Electrolytic cell equipped with concentric electrode pairs
US-9222181-B2 · Dec 29, 2015 · US
US2016137533A1 · US · A1
| Field | Value |
|---|---|
| Publication number | US-2016137533-A1 |
| Application number | US-201514941447-A |
| Country | US |
| Kind code | A1 |
| Filing date | Nov 13, 2015 |
| Priority date | Nov 14, 2014 |
| Publication date | May 19, 2016 |
| Grant date | — |
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Electrochemical treatment of chromium-containing wastewater has the advantage of simultaneously reducing hexavalent chromium (Cr VI ) and reversibly adsorbing the trivalent product (Cr III ), thereby minimizing the generation of waste for disposal and providing an opportunity for resource reuse. The application of electrochemical treatment of chromium can be often limited by the available electrochemical surface area (ESA) of conventional electrodes with flat surfaces. Here, the preparation and evaluation of carbon nanotube (CNT) electrodes containing of vertically aligned CNT arrays directly grown on stainless steel mesh (SSM). The 3-D organization of CNT arrays increases ESA up to 13 times compared to SSM. The increase of ESA can be correlated with the length of CNTs, consistent with a mechanism of roughness-induced ESA enhancemen, and the increase directly benefits Cr VI reduction by proportionally accelerating reduction without compromising the electrode's ability to adsorb Cr III . The results suggest that the rational design of electrodes with hierarchical structures represents a feasible approach to improve the performance of electrochemical treatment of contaminated water.
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What is claimed is: 1 . A composition for removing heavy metals from wastewater, comprising: a binder-free electrode comprising, an oxide buffer layer, a substrate comprising a material constructed in a pattern, and a layer of catalyst nanoparticles; and an array of vertically aligned carbon nanotubes grown on the electrode. 2 . The composition of claim 1 , further comprising a negatively polarized electrode configured to provide electrons for Cr VI reduction and Cr III absorption through electrostatic attraction. 3 . The composition of claim 1 , wherein the oxide buffer layer is an aluminum oxide. 4 . The composition of claim 1 , wherein the oxide buffer layer is formed by immersion of the substrate in both (a) a polyacrylic acid solution, and (b) a boehmite (γ-AlOOH) nanoplate suspension. 5 . The composition of claim 1 , wherein the substrate comprises a porous stainless steel mesh, the stainless steel mesh comprising a plurality of stainless steel wires, the wires having a curved surface. 6 . The composition of claim 1 , wherein a layer of the catalyst nanoparticles are deposited on the oxide buffer layer. 7 . The composition of claim 1 , wherein the catalyst nanoparticles comprise magnetite (Fe 3 O 4 ) nanoparticles. 8 . A method of manufacturing a composition, comprising: cleaning a substrate; coating the substrate with the oxide buffer; depositing a layer of catalyst nanoparticles onto the oxide buffer layer layer, whereby a binder-free electrode is obtained; and growing an array of vertically aligned carbon nanotubes on the binder-free electrode, whereby the composition of claim 1 is obtained. 9 . The method of claim 8 , further comprising negatively polarizing the binder-free electrode to provide electrons for Cr VI reduction and Cr III absorption through electrostatic attraction. 10 . The method of manufacturing of claim 8 , wherein the oxide buffer layer is an aluminum oxide. 11 . The method of manufacturing of claim 8 , wherein the oxide buffer layer is formed by immersion of the substrate in both (a) a polyacrylic acid solution, and (b) a boehmite (γ-AlOOH) nanoplate suspension. 12 . The method of manufacturing of claim 8 , wherein the oxide buffer layer is deposited on the substrate using a wet chemistry method. 13 . The method of manufacturing of claim 8 , wherein the substrate comprises a porous stainless steel mesh, the stainless steel mesh comprising a plurality of stainless steel wires, the wires having a curved surface area. 14 . The method of manufacturing of claim 8 , wherein the catalyst nanoparticles comprise magnetite (Fe 3 O 4 ) nanoparticles. 15 . A method of removing heavy metals from wastewater, the method comprising: providing the binder-free electrode with vertically aligned carbon nanotubes of claim 1 ; and exposing a wastewater comprising Cr VI to the binder-free electrode with vertically aligned carbon nanotubes, whereby Cr VI is reducted to Cr III . 16 . The method of claim 15 , further comprising negatively polarizing the electrode to provide electrons for Cr VI reduction and Cr III absorption through electrostatic attraction. 17 . The method of claim 15 , wherein the oxide buffer layer is an aluminum oxide. 18 . The method of claim 15 , wherein the oxide buffer layer is formed by immersion of the substrate in both (a) a polyacrylic acid solution, and (b) a boehmite (γ-AlOOH) nanoplate suspension. 19 . The method of claim 15 , wherein the substrate comprises a porous stainless steel mesh, the stainless steel mesh comprising a plurality of stainless steel wires, the wires having a curved surface area. 20 . The method of claim 15 , wherein the catalyst nanoparticles comprise magnetite (Fe 3 O 4 ) nanoparticles.
characterised by the deposition of metallic material · CPC title
Catalytic coating · CPC title
Electrodes · CPC title
characterised by the method of coating (C23C16/04 takes precedence) · CPC title
Heavy metals or heavy metal compounds · CPC title
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