|
Journal of Culture Collections
National Bank for Industrial Microorganisms and Cell Cultures
ISSN: 1310-8360
Vol. 3, Num. 1, 2002, pp. 33-37
|
Journal of Culture Collections, Volume 3, 2000-2002, pp. 33-37 DIMETHYLTEREPHTHALATE
CATABOLISM BY PSEUDOMONAS SP.
Lilia
Tserovska1* and Rajcho Dimkov2
1National
Bank for Industrial Microorganisms and Cell Cultures, 1113 Sofia,P.O.Box
239, Bulgaria,
2The SofiaUniversity,
Biological Faculty, Department of Hydrobiology and Ichthyology, 8 "Dragan
Tzankov" st., 1421 Sofia, Bulgaria
Code Number: cc02004
Summary
Pseudomonas
sp. strain 054 isolated from polluted soil utilizes dimethylterephthalate
(DMT) as a sole carbon and energy source. The degradation of this compound
starts with a two-stage hydrolysis of the ester bonds to monomethylterephthalate
and terephthalic acid. In the meta-pathway for cleavage of the aromatic
ring the latter is metabolized to protocatechuate. The induction of the
ester hydrolysis is slightly specific, while the oxygenase mechanism is
induced by substrates with aromatic structure.
Introduction
The phthalates
and their derivatives are widely distributed and applied in various industrial
productions. At the same time they are among the first compounds included
in the list of the environmental pollutants [7]. This provokes big scientific
interest to their biological degradation [4, 8, 11, 18]. The catabolic schemes
of a number of phthalate derivatives have already been investigated [2, 9,
14]. However, the metabolism of the terephthalic acid (TA) and its esters
is considerably less studied. The dimethylterephthalate (DMT) is the main
row material for the production of the Bulgarian fiber Jambolen. In other
countries the textile fibers Lavsan, Terilen, Dacron, etc., are prepared
from the same monomer. Some bacteria from the genera Rhodococcus [19]
and Mycobacterium [15] and some fungi from the genus Aspergillus [6]
are found to degrade terephthalates.
In the
present paper the assimilation of DMT by Pseudomonas sp. strain 054
is discussed. The strain is isolated from polluted soil and adapted to utilize
this aromatic compound. The stages of the metabolism of the dimethyl ester
are investigated.
Materials
and Methods
Microorganism
and cultivation. The investigated microorganism Pseudomonas sp.
strain 054, was isolated from the soil by enrichment procedure [20]. The
culture was grown on a minimal salt medium supplemented with DMT in concentration
1000 mg/l as a sole carbon and energy source. The cultivation was performed
on a rotor shaker, 200 rpm, at 28oC for 4 days. The residual
substrate amount was colorimetrically determined [20]. The biomass was
estimated on the basis of the optical density and the dry mass [21].
Thin
layer chromatography (TLC). The intermediate products of the DMT degradation
were determined by TLC. The culture liquid (24th hour and 48th hour
of cultivation) was filtrated. Concentrated HCl was applied to acidify
the filtrate to pH 2. Ethylacetate was used for the extraction. The obtained
extract was dried over Na2SO4 for 24 hours. A rotary
evaporator was used for the solvent separation. The residue was applied
to a Kieselgel plate 60 F 254 in a system of solvents - benzene:dioxane:acetic
acid = 90:25:4 [4]. For detection of the spots UV absorption at 254 nm
was used.
Preparation
of the cell-free enzyme extract. The cell-free extract for the enzymological
investigation was harvested by centrifugation of the culture liquid (48th hour)
on Beckman centrifuge, 12 000 g for 10 min at 4oC. The received
biomass was washed twice with a buffer, pH 7.6. An ultrasound disintegrator
UD-20 was used for the cell disruption at 20 kHz for 2-3 min. The intact
cells and the cell debris were separated by centrifugation at 12 000 g
for 3 min at 4oC [5].
Determination
of the esterase activity. The esterase activity was assayed by a modified
method of Poutanen [16]. The enzyme sample (with 0.05 - 0.2 mg protein
content) and a-naphtylacetate in 50 mM citrate
buffer, pH 5.3, were incubated in a shaker for 15 hours at 26oC.
Than the absorption at l =
535 nm was measured. One esterase unit was defined as the amount of enzyme,
which produced 1 mM a-naphtole for 1 min under the standard assay conditions.
Determination
of the protocatechuate-4,5-dioxygenase activity. The enzyme activity
was determined spectrophotometrically by the method of Ono [17]. The reaction
mixture (3 ml) contained 1 mM protocatechuate, 150 mM TRIS-acetate buffer,
pH 9.0, and a suitable amount of the enzyme. The accumulation of the product
was measured at 410 nm. One unit of the enzyme activity was determined
as that amount which grades 1 mM protocatechuate
per 1 min at 24oC.
Determination
of the protein. Protein in the enzyme extract was determined by the
method of Lowry using bovine serum albumine as a standard [12].
Results
and Discussion
Pseudomonas sp.
strain 054 utilized DMT as a sole carbon and energy source. The degradation
of this aromatic compound and the bacterial growth are presented in Fig.
1. DMT was totally assimilated up to the 96th hour of the
culture growth. No residual amount of the substrate was detected after this
hour.
The intermediate
products, which were produced by the catabolism of the aromatic substrate,
were proved by thin layer chromatography. Two intermediate products were
detected for the both samples. The Rf-values of the spots 1 and 2 were identical
with those of the standard monomethylterephthalate (MMT) and .terephthalic
acid (Table 1). As an intermediate metabolic
product protocatechuate was not registered. These results made us suggest
that the initial steps of the metabolism of this aromatic substrate included
a two-stage hydrolysis through the monoester. A similar result was observed
for Rhodococcus by Slizen [19] and for Aspergillus niger by
Ganii [6]. Another result was reported by Kurane [10]. Nocardia erythropolis possessed
a much higher affinity of the phthalate-hydrolysing enzyme for the monoester.
