HP0 4 and 2.5%. (w/v), agar. Also, 2.0%. (v/v) of a. 0.04%. (w/v) s o l u t i o n of
p h e n o l r e d was added, w i t h the pH of the medium a d j u s t e d to 6.8
p r i o r ...
THE
CHARACTERIZATION
THERMOPHILIC
OF
DEGRADATION
THE OF
AEROBIC
POTATO
-
WASTES
by SHERMAN B.Sc., Sc.
A
U n i v e r s i t y
( A g r . ) ,
THESIS THE
JACK
o f
B r i t i s h
U n i v e r s i t y
SUBMITTED
o f
IN
REQUIREMENTS MASTER
YEE Columbia,
B r i t i s h
Columbia,
PARTIAL
FULFILLMENT
FOR
DEGREE
OF
THE
OF
SCIENCE
i n THE
FACULTY
OF
Department
We
accept to
THE
t h i s
the
GRADUATE
of
t h e s i s
OF
APRIL,
©
Food
r e q u i r e d
UNIVERSITY
Sherman
1971
STUDIES
Science
as
conforming
s t a n d a r d
BRITISH
COLUMBIA
1980
Jack
Yee,
1980
197
OF
In presenting this thesis in partial fulfilment of the requirements for an advanced degree at the University of B r i t i s h Columbia, I agree that the Library shall make i t f r e e l y available for reference and study. I further agree that permission for extensive copying of this
thesis
for scholarly purposes may be granted by the Head of my Department or by his representatives.
It is understood that copying or publication
of this thesis for f i n a n c i a l gain shall not be allowed without my written permission.
Department The University of B r i t i s h Columbia 2075 Wesbrook Place Vancouver, Canada V6T 1W5
BP
75-51 1 E
ABSTRACT
Feasibility c a u s t i c potato t i o n was solids
o f the
p e e l waste by
examined.
biodegradation
aerobic-thermophilic
Fermentation
utilization,
Examination of these
characteristic varied
behaviour,
between t h e
of t h e r m o p h i l i c as
an
tation
The
the
solids
thermophilic
content
of
Protein
amino a c i d a n a l y s e s
and
of using
the
content
remaining
Increases strate
was
pheric
nitrogen
magnitude
was
flora
sufficient
c r e a t i n g the
i n the
fermentation.
fermen-
strains within
to
f i x atmospheric
remaining
animal
to the
the
reduced improve-
residue. feasibility
feed.
content
of
conversion
the
sub-
of
atmos-
n i t r o g e n - f i x i n g microorganisms
within
Microbial identification
organisms belonged
No
as
waste was
a noticeable
supported
nitrogen
due
potato
with
i n the
residue
assumed t o be by
the
fermentation
nitrogen
these
distinct
naturally occurring
t h e i r propagation
ment i n the
the
fermentation
showed
potato
of
organic
the
parameter
rate
characteristics. The
by
to
parameters
m i c r o o r g a n i s m s o f the
inoculum, with
total
respect
t h o u g h the
trials.
fermenta-
t e m p e r a t u r e , pH,
d i s s o l v e d o x y g e n and
n i t r o g e n were c h a r a c t e r i z e d w i t h process.
of n e u t r a l i z e d -
this
t o the
species
nitrogen. ii
species
i n d i c a t e d that
Bacillus
coagulans.
have been p r e v i o u s l y
reported
I t was fermentation for
caustic
advantages validity in
t h a t an a e r o b i c - t h e r m o p h i l i c
c a n be u t i l i z e d potato
as a w a s t e
p e e l waste.
Besides
treatment
process
t h e numerous
o f an a e r o b i c - t h e r m o p h i l i c f e r m e n t a t i o n ,
f o r the u t i l i z a t i o n
the treatment
disposal
concluded
of potato
of this
fermentation
p e e l waste
o f the waste.
iii
i s the near
the
process total
TABLE
OF
CONTENTS
Page
INTRODUCTION
1
LITERATURE
7
I. II.
REVIEW
T h e r m o p h i l i c A p p l i c a t i o n
B a c t e r i a of
the
7
A e r o b i c - T h e r m o p h i l i c
B a c t e r i a MATERIALS I.
AND
9
METHODS
Analyses
of
Wastes 1. T o t a l 2.
II.
, the
, .
C a u s t i c
Soda
Potato
13
P e e l 1
K j e l d a h l
N i t r o g e n
D e t e r m i n a t i o n
T o t a l Carbon and D e t e r m i n a t i o n
I n o r g a n i c
3.
T o t a l
Phosphorus
D e t e r m i n a t i o n
4.
T o t a l
Sodium
5.
Ash
6.
S o l i d s
7.
Measurement Samples
13 16 17
D e t e r m i n a t i o n
19
D e t e r m i n a t i o n
C o n s t r u c t i o n
the
the
1.
C o n s t r u c t i o n
of
2.
Top
f o r
3.
System
4.
B a f f l e s
5.
The
Assembly
Power
19
pH
of
the
P l a n t 19
of
f o r
13
Carbon
D e t e r m i n a t i o n
of
3
Fermentation the
Fermenter
Fermenter
Substrate
System
..
C e l l s
C e l l s
....
A g i t a t i o n
20 20 20 22 28
T r a i n
f o r
i v
the
A g i t a t o r
....
29
Page
III...
6.
A e r a t i o n
7.
Flow
8. 9.
Meters
31
.
33
Sparger
C o n s t r u c t i o n
33
Tubing
Connections
35
10.
M o n i t o r i n g
11.
C a l i b r a t i o n
of
12.
L o c a t i o n
of
the
System
of
the
System
Measurements
37
Heat
the
Thermocouples
40
C o n s t r u c t e d
M e c h a n i c a l
2.
M e c h a n i c a l Heat Input D e t e r m i n a t i o n the Absence of A i r Sparging
3.
Adjustments
4.
M e c h a n i c a l
D e t e r m i n a t i o n
Heat of
D e t e r m i n a t i o n
Heat
6.
Heat Loss D e t e r m i n a t i o n of Surface Foam
of
from
Input P o t a t o
5.
Analyses
the
the
The
2.
S a n i t a t i o n of the A c c e s s o r i e s P r i o r
..
42
i n 42
i n
Fermenter i n
43 C e l l
the
....
44
F e r m e n t a t i o n .
Temperatures
v
45 45
Fermenter V e s s e l to O p e r a t i o n from
44
Presence
Substrate
Measurements Taken m e n t a t i o n T r i a l s i)
42
S o l i d s
T h e r m o p h i l i c
1.
3.
P o t a t o
...
43
Presence Lost
Input
37
1.
the
IV.
System
the
and 46
F e r 46 46
Page
i i ) i i i )
V.
VI.
VII.
D T F N
i s s o l v e d Oxygen and pH o t a l S o l i d s Remaining i n the ermenter and T o t a l K j e l d a h l i t r o g e n
" T r u e "
P r o t e i n
a c e t i c
A c i d
Amino
A c i d
M i c r o b i a l 1.
N i t r o g e n
(TCA)
Using
47
47
T r i c h l o r o -
P r e c i p i t a t i o n
49
A n a l y s i s
50
I d e n t i f i c a t i o n
51
P r e p a r a t i o n of I s o l a t i o n F i x i n g B a c t e r i a
Media,
f o r
N51
. i) . i i )
Yeast Carbon Base (YCB) Medium N i t r o g e n F i x a t i o n Medium f o r Non-Symbiotic S o i l M i c r o organisms
i i i )
N i t r o g e n - F i x i n g
Medium f o r
A z o t o b a c t e r
B e i j e r i n c k i a
and
.
51
Genera i n
S o i l 2.
I s o l a t i o n
3.
V i s u a l
51
52 of
the
Microorganism
Appearance
of
the
52
M i c r o b i a l
C o l o n i e s
53
4.
Gram
53
5.
Spore
S t a i n i n g
( W i r t z - C o n k l i n )
6.
L i p i d
S t a i n i n g
(Burdon's
7.
M o t i l i t y
8.
C a t a l a s e
9.
Anaerobic
R e a c t i o n
Method)
53 ....
54 54
R e a c t i o n Test
55 55
v i
Page
10.
O b l i g a t i v e
11.
Voges-Proskauer
12.
pH
13.
M e t h y l
14.
Temperature
15.
Growth
i n
Lysozyme
58
16.
Growth
i n
NaCl
59
17.
Growth
in
Sodium
18.
pH
19.
A c i d
Test
Test
55
(V-P)
56
Voges-Proskauer Red
Range
B r o t h
56
Test
57
Range
D e t e r m i n a t i o n
57
A z i d e
59
Test
59
Formation
from
Carbohydrate
Substrates
60
20.
S t a r c h
61
21.
U t i l i z a t i o n of Sodium Sodium P r o p i o n a t e
H y d r o l y s i s
62
23.
Dihydroxyacetone
24.
P r o d u c t i o n
25.
Deamination
26.
Decomposition
of
Casein
66
27.
Decomposition
of
Tyrosine
66
28.
R e a c t i o n
Composition P e e l
of
i n
AND of
N i t r a t e
and
R e d u c t i o n
RESULTS
of
C i t r a t e
22.
EXPERIMENT I.
i n
A n a e r o b i c
of
to
N i t r i t e
P r o d u c t i o n
64
Indole
64
P h e n y l a l a n i n e
Litmus
65
M i l k
67
DISCUSSION the
C a u s t i c
Wastes
62
68 Soda
P o t a t o 68
v i i
Page
1.
Carbon-Nitrogen Phosphorus Content
2.
II.
2.
3.
III.
IV.
V.
GENERAL
68
Measurements F e r m e n t a t i o n
C o n s t r u c t i o n System
of
the
7 5
78
F e r m e n t a t i o n 78 Input
Measurements of Heat System C o n s t r u c t e d
Loss
C o n t r o l
F e r -
of the System
Measurements of Heat System C o n s t r u c t e d
P o t a t o 2.
M o i s t u r e
Other F a c t o r s A f f e c t i n g the m e n t a t i o n of the Substrate
R e s u l t s of mentations 1.
Carbon-
and
Requirements
Assembly and T h e r m o p h i l i c 1.
R a t i o ,
R a t i o
from
the 80
from
the 84
the A e r o b i c - T h e r m o p h i l i c of P o t a t o Wastes T r i a l s
of
of
87
A e r o b i c - T h e r m o p h i l i c
Fermentations
91
A e r o b i c - T h e r m o p h i l i c F e r m e n t a t i o n Sodium H y d r o x i d e - T r e a t e d P o t a t o
R e s u l t s Residue
F e r -
the
Analyses
of
the
of 110
Fermented 115
I d e n t i f i c a t i o n of the A e r o b i c - T h e r m o p h i l i c B a c t e r i a Present i n the T h e r m o p h i l i c F e r m e n t a t i o n of Potato Wastes
DISCUSSION
125
139
CONCLUSIONS
143
v i i i
Page LITERATURE
CITED
145
APPENDICES
152
Appendix A
153
Appendix B
154
Appendix C
155
Appendix D
;
ix
156
LIST
OF
TABLES
Table
1
^
Composition waste
2
and
of
f r e s h
Comparison
of
t h e r m o p h i l i c
3
Amount
of
r e s i d u e
c a u s t i c
p e e l
p o t a t o
the
70
v a r i o u s
p o t a t o
n i t r o g e n
as
p o t a t o
f e r m e n t a t i o n s
i n
compared
a e r o b i c -
the
to
the
94
fermented i n i t i a l
p o t a t o
used
4
116
K j e l d a h l of
the
n i t r o g e n
" t r u e "
fermented a c i d
5
the
Amino
p o t a t o
a c i d
r e s i d u e
6
p r o t e i n
n i t r o g e n
u s i n g
the
118
w i t h
of the
the
fermented
p o t a t o
used
f e r m e n t a t i o n
a c i d
120
requirements
to
the
v a l u e s
of of
chickens the
residues
Toxic
i n
b a s i s )
t r i c h l o r o a c e t i c
c o m p o s i t i o n
compared
compared
7
(wet
p r e c i p i t a t i o n
Amino
i n
d e t e r m i n a t i o n
sodium
fermented 122
l e v e l s
f o r
x
p o u l t r y
123
Table ,8
Page Atmospheric stated
nitrogen-fixing
i n Bergey's
Manual of
organisms
as
Determinative
Bacteriology 9
126
Characteristics
o f the
on n i t r o g e n - f r e e
media; Y e a s t
modified Meiklejohn's specific
medium
organisms
and
isolated
Carbon
Base,
Azotobacter 132
xi
LIST
OF
FIGURES
Figure
1
Page
C a u s t i c
p o t a t o
m e c h a n i c a l
2
3
waste
from
the
p e e l e r
P o l y p r o p y l e n e the
b a f f l e
Top
assembly,
vent
p e e l
14
f e r m e n t a t i o n
assembly
p o r t s ,
w i t h
b o l t e d
v e s s e l
w i t h
i n s e r t e d
sampling over
the
21
p o r t
and
fermenter
v e s s e l
23
4
Assembly
of
5
A g i t a t o r
assembled
t i o n e d
6
on
I m p e l l e r w i t h
Drive
aluminum
aluminum
i n
the
system
w i t h
top
o f
between
a g i t a t o r
shaft
i m p e l l e r
over
i m p e l l e r the
assembly
c o u p l i n g
i m p e l l e r
24
p o s i -
s h a f t
p o s i t i o n ,
foam-breaking
towards
7
the
the
26
the
s i t u a t e d
aluminum
w i t h d r i v e
sparger,
the shaft
shaft
...
27
aluminum and 30
x i i
F i g u r e
8
Page
A e r a t i o n
system
r e g u l a t o r , a i r
9
the
Sparger
to
11
head
and
the
Thermocouple
Data
and
w i t h
t e f l o n
aluminum sparger
sparger
b a l l s ,
aluminum
head
head
34
c o n s i s t i n g the
t e f l o n
sparger
p o s i t i o n e d
t u b i n g
of
the
sparger
head
w i t h i n
36
the
v e s s e l
r e c o r d e r
m e n t a t i o n
13
r e g u l a t o r s
assemblies
s t e e l
fermenter
12
the
aluminum
s t a i n l e s s head
r e s e r v o i r -
32
assemblies
a t t a c h e d
10
t w i s t c o c k
a i r
f l o w m e t e r s
Sparger
and
w i t h
38
used
to
m o n i t o r
temperatures
e l e c t r o n i c
thermocouple
Fermenters
assembled
along i c e
w i t h i n
the w i t h
f e r the
p o i n t
the
39
i n s u l a t e d
room
14
41
D i s s o l v e d for
a i r
oxygen
s a t u r a t e d
probe water
e r a t u r e s
c a l i b r a t i o n at
h i g h
curve
temp48
x i i i
Figure 15
Page Thermophilic waste
fermentation
substrate; i n i t i a l
16
Mechanical
17
Heat
loss
heat
of a potato 73
trial
83
input
determination
from
heated
aqueous s y s t e m s ; w i t h and w i t h o u t
a 85
heavy s u r f a c e foam 18
Thermophilic
fermentation of a potato
waste s u b s t r a t e ; no. 3 19
Thermophilic
92 See psefct
fermentation of a potato
waste s u b s t r a t e ; no. 4 20
Thermophilic waste
fermentation
substrate with
5.66
106 See of a potato percent
sodium 112See pocket
content 21
Gram r e a c t i o n the
isolated
p^eL
and c e l l u l a r m o r p h o l o g y o f organism
xiv
130
ACKNOWLEDGEMENT
The tude and
author wishes
t o D r . P.M. T o w n s l e y guidance
during
I would
to express h i s s i n c e r e s t
f o r h i s enthusiasm,
the course o f t h i s
also wish
to thank
grati-
encouragement
study.
t h e members o f my
committee:
P r o f . T.L. C o u l t h a r d , Dr. B . J . Skura, Dr. J .
Vanderstoep
and f o r m e r member D r . H.S. Saben f o r t h e i r
advice
and wisdom. Thanks a r e a l s o
Alpin
extended
and Mr. B. W a l s h f o r t h e i r
xv
t o D r . D. A l i ,
assistance.
M r s . L.
Dedicated t o my
late
with
love
Grandmother
xv i
1.
INTRODUCTION
I d e a l l y , many food p l a n t wastes should be developed as a u t i l i z a b l e r e s o u r c e , but t h i s i s not p o s s i b l e due
always
i n p a r t to unfavorable economics and to the
l a c k of s u i t a b l e technology.
