It has only been in the last 20 years that the idea of
microbes forming colonies on surfaces in shallow, intertidal and deeper waters,
has come to light. But now we are faced with exciting research showing the
complex nature of microbial mats and how their diversity and interactions with
the microhabitat around them are formed. These delicate systems are placed
under many pressures everyday such as light, nutrient and oxygen availability. Preisner
et al looked into microbial mats and how taxa within these diverse systems can
provide stable biological reservoirs that are influenced by environmental
stressors such as salinity brought on by natural disasters, in this instance,
Hurrican Irene which hit the coast at the end of August 2011. Microbial mats
can arguably have some of the highest diversity which, these in turn, influences
foundations of ecological processes so any additional stressors should be
recognised and taken into account when understanding these delicate microbial
ecological interactions. Much of the greatest diversity is within low abundance
taxa, which this study takes into account. While much of the biomass of
microbial mats is common within a few dominant taxa, both the dominant and
‘rare’ taxas show different activity levels within environmental pressures.
The paper studied a microbial mat on San Salvador Island in
the Bahamas on August 1st-2nd in 2011 (Pre Hurricane
Irene) and again on August 1st – 2nd in 2012 (Post
Hurricane Irene). This microbial mat consisted of well-defined layers, which as
we understand from general knowledge of microbial mats, can have steep
gradients of oxygen, light and sulfide availability. These gradients were taken
into account to an extent in this paper, however it is not the primary focus.
Post disturbance the reduction in salinity showed that
general community composition was not affected significantly diurnally however
general archaea decreased from 57% to 33% and Bacteria increased from 43% to
67%. Most taxa showed low activity across conditions but activity levels in
general did increase after disturbance. This highlights how these communities
are sensitive to environmental change. Pre-disturbance showed to favour
Halobacteria as they are shown to thrive in lower salinities, Halobacteria held
48% of the community biomass predisturnbance however these results were
favouring towards one OTU halobacteriaceae. Halobacteriaceae are defined by
their halophilic nature and are abundant in hypersaline conditions. Post
disturbance showed abundance and activity decrease in Halobacteria from 48% to
31%, however abundance and activity increased in Proteobacteria, Cyanobacteria,
Thermoplasmata, Thaumarchaeota and Crenarchaeota.
Cyanobacteria are known to be tolerant of a range of
salinities however results did show a decrease in its nitrogen fixating
abilities. Cyanobacteria are important for the formation of microbial mats,
filamentous Cyanobacteria such as Phormidium are dominant members in the mats
and although not mentioned in this paper, it is important to remember the
interaction of this microorganism with microbial mats so when disturbance
occurs we can understand any impacts it will have on healthy mats.
The sample site chosen is often disturbed by natural
disasters like hurricanes, so is therefore used to environmental pressures such
as wide ranges of salinity, high irradiance and high temperatures. This study
site does seem ideal for studying larger communities of microbial diversity in
relation to salinity, however it does suggest that these communities are
already well adapted to cope with pressures, therefore it would be interesting
to see the diversity and activity rates in communities in other, less
pressurised areas.
Paper reviewed: Preisner,
E. C., Fichot, E. B., & Norman, R. S. (2016). Microbial Mat Functional and
Compositional Sensitivity to Environmental Disturbance. bioRxiv, 063370. http://www.biorxiv.org/content/biorxiv/early/2016/07/12/063370.full.pdf
Hi Elle, had never thought about the impacts of ntural disasters on the microbial communities other than possible human vectors like Vibrio cholerae. It seemed this study looked quite heavily towards the salinity factors but did they mention anything about other water quality adjustments such as lower dissolved oxygen due to the addition of anthropoegeic organic matter such as sewage or the increase of light attenuation.
ReplyDeleteFinally did they mention anything about the estimated recovery of the area and how the long term effects will impact the ecology of the impacted area?
