GB2267290A - A Process for the electrolytic destruction of nitrate in aqueous liquids - Google Patents
A Process for the electrolytic destruction of nitrate in aqueous liquids Download PDFInfo
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- GB2267290A GB2267290A GB9211222A GB9211222A GB2267290A GB 2267290 A GB2267290 A GB 2267290A GB 9211222 A GB9211222 A GB 9211222A GB 9211222 A GB9211222 A GB 9211222A GB 2267290 A GB2267290 A GB 2267290A
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- United Kingdom
- Prior art keywords
- ammonia
- anolyte
- nitrate
- catholyte
- compartment
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- 229910002651 NO3 Inorganic materials 0.000 title claims abstract description 26
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 title claims abstract description 22
- 239000007788 liquid Substances 0.000 title claims abstract description 18
- 238000000034 method Methods 0.000 title claims description 31
- 230000006378 damage Effects 0.000 title description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 78
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 37
- -1 hydrogen ions Chemical class 0.000 claims abstract description 21
- 239000012528 membrane Substances 0.000 claims abstract description 19
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 16
- 239000001117 sulphuric acid Substances 0.000 claims abstract description 16
- 235000011149 sulphuric acid Nutrition 0.000 claims abstract description 16
- 150000002823 nitrates Chemical class 0.000 claims abstract description 11
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims abstract description 10
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 claims abstract description 10
- 229910021653 sulphate ion Inorganic materials 0.000 claims abstract description 9
- 150000001768 cations Chemical class 0.000 claims abstract description 7
- 150000004820 halides Chemical class 0.000 claims abstract description 6
- 239000001257 hydrogen Substances 0.000 claims abstract description 6
- 229910052739 hydrogen Inorganic materials 0.000 claims abstract description 6
- 229910052757 nitrogen Inorganic materials 0.000 claims abstract description 5
- 229910052938 sodium sulfate Inorganic materials 0.000 claims abstract description 5
- 235000011152 sodium sulphate Nutrition 0.000 claims abstract description 5
- 150000001450 anions Chemical class 0.000 claims abstract description 4
- 229910052920 inorganic sulfate Inorganic materials 0.000 claims abstract description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 10
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 9
- 238000005342 ion exchange Methods 0.000 claims description 6
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 claims description 4
- 229910052799 carbon Inorganic materials 0.000 claims description 4
- 229910021397 glassy carbon Inorganic materials 0.000 claims description 3
- 230000015572 biosynthetic process Effects 0.000 claims description 2
- 239000011261 inert gas Substances 0.000 claims description 2
- 230000002035 prolonged effect Effects 0.000 claims description 2
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims 1
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims 1
- 235000011114 ammonium hydroxide Nutrition 0.000 claims 1
- 239000000126 substance Substances 0.000 claims 1
- 239000000243 solution Substances 0.000 description 26
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 6
- XTEGARKTQYYJKE-UHFFFAOYSA-M Chlorate Chemical compound [O-]Cl(=O)=O XTEGARKTQYYJKE-UHFFFAOYSA-M 0.000 description 4
- 229920000557 Nafion® Polymers 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000000460 chlorine Substances 0.000 description 3
- 229910052801 chlorine Inorganic materials 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 230000003647 oxidation Effects 0.000 description 3
- 238000007254 oxidation reaction Methods 0.000 description 3
- 239000011780 sodium chloride Substances 0.000 description 3
- QDHHCQZDFGDHMP-UHFFFAOYSA-N Chloramine Chemical class ClN QDHHCQZDFGDHMP-UHFFFAOYSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- CPELXLSAUQHCOX-UHFFFAOYSA-N Hydrogen bromide Chemical compound Br CPELXLSAUQHCOX-UHFFFAOYSA-N 0.000 description 2
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 2
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 238000001704 evaporation Methods 0.000 description 2
- 230000008020 evaporation Effects 0.000 description 2
- 239000010439 graphite Substances 0.000 description 2
- 229910002804 graphite Inorganic materials 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229910017464 nitrogen compound Inorganic materials 0.000 description 2
- 150000002830 nitrogen compounds Chemical class 0.000 description 2
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 2
- JHJLBTNAGRQEKS-UHFFFAOYSA-M sodium bromide Chemical compound [Na+].[Br-] JHJLBTNAGRQEKS-UHFFFAOYSA-M 0.000 description 2
- 239000010936 titanium Substances 0.000 description 2
- 229910052719 titanium Inorganic materials 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 239000004677 Nylon Substances 0.000 description 1
- 108091006629 SLC13A2 Proteins 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 description 1