G e n e r a l l y , wastes have been
t r e a t e d as a management or d i s p o s a l problem.
Agricultural
wastes c o n s t i t u t e by f a r the l a r g e s t volume of o r g a n i c wastes, amounting to over 200 m i l l i o n tons i n Canada i n 1975
(42).
Beef and d a i r y c a t t l e manure accounts
f o r the
m a j o r i t y of the animal wastes while the l a r g e s t p r o p o r t i o n of
the p l a n t wastes are c o n t r i b u t e d by straw r e s i d u e s .
the v a r i o u s food i n d u s t r i e s , potato p r o c e s s i n g of
over 450,000 tons a n n u a l l y , f r u i t
wastes exceed are produced significant
one m i l l i o n tons and meat p r o c e s s i n g wastes at l e v e l s of 150,000 tons.
importance
Other wastes of
i n r e l a t i o n to our environment are industries
(42).
recent y e a r s , the d i s p o s a l of l a r g e volumes
of wastes has become a matter to
accounts
and other vegetable
those from d a i r y , brewery and d i s t i l l e r y In
Of
of s e r i o u s economic
the processed potato i n d u s t r y .
I f the s o l i d
wastes are not s o l d d i r e c t l y as c a t t l e
concern
potato
feed, they must
be t r e a t e d by -a c o n v e n t i o n a l waste d i s p o s a l method i n which the cost may
be economically
unfavourable.
2.
The
composition
o f a waste
processing plant i s largely Generally,
determined
the p o t a t o p r o c e s s raw
washing of the
potatoes;
washing
t o remove s o f t e n e d t i s s u e ; p o r t i o n s ; shaping,
washing
treatment
which
final
tion;
packaging.
from
potato
The
itself.
are
to the p o t a t o
and
stream
cleaning dients
and
include dirt
in lesser
they
types can
amounts.
operation tively
o f waste be
silt,
caustic
fraction
has
was
i n the
food ingrei n the
discharged.
s t e p s o f the p r o c e s s i n g
can be
t r e a t e d more
w i t h i n the p l a n t . more waste
than
c o n s i d e r e d t o be
of over
which
considered separately since
a p o l l u t i o n problem. a pH
the
soda, f a t ,
streams
being
1 2 and
Since
an
caustic
in this
other
a t t a c k on
t h e most
The
effec-
the p e e l i n g
a l l o f the
p o t a t o p r o c e s s i n g o p e r a t i o n s combined, major f r a c t i o n
to
present
other
most
combined b e f o r e
i n some c a s e s ,
generates
and
streams
related
be
heat
preserva-
components
w h i c h may
removed a t d i f f e r e n t
and,
alleviating
separation;
o f waste
The
Normally,
s h o u l d be
i f separated
operation
or
t o remove
p r o c e s s i n g or
preserving chemicals,
p r o c e s s i n g p l a n t are The
and
processing plants is closely o f the p o t a t o
waste
used.
p e e l i n g , which i n c l u d e s
composition
composition foreign
a potato
the p r o c e s s
trimming,
defective
is optional;
by
from
i n v o l v e s the f o l l o w i n g
steps:
and
stream
form
this
important
in
p e e l waste i t cannot
be
3.
used
as l i v e s t o c k
cessing tion.
i twill
f e e d , and i f dumped w i t h o u t
form
a g e l that i s r e s i s t a n t
In a d d i t i o n , with
solution
t h e use o f c a u s t i c
as a p e e l i n g a g e n t ,
the h i g h
t h e waste w a t e r may make t h e s o i l and
toxic
treatment
sodium
impermeable
used
hydroxide
to water
the
temperature
of this
aerobic organisms
before the
investigation
to degrade p o t a t o
High
developed
i n the degradation
process
However,
was
a e r o b i c t h e r m o p h i l i c waste
o f the d e g r a d a t i o n . energy
systems are
industry.
o f the t h e r m o p h i l i c p r o c e s s
by t h e h e a t
exothermal
in this
The p u r p o s e
p r o c e s s i n g c a n be u s e d
uniqueness
sludge
i n v o l v e a lengthy treatment
whether exothermic
The
created
t o decomposi-
sodium c o n t e n t i n
and a c t i v a t e d
commonly
i s discharged.
to determine
This
lagoons
processes
these processes waste
pro-
t o p l a n t growth ( 4 1 ) . Aerated
treatment
further
wastes.
i s p r o v i d e d by temperatures
are
m e t a b o l i c a l l y by t h e of the s u b s t r a t e .
i s intensified,
within limits,
by
higher
s u b s t r a t e c o n c e n t r a t i o n s s i n c e t h e amount o f h e a t
energy
increases proportionally
substances increased rate
being biochemically converted exothermic
heat
o f the r e a c t i o n
of substrate degradation
of the process The
t o t h e amount o f o r g a n i c
over
thus
(43).
a c c e l e r a t e s the
increasing
the e f f i c i e n c y
t h a t a t t a i n e d by m e s o p h i l i c
increased reaction
rates result
The
systems.
i n shorter detention
4.
times
i n
degree
comparison
of
waste
t h i s
a
i n
high
order
c e n t r i f u g a l
some
are
of
the
showed
at
f i l t e r
t o g e t h e r
w i t h
systems
animal
or
vacuum
f e e d ,
not
is
is
the
waste,
Water
s e p a r a t i o n
w h i c h must u l t i m a t e
a
lower of i n
s p e c i a l
u t i l i z a t i o n
of
f o r
not
compared
organisms
the
to
sludge
(61).
a
p r o c e s s , vacuum
p r o v i d e s
an
s e p a r a t i o n
p r i o r
to
a
(20) g r e a t l y
m e s o p h i l i c
demand. pathogenic
t h e r m o p h i l i c
s i g n i f i c a n c e
p r i m a r y
purpose.
Garber had
to
continuous
t h i s
on
an
n o r m a l l y
p e e l i n g
be d e w a t e r e d
coagulant
the
is
process
sludge
In
f e a s i b l e
dewater
d i s p o s a l .
as
waste
s o l i d s - l i q u i d
d i g e s t e d
y i e l d
of
and
c a u s t i c
e a s i l y
improving
achieved of
f i l t e r s
t h e r m o p h i l i c
d e s t r u c t i o n
temperatures
ment
i n
volume
c o m m e r c i a l l y
p r e s s i n g
t h e r m o p h i l i c
The
o c c u r s .
p o t a t o
c o n c e n t r a t i o n
vacuum
from
the
sludge
p r o c e s s i n g
improved sludge,
b e n e f i t
that
by
w i l l
Thus
d i g e s t e d
f u r t h e r
of
used
r e s u l t
pH,
(61).
form
continuous
which
a d d i t i o n a l
s e p a r a t i o n
to
c o n c e n t r a t i o n .
The
f i l t e r
a p p l i e d
s o l i d s
u n i t s
high
as
s e t t l e a b l e
dewatering
i t s
same
d e c r e a s i n g
the
A d d i t i o n a l
w i t h
to
reduce
Both
s o l i d s
the
to
t r e a t m e n t ,
employed.
f o r
c o n t r i b u t i n g
p r o c e s s ,
s o l i d s - l i q u i d
important
o b t a i n
thus
systems
c o s t s .
With
is
m e s o p h i l i c
p u r i f i c a t i o n ,
o p e r a t i o n a l
improved
to
waste
(4,55). from
to
t h i s
animals
t r e a t -
As
an
process
5.
is
a p o s s i b l e asset
Even
i f the
aspects
sludge
w o u l d be
mesophilic
because was
is
discarded
temperatures
especially tion by
during
ambient
insulation
t o the
overall
at t h e r m o p h i l i c
The
fermentation
sufficient
i n the
substrate
are or
of
the
Accordingly,
treatment
successful
system
adequate i s an
of
increased
a p p l i c a t i o n of a t h e r m o p h i l i c
etc.) and
to
installations,
temperature
important
pro-
surviving
resistant
c o n t r o l and
pro-
respect
salinity,
Larger
because o f t h e i r
with
biological
(pH,
less
composition. and
as
capable
for
t i o n mass.
be
thermophilic
especially
stability
duration
r e a c t i o n s may
o f the
however, show g r e a t e r a longer
fermenter
conditions.
known t h a t
becomes u n s t a b l e
waste
unaffected
substrate,
change
of the
is
in the
fermentations
conditions
stability
species
the
decomposi-
approach e n v i r o n m e n t a l extremes fewer
systems,
of
cesses the
the
rate
p o s s i b l e disadvantage
It i s well
health
manner.
treatment
temperatures provided
temperature.
than
in thermophilic
c o l d season.
i s i t s poor process
public
concern
mesophilic
f r e e z i n g environmental
The
to
less
the
i s a p p l i e d , whereas m e s o p h i l i c
hampered by
cess
the
soil,
in a similar
achieved
i n the
accomplished
low
on
of c o n s i d e r a b l y
sludge
advantageous
i t s pathogen-free q u a l i t y .
disposed
In c o m p a r i s o n , increased
of
maintenance fermenta-
monitoring
requirement digestion
for
the
operation.
6.
The to the
purpose
e s t a b l i s h the
ratory process during
this
composition
caustic potato
lability
of
peel
of
waste,
to microorganisms.
system has the
of
thermophilic
in
the
laboratory
thermophilic
and
enable
conditions system,
as
size
enough s t a b i l i t y
if
the
are to
threefold.
substrate,
to
to
i n which
adequate
the
and
peel
to
avaia
controllability
with
Thirdly, this
substrate
characterize
waste.
labo-
thermophilic
study.
obtainable
d i g e s t i o n of potato
namely,
construct
operational
study
First,
its nutritional
Secondly,
sufficient
d i g e s t i o n to
t h e s i s was
the
7.
LITERATURE
I.
T h e r m o p h i l i c
The l o g i c a l known
19,21).
workers
of
(45)
p r i o r and
Gaughran
the
of
thermal
and
1927
and
on
temperatures p u b l i s h e d
a
b e l o n g i n g
to
K o f f l e r
a
he
and
more
M i g u e l the
d e s c r i b e d
and
and
Pace
F a r r e l l
the
B a c i l l u s
of
both
w a t e r . e a r l y sporu-
e x c e l -
t h e r m o p h i l i c i n v o l v i n g p r o t e i n s
growth
and
a (1,11,
the
reviewed
t h e i r
of
p r e s e n t e d
s t u d i e s
of
been
b a c i l l i .
the at
Campbell
t h e r m o p h i l i c
and
from
s t r u c t u r a l
p h y s i o l o g y
r e c e n t l y ,
(1)
(11)
has
b i o -
methodology
c o n c e r n i n g
d i s c u s s e d
of
1879
b i b l i o g r a p h y
art
enzymes
i n
b a c t e r i a
A l l e n
the
d e s c r i b i n g
genus
to
t h e r m o p h i l i c
(29)
m i c r o b i a l
r e v i e w the
of
of
a b i l i t y
d i s c o v e r y
o u t l i n e d
complete
which
the
temperatures
t h e r m o p h i l i c
Campbell
the
b a c t e r i o p h a g e s .
i n
(40)
or
r e c o r d e d
c r e d i t e d
Tanner
s t a t e
s t a b i l i t y
on
i n i t i a l
subsequently,
the
t h e r m o p h i l e s .
l i t e r a t u r e
e l e v a t e d
n o n - s p o r u l a t i n g
(21),
reviews
at
was
p r e s e n t e d to
phenomenon
The
a e r o b i c
microorganisms. the
grow
b a c t e r i u m
study
Robertson
l e n t
to
M o r r i s o n
the
l a t i n g
t h e r m o b i o s i s
c e n t u r i e s .
t h e r m o p h i l i c
f o r
B a c t e r i a
e n t i t i e s
f o r
REVIEW
e l e v a t e d (19)
b a c t e r i a
a s s o c i a t e d
8.
Many these many
of
the
microorganisms i n s t a n c e s
t u r e s ;
t h a t
are
i s ,
or
forms.
G e n e r a l l y ,
l a r
and
the
organisms
r a p i d
are
at
high
o b l i g a t e
c e l l u l a r
obvious, f o r
r e l a t i v e l y
is
the
q u e s t i o n e d
these which
have
of
the
would
n o r m a l l y
d e s t r o y e d
most
l i f e
o f f e r e d . c e l l u -
t h e r m o p h i l i c than
c e l l s or
of
e s s e n t i a l
s t a b l e
the
i n tempera-
been
the
and
how
h i g h
components
heat
Secondly,
of
to
t h a t
l i f e
more
have
t e m p e r a t u r e s ,
e x p l a n a t i o n s
necessary
c o u n t e r p a r t s .
s t u d i e s
temperatures
the
two
most
r e s y n t h e s i s
at
a c t u a l l y
i n a c t i v a t e
components
p h i l i c
grow
growth
d e s t r o y
F i r s t l y ,
mentioned
are
t h e i r
meso-
capable
i n a c t i v a t e d
of
c e l l u l a r
components. Numerous of
the
to
occur
d e s e r t
t h e r m o p h i l i c i n
such
sands
i s o l a t e d a l l
s t u d i e s
from
domestic
v a r i e t i e s ,
raw
and
from and and
(1,21).
i n f l u e n c e
on
and
there
seems
are
members
the
and
man,
the
f r e s h
l i t t l e
n a t u r a l l y
of
have
the
doubt
w a t e r ,
m i l k ,
masses
been
t r o p i c a l
g r a i n s
c o n d i t i o n s
d i s t r i b u t i o n be
i n
u b i q u i t o u s
Thermophiles
p a s t e u r i z e d
C l i m a t i c
to
They
from
from
the
as
snow.
s a l t
e s p e c i a l l y
m a t e r i a l s
of
c l i m a t e s
f a l l e n
animals
from
v e g e t a b l e s ,
i n
a i r ,
shown
microorganisms.
d i v e r s e
and
have
of
from
have
o c c u r r i n g
a p p a r e n t l y
s o i l
been
of
of
a l l
s t o r e d
d e c a y i n g
the
i n
feces
foods
t h e r m o p h i l i c
t h a t
found
s o i l s ,
from
and
nature
p l a n t have
no
b a c t e r i a
t h e r m o p h i l e s i n h a b i t a n t s
9.
and
can
be
c o n t a c t is
i s o l a t e d
w i t h
e v i d e n t
s o i l .
t h a t
p l a c e
whenever
or
a r t i f i c i a l
an
II.
cess
is
for
a
the
u t i l i z e d
t a i n e d
of
The
s u b s t r a t e
a l t h o u g h ,
McCarty
energy and
Andrew
noted the
t h a t
a
In
these
t h a t i n
the
t h i s
i n
d i s t r i b u t i o n ,
w i t h i n
w i l l a
i t
take
n a t u r a l
to
the
to
be
i n
the
t h e i r
of
composting to
was
phase,
as
by
per
m i c r o -
cent
range,
i n i n
systems
to
amount
as
70 of
R i c h
of M c C a r t y ' s
wastes
con-
the
c l o s e r
r e s p o n s i b l e
s o l i d
composting,
l i q u i d
was
(35).
and
the
environment.
d i s c u s s i o n
energy
of
energy
s i g n i f i c a n t
surrounding
method
s y n t h e s i s
20-40
i t
a
p r o -
microorganisms
t r a n s f e r
the
a
t h a t
c e l l
c e l l
obvious
escaped
r e c o g n i z a b l e
f o r
as
wastewater
t h e r m o p h i l i c
usable
treatment
c o n s i d e r e d
o r g a n i c
t h a t
i n
c o n t r a s t
is
of
B a c t e r i a
wastewater
acknowledged
to
(44),
and
wastewater
e f f i c i e n c y
was
l o s t
come
organisms
f a v o u r a b l e
c o n c e n t r a t e d
c o n s i d e r e d
temperatures
75°C. is
was
has
A e r o b i c - T h e r m o p h i l i c
energy
was
It
the
of
n u t r i e n t s
c e n t .
are
which
u n i v e r s a l
of
development
organisms
per
t h e i r
a e r o b i c - t h e r m o p h i l i c
showed
maintenance.
to
m a t e r i a l
environment.
r e c e n t
(37)
Due
c o n d i t i o n s
treatment
McCarty
any
p r o l i f e r a t i o n
A p p l i c a t i o n
The
from
paper,
f o r high
where
r a i s i n g as
70-
there
a e r o b i c - t h e r m o p h i l i c
10.
d i g e s t i o n heat
of
wastewater,
l i b e r a t e d
r e a d i l y
by
d i s s e m i n a t e d Kambhu
s i m u l a t i o n t h a t
the
s u f f i c i e n t
organic
s o l i d s
m o p h i l i c
of
range.
a c t i v a t e d
of
working
w i t h
manure,
showed
was
make
i n
the
t h e i r
heat
was
by
PSpel
w i t h
o r g a n i c
s o l i d s
by
10.5
day
p e r i o d .
