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Actinomycetes
University of Udine, Mycology Department
ISSN: 0732-0574
Vol. 1, Num. 3, 1990, pp. 75-78
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Actinomycetes, 1990 Vol. 1, Part 3, p75-78
Streptomycetes Of Sandy Biotopes At Various Stages Of
Natural Overgrowth
K.I.ANDREYUK, H.V.VALAGUROVA and K.A.MYATLIKOVA
Institute of Microbiology and Virology, Kiev, USSR
Code Number: AC90011
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Abstract.
Members of the genus Streptomyces play an important
role in the contamination of lifeless sandy substrates. This
is the result not only of their mycelial structure but also of
their high ecological plasticity. Streptomycetes are
characterized by a wide range of trophical abilities that
permit them to adapt to various conditions of the environment
and at the same time influence it. The ability of
streptomycetes to synthesize biologically active compounds
including antibiotics, vitamins and other metabolites permits
them to serve as a factor regulating the composition of the
microbial community at various stages of the primary
succession of microbial coenosis.
Sands and sandy soils are wide spread in soil-climatic
zones. On the banks of deep-water rivers even at present one
can see the plots of flood-lands typical of the primary stages
of soil formation.
Various microorganisms (Mycobacterium, Pseudomonas,
Arthrobacter, Fungi) take an active part in the
transformation of parent rock. There is insufficient
information about streptomycetes (Sushkina and Gael, 1975;
Avakyan et al., 1981; Forster et al., 1981;
Parinkina, 1985).
The aim of this work was to study the streptomycete flora
in sandy biotopes undergoing the various stages of natural
overgrowth.
Materials And Methods
Samples. Samples of sandy substrates were collected
at depths of 0-2 and 2-20 cm in plots with the successive
ranges: 1) sand without vegetation; 2) sand partly covered
with algae; 3) sand partly covered with moss-lichen
associations; 4) primitive sandy soil under meadow
phytocoenosis.
Isolation and counting of streptomycetes.
Streptomycetes were isolated by spreading samples (water
suspension 1:1,000,000) on solid nutrient media: peptone-beef
agar for the forms utilizing organic nitrogen; starch-ammonium
agar for the forms assimilating mineral nitrogen; water agar
("starvation-agar") and Eshby medium for oligotrophic forms;
cellulose medium for cellulose-destroyers. The plates were
incubated at 28 C for 7-10 days before the colonies were
counted. Subcultures were made and checked for purity.
Qualitative study of isolates. Isolates were placed
in series from the results of morphological observations and
properties exhibited in the tests and media proposed by
Shirling and Gottlieb (1966).
Streptomycetes influence on bacterial cultures. The
influence of streptomycetes on the growth of a bacterial test-
culture was determined by the block method (Gause et al.,
1957). The most frequently occurring spore-forming
bacterium, Bacillus sp., was used as the test-culture.
The number of streptomycetes (antagonists and stimulators) was
calculated as follows. A thin layer of peptone-beef agar,
containing the test-culture cells, was poured into agar plates
containing streptomycete colonies and then incubated for 2
days at 28 C. The amount of antagonistic and stimulating
streptomycetes was estimated respectively from the number of
zones without growth or with abundant growth.
Results And Discussion
Number and diversity of streptomycetes. The
increase in amounts of microorganisms and the intensification
of microbiological processes goes from lifeless sand to
primary meadow soil through intermediate stages in the
examined range of biotopes (Andreyuk et al., 1989).
Members of the genus Streptomyces were found to be
very abundant in sandy substrates. From 14,000 to 6,000,000
million units were counted per gram of substrate (Table 1). As
can be seen from this table the number of streptomycetes is
rather variable and possibly depends on factors including
season of the year, biotope property and depth of sample.
It is known that streptomycetes can assimilate various
compounds due to their strong enzymatic system. The microbial
communities of the examined biotopes, which are poor in
nutrients, contained sufficient amounts of various compounds,
simple and complex, for the streptomycetes to utilize (Table
2).
Table 1. Streptomycetes (10^3/g) in sandy biotopes.
Biotopes Layer May August November
(cm)
----------------------------------------------------------
Sand without vegetation 0-20 14.3 ND 127.6
Algal association 0-2 50.0 197.0 78.3
2-2 447.8 670.0 44.3
Moss-lichen association 0-2 170.4 277.0 63.0
2-20 60.1 113.0 200.0
Meadow phytocoenosis 0-2 6787.2 2411.7 6660.0
2-20 4159.4 4344.0 2700.0
Table 2. Streptomycetes (10^3/g and percentages) in microbial
communities with different nutritional requirements.
