Saturday 19 November 2016

How chronic PAH pollution impacts coastal benthic communties



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

2 comments:

  1. Hi Johanna,

    You 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.

    ReplyDelete
  2. Hi Evan,

    Thanks 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

    ReplyDelete

Comments from external users are moderated before posting.

Note: only a member of this blog may post a comment.