With
f r e s h
sludge,
i t
near
50°C
even
from
20°c
to
was
a
21.5
75%
5°C.
s o l i d s
amount
of
oxygen X)
et
o r g a n i c a l . can
d e s t r u c t i o n
m e s o p h i l i c
(4.6
of
and
waste
(50)
less
but time
study to
and
of
wastes of
content
a
found
m a t e r i a l
i n
concluded
w i t h (20%
a
l e s s ) .
primary
r a i s e
ther-
and
the
and
(43) l i q u i d
10.8%
s o l i d s
was
reduced of
decreased
t h a t as
there
l i t t l e
as
a e r o b i c degree
o p e r a t e d
w i t h
much
the
temperature
same
o p t i m a l l y
of
in
of
f e e d i n g
t h a t
the
system
sludge,
Ohnmacht
temperature
authors
an
computer
f r e q u e n t
a c c o m p l i s h as
the
i s
d e s t r u c t i o n
m a i n t a i n
treatment
s u p p l i e d i n
to
ambient
l a t t e r
d i g e s t i o n
t i o n a l
input
the
The
Smith
t h e r m o p h i l i c
p o s s i b l e
though
r e d u c t i o n
hours.
organic
was
a
sludge
the
a
heat
d i g e s t i o n
model
t h a t
over
n o t i c e
s e l f - s u s t a i n i n g
c o n c e n t r a t i o n 901
by
the
i n d u s t r i a l
t e s t
the
s u p p l i e d
body.
to
system.
showed
in
b a t c h
since
the
process
sludges,
a
d i f f i c u l t
t h e r m o p h i l i c
r e a c t o r
sewage
to
generated
s o l i d s ,
the
more
(2 8)
a e r o b i c
However,
sludge
temperature
l o s t
Andrew
heat to
is
microorganisms and
and
study
i t
the
g r e a t e r A l s o
of conven-
same l o a d i n g the
same
11.
r e d u c t i o n tank
o f
which
was
m e s o p h i l i c of
a i r
and
i n
organic
order
permit
sludge.
L o l l
the
b i o c h e m i c a l w i t h
p h i l i c the
using
r e d u c t i o n t i o n A
5
t e s t s t o
w i t h i n ment,
3
higher
(36)
that
by
r e p o r t e d
demand demand
reduced
a
was
previous
B.O.D.,-
as
between
w i t h
during
r e t e n t i o n
5-day which
time
time
at
had been
reduced
t h e
s o l i d s
a
t h e by
about
95%.
L o l l
o f
p o i n t
degraded,
m i c r o b i a l
i t
reached waste f o r
where
m e t a b o l i c
conthermo-
whereas,
a i n
shown,
b i o l o g i c a l b a t c h
and p i g
a l l three
t o
50°C
o f
t h e
t h e bulk
and then
In
was
temperature
The temperature
and t h e
73%,
t h e beginning
ambient
reduced
(68%).
(35)
46°C
u n d i l u t e d
anaerobic
parameter,
used
a f t e r
t h e
by
molasses was
o f
701
same
p l a c e
content
about
only
i n
d i g e s t e r
by
by
a
i n
process
d i g e s t i o n ,
a n d 97% was
p e r i o d
a
t o
about
used
treatment
B.O.D.,-
temperatures
rose
due
t h e
waste,
17°C and 20°C.
substances
(B.O.D..
r e f e r e n c e
95%
yeast
maximum
the
(C.O.D.)
paper
a
between t o
a
from
i n
r e q u i r e d
was
t h e a e r o b i c - t h e r m o p h i l i c
r e d u c t i o n
t o
gas
o f
substrate a
Oxygen
a e r o b i c - t h e r m o p h i l i c
7-day
Maximum
systems.
n o r m a l l y
t h e d i g e s t i o n
oxygen
o f
accomplished
t h e volume
minimize
oxygen
In
be
l o s s
d i g e s t i o n
C.O.D.
when
t o
c o u l d
heat
l i q u o r s
c h e m i c a l
t r a s t
o n e - s i x t h
o p e r a t i n g
t o
sludge
matter
o f
reached
t h e
e x p e r i -
v a r i e d f e r m e n t a t i o n t h e
subsequently
a c t i v i t y .
manure. s u b s t r a t e s .
were o f
diges-
organic decreased
12.
Recently, bacterial cells high organic attention.
the recovery
o f p r o t e i n i n the form o f
from the t h e r m o p h i l i c aerobic treatment o f
s t r e n g t h wastewater has r e c e i v e d The p r o t e i n content
considerable
and n u t r i t i o n a l p r o f i l e of
t h e r m o p h i l i c microorganisms may be b e t t e r than that from m e s o p h i l i c
organisms
(4,55).
Bellamy
(4)
obtained
concluded
that the t h e r m o p h i l i c p r o t e i n c o n t a i n e d r e l a t i v e l y h i g h conc e n t r a t i o n s o f l y s i n e , tryptophane and s u l f u r amino a c i d s and
should have a high n u t r i t i o n a l value
f o r monogastric
animals as w e l l as f o r ruminants. I n v e s t i g a t i o n s on the a p p l i c a t i o n of the a e r o b i c t h e r m o p h i l i c degradation
process
o f o r g a n i c wastewaters
o r i g i n a t i n g from the food i n d u s t r y are almost
non-existent
i n comparison to the i n f o r m a t i o n a v a i l a b l e on animal waste management.
I t i s evident
that the p o t e n t i a l of
the t h e r m o p h i l i c m i c r o b i o l o g i c a l treatment o f high wastewater should be of i n t e r e s t industries.
to the food
strength
processing
13.
MATERIALS
I.
Analyses
of
the
C a u s t i c
F o u r - g a l l o n were of
o b t a i n e d
Fraser
The
samples
of
B r i t i s h
at
5°C.
the
and
a c c o r d i n g
to
S o l t e s s
sample
was
were
915
p l a n t
p e e l e r s
a
f r e s h l y
at
homogenized
1)
B.C.
the
r e f r i g e r a t e d were
waste
(Figure
C h i l l i w a c k ,
samples
o r g a n i c
n i t r o g e n
(16)
r a p i d .
C o r p . ,
T o t a l
The Model
i n
Wastes
p o t a t o
l a b o r a t o r y ,
N i t r o g e n
the
c a l c u l a t e d
2.
the
P e e l
l y e - p e e l e d
L t d . ,
K j e l d a h l
U n i v e r s i room
subsequently whole
p o t a t o e s
on
Carbon
samples
T o t a l
amount u s i n g
dry
was
done
method
n i t r o g e n
Auto
i n
i n
A n a l y s e r
N.Y.).
A l l
t r i p l i c a t e of
Concon
each II
d i g e s t e d (Technicon
n i t r o g e n
analyses
b a s i s .
and
were
Organic
of
an
Tarrytown, a
D e t e r m i n a t i o n
m i c r o - K j e l d a h l
The
d e t e r m i n e d
Instruments
P o t a t o
c a u s t i c
s t o r e d
to
METHODS
v a r i e t y .
T o t a l
and
to
p r o c e s s i n g
T o t a l
ol.
brought and
of
the
Foods
compared
same
from
F r o s t e d
Columbia,
These
analyzed of
were
Soda
samples
d i r e c t l y
V a l l e y
AND
Inorganic
a n a l y z e d
Carbon
Carbon
by
A n a l y s e r
using
D e t e r m i n a t i o n
a
Beckman
connected
to
a
14.
Figure
1.
Caustic peeler.
potato peel
waste
from
the
mechanical
15.
Beckman
Infra-Red
F u l l e r t o n ,
CA).
p h t h a l a t e ppm)
(100
were
carbon
-
A n a l y z e r Standard
s o l u t i o n s
500
and
p r e p a r e d
ppm)
and
C a l i b r a t i o n
organic
were
versus
to
a
a
samples
constant
weight
i n
d e t e r m i n a t i o n " ) and
i n t o
p e s t l e . a
Works,
7
ml
water.
p a r t i c l e s
were
s o l u t i o n
to
volume
d e i o n i z e d
40
was i n
a
w a t e r .
100
ml
Twenty
(400
ppm
i n
i n j e c t e d
i n t o
the
Beckman
H a m i l t o n A l l
was
t h o r o u g h l y
of
p o r t i o n
the
Tissue
s o l u t i o n s .
d r i e d
T o t a l
of
p o t a t o
Carbon
(Hamilton used
soaking
i n
i n a
of
d i s t i l l e d -
and
w i t h
the
s o l u t i o n . made
d i s t i l l e d -
f i n a l
s o l i d s )
A n a l y z e r Co.,
was
u n t i l i n
t h i s
sample was
w i t h
W h i t t i e r ,
these
w i t h
(Corning
homogenizer f l a s k
on
powder
amount
suspended
the
p r e s s u r e
powder
G r i n d e r
m i c r o l i t e r s
glassware by
r e a d i n g
stock
a
the
s m a l l
v o l u m e t r i c
of
of
t o t a l
and
s e c t i o n
to
50
d e t e r m i n a t i o n ,
carbon
homogenized
and
from
syringe
c l e a n e d
a
was
f i n e
terms
(see
f o r
m i l l i v o l t
crushed
w i t h
sample
s o l u t i o n
c a l i b r a t e d
mg
removed
t o t a l
oven
then
N.Y.)
e x t r e m e l y
carbon
(2)
-were d r i e d a t a t m o s p h e r i c
Ten-Broeck
The
f o r
(10
33.047
p l o t t i n g
d r y i n g
and
A
C o r n i n g ,
d e i o n i z e d
up
a
hydrogen
b i c a r b o n a t e
c a r b o n - c o n t a i n i n g
p o t a t o
p l a c e d
This
the
by
Inc.,
potassium
A.O.A.C.
curves
The
mortar
Glass
of
of
i n o r g a n i c
p r e p a r e d
c o n c e n t r a t i o n
" S o l i d s
to
f o r
r e s p e c t i v e l y .
Instruments
sodium
a c c o r d i n g
d e t e r m i n a t i o n
carbon
(Beckman
a CA).
experiments
potassium
16.
dichromate-concentrated The
glassware
rinsed
was
3.
Total
of
Phosphorus
digestion,
into
estimated
A blank,
in distilled-
of t h i s
to the autoanalyzer
i n a chromic
acid
on t h e
After
Technicon
the samples.
concentrated
for this
was
After soaked
water.
o f the p o t a t o was
standard.
a n a l y s i s was
solution.
within
standard
as a r e f e r e n c e
o f h o t H C l ( 2 ) and t h e n
deionized-distilled
were
flasks.
s o l u t i o n was p r e p a r e d
water, the glassware
solution
samples
and f r e s h p o t a t o e s
range o f the phosphorus c o n t e n t
glassware
i n the
c o n t a i n i n g only the r e a g e n t s ,
i n conjunction with
A dilution
All
aqueous
solution,
used
Oven d r i e d
Kjeldahl digestion
A KH^PO^ s t a n d a r d
distilled
and t h e n
to those
t h e samples were a n a l y z e d
was p r e p a r e d
night
similar
p o t a t o p e e l waste
Auto-Analyzer.
samples.
acid
f o r t h e p r e p a r a t i o n o f t h e samples
nitrogen determinations.
the c a u s t i c
applied
water
overnight.
Determination
a n a l y s i s was
w e i g h e d and p l a c e d
the
solution
the chromic
distilled
method u s e d
phosphorus
Kjeldahl
in
acid
water.
The for
removed from
thoroughly
deionized
sulfuric
soaked
rinsing
over-
i n deionized-
i n a 1 to 1 rinsed i n
4.
T o t a l
analyses
Sodium
A
wet
ashing
of
the
d r i e d
spectrophotometry. a
30
ml
acids
D e t e r m i n a t i o n
volume
added
The
m i x t u r e
to
encourage
c o m p l e t i o n i n t e n s e l y
was
to
a a
the
c o l d
reduce
the
volume
the
d i g e s t i o n
was
i n d i c a t e d
the
neck
A l l o v e r n i g h t s u l f u r i c
i n
soak
to
r i n s e the
i n
was
sodium
a b s o r p t i o n
c a r r i e d
out
u s i n g
d i g e s t i o n
f l a s k
was
f l a s k and
f l a s k .
heated
c h a r r i n g .
was
s o l u t i o n .
A f t e r
heated
more
p e r c h l o r i c
s u l f u r i c
s l o w l y
The
a c i d
a c i d
end
of
fuming
i n
of
the
t h i s
a n a l y s i s
potassium
glassware
f o l l o w e d
a l l
f o r
by
was a
r i n s e d
sodium
water
soaked
d i c h r o m a t e - c o n c e n t r a t e d i n
c o n c e n t r a t e d
remaining
was
was
d e i o n i z e d n i t r i c
ions.
A
employed
a c i d f i n a l
to
remove
a c i d . An
Ash,
by
d e i o n i z e d - d i s t i l l e d
n i t r i c
atomic
The
w a t e r ,
remove
the
atomic
w i t h o u t
the
the
glassware
s o l u t i o n
a c i d .
d i s t i l l e d
of
f o r
f l a s k .
the a
the
n i t r i c
to
the
by
K j e l d a h l
d i g e s t i o n
excess
used
n i t r i c - p e r c h l o r i c - s u l f u r i c
and
and
of
of
d i g e s t i o n ,
remove
was
samples
long-neck
smooth
(24)
d i g e s t i o n
m i x t u r e
added
a
of
p o t a t o
Sample
of
i n t o
method
o v e r a l l
a b s o r p t i o n
D i v i s i o n
of
standard
curve
spectrophotometry F i s h e r
S c i e n t i f i c
was
c a l i b r a t e d
(Model Co.. ,
82-800,
Waltham,
MA)
by J a r r e l l using
18.
v a r i n g
d i l u e n t
composed F a i r
of
Lawn,
standard from f o r
0
to
t h i s
t h i s
sodium
10
On i t
of
0
more
From
o b t a i n e d
to
This of
sodium
the
of
sodium
curve. two of
d r i e d
i o n
from
the
p o t a t o and
samples
p r e p a r e d
ure
and
standard
was
ranged
r e q u i r e d Standard d e t e r m i n a t i o n
(20
Along exact
to
the
e q u a t i o n
was
=
0.041x
run
f o r
f r e s h so
of f o r
the
the
w i t h
the
samples,
the
standard
sample
200
glassware
were
c o n c e n t r a t i o n
f i n i t e
each
samples.
and
p o t a t o
and
as
0.004).
the
p e e l i n g s
ppm
reagents
-
c o n c e n t r a t i o n
and
from
range
were
(y
the
a d j u s t e d
the
a p p l i e d
o b t a i n e d
waste,
were
same
o v e r a l l
p o r t i o n
the
l i n e
curve
t i s s u e )
the
f o r
Co., the
curve.
was
s t r a i g h t
readings
analyses
the
l i n e a r
p r e p a r e d
p e e l
s o l i d s ) .
c o n t a i n i n g
the
of
s o l u t i o n
curve.
a
w i t h i n
f o l l o w i n g
p r o f i l e
a n a l y s i s
c o n c e n t r a t i o n s
p o t a t o
the
c a l c u l a t e
p i t h
stock
S c i e n t i f i c
c a l i b r a t i o n
standard to
D u p l i c a t e
was
the
standard
used
would f a l l
t h a t
were
was
These
d i f f e r e n t
ppm
f i n i t e
(parenchyma
a n a l y z e d .
of
commercial
( F i s h e r
f i n i t e
a n a l y s i s ,
C a u s t i c pulp
more
r e g r e s s i o n
t h i s
e q u a t i o n
the
10
f i n i t e
f o r
found
p o r t i o n
L i n e a r data.
A
a
d e t e r m i n i n g
was
ppm.
l i n e a r
of
b i c a r b o n a t e
N . J . ) .
curve,
s o l u t i o n s of
c o n c e n t r a t i o n s
ppm,
i n a
c l e a n i n g samples.
at terms b l a n k p r o c e d -
19.
