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Decontaminating pesticide-polluted water using engineered nanomaterial

January 15, 2020 | Audrey-Maude Vézina

Update : September 15, 2020

Atrazine is one of the most widely used pesticides in North America. Professors My Ali El Khakani and Patrick Drogui of INRS have developed a new method to degrade it which combines a new nanostructured material and sunlight.

Atrazine is found throughout the environment, even in the drinking water of millions of people across the country . Conventional water treatments are not effective in degrading this pesticide. Newer processes are more effective, but use chemicals that can leave toxic by-products in the environment.

Méthodes pour dégrader les pesticides

Professor My Ali El Khakani, an expert in nanostructured materials (Centre-EMT), and Professor Patrick Drogui, a specialist in electrotechnology and water treatment (Centre-ETE), have joined forces to develop a new ecological degradation process for atrazine that is as chemical-free as possible.

“By working synergistically, we were able to develop a water treatment process that we would never have been able to achieve separately. This is one of the great added values of interdisciplinarity in research,”

says Professor El Khakani, lead author of the study, whose results have been published January 15 in the journal Catalysis Today.

The researchers use an existing process, called photoelectro-catalysis or PEC, which they have optimized for the degradation of atrazine. The process works with two photoelectrodes (light-sensitive electrodes) of opposite charges. Under the effect of light and an electrical potential, this process generates free radicals on the surface of the photoelectrodes. Those radicals interact with atrazine molecules and degrade them. “The use of free radicals is advantageous because it does not leave toxic by-products as chlorine would do. They are highly reactive and unstable. As their lifetime is very short they tend to disappear quickly,” explains Professor Drogui, co-author of the study.

The Materials’ Challenges

My Ali El Khakani, professeur en matériaux nanostructurés à l’Institut national de la recherche scientifique
Professor My Ali El Khakani

To make photoelectrodes (light-sensitive electrodes), Professor El Khakani has chosen titanium oxide (TiO2), a material that is very abundant, chemically stable, and used in many applications including white pigment in paints or sunscreens. Usually, this semiconducting material converts the light energy provided by UV rays into active charges. In order to take advantage of the entire solar spectrum, i.e. visible light in addition to UV, Professor El Khakani had to make the TiO2 films sensitive to visible light. To this end, his team modified titanium oxide on an atomic scale by incorporating nitrogen and tungsten atoms using a plasma process. This doping reduces the photon energy required to trigger PEC in these novel photoelectrodes.

Professor El Khakani also faced the challenge of treating large water volumes. Since the PEC process is genuinely a surface phenomenon, the treatment of a large volume requires a large surface area of the photoelectrodes. For this this, Professor El Khakani’s team exploited to the advantages of nanostructuring the surface of photoelectrodes.

“Instead of having a flat surface, imagine sculpting it on the nanoscale to create valleys and mountains. This increases the active surface available without changing the physical surface. The active surface is artificially increased by several thousand times compared to the physical surface. With 1 g of material, active surface areas between 50 and 100 m2 can be achieved—that’s the about the surface of an apartment! ”, says Professor El Khakani.

Efficiency and Its Limits

Patrick Drogui professeur en électrotechnologies et traitements des eaux à l’Institut national de la recherche scientifique
Professor Patrick Drogui

Once the photoelectrodes were developed and integrated into a PEC reactor, Professor Drogui’s team optimized the PEC process. His team first used samples of demineralized water to which atrazine was added. PEC with the photoelectrode eliminated about 60% of the pesticide after 300 minutes of treatment. Researchers then moved on to real samples of water collected from the Nicolet River (QC, Canada) near areas of intensive corn and soybean agricultures where herbicides are often used.

When using actual water samples, only 8% of the atrazine was degraded initially. This low percentage is due to the presence of suspended particles that prevent much of the light from reaching the photoelectrode. In addition, the species and particles present in the solution can attach to the electrode thus reducing its active area. Capitalizing on its expertise in water decontamination, Professor Drogui’s team carried out pretreatments based on coagulation and filtration of certain species before applying the PEC approach again. They then succeeded in degrading 38 to 40% of atrazine present in the real samples.

The treatment efficiency remains relatively low compared to synthetic water because real water contains bicarbonates and phosphates that trap free radicals and prevent them from reacting with atrazine. “Pre-treatment by chemical coagulation helps remove phosphates, but not bicarbonates. Calcium could be added to precipitate them, but we want to minimize the use of chemicals anyways”, says Professor Drogui.

According to the researchers, their optimized PEC process could be used as a tertiary treatment, after removing suspended particles and coagulable species. However, a pre-industrial demonstration stage is required before thinking about large-scale use. Finally, PEC has been used to degrade atrazine, but the two teams continue to work together to address other emerging pollutants and antibiotic residues in water.

About the study

Photo-electrocatalytic oxidation of atrazine using sputtured deposited TiO2:WN photoanodes under UV/visible light, by Simon Komtchou, Nazar Delegan, Ahmad Dirany, Patrick Drogui, Didier Robert et My Ali El Khakani, was published in Catalysis Today. This research was supported by funding from the Natural Sciences and Engineering Research Council of Canada (NSERC), the Ministère des relations internationales, francophonie et commerce extérieur (MRIFCE) du Québec and the Fonds de recherche du Québec—Nature et technologies (FRQNT) through their strategic network Plasma-Québec. DOI: