Previous Article | Next Article 
Appl Environ Microbiol, April 1998, p. 1548-1549, Vol. 64, No. 4
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
A Small-Scale Method for Screening of
Lignin-Degrading Microorganisms
Ulrike
Temp,1
Claudia
Eggert,1 and
Karl-Erik L.
Eriksson2,*
Institute of General Microbiology and
Microbial Genetics, Friedrich-Schiller Universität Jena, 07743 Jena, Germany,1 and
Department of
Biochemistry and Molecular Biology and Center for Biological Resource
Recovery, University of Georgia, Athens, Georgia
30602-72292
Received 31 October 1997/Accepted 23 January 1998
 |
ABSTRACT |
A new method to facilitate rapid screening of lignin-degrading
microorganisms was developed. Fungal strains are cultivated in tissue
culture plates containing 14C-ring-labeled dehydrogenation
polymerizate (DHP) (synthetic lignin). Evolved
14CO2 is trapped in barium-saturated filter
paper and is detected by exposing the paper to X-ray film. Analysis of
the autoradiograms, carried out by density measurement with an image
analysis program, allows for a semiquantitative estimation of the
amount of 14CO2 evolved. The method is
especially useful for screening for new, powerful lignin-degrading
strains in both man-made and natural environments. It eliminates the
need for special equipment for their cultivation and trapping of
14CO2 as well as laborious sample analysis. The
method has in this study been used to test three novel fungal isolates
and a laccaseless mutant of the basidiomycete Pycnoporus
cinnabarinus. Their ligninolytic capacities were compared with
those of the potent lignin degrader Ceriporiopsis subvermispora.
 |
TEXT |
Higher fungi which cause white rot
in wood are the most efficient lignin degraders in nature. They are the
only microorganisms known to date capable of completely degrading
lignin to carbon dioxide and water (5). White rot fungi that
can selectively delignify wood and the enzymes involved in this process
are important because of their potential application for the removal of
lignin from ligninocellulosic materials, which would facilitate
biopulping, biobleaching (1, 8), and detoxification of
environmental pollutants (2, 7).
The lignin-degrading ability of a microorganism is commonly evaluated
by measuring 14CO2 evolution from
14C-labeled lignin preparations, such as
14C-ring-labeled dehydrogenation polymerizate (DHP). The
measurement of 14CO2 evolution is the most
sensitive and accurate method for testing ligninolytic activity
(5). Standard experiments are carried out in culture flasks
and require special equipment for trapping of
14CO2 (6). Besides the fact that
specifically radiolabeled lignins or lignin model compounds and the
disposal of the radioactive waste produced during such experiments are
expensive, screening a large number of microorganisms is very laborious
and time-consuming. In our efforts to study the mechanisms of lignin
degradation by white rot fungi, we developed a small-scale method for
fast and easy evaluation of their ligninolytic capacity. The method has been modified after a protocol used by Tabor et al. (10) for the screening of bacterial mutants for their biosynthetic pathway for
amines.
The ligninolytic capacities of three unidentified basidiomycetes
isolated from decaying hardwood and a mutant strain of the white rot
fungus Pycnoporus cinnabarinus (ATCC 200748) rendered laccaseless by UV radiation (3) were evaluated and compared to that of cultures of Ceriporiopsis subvermispora
[L-6322-Sp (8501)]. The fungal strains were grown on 2% (wt/vol)
malt extract agar (1% agar) plates for 10 days. Agar blocks (0.5 by
0.5 cm) from these precultures were transferred into the wells of
sterile tissue culture plates (Falcon 3046) containing 3 ml of sterile liquid basal medium (4). The fungi were cultivated at 25°C for 3 days to establish mycelial growth prior to addition of
radiolabeled DHP. 14C-ring-labeled DHP of coniferyl alcohol
was prepared by the 'Zutropfverfahren' (E. Odier and P. Heckman,
Institut National de la Recherche Agronomique, Paris-Grignon, France)
and previously characterized as described in reference
5. On day 4, 14C-DHP (5,000 dpm)
dissolved in 5 µl of dimethylformamide was added to each well. After
24 h, sterile filter papers (Whatman 3 MM, cut exactly to the size
of the tissue plate) were soaked in sterile saturated barium hydroxide
solution and placed over the wells. Plastic lids were tightly fastened
and clamped to the plates, which were then incubated at 30°C for an
additional 5 days. Evolved 14CO2 was trapped in
the filter papers as insoluble BaCO3.
The filters were then removed and exposed to X-ray film (Kodak XAR-5)
for 5 days. Dark circles on the autoradiogram corresponding to the
positions of individual wells were formed by evolved and trapped
14CO2. The intensity of the dark circles
disclosed the ligninolytic capacity of the respective fungal culture.
Analysis of the autoradiograms was performed with a Macintosh Power PC
9500 computer by using a scanner (UMAX Powerlock II) and the public
domain NIH image analysis program (developed at the National Institutes
of Health and made available for the public via
http://rsb.info.nih.gov/nih-image/).
All cultivations were performed in triplicate with independent culture
plates. Uninoculated samples containing 3 ml of liquid basal medium (pH
4.6) and radiolabeled DHP (5,000 dpm) were used as a control on each
culture plate.