5.
Ash
A l a i n
c l e a n ,
c r u c i b l e
p r i a t e The
D e t e r m i n a t i o n
amount
sample
weight
6.
w i t h of
was
was
p o t a t o
samples
aluminum
oven.
This
of
t h e r m o p h i l i c
the
the
the
sampling t i f i c
dishes.
was
added a
weight
chosen
w i t h o u t These
i n t o
t h i s and
p o r c e -
an
appro-
then
constant
reweighed. c o o l e d
p r e h e a t e d
These
f e r m e n t a t i o n
were
at
to
d r i e d
80°C
be
i n
p r e -
at
a
atmos-
d r y i n g
r e p r e s e n t a t i v e
temperature.
causing
and
It
p o s s i b l e
d r i e d
samples
pH
the
were
a l l o w e d
heat
a l t e r a -
used
f o r
analyses.
pH
of
of
the
the
c a u s t i c
p r o c e s s i n g
p l a n t
using
meter
Co.,
To
u n t i l
p l a c e d
constant
d r y i n g
Measurement
The from
a
samples.
p r e v i o u s
7.
to
temperature
s u f f i c i e n t of
was
550°C
were
d r y i n g
pressure
t i o n
weighed.
sample at
d e s i c c a t o r - c o o l e d
D e t e r m i n a t i o n
p h e r i c
f o r
was
and
o b t a i n e d .
The
the
cover
i g n i t e d
S o l i d s
weighed
p r e i g n i t e d
a
pH
P i t t s b u r g h ,
were
of
P l a n t
p o t a t o
p e e l
r e c o r d e d
(Accumet. Model
PA).
Samples
samples
w i t h i n 230 ,
2
h
F i s h e r
o b t a i n e d of S c i e n -
20.
II.
C o n s t r u c t i o n
1.
1 J "
s t e e l
an
of
on
t h i s
inner
p l u s
brads
These wine
p l a s t i c
i n
i n s u l a t i n g
This
form,
i n e r t
the
wheels
2.
to
Top
decrease
15
are
were
i n s u l a t i n g
or
Assembly
assembly
water
of
i n s u l a t i o n
since
s e t t l e value
f o r
49
cm
be
m a t e r i a l
the
p l a s t i c
and
10.0 whole
b a t c h
most
(Figure
the
to
diameter
domestic
to
d u r i n g
The
r e s p e c t i v e l y .
w i t h i n
The
found
e v a p o r a t i o n
x
was
Fermenter
was
cm
i t
of
w i t h
accommodate
2).
The
c o n t a i n e r s
C o n s t r u c t i o n ,
m o b i l i t y
f o r
to
56
d u r a b i l i t y
Grace
t o g e t h e r
of
these
c e l l s
f a s t e n e r s .
made
c o n s i d e r e d
i n s t r u c t i o n s .
f a c i l i t a t e
f a s t e n e d
u t i l i z e d
and
R
fermenter
c o n t a i n e r ,
chosen
not
two
was
cm
surrounding
was
C e l l s
c o r r u g a t e d
the
cost
would
package
the
s h e l l
( Z o n o l i t e ,
and
This to
of
m a t e r i a l
The
5
to of
and
m a t e r i a l
ON).
cm
c o n t a i n e r s
terms
of
c o n t a i n e r
bottom
v e r m i c u l i t e
from
7
f e r m e n t a t i o n s
s u i t a b l e
on
and
x
System
Fermenter
plywood,
5/8"
p o l y p r o p y l e n e
side
space.
J "
plywood
a p p r o x i m a t e l y
the
was
outer
the
s h e l l
w i t h and
F e r m e n t a t i o n
of
e x t e r i o r
c o n s t r u c t e d
s i z e
the
C o n s t r u c t i o n
The were
of
Scarborough,
i n
a
f r e e
i n s u l a t i n g
was
determined
u n i t
:
was
l o a d i n g
and
mounted c l e a n i n g .
C e l l s
be
necessary
minimize
i n
s u b s t r a t e
order o v e r f l o w
Figure
2.
Polypropylene fermentation vessel t h e b a f f l e a s s e m b l y (B) i n s e r t e d .
(A)
with
due
to
e x c e s s i v e
to
have
to
the
the
a
heat
i n s u l a t i n g
e f f e c t
of
foam,
which
l i q u i d .
This
of
the
f e r m e n t i n g
c i r c u l a r
CA)
a t t a c k
by
the
to
prevent
bored p o r t
f o r
to
act
the
system
3.
as
System
The 2.5
cm
x
aluminum
3.8
tygon
c o u p l i n g
top
s e a l e d
and
w i t h
assembly. sampling
t u b i n g i n
Inc., wood
a
to
top
diameter) as
p o r t . serve
as
were
hole
e n t r y (6
other
an
water
gasket
the
The
by
edge
rubber
Another
m i n i m i z i n g
body
a i r
l o s s
holes vent from
a e r a t i o n .
f o r
x
The
served
a
w i t h
a l t e r
fermenter
hole
Substrate
i m p e l l e r cm
the
c e n t e r
condenser
d u r i n g
might
The
as
covered
the
which
on
c o n s t r u c t e d
p r o t e c t e d
cm
used
was
Co.
(2.5
was
comparison
F l e c t o
holes
shaft
a
top
Four
i m p e l l e r
w i t h
to
b o l t s . was
c o n s i d e r e d
s u b s t r a t e .
a t t a c h e d
wing-nut
top.
stoppered
c o a t i n g
the
i n
h e a v i l y
b a c t e r i a ,
of
was
accumulated
Varathane,
This
c o n t a i n e r
the
the
and
was
leakage.
diameter)
were
3).
r e t e n t i o n
plywood
( F l e c t o
p r o f i l e
top
p l a s t i c
i n t o
\"
c e l l u l o s i c
spaced
of
of
f i n i s h
n u t r i t i o n a l
evenly
cm
p i e c e
(Figure
The 5
assembly
on
Oakland,
the
top
e f f e c t
p l a s t i c - l i k e
from
The
minimal
top
from a
a
foaming.
2.5 as
was mm
A g i t a t i o n
c o n s t r u c t e d
aluminum
shown
i n
p l a t e
Figure
4.
of
4 on The
p i e c e s a
of
c e n t r a l r e c t a n g u l a r
2 3 .
Figure
3.
Top a s s e m b l y (A) w i t h s a m p l i n g p o r t (B) and vent p o r t s (C), b o l t e d over the fermenter vessel.
24.
Figure
4.
Assembly
of
the
aluminum
impeller.
25.
p l a t e s
were
aluminum
welded
onto
1.6
cm
I.D.
x
t h i c k )
forming
at
r i g h t
to
the
53.5
2.5
angles
bottom
cm
to
of
l o n g ,
cm
each
an
w i t h
the
o t h e r .
aluminum A l l e n
4
The
equal
1.6
(Figure
(3.2
cm
O.D.,
quadrants
c o u p l i n g
s h a f t ,
screws
c o u p l i n g
was
a t t a c h e d
cm
diameter
5)
to
form
x the
a g i t a t o r . Another 2.5
cm
h a l f
x
of
5.2 the
cm
to
the
course
was
p o s i t i o n e d
were
2.5
was
m e c h a n i c a l l y
the
of
p l a c e d
balance
the on
opening
d y n a m i c a l l y
on
mm,
s h a f t . break
attached The
the
purpose
foam
s h a f t
of
the
top
aluminum the
was
so
s h a f t
i n
prevent
the
a
top
top
up
This i t
Both such
p l a t e s ,
t h i s
t h a t
a g i t a t i o n
to
to
b u i l t
6).
assembly.
e n t i r e
r e q u i r e d
of
which
the
aluminum
aluminum
c l o s e
(Figure
balance
i m p e l l e r
d u r i n g i m p e l l e r
was
s l i g h t l y
i m p e l l e r s way
as
to
assembly.
shaft
A
wobble
d u r i n g
o p e r a t i o n . The
dimensions
were
determined
heat
c o n t r i b u t i o n
dimensions
were
p r o v i d e d
w i t h
from
(see
such
the
pages
t h a t
m i n i m a l
During
the
the
of
blades
the
of
a g i t a t i n g
p r e l i m i n a r y
system. s i z e
w i t h
f e r m e n t a t i o n
the
system
i m p e l l e r
be
i m p e l l e r
i m p e l l e r
was
below
x
s i m i l a r
42
the
experiments and
were
43).
g r e a t e s t
f r i c t i o n a l
m e c h a n i c a l
i m p e l l e r on
The
the
f i n a l
a g i t a t i o n
heat
input
d e t e r m i n a t i o n
reduced
a p p r o x i m a t e l y
m e c h a n i c a l i m p e l l e r
would
i n t o
heat
blades
the experiment, 1/8"
Figure
5.
A g i t a t o r assembled w i t h on aluminum s h a f t .
impeller
positioned
I m p e l l e r (A) i n p o s i t i o n , o v e r t h e s p a r g e r ( C ) , w i t h the foam-breaking i m p e l l e r (B) s i t u a t e d t o w a r d s t h e t o p o f the aluminum s h a f t .
28.
at
a
time
(on
a l l
the
m e c h a n i c a l
the
d e s i r e d
o u t s i d e a
second
1
of
input The
each
min
f o r
m a i n t a i n
i n t o
the
l i n e a r
blade
of
the
system
d i s t a n c e the
fermenter
balance) was
#1
reduced
t r a v e l l e d
i m p e l l e r and
u n t i l
was
196.4
to
by
189
the
m
m/min
over
f o r
the
B a f f l e s
(Brown
f i n s and
together
f o r
by
t h i c k n e s s ,
j o i n e d
w i t h
aluminum
snugly
f i t t e d
i n t o the
of
to
v o r t e x i n g
" w h i r l p o o l e d " , c r e a t e d the
a
side
propylene vigorous
was
m i x i n g
the
b l e n d e r "
d e f l e c t e d
of
formed
inner
m i x i n g
c o n t a i n e r . the
p i e c e s 2
5 of
and
cm
x
of
40.5
aluminum
6.
No.
These
cm
18 and
p l a t i n g were
r i v e t s .
were
of
c o n s t r u c t e d
p l a t e s
Figures
fermenter
then
"Waring
see
the
were
aluminum
pop
b a f f l e s
c o n t a i n e r s prevent
b a f f l e
cross-membering
same
The
the
Sharpe)
the
at
to
fermenter.
The
h e l d
heat
of
of
4.
gauge
blades
l e v e l .
edge
p e r i o d
4
The
i n t o
a
of
the
sides c e l l s .
e f f e c t towards r e s u l t
s u b s t r a t e .
were
medium.
be
If
decreased.
i n
which
the was
and
the
c e n t e r a
more
were
p o l y p r o p y l e n e
B a f f l e s
l i q u i d would
hoop
of
r e q u i r e d
the The
s u b s t r a t e b a f f l e s
s u b s t r a t e the
p o l y -
c o n s t a n t ,
29.
5.
The
Power
Power (Canadian speed
of
T r a i n
was
General t h i s
f o r
the
s u p p l i e d
E l e c t r i c
motor
from
Co.,
(1760
r.p.m.)
c r e a t e d
e x c e s s i v e
m e c h a n i c a l
was
d e v i s e d
to
the
3:1
r a t i o
(motor
was
used,
thus
p u l l e y
a p p r o x i m a t e l y
one
the
determined
s h a f t ..was
a g i t a t o r r.p.m.
speed
f o r
the
shaft
same was
motor. to
a c c o m p l i s h
(Figure
and
s h a f t
of
a
our
The
requirements
p u l l e y
p u l l e y the
system
strobe
r a t i o )
of
by
r.p.m.
l i g h t .
584
A
a g i t a t o r
number
was
ON).
i m p e l l e r .
s h a f t
motor
r.p.m.
of
The and
607
shaft
i n
assembly
as
the
a
f i x e d
b l o c k s
t h i s
f i x e d
a l s o
to
or
a g i t a t o r
c o l l a r
the
an
aluminum
s h a f t .
p o s i t i o n
p o s i t i o n
a l l o w
was
d r i v e
j u x t a p o s e d
bearings ( r e q u i r e d
s h a f t
This
to
to
were to
r o t a t e
shaft
the
used
decrease f r e e l y
7). An
length)
#1
A
the
exact
u s i n g
e l e c t r i c
#2.
diameter
p i l l o w
of
r.p.m.
The
fermenter
d r i v e
mounted
Two
wobbling)
f o r
f e r m e n t e r The
of
t h i r d .
h.p.
exceeded
d r i v e
the
J
heat.
speed
to
r e d u c i n g
a
P e t e r b o r o u g h ,
and
reduce
A g i t a t o r
was
aluminum used
(Figures
6
to and
c o u p l i n g
j o i n
the
7).
It
(3.8
cm
diameter
a g i t a t o r
s h a f t
formed
sleeve
a
to
x the
over
4.8
cm
d r i v e each
30.
Figure
7.
Drive (A)
system
between
s h a f t
(C).
assembly the
d r i v e
w i t h s h a f t
the (B)
aluminum and
c o u p l i n g
a g i t a t o r
31.
end o f b o t h s h a f t s and
to reduce
tated
setting
6.
up o r d i s m a n t l i n g
Air
created
was
supplied
reciprocal
a i r action
action
was
utilized
The
bottle
decreased against
compressor.
pulsated
deterred
using
towards
Two
An a i r r e s e r v o i r
polyvinyl
bottle
tubing
(Figure 8).
cotton. acted
with p l a s t i c
attachment.
The
as a
tubing
The b o t t o m
fittings,
h o l e was
The b o t t l e
the a i r flow.
cotton
filter
from the
the p l a s t i c
w h i l e t h e t o p h o l e was
to c o n t r o l
system
and t h e o t h e r n e a r t h e t o p .
to the a i r flow meters.
a regulator
and a l s o
h o l e s were b o r e d i n t o
the bottom
of a i r flow
c a u s e d an e x c e s s i v e
f r o m t h e a i r and o i l d r o p l e t s
from t h e c o m p r e s s o r led
than flowed e v e n l y .
and a l s o
effect
was
The a i r f o r c e d
t h e p r o p e r measurement
a 2 liter
the p u l s a t i o n
h o l e s were f i t t e d for
rather
at the s p a r g e r .
particles
system.
A problem
was p a c k e d w i t h n o n a b s o r b e n t
compressor. one
the a g i t a t i o n
facili-
t o t h e f e r m e n t e r s by an a i r
through the a i r f l o w meters violent
The c o u p l i n g
( W e b s t e r . C o . , London, ON).
by t h i s
impeller
System
from the compressor This
power t o t h e
the wobbling e f f e c t .
Aeration
compressor
to t r a n s f e r
as
bottle, These required
the a i r i n t a k e the o u t l e t
t o p was
which
u s e d as
F i g u r e
8.
A e r a t i o n system w i t h a i r (A), t w i s t c o c k r e g u l a t o r s meters (C).
r e s e r v o i r - r e g u l a t o r (B) and a i r f l o w
33.
7.
Flow
Meters
The Inc., of
Great
a i r
s p e c i f i c
a i r
f l o w
Another f l o w
to
i n t o
each
c a p a c i t y
o b t a i n
meters.
a i r
(Figure
t u b i n g
8)
The
sparger
so
that
r e q u i r e d
i n
readings
was
attached
to
the
the
proper
Gilmont
They
by
as
and
by
chosen
amount
to
used
a
Each
graph
was
of
the
a i r
r e g u l a t o r s ,
as
meet
i n t e r p o l a t i o n .
each
a i r f l o w
going
the
f e r m e n t a t i o n .
Gilmont
were
from
determine were
p r e c e d i n g
a c t i n g
Instruments
" c u t - o f f s "
i n t o
the
v i a
the
the to
stop
fermenter
on
x the
C o n s t r u c t i o n
e n t e r e d the
was
t e f l o n
O.D.
r e q u i r e d
fermenter.
connectors
Sparger
p l a c e d
mm
3,
no.
.
was
7
were
c o m p l e t e l y
A i r
hard
(model
c a l i b r a t e d
Besides
f l o w
8.
or
was
r e g u l a t o r
t w i s t c o c k the
N.Y.)
meter
s u p p l i e d
meters
Neck,
input
the
f l o w
5
of
the
composed
of
an
I.D.,
sparger
i m p e l l e r .
