Previous Article | Next Article 
Applied and Environmental Microbiology, October 2003, p. 6337-6339, Vol. 69, No. 10
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.10.6337-6339.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
Petroleum Pollution Bioremediation Using Water-Insoluble Uric Acid as the Nitrogen Source
Omry Koren, Vishnia Knezevic, Eliora Z. Ron, and Eugene Rosenberg*
Department of Molecular Microbiology and Biotechnology, Tel Aviv University, Ramat Aviv, Israel 69978
Received 30 April 2003/
Accepted 9 July 2003

ABSTRACT
The biodegradation of hydrocarbon pollutants in open systems
is limited by the availability of a utilizable nitrogen source.
This limitation can be overcome by using uric acid. Enrichment
cultures grown on crude oil-uric acid media yielded mixed and
pure cultures that degraded petroleum. In a simulated open system,
uric acid bound to crude oil and was available for bacterial
growth and petroleum biodegradation.

INTRODUCTION
The rate-limiting step in the microbial degradation of petroleum
hydrocarbon pollutants in open systems, such as lakes, oceans,
and wastelands, is generally a utilizable source of nitrogen
(
1,
2,
13,
14). Since petroleum contains only traces of nitrogen,
the required nitrogen must come from the surrounding environment.
In the laboratory, the nitrogen requirement for optimum growth
of hydrocarbon oxidizers can be readily satisfied with urea
or salts that contain ammonium or nitrate ions. However, these
nitrogen sources have a high water solubility, which reduces
their effectiveness in open systems because of rapid dilution.
Thus, there is at present no practical microbial solution to
the reoccurring problem of petroleum pollution in the sea. To
overcome the N limitation for petroleum degradation in open
systems, Atlas and Bartha (
3) studied the effectiveness of several
oleophilic nitrogen compounds with low C/N ratios. Subsequently,
an oleophilic fertilizer (Inipol EAP 22) was used in the bioremediation
of polluted shorelines after the
Exxon Valdez spill (
1,
11).
Initial reports of success (
7,
12) have been challenged (
5).
Another approach has been the use of a water-insoluble polymer,
based on a urea-formaldehyde formulation, which adheres to oil
(
15,
16).
Uric acid is the major nitrogen waste product of birds, terrestrial reptiles, and many insects. It has a low solubility in water and is the major component of guano fertilizer, suggesting that it might be a useful nitrogen source for the bioremediation of petroleum pollutants in open systems. Many different species of bacteria are known to degrade uric acid (4, 6, 19, 20). We report here the isolation and characterization of a strain of Acinetobacter that can grow on crude oil with uric acid used as the sole nitrogen source. Furthermore, we show that uric acid binds to crude oil and is therefore available for bacteria which grow at the hydrocarbon-water interface.

Isolation and characterization of Acinetobacter sp. strain OK1.
We used weathered crude oil as the carbon source, uric acid
as the nitrogen source, and pigeon droppings as the inoculum
to obtain a mixed culture after several transfers that emulsified
and partially degraded the crude oil. Plating on Luria-Bertani
agar yielded five colony types: two were unable to grow, two
grew poorly, and one grew well on the hydrocarbon-uric acid
medium. The strain that grew well, referred to as OK1, was chosen
for further study. A comparison of the growth of strain OK1
and the mixed culture on the crude oil-uric acid medium is shown
in Fig.
1. Strain OK1 is a gram-negative, strictly aerobic,
nonmotile, oxidase-negative short rod. These properties are
typical of the genus
Acinetobacter (
8,
10). The Biolog (Biolog
Inc., Haywood, Calif.) and API-20 (BioMerieux, Marcy l'Etoile,
France) identification kits indicated that strain OK1 was an
Acinetobacter strain, most closely related to
Acinetobacter baumannii (identity, 76%). The 16S strain ribosomal DNA sequence
of strain OK1 (821 bp in length; GenBank accession no.
AY260854)
had the closest similarity to
A. baumannii (DSM 3008), with
an identity of 813 of 821 nucleotides (99%). In consideration
of all the phenotypic and genotypic tests performed, it appears
that strain OK1 is a new
Acinetobacter species which is most
closely related to
A. baumannii.

Adhesion of uric acid and strain OK1 to crude oil.
Uric acid crystals adhered to droplets of crude oil in the culture
medium (Fig.
2). When low ratios of uric acid to crude oil (1/20,
wt/wt) were used, the crude oil-uric acid complex had a density
less than 1.0 and floated to the surface of the medium, whereas
at higher ratios (1/2), the complexes sedimented. These data
also demonstrated the interaction between uric acid and crude
oil. The BATH test (
17) showed that strain OK1 adheres avidly
to hexadecane.

