It has long been known that diazotrophic cyanobacteria are
capable of fixing atmospheric nitrogen into biomass for their own nutrition,
conferring the advantage that they are free from dependence on dissolved
organic/inorganic nitrogen (DON and DIN) supplies. It is also known that this
process may contribute significantly to the amount of nitrogen available in an
environment. This study aimed to quantify the transfer of diazotrophic nitrogen
into an estuarine ecosystem during a summer bloom of Nodularia spumigena.
The relative contribution of diazotrophs to total nitrogen
input has already been shown to vary greatly between aquatic systems, dependent
on the trophic status of the ecosystem, as well as the seasonality, frequency
and size of algal blooms. Studies in lake systems have produced estimates
ranging from 6-82% of annual nitrogen input, whereas estuaries have been the
focus of fewer studies, with estimates range from 3-39% of annual nitrogen
input being fixed by diazotrophs. The conventional view is that diazotrophic
cyanobacteria are less successful in estuarine systems due to increased grazing
pressure from zooplankton and environmental stress.
The experimental method used in this study is promoted as a
more cost-effective way of estimating the diazotrophic nitrogen contribution to
an environment. The authors explain the expenses and limitations of the
mesocosm-scale incubation assays and the 15N labelled N2
tracers used in past studies, and endorse their own in-situ techniques as an
economically viable alternative. A comparison of stable nitrogen isotopes 15N
and 14N in pre- and post-bloom samples, together with measurements
of plankton abundance using chlorophyll fluorescence, among other techniques,
were used to ultimately determine diazotroph contribution.
These techniques generated a conservative estimate of
diazotrophic nitrogen flux of 146 tons, accounting for 177% of the total summer
nitrogen-load. The authors acknowledge the difficulties of placing this result
in the context of total annual nitrogen flux, yet by using data from a study
the previous year, they estimated a total annual nitrogen yield of 695 tons,
taking into account fluvial, atmospheric and diazotrophic sources. They
therefore state that this ‘back of the envelope calculation’ suggests
diazotrophic cyanobacteria are responsible for 22% of the annual total nitrogen
load.
However, it had been shown in a previous study that N. spumigena are un-grazed in the
estuary studied, so the results may offer limited inferences for other
estuarine systems where cyanobacteria are more heavily grazed, as well as
estuaries that experience less severe algal blooms. These limitations, along
with any sources of potential methodological error are acknowledged by the
authors.<>
Despite the differences between estuarine systems, the
result of 22% contribution to total nitrogen load by diazotrophs sits directly
central in the range of previous estimates. This study thus does not challenge
the conventional view in its field, its contribution is rather in its
suggestion that the experimental method used is the most cost effective
technique for further research in the field.
Woodland, R. J., & Cook, P. L. (2013). Using stable isotope ratios to estimate atmospheric nitrogen fixed by cyanobacteria at the ecosystem-scale.Ecological Applications.
The estimates given for annual nitrogen input by diazotrophs vary across enormous ranges. Do you think the reason for this is mostly due to variance in diazotroph success between aquatic systems, or more because of variance in their success between seasons?
ReplyDeleteThe great range shown in the estimates within each system is probably due to a large effect of the seasonality of algal blooms, as well as variance between the locations studied in those separate studies. In the paper the authors discuss the large differences seen between estuaries with different flow rates, for example, yet they are all still included in overall estuary estimate (3-39%).
ReplyDeleteThe 6-82% range in lake systems shows there is a huge impact of seasonality, and probably other factors too.
The difference in diazotrophic contribution between the lake systems and estuary systems is probably due to their relative success in each.