Rosa Galvez-Cloutier

Bioremediation of Metal Contamination

A study was initiated to evaluate the use of the fungus Aspergillus niger for bioleaching and then todetermine the effect of process steps, the tailingsconcentration and type of substrate. An oxidized miningtailing containing mainly copper (7240 mg kg-1 tailings) was studied. A sucrose and mineral salts medium was initially used to produce citric and gluconic acids by A. niger atvarious concentrations of tailings (1, 5, 7, 10 and 15% w/v).Maximal removal of up to 60% of the copper was obtained forthe 5% tailings when the organic acid supernatant was addedto the tailings. In a single step process, A. niger wasthen grown in the presence of mining tailings at variousconcentrations. Maximum copper solubilization (63%) occurredwith 10% mining tailings using sucrose as the substrate.Other substrates were then evaluated including molasses, corncobs and brewery waste (10% mining tailings). Sucrose gavethe best results for copper removal, followed by molasses,corn cobs and brewery waste. Other experiments usingultrasound as a pretreatment showed that 80% removal of thecopper could be obtained for a 5% tailings concentration. Inconclusion, leaching of copper from mining tailings istechnically feasible using A. niger but furtherresearch will be required to increase the economic feasibilityof the process.

An Evaluation of Fresh Water Sediments Contamination: The Lachine Canal Sediments Case, Montréal, Canade. Part II: Heavy Metal Particulate Speciation Study

Over the last century, discharge of industrial effluents and municipal wastewater have contaminated the Lachine Canal sediments. This study investigated the associations between heavy metals and natural sediment constituents. X-ray Diffraction, Transmission Electron Microscopy and geochemical analysis revealed that the sediments consisted mainly of silt and clay size fractions composed of: feldspar, illite, kaolinite, chlorite, calcite and dolomite as well as minor amounts of Fe minerals. Organic matter and amorphous metal oxides were also identified. Each of these constituents bound heavy metals at varying degrees as assessed by a sequential chemical extraction (SCE) protocol. The associations with each geochemical phase were (in order of decreasing significance): 1) residual phase, 2) oxide phase, 3) carbonate phase, 4) organic phase and 5) exchangeable phase. According to the cation exchange capacity (CEC), carbonate and oxide content measurements, the heavy metals occupied a minor fraction of the total capacity of the sediments to retain metals by these mechanisms. The SCE results revealed that the partition patterns varied with pH. The phases associated to the carbonate and the exchangeable phases were the most sensitive to a change in pH with the residual phase being almost unchanged. The Zn and Cd were sensitive to release when the conditions drifted to acidic conditions. The partition patterns for various grain size fractions (<53 µm, 53–75 µm, 75–175 µm and <175 µm) revealed that no particular fraction accumulated a certain heavy metal. Finally, from protocols, techniques and results interpretation in this study, various engineering applications such as the technical choice of clean-up scenarios, screening of remediation techniques and the development of remediation quality criteria were proposed within the framework of the management of contaminated sediments.

An Evaluation of Fresh Water Sediments Contamination: the Lachine Canal Sediments Case, Montréal, Canada. Part I: Quality Assessment

Due to industrialization over the past 100 years, the sediments at the bottom of the Lachine Canal and Bay have become contaminated. This study investigated the heavy metal accumulation mechanisms within the Lachine Canal sediments and was carried out in three phases. Phase I is covered in the present article, while phases II and III will be discussed in a following paper. During Phase I, 28 parameters were measured on 44 sediment samples collected along the Lachine Canal and Bay. The results revealed the presence of a wide variety of both organic and inorganic contaminants. Heavy metals such as Zn < Pb < Cr < Ni < Cu < Cd (in order of decreasing abundance) in addition to organic contaminants (PAHs < MAHs < PCBs) were found in high concentrations exceeding background concentrations and various quality criteria levels. The total load of both organic and inorganic contaminants was found to be higher in the canal than in the bay zone. Correlation analysis was performed to evaluate sediment assessment values with respect to known adsorptive phases such as % clay fraction, TOC (Total Organic Carbon), and % CaCO3. Although a positive correlation existed between % clay fraction or TOC and the total cumulative load of heavy metals, the correlation could not be assessed as conclusive. Significant correlations were obtained between Pb, Ni, and Zn and the carbonate content of the sediments. Pollution Indices (PI) were used according to the format proposed by Canadian authorities and as such were evaluated as incomplete.