- 229910052921 ammonium sulfate Inorganic materials 0.000 description 1
- 239000001166 ammonium sulphate Substances 0.000 description 1
- 235000011130 ammonium sulphate Nutrition 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000011324 bead Substances 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 239000003575 carbonaceous material Substances 0.000 description 1
- 238000005341 cation exchange Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000003487 electrochemical reaction Methods 0.000 description 1
- 238000000909 electrodialysis Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 230000001815 facial effect Effects 0.000 description 1
- 229920002313 fluoropolymer Polymers 0.000 description 1
- 239000004811 fluoropolymer Substances 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910000042 hydrogen bromide Inorganic materials 0.000 description 1
- 229910001410 inorganic ion Inorganic materials 0.000 description 1
- 229920003303 ion-exchange polymer Polymers 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 229910000510 noble metal Inorganic materials 0.000 description 1
- 229920001778 nylon Polymers 0.000 description 1
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 1
- 229940085991 phosphate ion Drugs 0.000 description 1
- 235000021110 pickles Nutrition 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 229920001343 polytetrafluoroethylene Polymers 0.000 description 1
- 239000004810 polytetrafluoroethylene Substances 0.000 description 1
- 229940058401 polytetrafluoroethylene Drugs 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000005086 pumping Methods 0.000 description 1
- 239000012492 regenerant Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- VWDWKYIASSYTQR-UHFFFAOYSA-N sodium nitrate Inorganic materials [Na+].[O-][N+]([O-])=O VWDWKYIASSYTQR-UHFFFAOYSA-N 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
- C02F1/4676—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/16—Nitrogen compounds, e.g. ammonia
- C02F2101/163—Nitrates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/46115—Electrolytic cell with membranes or diaphragms
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/4618—Supplying or removing reactants or electrolyte
- C02F2201/46185—Recycling the cathodic or anodic feed
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
Abstract
Nitrates in an aqueous liquid are destroyed by circulating through the cathode compartment of an electrolytic cell a liquid which contains the nitrate and in the anode compartment an anolyte, said electrolytic cell comprising a cathode on one side of a cation selective membrane which is permeable to hydrogen ions and an anode on the other side of the membrane, which membrane serves to divide the electrochemical cell into the anode compartment and the cathode compartment, the anolyte comprising a halide free solution comprising an anion which is electrochemically inactive, preferably sulphate ions, e.g. a solution of sulphuric acid or an inorganic sulphate, such as sodium sulphate, and thereafter passing electric current through the electrochemical cell so that nitrate ions in the cathode compartment are reduced to ammonia. The ammonia is separated from the catholyte, dissolved in sulphuric acid and used as the anolyte to oxidize ammonia to nitrogen.
Description
A PROCESS FOR THE DESTRUCTION OF
NITRATE IN AOUEOUS LIOUIDS This invention relates to the destruction of nitrates in aqueous liquids. In many places in
Europe, including the United Kingdom, the use of fertilisers in agriculture has led to an increase in the nitrate content of ground water. As a result, the water extracted from some boreholes is now above the limit of 50mg/litre (50 ppm) which has been set by
European Community legislation. Nitrate-containing solutions can also arise as a result of various industrial processes. For example, the treatment of nitrate-containing brackish water by electrodialysis or reverse osmosis produces a stream in which the nitrates are concentrated. The washings from plants using pickle liquors based on nitric acid are another example. Solutions resulting from the scrubbing of nitric oxides from gas streams will also contain nitrates.
Removal of nitrate from aqueous liquids by ion exchange is a favoured technique for treating such water but regeneration of the resin produces an effluent which is high in nitrate, usually from 3 to 4 g/l and also in chloride. Disposal of this solution is often expensive or impractical.
In European Patent Application 0 412 175A there is disclosed a method for removing nitrogen compounds from an aqueous liquid containing nitrogen oxides and/or nitrates using an electrolytic cell in which the liquid containing the said nitrogen compound is electrolysed in the cathode compartment. A cation-selective membrane separates the cathode compartment from the anode compartment and there is used in the anode compartment an anolyte which contains an aqueous solution of an alkali halide, in particular sodium bromide or sodium chloride. While it is essential that the method of EP-A-0 412 175 contains the halide in the anolyte, there is disclosed the use in the anode compartment of a mixture of a solution of hydrogen bromide and sulphuric acid.
