Metal and metal oxide nanoparticles present a series of challenges
for terrestrial ecotoxicology. Chemical transformations of the nanoparticle
may modify the exposure of organisms to nanoparticles. Additionally, the
chemistry of the soil itself may influence exposure, for example by promoting
particle aggregation or dissolution. Within the TINE project, we aim
to develop models to take account of these processes, based on sublethal
exposures of zinc oxide (ZnO) and silver (Ag) particles to the earthworm
Eisenia fetida across a range of soil types. The exposure model will account
for (i) particle dissolution and consequent toxicity of the ionic metal across
soil types; (ii) variation in the toxicity of undissolved nanoparticles across
soil types. Initial results will be shown from earthworm exposures to ZnO
nanoparticles, non-nano ZnO and ionic Zn, in a set of soils created in the
laboratory by liming of an acidic heathland soil from the southern UK.
Initial results show that (i) exposure to all three types of Zn result in effects
on earthworm reproduction; (ii) the toxicity consistently increases with
decreasing soil pH; (iii) ZnO, both nano and non-nano, is consistently
less toxic on a Zn basis than ionic Zn; (iv) the toxicity in ZnO exposures
cannot be solely attributed to ionic Zn formed by particle dissolution; (v)
accumulation of Zn by the worms is higher in particle exposures than in
ionic exposures. Taken together, these findings suggest that direct nanoparticle
toxicity to earthworms does occur in soil exposures. The differences
in uptake and toxicity between ZnO particles and ionic Zn suggest that (i)
particles are directly taken up by earthworms; (ii) uptake does not trigger
zinc elimination processes in the worm, hence the relatively high accumulation
of Zn in particle exposures; (iii) on a Zn basis, particles are less toxic to
worms than ionic Zn once within the tissues. We will discuss these findings
in the context of developing the concepts behind the earthworm-nanoparticle
exposure model