This
bubbles
i n
the
(Figure
6) .
fermenter
bottom
sparger mm
the
head was
head
l o c a t i o n f e r m e n t i n g
fermenter aluminum
(Figure bent
c o u l d
i n t o be
ensured l i q u o r
9). a
c e l l
tube The " J "
s i t u a t e d d i s p e r s i o n by
the
sparger
which
(Figure
w i t h
an
6). aluminum
aluminum
tube,
c o n f i g u r a t i o n under of
the
the
i m p e l l e r
:. a i r
34.
F i g u r e
9.
Sparger a t t a c h e d the
a s s e m b l i e s , to
aluminum
the
w i t h
t e f l o n
sparger
aluminum
sparger
head
(C) .
t u b i n g
head
(B)
(A) and
35.
The aluminum was
bar
d r i l l e d
A l s o
t h i s
tube
which
of (6
bore was
countersunk s t e e l
vent
b a c k f l o w
the used
the
system.
p l a s t i c the
head
was
t h i s
p l a s t i c
9.
to
( t e f l o n )
to
the
to
remained
Tubing
When
r e g u l a t o r s
or
p r o v i d e
sparger
x
6
of
mm
deep)
b e a r i n g
the
d i f f u s e
i n
up
s i m i l a r
used.
(Figure
head
the
a
U n l i k e
s t a i n to
p r e -
sparger
o u t s i d e which
a i r
of was
e n t e r i n g
were
d r i l l e d
d i f f u s i o n . i n
was
E s s e n t i a l l y ,
the
a i r
a i r .
aluminum
p l u g
cap
diameter)
proper
s e v e r a l
a
p l a c e .
mm
head,
a
The
(2
sparger
as
f l o w .
r e c e i v e
the
r e c e i v e
i n t o
break
the
also
a c t e d
or
holes
to
l i q u o r
a i r to
the
the
an
bar
f o r
end
b e a r i n g
s t a b l e
passage
of
the
One
threaded
a f t e r
of
to
p r o v i d e
decompose
c e n t e r
attachment
w i t h
was
c o n s t r u c t e d
f o r
b a l l
b a l l
was
The
f e r m e n t a t i o n
was
head,
P l a s t i c system.
This
Numerous
cap
to
diameter
the
used
aluminum
tended
tapped
of
r e t a i n
cap
i n t o
was
cm
head
diameter.
diameter)
i n t e r f e r e
sparger
the
cm
mm
b a l l .
would
to
1.3
sparger
threaded.
(1
less
which
aluminum
A
c o n s t r u c t i o n aluminum
f e r m e n t a t i o n s ,
hard to
which
the
hard
10).
Connections
t u b i n g
connections a i r f l o w
was
used
were
meters,
throughout
made, e t c . ,
f o r these
the
example,
a e r a t i o n at
connected
the
36.
Figure
10.
Sparger
head
s t a i n l e s s sparger head
head
(C).
assemblies
s t e e l (B)
b a l l s and
c o n s i s t i n g (A),
the
the
of
the
t e f l o n
aluminum
sparger
j o i n t s
were
o f f s "
due
h e l d
to
the
Taken
from A
to
monitor
to
the
the
the
o b t a i n e d
a t t a c h e d Corp., i n
to
through
(°C)
using
a
OH)
The
t i o n s
on
the were
on
of
immersed
n o t c h
i c e
p l a c e d
as
11).
(Omega r e f e r e n c e .
" p r i n t
readings
i n t o
(Figure
( D i g i t e c , a
a t t a c h e d p r o t r u d e d
p o i n t
used
which
used i c e
r e c o r d e r . i n
and
fermenter
was
i n t o
was
U n i t e d
o u t "
(Figure
was These
12).
temperature
readings
Thermocouples
e l e c t r o n i c
D i g i t e c
the
u t i l i z e d
t a b l e .
thermocouples
r e s p e c t i v e
a
r e c o r d e r
(m.v.)
c o n v e r s i o n
t h e i r
CT)
t r a n s l a t e d
C a l i b r a t i o n
p l a t e s
thermocouple
data
Dayton,
were
It
system.
l e d
a
"Measurements
the
It
Stamford,
on
was
of
" b l o w
compressor.
thermocouple
aluminum
top
prevent
T r i a l s " )
the
the
to
the
s e c t i o n
of
m i l l i v o l t
readings
couples
on
of
tape by
F e r m e n t a t i o n
one
Inc.,
m.v.
11.
a l s o
temperature on
and
e x e r t e d
(see
e l e c t r o n i c
E n g i n e e r i n g ,
Systems
the
gasket An
was
pressure
f e r m e n t e r .
rubber
This
wires
c o p p e r - c o n s t a n t a n
b a f f l e
the
w i t h
M o n i t o r i n g
10.
i n t o
on
an
i c e
were
c a l i b r a t e d
p o i n t s The bath
and
ends
of
along
w i t h
channel the w i t h
p o s i -
thermoa
38.
Figure
11.
T h e r m o c o u p l e s (A) p o s i t i o n e d menter v e s s e l .
within
the
fer-
39.
Figure
12.
Data r e c o r d e r used to monitor the fermentat i o n temperatures a l o n g w i t h the e l e c t r o n i c thermocouple i c e p o i n t (A).
40.
thermometer.
A g i t a t i o n
"hot
The
thermometer
the
m.v.
s p o t s " .
aneously v o l t
w i t h
readings
t a b l e
and
a p p l i e d
both
to
compared
were
temperature
e n t i r e
room
t h i s
b u i l d
To
a a i r
c o n t r o l
was
used.
room
but
had
This the
of
heat not
the
d r i v e
conducted
to
a i r
also fan
the
Heat
s i m u l t The
m i l l i -
c o n v e r s i o n was
were
g r a d u a l l y
r e c o r d e d
a p p r o x i m a t e l y
assembly
was
(Figure
heat the a
decreased
and 80°C.
the
fan
d i r e c t e d the
by
heat
fermenter.
of
r e s u l t the
and
at on
the
of
fermenter.
h u m i d i f i e r
water the
t h i s
motors
the
temperature the
w i t h i n
However,
The
o p e r a t i o n l a r g e
l o c a t e d
13).
caused
decreased
was
d i s s i p a t e
i n t o
the
c i r c u l a t i o n .
i n c r e a s e ,
The
r e c o r d e d
u s i n g
reached
prevent
D i g i t e c .
readings
room
d u r i n g
only
the
to
System
ambient
h u m i d i f i e r
system
the
fermenter
poor
up
f e r m e n t a t i o n .
was
the
compressor t h i s
and
i n c u b a t o r
the
i t
of
°C
both
was
compared.
the
i n s u l a t e d
the
were
from
to
u n t i l
p a r t i c u l a r
and
c o n v e r t e d
bath
L o c a t i o n
was
readings
r e s u l t s
to
r e a d i n g
i c e
The w e l l
p r o v i d e d
the
12.
a
was
i n l o s s
motor system
the from and before
41.
Figure
13.
Fermenters
assembled
within
t h e i n s u l a t e d room.
42.
III.
Measurements
These the
system
t e r i a
would
a n i c a l the
by
heat
50°C
e r a t u r e
1.
of
b l e a c h
was
f l o r a ,
e . g . ,
a f f e c t
the
since the
i t
e n t i r e
i n p u t
the
fermenter
i n t o
which
used
was
2. a i r
a i r
of
stop
or
900
41.4°C.
below
a c c o r d i n g l y
M e c h a n i c a l
to
t h e r m o p h i l i c The
kept
be
i n t o
the
t o t a l
w e l l
bacmech-
below
s t a r t i n g
temp-
growth.
water
e t c .
a
growth
i n
and
the
was
was
The
Input
the
of
The
which
u n t i l temp-
a c c e p t a b l e made
to
t e m p e r a t u r e .
D e t e r m i n a t i o n
i n
the
Absence
sparging
was
c o o l i n g
c o n s i d e r e d
caused to
be
an
by
heat
removal
important
may
assembled
maximum
were
s m a l l
b i o l o g i c a l
was
c o n s i d e r e d
above
a
c e l l .
o p e r a t e d
Adjustments
o b t a i n
w i t h
water
system
p l a t e a u .
This
along
f e r m e n t e r
e n t i r e
50°C.
Heat
to
the
ml/min) to
was
the
impede
The
i n c r e a s e d was
tap
i n t o
b a c t e r i a ,
the
i n p u t
D e t e r m i n a t i o n
c o l d
p l a c e d
f l o w ,
w e l l
Medium a e r a t i o n
to
a l g a e ,
reached
system
was
Input
heat
p r o j e c t .
b a c t e r i a l
Heat
l i t r e s
from
c o n s i d e r e d
d e t e r m i n a t i o n .
was
s i n c e
the
temperature
e r a t u r e
r e q u i r e d
i n v a l i d a t e
b l e a c h
set
C o n s t r u c t e d
than
M e c h a n i c a l
a
were
t h e r m o p h i l i c
amount
the
t e s t s
System
other
F i f t y
(with
the
sources
mark f o r
of
through
h e a t - l o s s
43.
f a c t o r .
In
d e s c r i b e d absence
value c a l
was
of
o p e r a t e d
t h i s
the
heat
a i r a
input
r a t e
s e c t i o n
of
on i n
4.
r o t a t i o n
the
value
the
was
w i t h
p r e v i o u s l y
a g i t a t o r The
i n
the
system
was
r e a c h e d .
o b t a i n e d
i n
was
c r e a t e d
from
T h i s
the
mechani-
a e r a t i o n .
(speed
was
of
f o r
Substrate
fermenter
decreased
the
"System
by:
i m p e l l e r ) ;
( i . e . ,
r.p.m.
A g i t a t i o n " )
d e c r e a s i n g
l i n e a r
d i s -
x
(see
iTd) ;
and
the
i n s u -
c e l l .
Heat
D e t e r m i n a t i o n
i n
the
Presence
S o l i d s
the
i t
c o u l d
above
be
a
was
medium
used.
It
by
i m p e l l e r
the
Sodium
s u b s t r a t e
argued
d e t e r m i n a t i o n
f e r m e n t a t i o n ,
medium.
p o t a t o
heat
i m p e l l e r
the
a c t u a l
p o t a t o
the
the
Potato
u t i l i z e d
be
of
system
measured.
by
Since
s o l i d s
water
temperature
m e c h a n i c a l
M e c h a n i c a l
of
an
maximum
was
d e t e r m i n a t i o n
t r a v e l l e d
l a t i o n
tap
o p e r a t i o n
s p a r g i n g
to
a
Adjustments
The
tance
The
compared
3.
the
used.
u n t i l
was
e v a l u a t i o n ,
to
thought
water
was
not
i n d i c a t i v e
t h a t i n
h y p o c h l o r i t e the
the
c o n t a i n i n g
working
d e t e r
that
12.3
a d d i t i o n a l the
g
%
of
p o t a t o
heat
would
" p u r e e - l i k e "
s o l u t i o n
growth
system
of
was the
added
to
microorganisms
44.
during
t h i s
t e s t .
No
This
d e t e r m i n a t i o n
ture
was
i n
rounding was
Lost
from
the
The
heat
l o s t
from
order
to
poured
not
c o n t i n u e d
Heat
e v a l u a t e
i n s u l a t i o n .
t o g e t h e r was
was
was
a p p l i e d
u n t i l
a
to
the
maximum
system. tempera-
o b t a i n e d .
5.
mined
a e r a t i o n
i n t o
w i t h
the
four
was
the
the
F i f t y
exhaust The
recorded
c e l l
e f f e c t i v e n e s s of
and
temperature as
of
heated
the
t u b i n g s .
h o u r l y
C e l l
fermenter
l i t e r s
fermenter
a c t i v a t e d .
fermenter
Fermenter
the
s u r -
was
79.5°C,
top
a e r a t i o n
decrease
heat
d e t e r -
w a t e r ,
fermenter The
was
i n s t a l l e d system
w i t h i n
l o s t
from
the the
system.
6.
Heat
Loss
Surface
As
a
i n s u l a t i n g
was
determined.
t a t e
a
the
(69.6°C)
heavy normal was
i n
the
Presence
of
Foam
the
medium
D e t e r m i n a t i o n
comparison e f f e c t
of
During l a y e r
of
to a
foam
p r e v i o u s l a y e r
a g i t a t i o n foam
f e r m e n t a t i o n
used
the
c o n t a i n i n g
is
of
the
formed.
system, a
on
a
d e t e r m i n a t i o n , heat
r e t e n t i o n
aqueous In
hot
foam-forming
order water
p o t a t o to
i m i -
medium
commercial
45.
dishwashing on
to
the to
d e t e r g e n t .
c r e a t e
the
system
was
m a i n t a i n
a
IV.
The
heavy
c o n s t a n t
of
the
of
the
i n
22.7
f e r m e n t a t i o n p o t a t o e s p o t a t o a
was
preweighed
t a n t
weight
s p e c i f i c
t i o n .
These
water
w i t h i n
w i t h
a
Hobart
Mfg.
Co.,
A
and
random from
a
d i s h
the of
OH)
d e t e r m i n a t i o n , the
d e t e r g e n t
w i t h
of
each
%
of
s o l i d s
p r i o r 5-6
the
the
supermarket
t o t a l
box
box.
at
to
the
medium
s i z e
Each
macerate
o v e n - d r i e d
s o l i d s
was
of
weighed
macerated
and
M a c e r a t i o n
( K i t c h e n a
g
sampling
t o t a l
were
m i l l
The
l o c a l
p l a c e d
80°C
to
a
i n t o cons-
p r e s s u r e .
f e r m e n t e r .
food
Troy,
%
a
throughout
and
p o t a t o
p o t a t o e s the
g
from
f o r
p o r t i o n
atmospheric
amount
w i t h
turned
Fermentations
boxes.
determined
d r y i n g at
the
was
l e v e l .
o b t a i n e d lb)
o b t a i n e d
Knowing a
(50
was
ground
Throughout
r e p l e n i s h e d
foam
were
t r i a l s .
were
a e r a t i o n
S u b s t r a t e
kg
p o t a t o e s
and
T h e r m o p h i l i c
P o t a t o
Potatoes u s u a l l y
foam.
c o n t i n u a l l y
A n a l y s e s
1.
A g i t a t i o n
no.
3
A i d ,
the
f o r
the
mixed was
Model
s l i c i n g
p o t a t o e s , f e r m e n t a w i t h
tap
accomplished K5-A,
Hobart
attachment.
The
p o t a t o
s l i c e s
u n t i l of
s m a l l
the
were
p i e c e s
fermenter
2.
to
f o r
emptied Each
each
and of
the
washed.
w i t h
a p p r o x i m a t e l y area
shelves) The
The
and
of
c h l o r i t e
3.
w i t h
other
0.5%
v i o u s l y the
and
i t s
tap
water
f i n a l
working
volume
Fermenter
t r i a l s
V e s s e l
was
and
50
1.
A c c e s s o r i e s
t r i a l ,
washed
w i t h
the
fermenters
commercial
d e t e r -
were
d i s m a n t l e d
system
then
soaked
was
a f f e c t e d room
before
Taken
areas
were
components
s o l u t i o n . ( i . e . ,
washed
were
or
washed
The
whole
w a l l s
and
w i t h
r i n s e d
and
h y p o c h l o r i t e .
f r e e
of
hypo-
use.
from
the
F e r m e n t a t i o n
T r i a l s
Temperatures
a
d e s c r i b e d .
fermenter.
times
components
i n c u b a t o r
through
ambient
s e v e r a l
f e r m e n t a t i o n
h y p o c h l o r i t e
o t h e r
Temperature o b t a i n e d
s l i c e r
The
f e r m e n t a t i o n
Measurements
i)
the
e n t i r e
the
the
fermenter.
the
thoroughly
also
f l o o r
the
o b t a i n e d .
a l l
of
through
O p e r a t i o n
A f t e r
gent.
were
S a n i t a t i o n
P r i o r
were
passed
room
readings
f o r
the
f e r m e n t a t i o n
t h e r m o c o u p l e - r e c o r d e r A
second
temperature
thermocouple of
the
area
system was
as
used
surrounding
were p r e to
r e c o r d the
47.
i i )
D i s s o l v e d
Samples mately
12
r e c o r d e d ing
was
i n t o YSI
using
the
a
pH
taken
57
by
c a l i b r a t e d
to
b r a t i o n s
were
from
f e r m e n t a t i o n
bath was
This
at
21°C
r e q u i r e d
was
to
through oxygen
a
maximum
the
water
and
of
72°C
b a t h .