The present inventor has carried out research in the destruction of nitrates in aqueous liquids and has surprisingly found that an improved process for destroying nitrates is provided when the anolyte is free of halide ions and comprises an anion which is electrochemically inactive and is preferably sulphate ion but may be phosphate ion (P043'). The reason for this is that several unfavourable reactions occur when halides are introduced into the anode compartment. In the case of chloride, these include the evolution of chlorine, and the formation of chlorate, both of which are toxic. In the presence of ammonia, chlorine may react further to give chloramines, which are lachrymatory. Since the presence of chloride ions in the anolyte should, as a consequence, be avoided, the use of microporous separators, as described in EP-A-O 412 175 is also undesirable. These membranes cannot prevent the transport of chloride from catholyte to anolyte. It is also most unlikely that the desired anodic reaction, i.e. the oxidation of ammonia, could take place to any great extent in the presence of high chloride concentrations, since chlorine evolution will be the favoured reaction. The use of sulphate ions without chloride ions in the anolyte avoids these problems.
Accordingly, the present invention provides a process for destroying nitrates in an aqueous liquid which process comprises circulating through the cathode compartment of an electrolytic cell a liquid which contains the nitrate and in the anode compartment of the electrolytic cell there is circulated an anolyte, wherein said electrolytic cell comprises a cathode on one side of a cation selective membrane which is permeable to hydrogen ions and an anode on the other side of the membrane, which membrane serves to divide the electrochemical cell into the anode compartment and the cathode compartment, and wherein the anolyte comprises a halide free solution comprising an anion which is electrochemically inactive, preferably sulphate ions, e.g. a solution of sulphuric acid or an inorganic sulphate, such as sodium sulphate, and thereafter passing electric current through the electrochemical cell so that nitrate ions in the cathode compartment are reduced to ammonia.
Preferably the ammonia produced in the cathode compartment is separated from the catholyte and dissolved into sulphuric acid, thereafter the resulting solution is oxidized to nitrogen in the anode compartment of an electrolytic cell, which is conveniently the same cell in which the ammonia was produced. It is preferred that the cathode of the electrochemical cell is formed of Reticulated Vitreous carbon, which is preferably supported by a carbon backing plate.
For ease of operation on a large scale the catholyte and anolyte which are employed in the electrolytic cell are each circulated in a loop to and from the cathode compartment and anode compartment respectively and there is provided a holding tank in each loop. It is desirable that the nitrate levels of the cathode compartment are reduced to 50 parts per million or less and that the process is carried out such that a current deficiency of between 50t and 70% is obtained. By prolonged passage of current through the electrochemical cell the nitrate level of the catholyte can be reduced to below 1 ppm.
In a preferred process of this invention ammonia is separated from the catholyte after adjusting the pH to at least 11.5 by contacting outside the cathode compartment said catholyte with a counter flowing stream of inert gas and thereafter dissolving the ammonia gas which has been stripped from the catholyte in a solution of sulphuric acid.
The solution containing nitrate ions may also contain chloride ions and this will usually be derived from an ion exchange treatment. After stripping ammonia from the catholyte the solution is alkaline and is preferably neutralised to a pH of 6 to 7.5 and then concentrated by distillation or other means. The solution may then be returned to the ion exchange treatment plant.
It will be appreciated that the process of this invention operates in three stages:
(a) Reduction of nitrate to ammonia in the
catholyte of the electrochemical cell, according
to the equation: NO3 + 10H+ + 8e
NH4+ + 3H20 (b) Removal of ammonia from the catholyte as a vapour, and its subsequent dissolution into sulphuric acid.
(c) Oxidation of ammonia to nitrogen in the anode compartment of an electrochemical cell, according to the equation: 2NH4+
N2 + 8H + 6e
The electrochemical cell and the process of this invention will now be described with reference to the accompanying figure.
The electrochemical cell (11) which is used in stages (a) and (c) consists of a cathode compartment (1) and an anode compartment (2) divided by a cation selective membrane (3) which is permeable to hydrogen ions and is substantially impermeable to other inorganic ions. Conduction through this membrane is provided by the hydrogen ions. Catholyte and anolyte are circulated from holding tanks (4,5) respectively through the cell compartments using pumps (6,7). The catholyte contains the nitrate to be treated. The anolyte is a solution of sulphuric acid or sodium sulphate. It may also contain the solution of ammonia obtained in stage (b).