Each of the fungal strains studied developed a mycelial layer on the
surface of the culture medium during the 10-day cultivation. One of the
new fungal isolates (Fig. 1C) gave the
strongest signal on autoradiograms of all strains, indicating an even
higher ligninolytic activity than that of the efficient lignin degrader
C. subvermispora (9) (Fig. 1F). Weak
autoradiographic signals were obtained with one of the new strains
(Fig. 1B) and the laccaseless mutant of P. cinnabarinus
(Fig. 1E). The inability of the laccaseless mutant to release
significant amounts of 14CO2 is in good
agreement with our previous result, which was obtained by the
conventional method for measuring 14CO2
evolution (3). The third new isolate (Fig. 1A) used in this
study gave a signal almost as strong as those obtained for C. subvermispora (Fig. 1F). The background was low on all X-ray films, and the control well did not show any
14CO2 evolution (Fig. 1D). All samples, run in
triplicate on separate plates under identical conditions, gave
identical results. Data obtained from density reading analysis of the
autoradiograms are presented in Table 1.

View larger version (95K):
[in this window]
[in a new window]
|
FIG. 1.
Autoradiographic detection of
14CO2 released by fungal strains grown on
14C-ring-labeled DHP. Circles correspond to the culture
wells of the strains. (A) basidiomycete A; (B) basidiomycete B; (C)
basidiomycete C; (D) control; (E) P. cinnabarinus
laccaseless mutant; (F) C. subvermispora.
|
|
The method described here allows easy screening of ligninolytic
activity in a large number of microorganisms. It has clear advantages
over conventional culture flask experiments since the fungal organisms
can be simultaneously cultivated in small volumes of media containing
minimal amounts of 14C-DHP. This allows the testing of
large numbers of microorganisms and their lignin-degrading abilities in
a short period of time.
Both man-made environments, such as rivers and ponds, which for a long
time have received black liquor from pulping or wastewaters from pulp
bleaching, as well as natural environments can rapidly be screened for
useful lignin-degrading microorganisms. The method can also be used for
the screening of mutants deprived of their ability to produce one or
several lignin-degrading enzymes as well as for optimization of culture
conditions for efficient delignification. Various substrates, such as
pulp in which the lignin has been 14C labeled, can also be
used. Mineralization experiments can be downsized even further by using
24- or 96-well microtiter plates. The technique, as described above,
allows a semiquantitative analysis of evolved
14CO2 by using density readings of the
autoradiograms. Alternatively, quantitative analysis can be carried out
by scintillation counting of the filter papers.
In conclusion, the method is a useful tool for rapid screening of large
numbers of microorganisms for their ligninolytic capacity to obtain
more potent and specific lignin-degrading white rot fungi than those
already known.
 |
ACKNOWLEDGMENTS |
Financial support for this work consisted, in part, of a fellowship
from the Alexander von Humboldt-Stiftung to C.E., National Science
Foundation grant MCB-9507331, and funds from the University of Georgia
Biotechnology Grant Program.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Biochemistry and Molecular Biology and Center for Biological Resource Recovery, B304 Life Sciences Building, University of Georgia, Athens,
GA 30602-7229. Phone: (706) 542-4453. Fax: (706) 542-2222. E-mail:
eriksson{at}uga.cc.uga.edu.
 |
REFERENCES |
| 1.
| Blanchette, R. A. 1995. Degradation of
the lignocellulose complex in wood. Can. J. Bot. 73(Suppl.
1):999-1010.
|
| 2.
|
Boominathan, K., and C. A. Reddy.
1992.
Fungal degradation of lignin: biotechnological applications, p. 763-822. In
D. K. Arora, R. P. Elander, and K. G. Mukerji (ed.), Handbook of applied mycology, vol. 4. Fungal biotechnology.
Marcel Dekker, Inc., New York, N.Y.
|
| 3.
|
Eggert, C.,
U. Temp, and K.-E. L. Eriksson.
1997.
Laccase is essential for lignin degradation by the white-rot fungus Pycnoporus cinnabarinus.
FEBS Lett.
407:89-92[Medline].
|
| 4.
|
Eggert, C.,
U. Temp, and K.-E. L. Eriksson.
1996.
The ligninolytic system of the white rot fungus Pycnoporus cinnabarinus: purification and characterization of the laccase.
Appl. Environ. Microbiol.
62:1151-1158[Abstract].
|
| 5.
|
Eriksson, K.-E. L.,
R. A. Blanchette, and P. Ander.
1990.
.
Microbial and enzymatic degradation of wood and wood components.
Springer Verlag, Berlin, Germany.
|
| 6.
|
Haider, K., and J. Trojanowski.
1975.
Decomposition of specifically 14C-labeled phenols and dehydropolymers of coniferyl alcohol as models for lignin degradation by soft and white rot fungi.
Arch. Microbiol.
105:33-41.
|
| 7.
|
Hammel, K. E.
1989.
Organopollutant degradation by ligninolytic fungi.
Enzyme Microb. Technol.
11:776-777.
|
| 8.
|
Kirk, T. K., and H.-M. Chang.
1981.
Potential application of bioligninolytic systems.
Enzyme Microb. Technol.
3:189-196.
|
| 9.
|
Rüttimann-Johnson, C.,
L. Salas,
R. Vicuña, and T. K. Kirk.
1993.
Extracellular enzyme production and synthetic lignin mineralization by Ceriporiopsis subvermispora.
Appl. Environ. Microbiol.
59:1792-1797[Abstract/Free Full Text].
|
| 10.
|
Tabor, C.,
H. Tabor, and E. H. Hafner.
1983.
Mass screening for mutants in the biosynthetic pathway for polyamines in Escherichia coli.
Methods Enzymol.
94:83-91[Medline].
|
Appl Environ Microbiol, April 1998, p. 1548-1549, Vol. 64, No. 4
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.