Accumulation and transformation of tellurite (TeO32−)
by a species of Fusarium and Penicillium citrinum was
examined using both
solid and liquid Czapek Dox medium. In liquid medium, tellurite partitioned
into soluble
and insoluble species, and in tellurite-containing (1 mM) liquid
medium
at pH 6, approx. 60% of added tellurite precipitated after 48 h. Experiments
showed that in liquid
medium containing 1 mM sodium tellurite, the Fusarium
sp.
accumulated a maximum of ∼0·6 μmol Te (mg D.W.)−1
after 48 h. P. citrinum accumulated a much lower amount of tellurium,
∼0·07 μmol (mg D.W.)−1
falling to <0·02 μmol (mg D.W.)−1
after 48 h. Both
organisms showed marked differences in the pattern of pH change of the
medium, with the pH increasing during growth of the
Fusarium sp. in 1 mM tellurite to ∼pH 6·7
after
2 wk. In contrast, the pH decreased during growth of P. citrinum
in 1 mM tellurite,
to a level of ∼pH 2·7 after 2 wk. On agar medium, test
fungi exhibited tolerance to high levels of tellurite (up to 100 mM
Na2TeO3) and this was associated with blackening
of
the growing colonies as well as the surrounding agar. TEM revealed the
deposition of large black granules, apparently in vacuoles, which
corresponded with the reduction of tellurite to amorphous
elemental tellurium. Precipitation of amorphous tellurium on
and around the biomass was also observed and confirmed by energy-dispersive
X-ray microprobe analysis. In addition to the reductive transformation
of
tellurite, Fusarium sp. also displayed
transformation of tellurite into a volatile form. The production of volatile
tellurium by Fusarium sp. occurred over the whole growth
period and amounted to an average value of 7·8 μmol Te
(∼0·16%) from 51 growth medium with an initial concentration
of
1 mM Na2TeO3. Although P. citrinum
also transformed tellurite to elemental tellurium, volatilization of
tellurium was not detected. It
is concluded that different mechanisms of tellurium transformation are
species-dependent and can be influenced by physico-chemical
changes in the medium, e.g. pH, which can affect tellurium
speciation into soluble and insoluble forms and bioaccumulation. In view
of the extremely small amounts of Te volatilized by the Fusarium
sp., this process cannot be considered to be an important
detoxification mechanism.