The anode (8) may be of a noble metal such as platinum, or platinised titanium. The cathode (9) is carbon. Best results are obtained with a carbon material known as Reticulated Vitreous Carbon (RVC).
This is made commercially by pyrolising a polymer foam. The open porous nature of RVC provides an enhanced surface area for the electrochemical reaction. A block or sheet or RVC is affixed to a non-porous graphite backing plate (10) with nylon screws (not shown). The whole assembly is constructed with materials which are not attacked by the catholyte, which is very corrosive to many materials, such as steel.
A direct current is passed through the cell by attaching electrical leads (not shown) to the cathode backing plate and to the anode. It is advantageous to arrange for the membrane to be close to the RVC, and to the anode, thereby improving the mass transport, and hence the efficiency of the cell.
After the catholyte has been treated in the electrochemical cell, provided it is not strongly buffered, it has a high pH. This facilitates the stripping of ammonia to the vapour phase by boiling, or by contacting the liquid with a gas (such as air) in a suitable apparatus in a manner known per se.
The ammonia vapour is easily re-dissolved into sulphuric acid. The resulting solution may then be used as the anolyte in the electrochemical cell, and after converting the nitrate and removing the resultant ammonia, the catholyte may be discarded or neutralised with hydrochloric acid, concentrated by evaporation and reused as regenerant for the ion exchange column.
The sulphuric acid anolyte may be used in a closed loop, with ammonia being dissolved and oxidized electrochemically at appropriate times. The ammonia concentration can be maintained at convenient levels, (it is not necessary to deplete it entirely in each batch). The acid concentration can readily be adjusted by evaporation or dilution, as necessary.
If the overall process is operated as described, the volumes of effluent to be discarded can be minimised. The sulphuric acid can be circulated many times through the anolyte loop by adjusting the water content, and the spent catholyte after neutralisation can be used to regenerate the ion exchange column.
This avoids the rejection of large quantities of chloride.
The invention will be illustrated further with reference to the following examples.
1. Reduction of nitrate to ammonia
The electrochemical cell of figure 1 was used as follows. The catholyte was 1 litre of solution containing 29.3 gm, NaCl and 4.25 gm, NaN03, i.e.
the nitrate ion concentration was 3100 parts per million (ppm). The anolyte was 1 litre of 2.45% sulphuric acid. The anode was a platinised titanium plate with an active area of 75mm x 75mm. The cathode consisted of a block of RVC, facial area 75mm x 75mm x 10mm deep, fixed to a graphite backing plate. The catholyte frame, with entry and exit ports for the flowing solution, fitted closely around the RVC so that any excess of solution to the backing plate was mainly through the pores of the RVC. The membrane was
Nafion 417 (a Du Pont product). A current of 3A was passed through the cell and sample analyses gave the data of Table 1.
Table 1
Time (hrs.) o 1 2 3 4 5 6 [N03 (ppm) 3100 2221 1523 943 580 134 32 [NH4+](ppm) 0 190 377 535 673 774 809 pH 9.0 12.0 12.3 12.4 12.4 12.5 12.5
The results show that the nitrate concentration may be reduced to below 50 ppm in about 5.75 hours. This corresponds to an overall current efficiency of 64%.
Small amounts of ammonia have been lost, either into the vapour phase, or by transport of the neutral species, NH3, across the membrane into the anolyte.
The latter is advantageous. Final concentrations of nitrite were < lppm.
2. Similar experiments were performed using the backing plate alone, i.e. by removing the RVC, or by replacing the RVC with an assembly of carbon chips.
Current efficiencies in these cases were 23% and 54%, respectively.
The Nafion membranes are based on perfluorinated ion-exchange polymers. Attached to the fluoropolymer chains are perfluorinated cation exchange sites. The membranes are permeable to cations but one cation is generally more permeable than others. In the case of
Nafion 417, hydrogen ions are permeable. The 400 series have sulphonic groups at the active sites. The Nafion membranes are reinforced with a polytetra fluoroethylene support cloth.
3. Removal of ammonia from the catholyte
The pH of a solution containing 29.3 gm/litre NaCl and 2.14 gm/litre NH4C1 (i.e. 720 ppm NH4+) was adjusted to 12.0. These conditions are equivalent to those of the treated catholyte. The solution was continuously circulated by pumping to the top of a trickle tower containing glass beads, and then returning to a holding container. The temperature was maintained at 5O0C. Air was passed upwardly through the tower, in counter flow to the liquid, to strip out the ammonia.
