(374f) Solar Photocatalytic Treatment of Atrazine-Contaminated Agricultural Water in the Rio Grande Basin
AIChE Annual Meeting
2006
2006 Annual Meeting
Environmental Division
Applications of Environmental Catalysis I
Wednesday, November 15, 2006 - 2:15pm to 2:33pm
To develop a cost-effective and nearly maintenance-free solar treatment process for herbicides in agricultural water, we studied the photocatalytic decomposition of dissolved atrazine, an herbicide contaminant common in the Rio Grande Basin rivers and agricultural run-off water. Atrazine (C8H14ClN5), widely used in corn, sorghum and wheat fields, is toxic to water-life (leopard frogs, etc) and can cause prostate cancer, cardiovascular damage etc. to human beings [1-3]. Without treatment, the atrazine-contaminated water is hazardous and detrimental to the water sustainability in the Rio Grande Basin.
The available atrazine treatment methods include active carbon adsorption, UVC decomposition and photocatalytic decomposition [4-10]. As photocatalytic decomposition has the potential to use visible light, it could be a nearly maintenance-free process for environmental remediation. In our lab, we demonstrated that atrazine decomposed under a 4W fluorescent light (Fig. 1) with Degussa P-25 and BA-PW25 (Ecodevice, Japan) TiO2 photocatalysts suspended in a 2 L atrazine solution. The kinetic data of the photochemical decomposition of atrazine can be fitted with a first-order rate equation:
dC/dt = - kC (1)
The photocatalysis results in a main product, hydroxyatrazine, that can further decompose to CO2 and water. Hydroxyatrazine is relatively harmless compared to atrazine. The optimum catalyst loading was found to be around 0.3% by weight (Fig. 2).
Fig. 1 Atrazine photocatalytic decomposition under 4 W fluorescent light in a 2 L batch reactor with BA-PW 25 as the photocatalyst.
Fig. 2. Optimum loading of BA-PW 25 photocatalyst in a suspension
Using a 395 nm optical filter, we also observed the activities of the photocatalysts, Fig. 3.
Fig. 3. Atrazine photodecomposition under 4 W fluorescent light with 395 nm filter in 2 L batch reactor.
In a sunny day, atrazine rapidly decomposes from 56 ppb to below 3 ppb in 30 minutes in a 2 L reactor with Degussa P-25 as the photocatalyst under sunlight, while another photocatalyst BA-PW 25 needs 6 hours (Fig. 4). The latter has the following kinetic equation with a R2= 0.997.
dC/dt = -0.448C (2)
Fig. 4. Atrazine photodecomposition in a 2 L batch reactor under solar light in a sunny day
Atrazine photodecomposition with immobilized photocatalyst will be reported in a separate paper.
References
- US EPA, Ambient Aquatic Life Water Quality Criteria for Atrazine-Revised Draft, EPA-822-R-03-03, 2003.
- V. Hequet, C. Gonzalez, P. L. Cloirec, Water Research (2001) 18, 4254-4260
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- National Renewable Energy Laboratory (2001, October). Photochemical treatment of pollutants (CDS-SS25-B001). CO. www.nrel.gov/research/industrial_tech/pollution.html
- Ye, X, Chen, D. H., Flaherty, D., Wang, B., Tadmor, R., Sternes, K., ?Photochemical Treatment of Herbicide/Pathogen Contaminated Agricultural Water in the Rio Grande Basin?, AIChE 2005 Annual Meeting at Cincinnati, OH, November 2005.
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