Phytoremédiation d’un sol contaminé par des contaminants organiques et inorganiques
The large number of contaminated sites in Quebec (Canada) and all around the world is a major public problem because of the toxicological risks they present for human and environmental health. In the municipality of Varennes (Quebec, Canada), located on the south shore of the Island of Montreal, the activities of a former petrochemical plant (Pétromont Inc.) have led to the accumulation of moderate to high concentrations of traces elements (TEs), polychlorinated biphenyls (PCBs), aliphatic petroleum hydrocarbons (C10-C50) and polycyclic aromatic hydrocarbons (PAHs) on the land. In 2010, a short rotation intensive culture (SRIC) of willow has been established on the site, in order to conduct a field-scale phytoremediation experiment. Although this plantation of Salix miyabeana was established with a remediation view, no significant effect was reported on the concentration of soil contaminants during the first years of growth. Plant-based remediation processes can be difficult to predict in the fiel and require improvement in order to increase their effectiveness. Fertilization with organic amendments, as well as manipulating the plant microbiome, are two agronomic techniques commonly employed in traditional crop management, in order to increase biomass production and improve overall plant health. These approaches can also influence the mobility and bioavailability of some compounds in the soil. Since such modifications are known to have the potential to significantly improve the efficiency of plants in removing or transforming soil contaminants, these two agronomic techniques are of growing interest in the field of phytoremediation. This doctoral research aims to improve scientific knowledge in the field-scale phytoremediation application by addressing some aspects that affect these two agronomic approaches. Inside the already established willow plantation, a first study was carried out to assess the impact of soil organic amendment on the phytoremediation efficacy of the two willow cultivars (‘SX61’ and ‘SX64’). The soil of some experimental plots was covered with ramial chipped wood (RCW) combined or not with spent mushroom substrate (SMS) of Pleurotus ostreatus. After three growing seasons, the results showed that the addition of SMS to the RCW had no effect on the growth of the willows, as well as on their effectiveness in removing or reducing the concentration of contaminants on the site. The results nevertheless suggest that RCW helps immobilize some PAHs in the soil, in addition to increasing the efficiency of willows to phytoextract Zn. The presence of willows appears to have significantly reduced the natural attenuation of C10-C50 on the site. In addition, the concentrations of PCBs, Cd, Ni and ten PAHs, showed seasonal oscillations, which suggests that the evapotranspiration inside the willow plantation mobilized some contaminants towards the rooting zones. Thus, the concentration of certain contaminants may tend to increase within a dense willow plantation over time. A second study was carried out inside the same plantation, in order to verify if the increases in concentration observed previously could be linked to the evapotranspiration that takes place inside a willow plantation. In order to eradicate the effect of plant transpiration, willows were harvested in certain plots of the plantation. The concentrations of organic and inorganic contaminants were followed over time (24 months) and compared with those observed in the unharvested plots. The results obtained showed that the removal of the willows limited the accumulation of certain contaminants on the soil surface, as observed in the uncut plots. These results suggested once again that the short rotation intensive culture of willows can lead to the migration of certain contaminants towards the roots and thus increase their concentrations on the soil surface near the root zones. Very few studies have reported results that seem to contradict the multiple purification benefits that are usually put forward in phytoremediation. However, such effects on contaminant mobilization could be relevant and suitable in a risk management context. The third and final study presented in this thesis explores the microbial communities associated with the roots of the two willow cultivars established on the experimental site for several years (six years). Root and rhizosphere microbial communities of Salix spp. have been studied in contaminated environments, but most of studies have been carried out on relatively young hosts. Therefore, little information exists regarding the microbial communities associated with older willows established in contaminated environments. The characterization of fungal, bacterial and Archean communities has shown differences in composition between the two willow cultivars, as well as between their compartments (i.e., roots and rhizosphere). Some taxonomic groups, belonging to each of the three domains, caught our attention, either by their abundance, or by their ecological functions already known to be potentially beneficial for the plant survival, or for increasing the degradation and extraction of various contaminants. This study therefore provides valuable information that can be used to improve certain microbiome engineering approaches that promote the establishment, survival, growth and phytoremediation performance of Salix spp. in contaminated environments. All the results presented in this thesis have fueled various reflections on the interest of using soil organic amendments and characterizing the root and rhizosphere microbiome of willows in order to improve the practices and implementation of phytoremediation with willows. This thesis also highlights a phenomenon of contaminant migration, influenced by the presence of fast-growing woody plants, which represents an obstacle for the evaluation of phytoremediation performance approaches with willows.
Salix Pleurotus Microbiome Culture intensive en courtes rotations (CICR) Mycoremédiation Contamination Ramial chipped wood (RCW) Spent mushroom substrate (SMS) Short rotation intensive culture (SRIC) Phytoremediation Mycoremediation Soil