) SCDR1 semi-continuous digestion, runl
SCDR2 semi-continuous digestion, run 2
Irvi1
s.d.
standard deviationsRT
solids retentiontir@
(days)suJ.p
sodium sulphidet
t,l-methio
sodium thioglycoJ.J.ateTSS
tot.al suspend.ed soLLds tg.f-1)Tvl'A total volatire fatty
acid, concentration as acetate(rng. r-1y
uwA
un-ionisedvolatite fatty
acid concentration as acetate(mg. t-1)
\rFA volatile fatty acid
(concentratlon)(rg.f-l) vSS votatite
suspended soHds(S.f-l)
Y*s
bLornassyietd coefficlent
(g VSS.S COD}p
specLfj.c gro$rthrate
(aa"-f,Fma*
maximurn opecific Atrowth rate