Biotopes Organic Mineral Nitrogen Carbon Cellulose
Nitrogen Nitrogen (minimal) (minimal)
--------------------------------------------------------------
Sand without
vegetation 25.2 47.3 76.5 72.7 0.03
(24.9) (17.3) (14.7) (21.6) (5.0)
Algal
association 79.4 359.4 299.8 192.5 7.6
(42.9) (61.6) (46.3) (38.3) (97.0)
Moss-lichen
association 7.6 128.9 20.8 151.4 15.1
(1.7) (21.5) (3.7) (18.4) (68.3)
Meadow
phytocoenosis 216.6 4510.4 1686.0 3300.0 6.1
(3.9) (21.5) (7.7) (9.6) (32.8)
Primary producers selectively effect the development of
the various microorganisms during the transformation of the
surroundings. Algae, moss, lichens and grasses in the range of
ecological biotopes examined serve as environment-builders.
A biotope in which algae serve as the edificator attracted
our attention. The specific weight of streptomycetes in
various trophical groups of microorganisms was quite high and
reached 97% in the community of cellulose destroyers.
Streptomycete contents in the next biotopes were less.
The discovery of streptomycetes with various trophical
abilities at all stages of primary plant succession on
alluvial sands shows the considerable role of these
microorganisms in inhabiting sandy substrates. At the same
time the diversity of streptomycete flora was small. The
representatives were from no more than three series - White,
Gray and Red.
The forms related to the Red series were found to be
numerically dominant in the streptomycete community of sand
without plants. The representatives of white streptomycetes
(White series) prevailed in sandy substrate under algae; the
members of the Red series were present in small amounts. Under
a moss-lichen association streptomycetes were represented by
forms with gray mycelium (Gray series) and minute amounts of
red forms. The streptomycete flora under meadow vegetation was
composed of forms of the White and Gray series.
Table 3. Influence of streptomycetes on culture
growth. (* + = stimulation, - = inhibition, 0 = no effect.
Average of five experiments).
No. Radius
Series (mm)*
-------------------
Gray 1 +4.0
4 +3.0
12 0
14 -1.0
18 +4.0
19 0
29 +5.0
32 +5.0
35 -6.0
39 +4.0
45 -1.0
White 7 0
8 -2.0
10 +5.0
23 -7.0
Red 25 0
27 -2.0
28 -3.0
31 0
33 -1.0
Role of streptomycetes in communities. On the basis
of streptomycete specific weight in microbial communities
forming in the examined biotopes, it is possible to assume
that these microorganisms are not just involved in substrate
consumption (Table 2).Because of the potential capacity of
streptomycetes and in particular of their ability to form
various biological active compounds (Krassilnikov, 1950;
Waksman, 1962; Andreyuk et al., 1974), one may suppose
that they can exert some influence on other components of the
newly forming microbial coenosis, for example on bacteria.
Twenty isolates of streptomycetes were tested for their
activity against one of the most frequently occurring
organism, Bacillus sp. (Table 3). Different effects
were exerted by streptomycetes on the Bacillus.
Parallel with the inhibition of the test-culture, also
growth intensification was observed and in same cases a
neutral reaction.
The data obtained on streptomycetes, inhibitors and
stimulators, in the community assimilating mineral nitrogen
are presented in Table 4. In sands without vegetation the
streptomycete flora consisted of equal quantities of
stimulators and antagonists, as regards Bacillus sp. A
possible explanation of this fact could be that at this stage
of organization the microorganism community is represented by
casual microorganisms with unstable relations.
Table 4. Streptomycetes inhibitors and stimulators of
Bacillus sp. in communities utilizing mineral nitrogen
(10^3/g and percentages)
Biotopes Inhibitors Stimulators Ratio
----------------------------------------------------
Sand without 5.6 5.6 1:1
vegetation (50.0) (50.0)
Algal association 103.2 36.7 2.8:1
(73.8) (26.2)
Moss-lichen 16.6 56.6 0.6:1
association (38.4) (61.6)
Meadow 506.6 2465.0 0.2:1
phytocoenosis (17.0) (83.0)
There were three times more antagonists than stimulators
in the biotope with algae. In the moss-lichen biotope and in
the meadow phytocoenosis this ratio was shifted towards
increasing numbers of stimulator streptomycetes.
The results obtained are in accordance with the known
state of general ecology (Odum, 1975; Rabotnov, 1983). There
is a prevalence of competition and rivalry for nutritional
sources in the pioneer organisms associations; during
ecosystem formation such relations change to mutual aid and
cooperation.
Thus as the biotope structure becomes more complicated by
natural overgrowings of flood-lands, there is an accompanying
change in qualitative streptomycete composition: the increase
in the number of forms stimulating bacterial growth. The role
of streptomycetes in examined biotopes is not limited by their
reducing functions. They also play a role as regulating
factors in the formation of microbial coenosis. The decrease
in antagonistic streptomycetes numbers owing to the increase
in stimulators shows the formation of microbial coenosis in
the range of biotopes "sand without vegetation ---> algal
synusia ---> moss-lichen association ---> meadow
phytocoenosis".
Acknowledgments.
The authors acknowledge the assistance Mrs. Galina A.
Tkacheva for technical help.
References
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E.S.Gumenko & G.A. Tkacheva (1989). Microbial communities of
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Wilkins Co., Baltimore, vol. 3.
Copyright 1990 C.E.T.A., The International Centre for
Theoretical and Applied Ecology, Gorizia
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