Petroleum
is a very complex chemical containging thousands of hydrocarbon molecules. In
the ocean, sediments are the natural sinks of these chemicals. However, in cold
environments, petrol can be very persistent causing both short and long-term
ecological effects. As oil exploration is becoming more common at higher
latitudes it is important to increase our knowledge of cold-environment bioremediation
microbes. Bioredemdiation is complex process in itself, involving various
microbial organisms. However, particularly in sediments, our understanding of
this pathway is disadvantaged as the biodiversity and heterogeneity of the
habitat increases its complexity. Most bioremediation work has made significant
advances in the both the tropical and
temperate environments. Saturated hydrocarbons include alkanes, branched
alkanes and cycloalkanes; and pose the highest proportion in crude oil. Some previous work has suggested that adding
alkanes to environments polluted with other, less degradable chemicals my
increase the break-down of these persistent substances. There are a surprising
number of microbes that use alkanes as a carbon-source including Alcanivorax, Thalassiolituus, Oleiphilus
and Oleispira. These organisms contain
various alkane-activating enzymes known as alkB.
It has been suggeste that alkB be used as biomarkers for the
characterization of aerobic alkane-degrading bacterial populations.
This
work studies the alkane-degrading genes and bacterial communities of Ushuaia
Bay, South America; described as a chronically polluted environment where
off-loading of petroleum is a daily occurrence.
Sediment
samples were collected via coring along the low-tide line and at a depth of 11m.
These were then stored at -80°C. There were three different treatments of the
original sample (OR08). These were the sediment with added 0.46ml of crude oil
(expOR08-O), the sediment with added crude oil, ammonium chloride and sodium
phosphate (expOR08-ON) and finally, the control sediment (expOR08-c). In order
to fully analyse the hydrocarbons, samples were extracted and treated with
activated copper and evaporated until 0.2ml was reached. This was loaded into a
alumina column to recover the aliphatic and aromatic fractions. Individual alkane
(from n-C10 to n-C35) concentrations, Pristine and Phytane isoprenoid levels,
total resolved alkanes and total aliphatic hydrocarbons were calculated for
each sample.
DNA
was also extracted from each sample using a FastDNA SPIN kit. Two DNA
extractions were conducted per sample. The
alkB gene fragments were then amplified using specific primers, these were
cleaned, cloned and sequenced. The V4 hypervaribale region of the 16S rRNA was
amplified using pyrosequencing and used to construct alkB gene libraries. The alkB
sequences were screened against the GenBank database using BLAST.
Alpha-diversity was calculated using OTU (operational taxanomic unit) analysis.
All
sample collected from the bay were seen to contain alkane homologous series,
isoprenoids pristine, isoprenoid phytane and unresolved complex mixtures.
Biodegradation indices showed that biodegradation was an on-going process. A
total of 30 OTUs were found and were estimated to cover 95% of the overall alkB gene diversity. Richness was found
to be 39-48 OTUs but this was described as a conserved estimate. Groups found
relating to alkB were mainly Proteobacteria. The most closely related
(and the most common OUT) to alkB were
deemed as uncultured microorganisms from cold marine sediments.
After
20 days expOR08-O showed a decease in the concentration of alkanes lower than
C20. However expOR08-ON showed further degradation of alkanes.
5
alkB gene OTUs were present in expOR08-O, 4 of which were also present in the
environmental samples taken; the most abundant in this treatment was most
closely related to Actinobacteria
however there were also Gammaproteobacteria.
expOR08-ON showed only two OTUs; Kordiimonas
gwangyangensis and Rhodococcus spp.
A
total of 44,380 reads were obtained from the V hypervariblae region that could
be amplified from the three treatments expOR08-O, expOR08-ON, expOR08-c and the
environmental samples. All OR slurries showed high richness and low dominance
values. Although the expOR08-c was 38% lower than the environmental sediments
(attributed to the laboratory conditions), expOR08-O had a lower richness value
still and the expOR08-ON was the most simplified.
The
authors goes on to explain that this study indicates a high diversity of alkB genes in highly polluted areas.
They say that this was consistent over time and space suggesting an ecological
relevance to the microbial communities of the sub-Antarctic sediments. The
closest matches to the alkB gene sequences
were from uncultured microbes suggesting further study in this area. It is
explained that different components such as the type of pollution present
factors into the communities present at a site. It is hinted that more studies
need to be conducted into various environmental factors and as to how these may
affect the population dynamics. As the addition of crude oil to the samples
resulted in faster degradation of the alkanes. Although these results are still
considered controversial. Previous studies have before suggested that the alkB-carrying microbes are positively correlated
to alkane concentration however, other studies have debunked this. However this
paper the presence of oil results in a strong amplification of alkB genes. This helps to take the first
steps toward using alkB genes as
biomarkers
Guibert
L.M, Loviso C.L, Marcos M.S, Commendatore M.G, Dionisi H.M & Lozada M.
2012. Alkane Biodegradation Genes from Chronically Polluted Subantarctic
Coastal Sediments and Their Shifts in Response to Oil Exposure, Microb. Ecol. 64: 605-616.
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