Hydrocarbons naturally enter the
marine environment at cold seeps along continental shelves. Natural seeps are
sporadic and can be diffuse or intense. The Gulf of Mexico is one of the most
oil rich basins in the world, the 2010 Macondo blow out leaked 15 times more
oil and gas than the Gulfs natural seeps. Microbial hydrocarbon degraders in
marine environments (e.g. Alcanivorax
spp. and Marinobacter spp.) work
together to acts as a metabolic network: primary oil degraders produce
surfactants to emulsify oil, secondary consumers intercept intermediate
molecules (e.g. alcohols and alkenes) increasing molecules bioavailability to
other organisms. This slick led to unprecedented changes in the marine
environment and microbial populations. This review paper explores microbial
responses to the deep water oil plume, surface slicks and sediment composition
changes.
Native microorganisms responded
rapidly until limited by environmental factors; increased archaea changed
nitrifying microorganism community structure. During the lifetime of the oil
plume the deep water bacterial community shifted and hydrocarbon degradation
gene presence increased. 16s PCR showed the blow out caused gammaproteobacteria
alkane degraders Oceanspirillales to dominate,
between 2 and 4 weeks later communities shifted to mostly PAH degraders, Cycloclasticus and Colwellia. After 6 months, communities near the well head diversified
to include alkane, PAH and methyl degraders (Methtlophilacaea, Methylococcaceae and Methylophaga). Despite the blowout being offshore and the majority
of hydrocarbons being weathered before reaching coastal waters oil
contamination on beaches affected microbial communities in a similar way to
those in deep water. Oil contaminated sands contained up to 4 times the
microbes in clean sands and followed similar assemblage changes to the deep
water. Taxonomic diversity decreased in response to the pollution but rebounded
a year later.
Sediments significantly changed,
within a few weeks large aggregations of marine snow were observed which sunk
and settled on the sea floor. Laboratory experiments showed the huge
aggregations were due to increased cell densities, activities of carbohydrate
degrading enzymes with the entrapment of oil droplets in an extensive matrix of
polysaccharides characteristic of aromatics and alkane reducing bacteria. When
deposited, aerobic oil degrading communities on the detritus were gradually
replaced by anaerobic decomposers. 8 months after the spill the top 2cm of
sediments local to the well showed 10-20% less organic carbon and nitrogen
compared to underlying sediment nutrients are likely to have been consumed by
pelagic and benthic microbiota.
This review article exploits a
unique situation to link studies and build a view of microbial effects and
habitats. In addition, lapses in knowledge can be identified: oil and gas are
rarely accurately measured in the marine environment making it difficult to
quantify oil degradation; marine snow provides a net to capture oil droplets,
but we need to investigate what happens to them in the water column and on the
seabed further; microbes are known to break down many hydrocarbon compounds
(e.g. alkanes, PAHs, methane) but we need to quantify and assess more
persistent compounds (e.g. tar).
Joye, S. B., Teske, A. P., Kostka,
J. E. (2014) Microbial Dynamics Following the Macondo Oil Well Blowout across
Gulf of Mexico Environments. BioScience.
64 (9): 766-777. http://bioscience.oxfordjournals.org/content/64/9/766.full
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