In recent
years, the effects and microbial responses to oil spills have garnered much interest.
However, estimates suggest oil spills to be significantly less important than
chronic pollution. In marine sediments, acute polyaromatic hydrocarbon (PAH)
pollution has been shown to lead to a decrease in α-diversity, as
a result of the increase in hydrocarbonoclastic microbes. However, few studies
have focused on the repercussions of chronic pollution. In their paper,
Jeanbille et al. (2016) examined the effect of chronic PAH pollution in coastal
sediments in the North Atlantic and the Mediterranean Sea. The community
structures of Bacteria, Archaea and Eukarya were mapped across both the regional and the continental
scale. Moreover, the impact of sediment contamination by PAHs on predicted
prokaryotic metagenomic functions was also investigated.
The sediment
samples were collected from the top (1-2 cm) of the surface layer using a
sampling box corer at 46 sites across the North Atlantic and the Mediterranean
Sea. The sites were characterized by site observation and proximity to
potential PAH pollution as either PAH-contaminated or uncontaminated prior to
sampling. Predictions of metagenomic functions for Bacteria and Archaea were
made using the PICRUSt database.
The
analysis of the environmental data showed salinity to be correlated with
latitude. Average temperate, sediment particle size (PSD) and the percentage of
total organic carbon were also higher in the Mediterranean samples. In both
regions, the mean PAH concentration was significantly higher in the
contaminated sites. Nevertheless, the difference between contaminated and
uncontaminated sites was larger in the Mediterranean samples. In most sites
(44), the origin of the pollution was identified as being from combustion
processes while the remaining sites (14) were most likely contaminated from
both combustion and direct input.
The
variance in α-diversity was not significantly
explained by PAH abundance. Moreover, the differences in β-diversity were mainly influenced by habitat and PAH pollution didn’t
influence prokaryotic communities on a continental scale. Neither did the
analysis of predicted metagenomic function show differences in the abundance of
PAH degradation pathways between regions or Bacteria
and Archea.
In contrast
to acute pollution, the authors showed microbial communities were not impacted
by chronic pollution. In general, α-diversity is not indicative of
stress under chronic pollution as the increase in tolerant species can lead to
recovery. However, β-diversity differed on regional and
continental scale. Compared to environmental selection, PAH pollution had
little effect on microbial communities on a continental scale. On a smaller
scale, the influence of environmental selection was reduced and the range of
PAH concentrations was greater. Thus, the pollution had a greater impact on the
benthic communities. Nevertheless, the authors acknowledge most of the variance
to be unexplained. The divergence between continental and regional impact,
indicates that results may not generally be transferable across different spatial scales.
Furthermore, the changes in bacterial community did not affect predicted
metagenomic functions and therefore not influence fundamental ecological
processes.
Out of the
three domains, Eukarya were the most
influenced by the chronic pollution. Macro-Eukarya richness decreased, while Dinophyceae dominated contaminated
samples along with crenoarcheotic Archaea.
The authors suggest these phyla could serve as potential biomarkers for PAH
contamination.
In
conclusion, the coastal benthic communities seemed remarkably resilient to chronic
PAH pollution. However, the study could have benefited from more sample sites,
especially in the Eastern Mediterranean and the North Sea. Personally; I think
that the regional breakdown should have been finer in order to identify sites
that are particularly impacted. I would also be interested in the potential
repercussions additive effects of different pollutants (e.g. plastic) have on
the resilience of benthic microbial communities.
Reviewed Paper:
Jeanbille,
M., Gury, J., Duran, R., Tronczynski, J., Ghiglione, J. F., Agogué, H., ...
& Auguet, J. C. (2016). Chronic polyaromatic hydrocarbon (PAH)
contamination is a marginal driver for community diversity and prokaryotic
predicted functioning in coastal sediments. Frontiers in microbiology, 7. Link: http://journal.frontiersin.org/article/10.3389/fmicb.2016.01303/full
Hi Johanna,
ReplyDeleteYou talk about PAH pollution having little effect on a continental scale, is this possibly because these pollution events only happen on a small scale or due to a break down of the PAH? If you are interested, a paper by Readman et al. (1987) talk about modelling some of the possible pathways that determine the fate of the PAH such as microbial degradation, biosynthesis, and chemical oxidation.
Thanks,
Evan
References:
Readman J.W., Mantoura R.F.C. and Rhead M.M., (1987). A record of polycyclic aromatic hydrocarbon (PAH) pollution obtained from accreting sediments of the Tamar estuary, UK: evidence for non-equilibrium behaviour of PAH. Science of the Total Environment. 66. pp.73-94.
Hi Evan,
ReplyDeleteThanks for your comment. I would think that the effect on a continental scale is related to degradation and tolerance to high PAH levels rather than small-scale of pollution.
I wasn’t able to find any concrete data on the PAH discharge into the marine environment in Europe. However, elevated levels of PAHs have been found in the soft tissues of blue mussels near industrial and urban areas (Olenycz et al., 2015). So, these organisms would be continuously exposed to PAH originating from combustion of organic matter. Also, I don’t think you would be able to find large areas of the European coast that aren’t near industrial and urban areas and thus unexposed to PAHs.
In their paper, Jeanbille et al. mention that PAH might be used as a carbon source by bacteria but don’t elaborate further on specific species or metabolic pathways. Species might also be replaced by species that are more tolerant to elevated PAH levels. Additionally, it has been shown that PAHs can be absorbed into the sediments at which point they become biologically unavailable (Kraaij et al., 2002). Jeanbille et al. also mention this in their paper but I didn’t think to include it in my review, which I now see I probably should have done.
I hope this answers your question at least in some way,
Johanna
Reference:
Kraaij, R., Seinen, W., Tolls, J., Cornelissen, G., & Belfroid, A. C. (2002). Direct evidence of sequestration in sediments affecting the bioavailability of hydrophobic organic chemicals to benthic deposit-feeders. Environmental science & technology, 36(16), 3525-3529. Link: http://pubs.acs.org/doi/abs/10.1021/es0102787
Olenycz, M., Sokołowski, A., Niewińska, A., Wołowicz, M., Namieśnik, J., Hummel, H., & Jansen, J. (2015). Comparison of PCBs and PAHs levels in European coastal waters using mussels from the Mytilus edulis complex as biomonitors. Oceanologia, 57(2), 196-211. Link: http://www.sciencedirect.com/science/article/pii/S0078323415000378