Abstract
The enhanced phytoremediation of metal contaminated soils holds great
promise for the recovery of soil health and functionality, while providing a
range of co-benefits, from an environmental and human health perspective,
derived from the revegetation of the degraded sites and the concomitant delivery
of ecosystem services. Due to diverse evolutionary co-selection mechanisms
between metal resistance and antibiotic resistance in bacteria, metal
contaminated soils are considered potential reservoirs of antibiotic resistant
bacteria (ARB) which can contribute to the existing antibiotic resistance crisis.
During the enhanced phytoremediation of metal contaminated soils, the
application of organic wastes (e.g., manure, slurry, sewage sludge) as soil
amendments can aggravate the risk of antibiotic resistance spread, because
they often contain ARB which harbor antibiotic resistance genes (ARGs) that
can then be propagated among soil bacterial populations through horizontal
gene transfer (HGT). Due to the magnitude and criticality of the antibiotic
resistance crisis, as well as the higher risk of spread and dispersal of ARB and
ARGs (they make copies of themselves) compared to metals, it is proposed here
to aim enhanced phytoremediation strategies towards decreasing the soil
resistome (and, hence, the risk of its potential link with the human resistome),
while reducing total and/or bioavailable metal concentrations and restoring soil
health and the delivery of ecosystem services. To this purpose, a decalogue of
practices is tentatively suggested. Finally, a proper management of plant and soil
microbial compositions is a most crucial aspect, together with the selection of the
right organic wastes and phytoremediation practices.