T o t a l T o t a l
f e r m e n t a t i o n ,
fermenter. p r i o r
to
This
a
the
of
f i r s t ,
a i r
then
probe
Oxygen
Y e l l o w
S p r i n g s ,
F u r t h e r
This
a c c o r d i n g l y
(Figure
12
(250
was
a n a l y s i s .
the
water
i n
i n c r e -
d i s s o l v e d 14).
Fermenter
N i t r o g e n
every
sample
d u r i n g
a
b u b b l i n g
r e c o r d e d
the
the
r e a d i n g
i n c r e a s e d
i n
of
i n t o
and
K j e l d a h l
c a l i -
s a t u r a t i o n a i r
OH)
expected
c o n t i n u o u s l y
Remaining
r e a d -
5739
temperature
S o l i d s
.
The
reached.
was
was
f e r m e n t e r .
b u b b l i n g
was
a p p r o x i -
d i r e c t l y
temperatures
oxygen
at
(D.O.)
probe
s u p p l i e r . the
w i t h
oxygen
Both
sample
subsequent
t h a t
a c t i v i t y
D.O.
Inc.,
the
match
by,
A p p r o x i m a t e l y the
by
fermenter
ion
model
Co.,
temperature
were
i i i )
YSI
s a t u r a t i o n
The
readings
to
the
w i t h i n
and
to
done
u n t i l
r e c o r d e d .
ments
l i q u o r
45°C
the
d i s s o l v e d
immersing
meter
pH
from
A
Instruments up
and
hydrogen
meter.
Oxygen
S p r i n g s
medium.
The
f e r m e n t a t i o n
model
the
removed
i n t e r v a l s .
also
(Yellow was
h
were
Oxygen
h ml)
f r o z e n Per
was and cent
course
removed s t o r e d t o t a l
at
from
of the
-20°C
s o l i d s
was
•—• -
Instrument
O—O -
Calibrated
o.
Ol
0
• -o-
i
1
'
1
10
20
30
40
-o
50
60
70
Temperature , °C
Figure 14. Dissolved oxygen probe calibration curve for air saturated water at high temperatures.
49.
determined c o n s t a n t
of
d r y i n g
the
sample
i n
an
d r i e d
sample
was
oven
at
80°C
to
a
w e i g h t .
Concon
K j e l d a h l
V.
by
The
same
and
S o l t e s s
n i t r o g e n
" T r u e "
P r o t e i n
(16)
w i t h
p r i o r
the
d i g e s t e d
to
the
Technicon
N i t r o g e n
U s i n g
u s i n g
the
measurement
Auto
of
method t o t a l
A n a l y z e r .
T r i c h l o r o a c e t i c
A c i d
(TCA)..
P r e c i p i t a t i o n
Samples were
ground
sample,
a
p i t a t e
5
ml
added
to
a l i q u o t
was
CT)
was
fermented
i n d i v i d u a l l y
p r e p a r a t i o n Norwalk,
of
at
mixed 7900
d i s c a r d e d
ensure
of
x
and
min
and
supernatant
The
d i f f e r e n c e to
w a r i n g
10%
then f o r a
between r e p r e s e n t
i n
TCA
was
1
The ml
p o t a t o e s To
at
7900
(Ivan
10%
f o r
g
f o r
TCA
p r o t e i n "
t o t a l
of The.
. p r e c i s o l u t i o n
The another
n o n - p r o t e i n
and
ml
S o r v a l l ,
r e s u l t i n g
of
x
5
added.
p r e c i p i t a t i o n .
v a l u e
"True
b l e n d e r .
min.
a n a l y z e d t h i s
f r e s h
c e n t r i f u g e d
f u r t h e r
r e - c e n t r i f u g e d
and
(W/.V)
30
completeness
was
c o n s i d e r e d
g
a
a
and
p r e p a r a t i o n the
i n
p o t a t o
n i t r o g e n .
n i t r o g e n
n i t r o g e n .
30
was
50.
VI.
Amino
A c i d
A n a l y s i s
Analyses p r i o r
to
Sample The
the
t i o n ,
and
s i z e
were
was
b o i l e d
out
i n
two
and
c y s t e i n e
was
done
a c i d
stages. r e s i d u e
These
authors
l i z e
the
mixture g l a s s
a c i d
the
p o t a t o
the
samples
fermented
using
p o i n t
a
of
removed
r e s i d u e .
Waring
b l e n d e r .
s t a r c h
g e l a t i n i z a - -
t h a t
r e s i d u e s of
was
then
f i l t e r
of
Cavins
et
c y s t i n e
a l .
h y d r o l y s i s
the
a c i d
a l k y l a t e d
r e q u i r e d
samples
Liu and
Chang
through
an
(34)
.
(12). to
s t a b i -
c o n d i t i o n s . f o l l o w e d .
p - t o l u e n e - s u l f o n i c
a c i d
This
u l t r a - f i n e
as
d i g e s t e d s i n t e r e d
A). samples
a n a l y z e r
(Phoenix
P r e c i s i o n
u t i l i z i n g
Chemical
c a r r i e d
the
under
f i l t e r e d
(Durrum
of
was
The
PA)
was
a l k y l a t i o n
f i l t e r e d
(Appendix
samples
a l k y l a t i o n
method
u s i n g
the, method o f
the
5 - g - ( 4 - p y r i d y l e t h y l ) - L - c y s t e i n e
the
accomplished by
of
s e l e c t i v e
to
found
above
P h i l a d e l p h i a , tem
to
i n t o
H y d r o l y s i s
suggested
on
reduced
a n a l y s i s A
a c c o r d i n g
was
and
on
l y o p h i l i z e d . Amino
This
performed
f e r m e n t a t i o n
p a r t i c l e
samples
were
a
were
Instruments
s i n g l e
C o r p o r a t i o n ,
a n a l y z e d
column
Palo
A l t o ,
on
an
amino
Co., e l u t i o n CA).
sys-
51.
VII.
Microbial Identification
1.
Preparation i)
of I s o l a t i o n Media f o r N - F i x i n g
Yeast Carbon Base
Bacteria
(YCB) Medium
This n i t r o g e n d e f i c i e n t media (Difco L a b o r a t o r i e s , D e t r o i t , MI) c o n t a i n s
low amounts of n i t r o g e n
of e s s e n t i a l n u t r i e n t s and vitamins growth.
The medium was f i l t e r
HA, 0.45 ym M i l l i p o r e membrane Corp., Bedofrd, MA), mixed with poured i n t o s t e r i l e p e t r i ii)
Nitrogen
i n the form
required f o r microbial
sterilized filter
through a Type
(Millipore
sterile
Filter
agar at 45°C and
dishes.
F i x a t i o n Medium f o r Non-Symbiotic
S o i l Microorganisms This mineral medium was adapted from "A P r a c t i c a l Manual o f S o i l M i c r o b i o l o g y
Laboratory
Methods" (56) and
i s used f o r the i s o l a t i o n o f Azotobacter
species.
A hard
agar i s r e q u i r e d f o r i n c u b a t i o n of the c u l t u r e s at 55°C; m o d i f i c a t i o n o f t h i s medium c o n s i s t e d o f u s i n g 2.5% agar. min,
The media was autoclaved
at 15 p s i (121°C) f o r 15
cooled to 45°C and poured i n 100 mm x 15 mm
plastic petri
dishes.
(W/V)
sterile
52 .
i i i )
N i t r o g e n - E i x i n g
and
B e i j e r i n c k i a
T h i s (38). 2.SI
It
is
agar
c l a v e d
composed
was
used
s e p a r a t e l y
t i o n s
were
added
to
p e t r i
c o o l e d
A,
two
15
to
50°C,
mixed,
was
and
adapted
s o l u t i o n s ,
s o l u t i o n
at
p s i
Genera
A z o t o b a c t e r
S o i l
medium
of i n
i n
f o r
A.
Both
(1,21 ° C ) and
poured
A
10 i n t o
15
of
100
and
M e i k l e j o h n
B,
i n
s o l u t i o n s
f o r
ml
from
were
min.
The
s o l u t i o n mm
x
15
which
B
a u t o s o l u -
were
mm
s t e r i l e
d i s h e s .
2.
from
m i n e r a l
Medium
the
I s o l a t i o n
of
the
A l i q u o t s
of
the
fermenter
temperatures. p l a t e d
media
d e h y d r a t i o n . D u r i n g
t h i s
i n c u b a t e d
p e r i o d ,
r e - i n o c u l a t e d
was
repeated
was
dependent
not
by
the
samples
Incubation
and
6
on
the
c a r r y - o v e r
new to
to
were at
media.
the
i n
a
were
the onto
from
the
24-48
h.
were
i s o l a t i o n
pure
c u l t u r e
fermenter
d i f f e r e n t to
This
by
3
bags
c o l o n i e s
s u p p l i e d
o b t a i n e d
t h e r m o p h i l i c
p l a s t i c
ranged
d i s t i n c t
n u t r i e n t s of
r e a c h i n g
55°C
ensure
l i q u o r
s t r e a k e d
p e r i o d s
v i s u a l l y
times on
f e r m e n t a t i o n
subsequent
The and
Microorganism
the
l i q u o r .
prevent
i s o l a t e d
procedure
whose media
growth and
53.
3.
V i s u a l
Appearance
I s o l a t e d media
were
grown
and
Co.,
the
c o l o n i e s
Appendix
4.
m i c r o b i a l
on
were
Gram
Gram of
24
h
Soy
and
c e l l s
5.
48
under
A f t e r
and
the
Agar
h
and
Bonner
3
d i f f e r e n t
(Becton,
24
morphology
M i t r u k a
h
the
to
or
when
of
D i c k i n s o n
growth,
c u l t u r a l
(39).
c h a r -
See
w i t h
s o l u t i o n
media The
were
removed
c u l t u r e s
v i s i b l e
growth
(groupings),
were
and
grown
Gram
o c c u r r e d . and
s t a i n e d The
morphology
n o t e d .
( W i r t z - C o n k l i n )
f i v e - d a y i n
a
microscopy.
was
3
(TSA).
S t a i n i n g
sporangia 5%
Agar
suspended
phase
a
from
were
Spore
were
to
f o r
from
Soy
p l a t e s .
a g g l o m e r a t i o n
Three 55°C
c o l o n i e s
C o l o n i e s
R e a c t i o n
r e a c t i o n ,
the
M i c r o b i a l
B.
T r y p t i c a s e
a f t e r
MD)
a c c o r d i n g
the
T r y p t i c a s e
examined
C o l o n i e s on
BBL
C o c k e y s v i l l e ,
a c t e r i s t i c s
of
n o t e d . of
o l d
c u l t u r e s
s t e r i l e The
Spores
water
l o c a t i o n were
m a l a c h i t e
grown
d r o p l e t and
and
by
TSA
and
n a t u r e
c o n f i r m e d
green
on
of
at
observed the
s t a i n i n g
c o u n t e r s t a i n e d
54.
w i t h
s a f r a n i n .
against (33)
red
The
spores
cytoplasm
under
observed
o i l
to
immersion
s t a i n
green
microscopy
.
6.
L i p i d
S t a i n i n g
Three-day s t a i n e d f i x e d
f o r
and
c l e a r e d .
the
Co., They
mately
3
the
sec f a t
7.
phase
observed
w i t h
F a i r
a
of
grown
l i p i d
Sudan
Lawn,
B l a c k
N.J.)
TSA
B
f o r
s o l u t i o n
10
w i t h
min
Appendix
r i n s e d .
The
c e l l s
b l u e - b l a c k
i n
55°C
were
were
heat
( F i s h e r
and
x y l o l
Z i e h l - N e e l s e n ' s
see
were
at
S l i d e s
d i l u t i o n ,
then
g l o b u l e s
on
b o d i e s .
c o u n t e r s t a i n e d
(1:10
and
colony
was
microscopy
f o r A
movement 0.2%
c e l l
m o t i l i t y .
i n t o
the
agar
TSA Using
and
suspended w i t h i n
g e l
v i s u a l l y
the
a g a r , ( 1 5 ) .
by
o i l
excess i n
t h i s
i n c u b a t e d
i n d i c a t e d s o f t
c o l o n i e s
Method)
C)
were
f o r
a p p r o x i -
s t a i n e d
c o l o u r
r e d
(48).
M o t i l i t y
A Under
o l d
were
C a r b o l - F u c h s i n
(Burdon's
presence
f l o o d e d
S c i e n t i f i c
and
were
i n
of
method,
d i f f u s i o n
s t e r i l e
immersion,
tubes
at
a
a l s o
d r o p l e t .
c e l l s
were
movement. used
c u l t u r e s
55°C. of
the
Brownian was
water
were
P o s i t i v e
m i c r o b i a l
to
observe stabbed
r e s u l t s
c e l l s
were
through
8.
Catalase
R e a c t i o n
Colonies grown
on
TSA
o b t a i n e d ,
a
c o l o n i e s a
.
p o s i t i v e
hydrogen
An
immediate
r e a c t i o n
was
observed
of
the
As d e t e r m i n a t i o n organism r o b i c A of
1%
j a r s
a
were
methylene
anaerobic
anaerobic
was
was
at
55°C.
of
prepared
v i s u a l l y .
c u l t u r e
on
of
added
to
were was the
i n d i c a t e d
.to
the.
above
e s t a b l i s h
f a c u l t a t i v e
or
o b l i g a t i v e
blue
w i t h
a
BBL
s o l u t i o n was
the
TSA
plates
Gas
Pak
the
tubes
of
TSA.
l o c a t i o n top
of
of
growth
the
along
the
anaerobism.
Test
to
used
the
whereas
degrees
Anaerobic
u s i n g
r e q u i r e d
before
was
media growth
bubbles
d,
2
Growth
i n d i c a t e d
conditions.
jars
were
c o n f i r m a t i o n was
s u f f i c i e n t
s o l u t i o n
f o r m a t i o n
a e r o b i c
stab
a
peroxide
approximately
O b l i g a t i v e
10.
A f t e r
c u l t u r e
Test
f o r
an
d i f f e r e n t
3
(33).
c u l t u r e s
i n d i c a t e d
length
55°C.
3%
i n c u b a t i o n
agar
at
s l a n t s
Stab
growth
the
Anaerobic
9.
A f t e r
from
Gas
Pak
included were
in
t e s t ,
a
whether
f u r t h e r the
anaerobe. and the
Anae-
c a t a l y s t jar
as
an
system. indicator
i n o c u l a t e d and p l a c e d
envelopes
were
activated.
into
Incubation
56.
11.
Voges-Proskauer
The
Test
(V-P)
Voges-Proskauer
t e s t
i s
the
presence
of
a c e t y l m e t h y l c a r b i n o l
is
o x i d i s e d
by
the
red
c o l o u r
F i v e
w i t h
m i l l i l i t e r s
p l a c e d
i n t o
(121°C)
f o r
15
from
3
l a t e d
end
t e s t e d the
c u l t u r e s
these
f o r
by
c u l t u r e
time
along
Organic
a f t e r
30
to
sence
of
a c e t o i n .
12.
pH
The also
the
7
i n i t i a l
pH
measured
of
Gordon
and
of
p e r i o d s , 3
w i t h
min
i n
d
the
which
peptone et
A c e t o i n
produces medium
a]
(22)
a u t o c l a v e d
ml
of
at
a
at
15
room
o l d of to
serve
V-P as
3,
a
(15). were p s i
were
i n o c u -
7
At
and
presence
40%
(W/V)
of
NaOH
0.75.mg
i s o l a t e d
d.
a c e t o i n s o l u t i o n
of
N.Y.).
90%
was to
c r e a t i n e
A
red
c o l o u r
i n d i c a t e s
the
p r e -
B r o t h
were
were b r o t h a
5
the
temperature
c u l t u r e s the
f o r
Rochester,
c u l t u r e s
c o l o n i e s
c u l t u r e s
a p p r o x i m a t e l y
Voges-Proskauer
the
from
the
i n c u b a t e d
Chemicals,
Before of
of
p r e p a r e d
Each
and
adding
60
were
media.
t r i p l i c a t e of
capped
determine
( a c e t o i n ) .
d i a c e t y l
media
to
min.
(Eastman
pH
V-P
tubes,
d i f f e r e n t i n
to
c o n s t i t u e n t of
t e s t
The
the
a
reagent
used
t e s t e d
measured a f t e r
c o n t r o l
f o r by
a c e t o i n ,
u s i n g
a
s t e r i l i z a t i o n comparison.
pH was
the meter.