Growth of strain OK1 on crude oil and uric acid following removal of water-soluble nutrients.
The major assumption in this study is that uric acid binds to
crude oil and is not diluted into the surrounding water. To
test this assumption, the growth of strain OK1 was measured
on crude oil-uric acid media after the media were mixed and
after the aqueous phase had been removed and replaced with water
three times (a simulated open system). Table
1 demonstrates
that high cell yields (2
x 10
8 to 6
x 10
8 cells per ml) and
petroleum degradation (48 to 50%) occurred with initial concentrations
of 0.25 to 1.0 mg of uric acid per ml. The unwashed control,
containing 1 mg of uric acid per ml, yielded 9
x 10
8 cells per
ml and 67% petroleum degradation. The use of water-soluble ammonium
sulfate and performance of the same washout procedure yielded
only 5
x 10
6 cells per ml and 2% petroleum degradation. As is
typical of many
Acinetobacter strains (
18), the growth of strain
OK1 on crude oil was accompanied by emulsification of the oil.
Preliminary data indicate that the extracellular emulsifier
is a glucosamine-containing polysaccharide.
View this table:
[in this window]
[in a new window]
|
TABLE 1. Growth of Acinetobacter sp. strain OK1 on crude oil and uric acid following removal of water-soluble nutrientsa
|

Growth yield as a function of crude oil and uric acid concentrations.
To determine growth yields of
Acinetobacter sp. strain OK1 as
a function of petroleum and uric acid concentrations, an overnight
culture was inoculated into salts medium containing various
concentrations of crude oil and uric acid. After incubation
with shaking for 96 h at 30°C, cell yields were determined
by spreading appropriate dilutions on Luria-Bertani agar. Growth
was proportional to crude oil concentrations ranging from 0
to 5 mg/ml (Fig.
3A) and uric acid concentrations ranging from
0 to 0.5 mg/ml (Fig.
3B), ultimately reaching 9
x 10
8 cells
per ml. The minimum doubling time during the exponential phase
on the crude oil-uric acid medium was ca. 50 min.

Hydrocarbon substrate specificity.
The ability of strain OK1 to utilize various aliphatic and aromatic
hydrocarbons as carbon sources was examined in salts medium
containing 0.5 mg of uric acid per ml and 2 mg of the test hydrocarbon
per ml. The tests revealed that strain OK1 grows on straight
and branched-chain (phytane and pristane) aliphatic hydrocarbons
containing 12 or more carbons. It failed to grow on shorter
alkanes or the 16 aromatic hydrocarbons tested. The Agha Jari
crude oil used in the above washout experiment contained only
14% aromatics (
9).
The major aim of this study was to test the hypothesis that uric acid can (i) serve as a nitrogen source for hydrocarbon-degrading bacteria and (ii) bind to crude oil, thereby making it a potentially useful nitrogen fertilizer for the bioremediation of petroleum pollution in open systems. The data reported here for the isolated Acinetobacter sp. strain OK1 support this hypothesis. Binding of uric acid to crude oil was demonstrated visually and by a simulated open-system growth experiment. Clearly, in a true open system, such as a lake, the complex would be exposed to a much larger body of water, and the uric acid would have to remain bound to the oil for at least a few days. Although the study reported here dealt exclusively with strain OK1, we have isolated many different bacterial species that can grow on crude oil and uric acid, including some that utilize polycyclic aromatics. Thus, uric acid can serve as a general water-insoluble nitrogen source for hydrocarbon oxidizers. The most important parameter to study in order to convert the in-principle concept developed here to a useful technology is probably the rate of transfer of hydrocarbon-bound uric acid to the aqueous phase. Without these data, attempting to use uric acid for petroleum bioremediation in an open system would be premature.

ACKNOWLEDGMENTS
This investigation was supported by the Pasha Gol Chair for
Applied Microbiology, the Manja and Morris Leigh Chair in Biophysics
and Biotechnology, and EU Project COMMODE.

FOOTNOTES
* Corresponding author. Mailing address: Department of Molecular Microbiology & Biotechnology, Tel Aviv University, Ramat Aviv 69978, Israel. Phone: 972-3-640 9838. Fax: 972-3-642 9377. E-mail:
eros{at}post.tau.ac.il.


