Introduction
Water covers most of the planet Earth. In
aquatic environments, phytoplanctonic algae are
the main primary producers. Currently, with the
degree of degradation of these environments, the
use of algae and several of their attributes for
monitoring or evaluating environmental quality is
increasing and justified by the advantages that
these organisms present. However, one of the
major difficulties in the use of phytoplanctonic
algae is the fact that they present an immense
diversity of shapes and sizes, which makes
interspecific comparison difficult and often
inappropriate.
Knowledge of the structure of
phytoplankton communities is of great importance
in limnological studies, in order to understand the
dynamics of these communities and their
interactions with the abiotic environment, as well
as to allow the monitoring of environmental
conditions that can be inferred from attributes like
species composition and biomass (Vadrucci et al.,
2007; Fonseca et al., 2014). Whereas species
composition require floristic inventories and
taxonomic identification, biomass can be
evaluated more directly by an estimate of the
biovolume or cell volume, based on
measurements of linear dimensions and adaptation
of shapes to standard geometric models
(Hillebrand et al., 1999; Sun & Liu 2003; Saccà
2017). So it becomes possible to make
independent comparisons of shape or size.
Perhaps the simplest and most useful way to do
this is by an estimate of the biovolume, using
linear measurements according to the geometric
shape of organisms, which can be done with a
common microscope available in all laboratories
that deal with this question. For these calculations,
there are formulae, some complex enough that
may require precious time to calculate. But this
time would be saved by taking the measurements
and automating the biovolume calculations. These
biovolume measurements can be used according
to the objectives of each study, whether from the
population, specific or general point of view of
the whole group studied.
In general lines, calculation of the
biovolume involves taking measurements of linear
dimensions (e.g. length, width, diameter, height,
etc.) from cells of each species (in μm) and the
calculation of the volume of each cell, using a
geometric formula which better represents the cell
shape and calculation of mean cell volume for the
respective species (in μm3). The biovolume (in
mm3 L-1) per taxon and sample is calculated by
multiplying the mean cell volume (in μm3) of the
taxon by the number of counted cells (cells mL-1
or cells L-1). Assuming that the phytoplankton
cells have a density equivalent to that of water (1
mm3 L-1 = 1 mg L-1), then the biovolume (in mm3
L-1) of phytoplankton cells can be converted in
wet weight (in mg L-1) or carbon content (in mgC
L-1).
Several computer programs have been
developed to aid in the calculation of the
biovolume of phytoplanktonic or bacterial
samples, using automatic or semi-automatic
methods of image analysis (Fry & Davies, 1985;
Bjørnsen, 1986; Bloem et al., 1995; Blackburn et