57.
13.
M e t h y l
Red
Test
V o g e s - P r o s k a u e r r e d
a c i d i t y
l i t e r s f o r
6
of
each
tube
and
the
tube 0.1
200 a
the
days.
from
of
t e s t
ml
V-P At
the
drops
was
shaken. of
14.
t e s t
T r i p l i c a t e soy
b r o t h
water ing a
were
baths
growth
at
t h r e e - d a y
temperature
tubes
at
each
75°C.
of At
at
temperatures
p e r i o d . (21°C)
these
red a
to
30°C of
the
f o l l o w i n g higher
i n c u b a t e d 5
added
and
composed
(951)
c o l o r a t i o n
ml
empty
was
e t h a n o l
n e g a t i v e
plus
i n d i c a t e s
t e s t .
D e t e r m i n a t i o n
of
c u l t u r e s
i n
a
constant
temperature
above
C u l t u r e s
i n v o l v e d the
ml
were
s o l u t i o n
m i l l i -
were
separate
temperatures.
D e t e r m i n a t i o n temperature
300
a
s o l u t i o n
red
Range
v a r y i n g
i n t o
red
A
i n c u b a t e d
at
i n t e r v a l ,
time
m e t h y l
Ten
t h i s
y e l l o w
Temperature
t e s t ) .
of
i n
water.
the
tubes
methyl
red
f o r
d u p l i c a t e
methyl
and
used
i n
p i p e t t e d
The
methyl
d i s t i l l e d
p o s i t i v e
end
of
was
V o g e s - P r o s k a u e r
b r o t h
c u l t u r e 5
g
(see
media
C u l t u r e
55°C
were
i n c u b a t i n g
were the
growth
t r y p t i c a s e
c u l t u r e s of
the
temperatures:
temperatures,
an
tubes
show-
r e c o r d e d
a f t e r
between
i n c u b a t e d
up
to
room 2
maximum
65,
weeks.
growth
d i f f e r e n t 60,
i n
70
e t h y l e n e
c u l t u r e s and g l y c o l
58.
base the
(Gulf
O i l ,
constant
t i o n .
temperature
range
of
the
c u l t u r e s
55,
room
of
i n
lysozyme
lysozyme
g
CA)
in
a p p r o x i m a t e l y
100
ml
v o l u m e t r i c f o r
20
room
(B
s t e r i l e
1
was
was
plugged
t e s t
tubes
i n
Growth
was
of
40,
35,
in
evaporai n v o l v e d
30,
25°C
c o t t o n
From
t h i s
w i t h i n
was
99
2.5
Also
and
14
HC1
was
up
to
lysozyme ml
of
tubes as
to 100
0.001%
c o n t r o l
c o o l ml
s o l u t i o n , n u t r i e n t
i n t o
c u l t u r e s
of
a
plugged
s t e r i l e
a l i q u o t s
w i t h
i n
c a r e f u l l y
a l l o w e d
made
ml
d.
N
f l a s k
and
adding
Angeles,
was
the
by
Los
0.01
m i x t u r e
i n o c u l a t e d 7
p r e p a r e d
s t e r i l e
i n o c u l a t e d
were at
was
volume
mixed
b r o t h .
r e c o r d e d
45,
b o i l i n g ,
The
and
b r o t h
decrease
Calbiochem,
This
dispensed
n u t r i e n t
n u t r i e n t
ml
HC1.
and
This
and
60
A f t e r
0.01:N
b r o t h .
grown
50,
non-absorbant
removed
used
d e t e r m i n a t i o n s
s o l u t i o n
grade,
temperature.
w i t h
to
was
(21°C).
f l a s k .
min.
s t e r i l i z e d
ON)
Lysozyme
0.1
b o i l e d
at
temperature
Growth
The
ml
bath
temperature
15.
to
water
low
at
w i t h
Toronto,
The
growth and
C a n a d a . L t d . ,
s t e r i l e
p r e v i o u s l y lysozyme comparisons.
59. 16.
Growth
Tubes w i t h f o r an 7
c o l o n i e s 48
h.
and
to
10%
s e a l
The
of
caps
N a C l - b r o t h
Azide
by
the
the
i n
t e s t
were
tubes
The
growth
pH
Co.,
( i n i t i a l
on
Sodium
tubes
tubes at
and
then
i n c u b a t e d
served
c o n t a i n i n g P a r a f i l m
to
55°C
i n o c u l a t e d
0,
was
decrease f o r
7
as 5, used
e v a p o r a t i o n .
and
14
d.
A z i d e
b r o t h
tubes
PA)
7
14
(Fisher was
Gram-Pac,
prepared
F i s h e r
as
d i r e c t e d
b r o t h .
The
p a r a f i l m
i n c u b a t e d
w i t h
c u l t u r e s
at
to
caps
of
the
prevent
55°C
and
dehyobserved
d.
t r y p t i c a s e
7.3)
i n o c u l a t e d
Test
C o c k e y s v i l l e , pH
w i t h
were
and
Range
were
n u t r i e n t
wrapped
tubes
at
BBL and
media
c h l o r i d e .
t e s t
were
manufacturer.
grown
18.
b r o t h
P i t t s b u r g ,
p r e v i o u s l y
for
b r o t h
c u l t u r e s
i n c u b a t e d
D u p l i c a t e
d r a t i o n .
b r o t h
dextrose
Co.,
n u t r i e n t
i s o l a t i o n
sodium
of
was
Growth
S c i e n t i f i c
3
n u t r i e n t
(w/v)
17.
the
n u t r i e n t
f o r
the
NaCl
c o n t a i n i n g
from
The
inoculum
i n
w i t h
soy
MD) IN
b r o t h
was
HCl
or
(Becton,
p r e p a r e d IN
NaOH
and to
D i c k i n s o n the y i e l d
pH a
a d j u s t e d s e r i e s
60 .
of A
media 10
ml
l i z e d
w i t h
p o r t i o n
through
( M i l l i p o r e tubes. a 3
a
F i l t e r
w i t h
used
f o r
were
of
tubes
each
of
observed
ym
the
over
u n i t
was
filter
M i l l i p o r e MA)
increments. s t e r i -
membrane
i n t o
s t e r i l e
and
system t e s t
i n o c u l a t e d
in
n u t r i e n t
b r o t h
from
caps
of
the
tubes
were
tubes
w i t h pH
a
1
grown
the
tubes
i n
p r e p a r e d
The and
11
media
B e d f o r d ,
p r e v i o u s l y
media
to
these
were
media.
3
0.45
Corp.,
7
t e s t
were
i n c u b a t e d
and
w i t h o u t
ranges
t e s t e d .
d
p e r i o d
f o r
at
inoculum The
the
c u l t u r e
presence
growth. F o l l o w i n g
the
v a r i o u s
f i n i t e these
growth
media a
w i t h 0.04%
Organic medium
of
0.1
d e t e r m i n a t i o n
showed pH
2.5%
(w/v)
(w/v)
s t e r i l i z e d
from
Ayers, agar
s o l u t i o n
Chemicals,
the
pH
i n h i b i t i o n , were
used
at a
to
15
Carbohydrate
Rupp
and
which
more
r e d e t e r m i n e
prepared.
of
bromocresol
p s i
N.Y.) (121°C)
S u b s t r a t e s
Johnson
was
Rochester, at
of
areas.
Formation
m o d i f i e d
growth
increments
s e n s i t i v e
A c i d
A
the
c u l t u r e s
range
19.
of
from
HA,
p a r a f i l m
C o n t r o l
tubes
each
Type
i s o l a t i o n
55°C.
of
of
c u l t u r e
wrapped
were
ranging
D u p l i c a t e
w i t h the
pH
(3)
F i f t e e n
were f o r
m i l l i l i t e r s
p u r p l e added 15
b a s a l
min.
(Eastman and
the
Ten glucose, were 15
s t e r i l i z e d P r i o r
t e s t
s t e r i l e
p l a s t i c
0.5%
The
14
d
of
p e t r i
p s i mm
a
and
by
s m a l l
i n t o
b a s a l a
100
was
noted
f o r
medium,
f i n a l mm
x
concen-
15
mm
p r o d u c t i o n a f t e r
of
7
d
a c i d and
H y d r o l y s i s
agar
Truant
(5).
p l a s t i c
p l a t e s
30
of
and
of
min
p r e p a r e d
medium
and
dispensed
the
s t a r c h
h y d r o l y s i s
i n
immediate
or
r e d d i s h
the
3
100
at
When
55°C. was
w i t h was
c o l o r
by
t e s t e d
Gram's
at
mm
of
v i s i b l e
of
were
x
by
s t a r c h c o l o r
growth
f l o o d i n g
i o d i n e .
the
s t r e a k e d
good
by
i n d i c a t e d
v i c i n i t y
h y d r o l y s i s no
i n t o
media
complete or
B l a i r ,
a u t o c l a v e d
i s o l a t i o n
h y d r o l y s i s p l a t e
was
to
d i s h e s .
i n c u b a t e d
the
a c c o r d i n g
The
p e t r i
from
s t a r c h
p o r t i o n
c o l o r
medium.
was
s t e r i l e
p a r t i a l a
poured
(121°C)
y i e l d
carbohydrates
f o r
the
absence
a
and
to
the
the
(121°C)
o b t a i n e d ,
blue
added
of
D(+)-
D ( - ) - m a n n i t o l
p s i
and
C o l o n i e s
was
was
15
growth
S t a r c h
Lennette
onto
at
and
of
p l a t e s .
c u l t u r e
S t a r c h
15
s o l u t i o n s
D ( + ) - x y l o s e
s o l i d i f i c a t i o n
(w/v)
the
aqueous
p e r i o d s .
20.
15
(w/v)
a u t o c l a v i n g
carbohydrate of
each
by to
t r a t i o n
on
cent
L ( + ) - a r a b i n o s e ,
min.
the
per
a
The dark
c u l t u r e ; was
change
i n d i c a t e d i n
the
62.
21.
as
carbon
of
K o s e r ' s
of
0.2%
(w/v), HP0
(w/v) the
of
Sodium
C i t r a t e
and
Sodium
P r o p i o n a t e
U t i l i z a t i o n
of
sodium
c i t r a t e
and
sodium
p r o p i o n a t e
sources
measured
N a C l ;
s o l u t i o n
media wrap
was
d u r i n g acids r e d
to
i n t o
on
15
used
around
i n c u b a t i o n . was
22.
show
a f t e r
a
y e l l o w
R e d u c t i o n
C u l t u r e s a c c o r d i n g
The
e s t a b l i s h e d
appeared
c u l t u r e s
the
to
and
caps
to
the
week
d i s s o l v e
It
was
of
N i t r a t e
grown
Haynes
i n
and
(NH ) 4
a
the
2
0.04% pH
as
the A
of
agar
of
s l a n t s .
3
i s o l a t i o n wax
d e h y d r a t i o n
these c o l o r
t u r n
at
p a r a f i l m
prevent
two of
p e r i o d , red
to
N i t r i t e
a
n i t r a t e
Pang
the
a u t o c l a v e d
from
and
of
w i t h
to
i n c u b a t i o n 6.8
0.1%
a u t o c l a v i n g .
a l k a l i n e
pH
composed
(w/v),
(v/v)
s l a n t s .
at
were
Gordon,
the
to
is
p r o p i o n a t e ;
s o l i d i f i e d
b r o t h
m o d i f i c a t i o n
0.05%
added,
u t i l i z a t i o n
i f 2
0 ;
was
tubes.
onto
2
2.0%
heated
min
sodium
- 7 H
p r i o r
n u t r i e n t
s t r e a k e d
4
a
medium
A l s o ,
red
was
or
M g S 0
6.8
t e s t
f o r
grown
were
phenol
using
The
c i t r a t e
agar.
medium
(121°C)
C u l t u r e s
of
by
(30).
(w/v),
a d j u s t e d
dispensed p s i
sodium
(w/v),
The
15
agar
0.021
2.5%
medium
and
was
c i t r a t e
(w/v),
and
4
U t i l i z a t i o n
(22)
.
at
phenol v i z . , pH
b r o t h Ten
o r g a n i c
8.2.
p r e p a r e d m i l l i l i t e r s
63.
of
medium
at
15
was
p s i
was
f o r
for
each
(121°C)
3,
7
w i t h
t i o n
p e r i o d ,
14
d;
were
w i t h
the
( g l a c i a l
a)
MO) a c e t i c
55°C.
a c i d
and
red
i n d i c a t e d t e e n t h 5
mg
were
of
i n
the
of
NOj.
14
days
beyond of
of
f o r
i n c u b a t i o n .
red
or
some
organisms
v e r y
may
be
not
m l . o f
r a p i d l y
d e t e c t e d
each
m i x i n g
5N
water
(Sigma ml
of
incuba-..
1
ml
t e s t can so
the
which
f o u r 4
was
s t i l l
the
r e q u i r e d
that the
the
the
the
present
i n d i c a t e
reduce
to
p r e v i o u s l y
demonstrate
is
a f t e r
a c i d .
p o s i t i v e ,
to
would
Co.,
r e s p e c t i v e l y
tubes
was
a c i d
1:2.5);
a c e t i c
a f t e r
r e a c t
the
a c e t i c i n
5N
2
( M a l l i n c k r o d t ,
Chemical
If
n i t r a t e
n i t r a t e
n i t r i t e
by
of
evapora-
g
not
c o l o r a t i o n
r e s i d u a l
end
development
This t h a t
prevent
0.8
g
to
made.
a c i d ,
n i t r i t e . d i d
were
f o l l o w i n g
100
added
n i t r i t e .
A
because
n i t r i t e
was
r e d u c t i o n
This
of
c u l t u r e s
dust
i n
c o l o r
presence
media.
the
y e l l o w
the
z i n c
t e s t e d
absence
or
the
day,
d i s s o l v e d
tubes
the
d i s t i l l e d
Louis,
p e r i o d
of
100
0.6
to
the
each
i n
media
t e s t e d
s u l f a n i l i c
St.
a
were
a u t o c l a v e d
t r i p l i c a t e
caps
At
and
i n c u b a t i o n of
the
from
d i m e t h y l n a p t h y l a m i n e ,
E i t h e r
The
i s o l a t i o n
at
b)
MO)
3 f o r
d i s s o l v e d
tubes
sets
used
drops
s o l u t i o n s : L o u i s ,
min.
c u l t u r e s 3
t e s t
three
from
the
i n t o 10
i n c u b a t i o n
c u l t u r e
St.
and
wraps
t i o n
t e s t
f o r
c u l t u r e
P a r a f i l m
of
dispensed
presence
a f t e r
n i t r a t e presence
t h i r d
day
of
64.
23.
Dihydroxyactone
A of
Gordon,
at
15
Haynes
p s i
(121°C)
s t e r i l i z e d once
g l y c e r o l
agar Pang
f o r
15
p l a s t i c
p l a t e
i n c u b a t i o n ,
the
p l a t e s
was or 500
s o l u t i o n
d i s t i l l e d composed R o c h e l l e m l .
u n t i l
of
needed,
used.
f o r
the
24.
of soy
t r y p t o n e b r o t h
c u l t u r e
g;
s o l u t i o n and
a
A
and
of
a
and
2
red
of
from
s t e r i l e
tubes
b r o t h
(Difco)
at
50
A
halo of
d.
B
A f t e r s o l u t i o n . 34.66
s o l u t i o n
g
B t a r t r a t e
d i s t i l l e d
water,
r e f r i g e r a t e d
i n
the
around
s t r e a k e d
p o t a s s i u m
kept
l a t e r ,
was
F e h l i n g ' s
and
and
a u t o c l a v e d i n t o
CuSO^-SF^O,
g
were
of
a
1:1
p l a t e s
the
r a t i o were
c o l o n i e s
examined which
d i h y d r o x y a c e t o n e .
Indole
the
3
i s o l a t i o n
c o n t a i n i n g and
T r i p l i c a t e
i n c u b a t e d
of
(sodium
B
h
w i t h
F e h l i n g ' s
NaOH,
m i x t u r e
p r o d u c t i o n
(BBL).
m l .
inoculum 10
procedure
was
poured
f o r
f l o o d e d
the
medium
and
The
composed
500
173
P r o d u c t i o n
i n t o
c o o l e d
2
C u l t u r e s l a t e d
was
using
This
i n c u b a t e d
were
A p p r o x i m a t e l y
the
.