Thanks,
Stefan
Hi Stefan,
DeleteNo, the paper did not mention looking into other water quality aspects, which i agree would definitely be a really good next step, especially when looking to the future as these natural disasters may become more frequent. I did find this paper however, which although is not marine I found it interesting and thought perhaps the key points could be brought across to our understanding of mats in the marine environment. Abed et al (2014) looked into mats in a freshwater wetland that had been used for redirected oil-polluted water run off. They found that the average number of OTUs were lower with higher oil level, and these microhabitats were heavily influenced by the increase of temperature, dissolved oxygen and sulfate concentrations. I understand this to show that these systems are heavily influenced by these environmental changes, whether it be a natural disaster like Hurricane Irene, or pollutant run off, changes to their delicate balance could have detrimental effects for communities within the mats. (i've cited the paper below if you wanted to have a read!)
And, to answer your second question, no sadly they did not seem to mention anything about the recovery time or long term effects on the area, however they did say there are papers currently underway to look at the ecological impacts discussed in this paper. They haven't mentioned if by the same authors or even when (this paper was published July, 2016) so i guess its a watch this space situation.
Thanks for your questions :)
Ellie
Oops sorry! Forgot to attach the citation...
DeleteAbed RMM, Al-Kharusi S, Prigent S, Headley T (2014) Diversity, Distribution and Hydrocarbon Biodegradation Capabilities of Microbial Communities in Oil-Contaminated Cyanobacterial Mats from a Constructed Wetland. PLoS ONE 9(12): e114570. doi:10.1371/journal.pone.0114570
http://journals.plos.org/plosone/article?id=10.1371/journal.pone.0114570
Hi Elle,
ReplyDeleteGreat post! You mentioned possible further research in comparing highly-impacted areas with less impacted areas. This reminded me of the shifting baseline syndrome which we discussed in Marine Ecology.
Thanks for bringing the topic to our attention!
Johanna
Hi Johanna,
DeleteOh yeah! I hadn't even thought of it like that - so you mean as the area gets more 'used' to natural disasters, it is regarded there as the norm, yet for other parts of the world or previous generations in that area, microbial mats would not be subject to this kind of pressure. So it is a changing in perception of microbial mats and what their normal conditions are.
Have i got this right? - Cool thought, thank you Johanna!
Ellie
Hi Elle,
ReplyDeleteAs Stefan mentioned i am interested in how other environmental factors effect the abundance of the specific microorganisms, as well as salinity.
You mentioned that the nitrogen fixing ability of the cyanobacteria decreases post disturbance, i was interested if there is any reasoning why this occurs?
Finally i find this paper very interesting as it begins to simply monitor the changes in abundances and biomass of microorganisms in response to natural disturbances, an feat that has already been done many times in the marine realm with marine mammals, fish and invertebrates. I feel that this may be a way forward in terms of fully understanding microorganisms and microbial mats.
Thanks
Natasha
Hi Natasha,
DeleteYes sorry to say that they did not take other environmental factors into account, however as you can see from my reply to Stefan, there do seem to be similar studies underway currently, so perhaps we will be able to understand more sooner rather than later.
As for your second question, i found it a little harder to answer as they did not seem to make one conclusion about why N2 fixing abilities decreased in cyanobacteria with the increasing saline conditions. They did refer to a paper by Pinckney et al from 1995, who suggested that extreme saline conditions can repress N2 fixing capabilities in cyanobacteria, even though Nitrogen fixing potential was present. They did not seem to expand on that point much more.
However, the paper (Priesner et al, 2016) discussed how cyanobacteria have been shown to have a range of salt tolerance and this can result in salinity specialisation and opportunities to exploit different niches from individual OTUs. It was also discussed that cyanobacteria held 7% of pre-disturbance bacterial communities but after salinity decreased, this rose to 14%. All of this suggests to me, that perhaps it is not the issue of cyanobacteria being unable to fix due to salinity, but it may be the reduction in particular OTUs and their Nitrogen fixing abilities.
I'm glad you enjoyed the blog, and I hope this has helped to answer your question without me jumping the gun, if you have any other insights that i may have overlooked please do write back.
Thanks,
Ellie
Pinckney J, Paerla HW, Beboutb BM. (1995). Salinity control of benthic microbial mat community
production in a Bahamian hypersaline lagoon. 187: 223–237