REFERENCES
1 - Atlas, R. M. 1991. Microbial hydrocarbon degradationbioremediation of oil spills. J. Chem. Technol. Biotechnol. 52:149-156.
2 - Atlas, R. M., and R. Bartha. 1972. Degradation and mineralization of petroleum in seawater: limitation by nitrogen and phosphorus. Biotechnol. Bioeng. 14:309-317.[CrossRef][Medline]
3 - Atlas, R. M., and R. Bartha. 1973. Stimulated biodegradation of oil slicks using oleophilic fertilizers. Environ. Sci. Technol. 7:538-541.[CrossRef]
4 - Bongaerts, G. P. A., and G. D. Vogels. 1976. Uric acid degradation by Bacillus fastidiosus strains. J. Bacteriol. 125:689-697.[Abstract/Free Full Text]
5 - Button, D. K., B. R. Robertson, D. McIntosh, and F. Juttner. 1992. Interactions between marine bacteria and dissolved-phase and beached hydrocarbons after the Exxon Valdez oil spill. Appl. Environ. Microbiol. 58:243-251.[Abstract/Free Full Text]
6 - Christiansen, L. C., S. Schou, P. Nygaard, and H. H. Saxild. 1997. Xanthine metabolism in Bacillus subtilis: characterization of the xpt-pbuX operon and evidence for purine- and nitrogen-controlled expression of genes involved in xanthine salvage and catabolism. J. Bacteriol. 179:2540-2550.[Abstract/Free Full Text]
7 - Crawford, M. 1990. Bacteria effective in Alaska cleanup. Science 247:1537.[Free Full Text]
8 - Grimont, P. A. D., and P. J. M. Bouvet. 1991. Taxonomy of Acinetobacter sp., p. 28-35. In K. J. Towner, E. Bergogne-Berezin, and C. A. Fewson (ed.), The biology of Acinetobacter. Plenum Press, New York, N.Y.
9 - Gutnick, D. L., and E. Rosenberg. 1977. Oil tankers and pollution: a microbiological approach. Annu. Rev. Microbiol. 31:379-396.[CrossRef][Medline]
10 - Juni, E. 1978. Genetics and physiology of Acinetobacter. Annu. Rev. Microbiol. 32:349-371.[CrossRef][Medline]
11 - Lindstrom, J. E., R. C. Prince, J. C. Clark, M. J. Grossman, T. R. Yeager, J. F. Braddock, and E. J. Brown. 1991. Microbial populations and hydrocarbon biodegradation potentials in fertilized shoreline sediments affected by the T/V Exxon Valdez oil spill. Appl. Environ. Microbiol. 57:2514-2522.[Abstract/Free Full Text]
12 - Pritchard, P. H., J. G. Mueller, J. C. Rogers, F. V. Kremer, and J. A. Glaser. 1992. Oil spill bioremediation: experiences, lessons and results from the Exxon Valdez oil spill in Alaska. Biodegradation 3:315-335.
13 - Rosenberg, E., S. Navon-Venezia, I. Zilber-Rosenberg, and E. Z. Ron. 1998. Rate-limiting steps in the microbial degradation of petroleum hydrocarbons, p. 159-171. In H. Rubin, N. Narkis, and J. Carberry (ed.), Soil and aquifer pollution. Springer-Verlag, Berlin, Germany.
14 - Rosenberg, E., and E. Z. Ron. 1996. Bioremediation of petroleum contamination, p. 100-124. In R. L. Crawford and D. G. Crawford. (ed.), Bioremediation: principles and applications. Cambridge University Press, Cambridge, United Kingdom.
15 - Rosenberg, E., R. Legmann, R. Kushmaro, R. Taube, E. Adler, and E. Z. Ron. 1992. Petroleum bioremediation: a multiphase problem. Biodegradation 3:337-350.
16 - Rosenberg, E., R. Legmann, A. Kushmaro, E. Adler, H. Abir, and E. Z. Ron. 1996. Oil bioremediation using insoluble nitrogen source. J. Biotechnol. 51:273-278.[CrossRef][Medline]
17 - Rosenberg, M., and E. Rosenberg. 1985. Bacterial adherence at the hydrocarbon-water interface. Oil Petrochem. Pollut. 2:155-162.[CrossRef]
18 - Sar, N., and E. Rosenberg. 1983. Emulsifier production by Acinetobacter calcoaceticus strains. Curr. Microbiol. 9:309-314.
19 - Shultz, A. C., P. Nygaard, and H. H. Saxild. 2001. Functional analysis of 14 genes that constitute the purine catabolic pathway in Bacillus subtilis and evidence for a novel regulon controlled by the PucR transcription activator. J. Bacteriol. 185:3293-3302.
20 - Vogels, G. D., and C. van der Drift. 1976. Degradation of purines and pyrimidines by microorganisms. Bacteriol. Rev. 40:402-469.
Applied and Environmental Microbiology, October 2003, p. 6337-6339, Vol. 69, No. 10
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.10.6337-6339.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.