KNaC^H^O^•4H 0
presence
i n d i c a t e d
(22)
p l a t e s .
and
water,
s a l t ) ,
Both
was
A
p r e p a r e d
min,
p e t r i
the
and
was
and
across
F e h l i n g ' s
P r o d u c t i o n
55°C
a
11
tubes f o r
10
media ml
(w/v) were 14
d.
of of
made The
were II
i n o c u -
(w/v)
t r y p t i c a s e f o r caps
each were
65.
wrapped a
t e s t
w i t h
p a r a f i l m
s o l u t i o n
shaken.
This
was
5
g,
The
presence
l a y e r
t u r n e d
25.
to
to
method
the
21
at
A
d
t e s t
the Four the agar
3
55°C,
s o l u t i o n
f o r m a t i o n or
w i t h
f i v e
growth
on
beneath
p h e n y l p y r u v i c
of
of
the the
of
were
media. caps
101
(w/v)
t h i s
s l a n t s . c o l o n i e s
a c i d .
HC1,
the
made
were
Haynes f o r
Co., 25
m l .
a l c o h o l
wrapped F e C l ^
i n was
used
s o l u t i o n
were
i n d i c a t e d
of f o r
to
(22).
the 7
c u l t u r e s and
wax. i n d i c a t e
p h e n y l a l a n i n e . p i p e t t e d
c o l o r a t i o n the
Pang
p a r a f i l m
from
green
and
was
a c i d
A
p r e p a r e d
each
Incubation
a l l
of
Chemical
when
agar
Gordon,
p h e n y l p y r u v i c
drops
R o c h e s t e r ,
P h e n y l a l a n i n e
tubes
i s o l a t i o n
and
p a r a d i m e t h y l -
Baker
i n d i c a t e d
of
c u l t u r e s
c o n c e n t r a t e d
p h e n y l a l a n i n e
D u p l i c a t e
of
ml
(22).
of
of
the
2
Chemicals,
(J.T.
and
was
S l a n t s the
ml
r e d
Deamination
a c c o r d i n g
from
75
of
Organic
a l c o h o l
i n d o l e
p i n k
each
i n c u b a t i o n ,
c o n s i s t s
(Eastman
N . J . ) , of
to
s o l u t i o n
i s o - a m y l
P h i l l i p s b u r g ,
A f t e r
added
t e s t
aminobenzaldehyde N.Y.),
wax.
of
f o r m a t i o n
over the of
66.
26.
Decomposition
Ten
grams
B a c t o - s k i m
of
d i s t i l l e d
i n
100
i n
100
of
d i s t i l l e d
at
15
p s i
t o g e t h e r ,
(121°C) and
water
f o r
poured
min,
i n t o
60
dishes.
The
p l a t e s
f o r
d
the
surface
to
D u p l i c a t e were
p l a t e s
made.
p l a t e s t i o n and
dry
from
I n o c u l a t i o n
were
i n c u b a t e d
p e r i o d s , beneath
the
the
was
f o r
p l a t e s
7
mm
x
15
kept
g
2.5
s t e r i l e
at
the
3
14
d.
room b e f o r e
i n d i c a t i n g
p l a s t i c
i n o c u l a t i o n . c u l t u r e s
s t r e a k
f o r
mixed
temperature
A f t e r
examined
agar
45°C,
i s o l a t e d
simple
of
s e p a r a t e l y
mm
of
and
and
about
agar
a
(Difco)
to
the
by
powder
a u t o c l a v e d
of
were
c o l o n i e s ,
water
c o o l e d
were
each
m i l k
were
15
p e t r i 3
Casein
of
d i s s o l v e d ml
ml
of
and
the
the i n c u b a -
c l e a r i n g
c a s e i n
around
decomposition
(22).
27.
Decomposition
One Rochester, water. an
p s i
N.Y.)
3
water.
(121°C)
f o r
of
was
S i m i l a r l y ,
a d d i t i o n a l
t i l l e d
gram
g
of
Tyrosine
L - t y r o s i n e suspended
4.6
g
of
(Eastman i n
20
n u t r i e n t
of
agar
was
These
were
a u t o c l a v e d
15
min,
c o o l e d
ml
to
of
agar
p r e p a r e d
Organic
i n
d i s t i l l e d (Difco) 200
ml
s e p a r a t e l y
about
Chemicals,
45°C
and
w i t h of at
d i s 15
thoroughly
mixed
t o g e t h e r .
60
x
mm
there
15
mm
was
an
throughout at
room
and
The
s t e r i l e even
the
made
d
i n c u b a t i o n ,
of
beneath
the
28.
each
of
R e a c t i o n
B a c t o - s k i m
(J.T. 1
of
i n t o The
Baker
a
i n
m i l k
was
Co.,
a u t o c l a v e d
(Fisher
of
the
S c i e n t i f i c
the
t i o n
of
the
i n d i c a t o r ,
t i o n
of
c a s e i n
(22).
c r y s t a l s were
agar
kept
surface
D u p l i c a t e
A f t e r
by
7
and
f o r
p l a t e s 14
c l e a r i n g
0.75
d i s s o l v i n g g
of
P h i l l i p s b u r g ,
at
15
p s i 6
were F a i r
observed
f o r m a t i o n
were
(121°C)
Lawn,
of
powder
i n t o
15
f o r
w i t h
N.J.)
f o r
c o l o r
c u r d ,
gas
min... each
p a r a f f i n
f o r
i n c u b a t i o n
1
dispensed:;
f o r
r e p l i c a t e s
F o l l o w i n g
were
N.J.)
covered
100
l i t m u s
m i l l i l i t e r s
w i t h
Co.,
and
c u l t u r e s
and
tubes
d e t e r m i n a t i o n .
d,
that
M i l k
F i f t e e n
r e d u c t i o n 14
the
examined
p r e p a r e d
i n o c u l a t e d ,
Three
p l a t e s
s t r e a k .
were
powder
tubes
were
e n s u r i n g
L - t y r o s i n e
dry
i n t o
.
water.
tubes
poured
dishes
c u l t u r e .
Litmus
m i l k
was
The
s i n g l e
p l a t e s
(22)
of
to
i s o l a t e d
Chemical
and
p e t r i
agar.
3 d
d i s t i l l e d
c u l t u r e . o i l
by
the
growth
Litmus g
f o r
i n o c u l a t e d f o r
p l a s t i c
s o l i d i f i e d
were
media
d i s t r i b u t i o n
temperature
then
r e s u l t i n g
l i t m u s
f o r
7
and
r e d u c -
and
d i g e s -
68.
EXPERIMENTAL
I.
Composition
of
the
Analyses r e q u i r e d the
to
waste
o b t a i n
the
of
removed
of
lye
a
samples was
the
from
p e e l i n g were
M o i s t u r e
As
a
d e f i c i e n t growth was
i n
t h i s
and
b i l i t y .
Since
a
R a t i o ,
of
of
q u e s t i o n
the
samples
c o m p o s i t i o n
p e e l
to
as
waste
d u r i n g
the
c o n s i d e r e d the
were of
determine
waste
Four
of
Wastes
a
s u b s t r a t e
samples course
t h a t
waste
p e e l i n g
the
the
t h a t
p r o c e s s .
Carbon-Phosphorus
R a t i o
and
Requirements
p o t a t o
e s s e n t i a l
maintenance
d e f i n i t e l y
was
P e e l
p l a n t
r e q u i r e d
p a r t i c u l a r
f e r m e n t a t i o n
some
P o t a t o
p e e l e r
It
DISCUSSION
the
r e p r e s e n t a t i v e
Content
sole
on
p o t a t o
p r o c e s s .
U t i l i z a t i o n able.
was
p o t a t o
C a r b o n - N i t r o g e n
1.
Soda
f e r m e n t a t i o n .
the
from
AND
p r o c e s s i n g
c a u s t i c
f a i r l y
d i s c h a r g e d
the
This
t h e r m o p h i l i c
were
C a u s t i c
i n f o r m a t i o n
m a t e r i a l .
s u i t a b i l i t y f o r
of
RESULTS
waste
s u b s t r a t e ,
n u t r i e n t
the
i t
was
q u e s t i o n -
was
c o n s i d e r e d
r e q u i r e m e n t s
microorganisms.
c o n c e r n i n g
a v a i l a b l e
alone
n i t r o g e n
i t s i n
There
n i t r o g e n the
f o r
waste
a v a i l a was
69.
low
(as
an
compared
to
i n s u f f i c i e n t
amount
f e r m e n t a t i o n . ammonia of
or
the
and to
some
o t h e r
i t
was
the
of
r a t i o
ranging
would
than
c o n s i d e r e d
et
a l
ing as
was (55)
glucose the
l a t i o n
of
a
r a t i o
r a t i o
to
be
d i f f e r e n t f o r
Toth
source
(57) of
growth. of
s t a t e d the
d e c o m p o s i t i o n
to
ensure
f o r
t h a t
o r g a n i c s
of
s o i l ,
and
c u l t u r i n g
w i l l t h a t
d e c o m p o s i t i o n .
C/N
of
a
m i x t u r e
of
l a r g e l y e x t r a Almost
of
13).
Surucu
medium
a
mixed the
raw
of
popu-
mixed
wastewater
organisms r e q u i r e -
medium
and
determine
a l l
c o n t a i n -
c h l o r i d e
found
content
n i t r o g e n
met
g r e a t e r
t h e r m o p h i l i c
n i t r o g e n
be
r a t i o
n u t r i t i o n a l
t h e i r
mixed
to
(8,
water,
demanding
the
the
They
stream
F o r m u l a t i o n
3.45
18.3:1
ammonium
organisms.
more
to
source the
growth
t h e r m o p h i l i c
l i m i t i n g
and
course
carbon
d e f i n e d
comprised and
a
the
the
had
a
of
a
c h e m i c a l l y
f o r
from
on
p r o l o n g e d
form
Since
of
a
d u r i n g
9.7:1
Even
n i t r o g e n a
the
requirement
maintenance
carbon
o b t a i n e d
ments C/N
the
t h e r m o p h i l i c
s i l a g e ,
having
as
t h i s
d i f f i c u l t .
developed
n i t r o g e n
c u l t u r e , and
,
be
i n
depends from
thought
m a i n t a i n
p o s s i b i l i t y .
(C/N)
and/or
to
was
by-product
organisms
t h a t
i t
element
the
f e r m e n t a t i o n 7.5
the
gaseous a
1),
p r e s e n t
of
was
thought
a t t a i n m e n t
Table
was
l o s s
f e r m e n t a t i o n
n i t r o g e n
or
The
maintenance
(8);
carbon,
must
organic
c o n s t i t u t e s c u l t u r e . the
the be waste
C/N
r a t e added t h a t
70.
Table
1.
C o m p o s i t i o n f r e s h
of
c a u s t i c
p o t a t o
C a u s t i c
P o t a t o
P e e l Waste, • %"Dry Weight r
T o t a l K j e l d a h l N i t r o g e n
Carbon
p e e l
waste
and
p o t a t o .
1.7
-
Unpeeled Fresh P o t a t o , % Dry Weight
2.0
Analyses
T o t a l Carbon Inorganic Carbon Organic Carbon
45.8 1.56 44.24
43.6 1.73 41.87
T o t a l
Phosphorous
0.031
0.028
(0.021)
T o t a l
Sodium
5.66
0.04
(0.03)
9.9
(5.6)'
Ash
19.9
M o i s t u r e
Dry
Content
M a t t e r
Content
pH
a
88. 9
79.2
11.1
20.8
12.5
R e s u l t s
o b t a i n e d
f o r
f r e s h ,
p e e l e d
p o t a t o e s .
71.
c o n t a i n s of
1.5
e x t r a
f o r
amounts
sample.
or
an
(N
x
T o t a l
6.25)
of
an
1.8%,
values
on
were
a
an
Fresh
store
c o n t e n t . p l a n t
values organic and
carbon v a l u e
Average
r e s p e c t i v e l y . ( t o t a l carbon
41.87%
f o r
and to
the
and The
n i t r o g e n
crude
t o t a l
f r e s h
K j e l d a h l
see
Table
l i t e r a t u r e
a n a l y s i s
of
samples
b a s i s ,
p r o t e i n
or
the
p l a n t
weight
r e p o r t e d
of
values f r e s h
value the
of
45.801, had
f o r
-
on a
p o t a t o e s of
44.24%
f r e s h
s t o r e
content
p o t a t o e s
n i t r o g e n 1.
These
values
carbon
r e p r e s e n t s
p l a n t dry
43.601
the
of
f o r
the
p r e s e n t ,
45.8:1.9
or
t o t a l
p l a n t
the 1.73%,
determined an
average
samples
p o t a t o . amount
i n
the
f o r
two
gives
b a s i s . carbon
and
above
bought
p r e s e n t
weight
1.561
the
samples
carbon
carbon)
c o n s i d e r i n g
n i t r o g e n
a
were
i n o r g a n i c
of
the
i n o r g a n i c
d i f f e r e n c e
carbon
(organic) amount
dry
bought
b a s i s ,
p o t a t o e s
T h e r e f o r e , K j e l d a h l
s t o r e
four
i n
51).
bought
samples
to
on. a
a d d i t i o n
r e q u i r e d
p r e s e n t
the
average
f o r
weight
s i m i l a r
average
The
of
the
were
n i t r o g e n
2.0%, an
value
dry
(47,
to or
1.9%
and
r e q u i r e s
analyses
n i t r o g e n
1.7
11.9%.
T o t a l gave
carbon
average
- 2.0%
1.8%
of
of
n i t r o g e n
T h e r e f o r e ,
from
average
t o t a l
K j e l d a h l
v a r i e d
y i e l d e d of
2.5%
n i t r o g e n .
the
t e s t e d
to
the
p l a n t
r a t i o
24.1:1
of
of
( t o t a l
a v a i l a b l e sample carbon organic
72.
C
to
It
t o t a l
was
organic
thought
r e q u i r e d
to
was
since
urea
N
that
r e p r e s e n t s a d d i t i o n
decrease i t
t h i s
was
44.24:1.9
of
a
n i t r o g e n
r a t i o .
r e a d i l y
or
The
2 3 . 3 : 1 ) .
source
n u t r i e n t
a v a i l a b l e
and
was
c o n s i d e r e d
f a i r l y
x
i n e x p e n s i v e . An
i n i t i a l
performed
w i t h
C/N
was
no
r a t i o
f r e s h l y s i m i l a r
a d d i t i o n a l t r i a l
whether
t h e r m o p h i l i c
c o n d i t i o n s
of
the
of
n i t r o g e n
of
system
the
t i o n
as
w i t h
the
even
i n
to
a
t h i s ion
were
was
and
c a u s t i c the
a d d i t i o n a l
on
t h i s
to
to
f o r
to
what And
thus,
the
e v e n t u a l
reached
and
were
would
c o n t i n u e d
a
i n
a
the
the
amount
f e r m e n t a -
m e c h a n i c a l
components
p o t a t o
f e r m e n t a t r i a l
S u r p r i s i n g l y , c o n t e n t ,
t h e r m o p h i l i c p r o l o n g e d .
and
advantageous,
source
r e q u i r e d .
l a t e r
and,
d u r a t i o n
determine
important
be
This
determine
the
reasonably
n i t r o g e n
not
be
p o t a t o .
n i t r o g e n
of
to
f e r m e n t a t i o n
low
costs
1)
f r e s h
of
e x t r e m e l y
samples,
s u b s t r a t e .
i n t e n s i f y the
was the
o b t a i n a b l e ,
would
and
u t i l i z e
s o d a - t r e a t e d
p l a n t
the
were
15)
Since
o b j e c t i v e :
improve
the
(Figure
p o t a t o e s .
added
p r o l o n g and
t r i a l
p r o c e s s i n g
c o n d i t i o n s
3)
product is
was
period?
presence were
the
reached,
c o n s i d e r e d
waste
to
t h r e e f o l d
c o r r e c t
c o n t r o l
c o n d i t i o n s
since
a
needed
2)
This
had
t h e r m o p h i l i c
t i o n ;
macerated
n i t r o g e n
i n i t i a l
i f
f e r m e n t a t i o n
to
t r e a t
F u r t h e r
s e c t i o n .
d i s c u s s -
73
73.
70 • —• A—A
-
Temperature of pH
fermentation
of fermentation
\
60
10.0
/
50 O
o