Assessment of Hydrocarbons (C10-C50), Polycyclic Aromatic Hydrocarbons (PAHs), and Trace Metals (TMs) Contamination in the Riverbanks of the Chaudière River Three Years after the Lac-Mégantic Railway Disaster (Southern Québec, Canada)

ABSTRACT On July 6, 2013, in downtown Lac-Mégantic (southern Québec, Canada), several tank cars carrying crude oil derailed. This resulted in a series of explosions and a huge fire that led to the terrible Lac-Mégantic disaster. This study deals with the characterization of the Chaudière River banks and bed in order to determine the current state of contamination by hydrocarbons (C10-C50), polycyclic aromatic hydrocarbons (PAHs), and trace metals (TMs). The highest concentrations of hydrocarbons found in the Chaudière River are respectively 960 mg kg−1 dry weight in soil and 760 mg kg−1 dry weight in river sediment. Over half of the all samples were under the detection threshold (i.e. > 300 mg kg−1 in soil and > 832 mg kg−1 in sediment). The concentration in river sediment PAH concentrations were low, with values below the detection threshold. TM concentrations in the soil and sediment are also very low, rarely exceeding class A and B thresholds and chronic effect reference values (164 mg kg−1) which constitute the criteria for soil quality and the protection of aquatic life established by the Québec Environment Ministry. These low levels are largely due to the efforts deployed by government authorities to limit the infiltration and dispersal of contaminants along the river, and to the hydrological conditions that also favoured the dispersal and dilution of pollutants.

Biodegradation of microcystin-LR using acclimatized bacteria isolated from different units of the drinking water treatment plant

Bacterial community isolated from different units of a Drinking Water Treatment Plant (DWTP) including pre-ozonation unit (POU), the effluent-sludge mixture of the sedimentation unit (ESSU) and top-sand layer water sample from the filtration unit (TSFU) were acclimatized separately in the microcystin-leucine arginine (MC-LR)-rich environment to evaluate MC-LR biodegradation. Maximum biodegradation efficiency of 97.2 ± 8.7% was achieved by the acclimatized-TSFU bacterial community followed by 72.1 ± 6.4% and 86.2 ± 7.3% by acclimatized-POU and acclimatized-ESSU bacterial community, respectively. Likewise, the non-acclimatized bacterial community showed similar biodegradation efficiency of 71.1 ± 7.37%, 86.7 ± 3.19% and 94.35 ± 10.63% for TSFU, ESSU and POU, respectively, when compared to the acclimatized ones. However, the biodegradation rate increased 1.5-folds for acclimatized versus non-acclimatized conditions. The mass spectrometry studies on MC-LR degradation depicted hydrolytic linearization of cyclic MC-LR along with the formation of small peptide fragments including Adda molecule that is linked to the reduced toxicity (qualitative toxicity analysis). This was further confirmed quantitatively by using Rhizobium meliloti as a bioindicator. The acclimatized-TSFU bacterial community comprised of novel MC-LR degrading strains, Chryseobacterium sp. and Pseudomonas fragi as confirmed by 16S rRNA sequencing.

Microwave-assisted one-pot conversion of agro-industrial wastes into levulinic acid: An alternate approach

Brewery liquid waste (BLW), brewery spent grain (BSG), apple pomace solid wastes (APS), apple pomace ultrafiltration sludge (APUS) and starch industry waste (SIW) were evaluated as alternative feedstocks for levulinic acid (LA) production via microwave-assisted acid-catalyzed thermal hydrolysis. LA production of 204, 160, 66, 49 and 12 g/kg was observed for BLW, BSG, APS, APUS, and SIW, respectively, at 140 °C, 40 g/L substrate concentration (SC), 60 min and 2 N HCl (acid concentration). Based on the screening studies, BLW and BSG were selected for optimization studies using response surface methodology. Maximum LA production of 409 and 341 g/kg for BLW and BSG, respectively were obtained at 160 °C, 4.5 M HCl, 85 g/L SC and 27.5 min. Results demonstrated the possibility of using brewery wastes as promising substrates for economical and higher yield production of LA, a renewable platform chemical and versatile precursor for fuels and chemicals.