Aims: Study of
processes of degradation of spent mineral, semisynthetic and synthetic motor
oils by selected hydrocarbon-oxidizing microorganisms and selection of
sorbents contributing to the optimization of processes of decontamination of
natural and wastewater from these types of pollutants.
Study Design: Studies were conducted on controlled
biodegradation with mineral, semi-synthetic and synthetic lubricating oils with
a consortium of nine types of hydrocarbons oxidizing microorganisms (HOM), in
concentrations with initial contamination of 90 ± 6, 400 ± 6 and 1000 ± 6
mg/dm3 per 400 cm3 of runoff under statistical conditions at temperatures from
+16 to +29 °C. The growth in the number of microorganisms was within 304 • 106
– 306 • 106 cl/cm3 (with continuous cleaning mode – in 14 days). Also, in the
experiment on the biodegradation of lubricating oils, HOM sorbing materials
were used: river sand, coal powder, polyethylene chips, crushed Tetra Pak,
sawdust and peat (natural sizes), husks (buckwheat, barley, wheat and oats)
with particle sizes - 0.017; 0.034; 0.07 and 0.1 mm. Their concentration was
(depending on the test series) 10, 20, 30, 40, 50 and up to 100 mg/dm3.
Methodology: Nine main bacterial strains, together with
various sorbents isolated from various industrial sewers, were used for the
biodegradation of natural and wastewater that were contaminated with spent
mineral, semi-synthetic and synthetic lubricating oils. Microorganisms from
environmental objects were isolated by direct seeding and by the method of
cumulative cultures. For comparison, different cultures of Alcaligenes (1 species), Micrococcus
(1 species), Brevibacterium (2
species), Bacillus (1 species), Flavobacterium (1 species), Clostridium (1 species) and Pseudomonas (2 species), which are part
of the oil- and oil-destroying microbiological consortium, were used.
Microorganisms are united in consortia according to
morphological, physiological and biochemical properties and are represented by
both gram-positive and gram-negative, mobile and stationary aerobic and
facultative anaerobic forms. The physiological activity of the strains is
variable, and their enzymatic activity is high.
The degree of biotransformation of wastewater was assessed
by the dynamics of chemical oxygen consumption (COC), biological oxygen
consumption (BOC5) and dissolved oxygen (O2) in the process of biodegradation
of wastewater pollution by chemical methods.
Results: In the presence of sorbents (husks of grain crops)
with microorganisms involved in the purification of water from transformer oil,
the process of habituation was revealed in the interval from 1 to 3 days of
contact and diesel oil, respectively, up to 3 days. At the same time, the
increase in the number of transformer oil reaches 10-12 times in the variant
with buckwheat and oat husks, and up to 18 times in the presence of barley
husks in water, and the increase in the number of diesel oil reaches 2-3 times
in the variants with wheat and barley husks.
According to the dynamics, the increase in the number of HOM
in semi-synthetic oil in the presence of grain husks reduces pollution in
concentrations from 50 mg/dm3 and reaches 55.0 - 63.7% by 6-9 days. The
proportion of mineral oils subject to biodegradation of HOM, in the same
period, exceeds more than 30%. The overall cleansing effect in the variants
with oat husks reaches 90.6%, barley 92.2%, and buckwheat and wheat 93.7 -
93.8%. Whereas the efficiency of water purification from used lubricating oils
in the presence of river sand, polyethylene shavings, grasses, coal powder and
peat remained at or below the levels observed under the influence of HOM.
Conclusion: In the biodegradation of natural and wastewater
from oil pollution, sorbents can be used through optimization with HOM, leading
to the achievement of the maximum permissible standard for water purification
from used lubricating oils. Thus, we recommend the controlled use of sorbents
of grain crops, such as oat husks, wheat, barley and buckwheat (particle size
0.017-0.034 mm with a concentration of 50 mg/dm3) together with HOM (up to 350
• 106 kl/cm3).
Author(s) Details
Ganiev I.M.
Kazan (Volga Region) Federal University (KFU) and Federal Center for
Toxicological, Radiation and Biological Safety (FSBSI «FCTRBS-ARRVI»), Russia.
Please see the book
here:- https://doi.org/10.9734/bpi/ibs/v9/834
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