It was rapidly hydrolysed to phthalic acid without accumulation of phthalate
monoester.
Table 1. Thin layer chromatography of
the products of degradation of DMT from Pseudomonas sp. strain 054.
Samples
|
Rf-values
|
|
Spot I
|
0.73
|
|
Spot II
|
0.53
|
Standards
|
|
|
DMT
|
0.82
|
|
MMT
|
0.73
|
|
TA
|
0.53
|
|
PC
|
0.41
|
For determination
of the esterase activity Pseudomonas sp. strain 054 was cultivated
on media with DMT, TA, succinate and tributyrin as sole carbon sources respectively.
The results are presented in Table 2. In all the cases enzyme activity was
observed which suggested that this enzyme was characterised by low substrate
specificity and constitutive synthesis. This was registered for Pseudomonas
fluorescens [1] and Micrococcus sp. strain 12 B [3]. In Nocardia the
phthalate-hydrolysing enzyme was isolated and purified by Kurane. It was
defined as a new type of lipase with broad substrate specificity [10]. This
enzyme had an inductive character as well as the DMT-esterase in Aspergillusniger [6].
We were
interested in the oxygenase activity of the tested strain Pseudomonas sp.
054. Cell-free extracts from cells growing on DMT, TA and succinate were
investigated for protocatechuate-4,5-dioxygenase activity. The obtained results
are shown in Table 2. The specific enzyme activity
of the cells, growing on DMT and TA was similar 2.45 and 1.98 U/mg protein
respectively. The cells growing on succinate did not show oxygenase activity.
This was an indication for the inductive synthesis of these types of enzymes.
This fact was confirmed by many authors for different aromatic compounds
[3,13,18]. Protocatechaute-3,4-dioxygenase activity was not registered. This
proved the suggestion that the assimilation of the compound was performed
by the meta-pathway cleavage of the aromatic ring.
Table 2. Esterase and protocatechuate-4,5-dioxygenase
activities of Pseudomonas sp. strain 054.
Growth substrate
|
Specific activity (U/mg protein)
|
Esterase
|
Protocatechuate-4,5‑dioxygenase
|
DMT
|
1.58 ± 0.011
|
2.453 ± 0.007
|
MMT
|
|
1.892 ± 0.003
|
TA
|
0.59 ± 0.005
|
|
Succinate
|
0.48 ± 0.010
|
0
|
Tributyrin
|
1.02 ± 0.008
|
|
In conclusion
we should underline that Pseudomonas sp. 054 showed high ability to
utilize DMT. For 96 hours it almost completely assimilated DMT in concentration
100 mg/l. Our investigation shows that the metabolism of this substrate starts
with hydrolysis to monomethylterephthalate and terephthalic acid. The aromatic
ring is decomposed in the meta-pathway. The esterase activity is a constitutive
property of the investigated strain while the oxygenase. activity is induced
by aromatic compounds.
References
- Chauret,
C., C. Mayfield, W. Inniss, 1995. Can. J.
Microbiol., 41, 54-63.
- Eaton,
R., D. Ribbons, 1982. Arch. Microbiol., 132, 185-188.
- Eaton,
R., D. Ribbons, 1982. J. Bacteriol., 151 (1), 48-57.
- Engelhardt,
G., P. Walnoffer, 1978. Appl. Envir. Microbiol., 35 (2), 243-346.
- Feist,
C., G. Hegeman, 1969. J. Bacteriol., 100 (2), 869-877.
- Ganji,
S., Ch. Karigar, B. Pujar, 1995. Bio-degradation, 6,
61-66.
- Ghisalba,
O., 1983. Experientia, 39 (11), 1247-1257.
- Keyser,
P., G. Pujare, R.W. Eaton, D.W. Ribbons, 1976. Envir. Health Perspect., 18,
159-166.
- Kurane,
R., T. Suzuki, Y. Takahara, 1980. Agric. Biol.
Chem., 44 (3), 523-527.
- Kurane,
R., T. Suzuki, S. Fukuoka, 1984. Appl. Microbol.
Biotechnol., 20, 378-383.
- Kurane,
R., 1986. Microbiol. Sci., 3 (3), 92-97.
- Lowry,
O., N. Rosenbrough, A. Farr, R. Randall, 1951. J. Biol. Chem., 193,
265-275.
- McClure,
N., W. Venables, 1986, J. Gen. Microbiol., 132, 2209-2218.
- Nakasawa,
T., E. Hayashi, 1978. Appl. Envir. Microbiol., 36 (2),
264-269.
- Naumova,
R., L. Usmanova, S. Zaripova, E. Officerov., 1986. Microbiol., 55 (2),
241-247.
- Poutanen,
K., M. Sundberg, 1988. Appl. Micro-biol.
Biotechnol., 28, 419-424.
- Ono,
K., M. Nosaki, O. Hayaishi, 1970. Biochem. And Biophys. Acta, 220,
224-238.
- Richter,
M., R.-M. Wittich, 1994, Biodegra-dation, 5, 63-69.
- Slizen,
Z., T. Zimenko, A. Samsonova, G. Volkova, 1989. Microbiologia, 58 (3),
382-386.
- Tserovska,
L., R. Dimkov, 1993. Acta Microbiol. Bulg., 30, 61-66.
- Tserovska,
L., R. Dimkov, Y. Topalova, 1995. J. Culture Collections, 1,
23-27.
Copyright 2002 - National Bank for Industrial Microorganisms and Cell Cultures
- Bulgaria
The following images related to this document are available:
Photo images
[cc02004f1.jpg]
|