The gas stream was then introduced into the bottom of a similar tower through which sulphuric acid solution (2.45%) of the same total volume was descending. The ammonia was re-absorbed into this liquid which was circulated without heating. The ammonia concentrations in each liquid are shown in Table 2.
Table 2
Time (hrs.) 0 0.5 1 1.5 2 2.5 3.5 [NH4+] (ppm) 715 401 229 135 67 36 17 (alkali) FNH4+(ppm) 0 268 449 531 605 633 670 (acid)
The results show that ammonia may be transferred from one liquid to the other. The process is accelerated by increasing the temperature of the alkaline-chloride solution side.
4. Oxidation of ammonia in the presence of sulphate
The electrochemical cell was used as previously described. The catholyte was 1.2 litres of NaC1 solution (29.3 gm/litre). The anolyte was ammonium sulphate dissolved in 1.2 litres of sodium sulphate solution (35.5 gm/litre) to give a concentration of about 800 ppm
NH4+. Both solutions were circulated as before, and a current of 3A was passed. The anolyte rapidly became acidic, and the ammonia concentration decreased as shown in Table 3.
Table 3
Time (hrs.) 0 1 2 3 4 6 8 [NH4+](ppm) 787 562 422 319 213 141 89 pH 6.0 2. 6 2. 2 2.0 1.9 1.7 1. 6 The results show that ammonia is oxidized by this method. No nitrate or nitrite was detected in the anolyte.
It is possible to operate a process in accordance with this invention by transferring the treated catholyte containing ammonia directly into the anode compartment to oxidize the ammonia to nitrogen, but for this to be a useful procedure it is necessary that the electrochemical species present in the solution are inactive at the anode as well as being inactive at the cathode. Solutions containing nitrates and sulphate, which in this connection is an electrochemically inactive species, can be treated by such procedure. If chloride ions are present in the starting liquid, then undesirable products, such as chlorate and chloramines are formed.
Claims (11)
1. A process for destroying nitrates in an aqueous liquid which process comprises circulating through the cathode compartment of an electrolytic cell a liquid which contains the nitrate and in the anode compartment of the electrolytic cell there is circulated an anolyte, wherein said electrolytic cell comprises a cathode on one side of a cation selective membrane which is permeable to hydrogen ions and an anode on the other side of the membrane, which membrane serves to divide the electrochemical cell into the anode compartment and the cathode compartment, and wherein the anolyte comprises a halide free solution comprising an anion which is electrochemically inactive, preferably sulphate ions, e.g. a solution of sulphuric acid or an inorganic sulphate, such as sodium sulphate, and thereafter passing electric current through the electrochemical cell so that nitrate ions in the cathode compartment are reduced to ammonia.
2. A process as claimed in claim 1 wherein the ammonia produced in the cathode compartment is separated and dissolved into sulphuric acid and thereafter the resulting solution is oxidized to nitrogen in the anode compartment of an electrolytic cell.
3. A process as claimed in claim 1 or claim 2 wherein the cathode of the electrochemical cell is formed of reticulated vitreous carbon, which is preferably supported by a carbon backing plate.
4. A process as claimed in any one of the preceding claims wherein the catholyte and anolyte employed in the electrochemical cell are each circulated in a loop to and from the cathode compartment and anode compartment respectively and there is provided a holding tank in each loop.
5. A process as claimed in any one of the preceding claims wherein the nitrate level of the cathode compartment is reduced to 50 parts per million or less and the arrangement is such that the current efficiency is obtained of between 50% and 70%.
6. A process as claimed in claim 5 wherein the nitrate level is reduced to below 1 ppm by prolonged passage of current through the electrochemical cell.
7. A process as claimed in any one of the preceding claims wherein ammonia is separated from the catholyte after adjusting the pH to at least 11.5 by contacting outside the cathode compartment said catholyte with a counter flowing stream of inert gas and thereafter dissolving the ammonia gas which has been stripped from the catholyte in a solution of sulphuric acid.
8. A process as claimed in claim 7, wherein resulting solution containing ammonia and sulphate ions is used as anolyte solution in the process as claimed in any one of claims 1 to 6.
9. A process as claimed in any one of the preceding claims wherein the solution containing nitrate ions also contains chloride ions which is derived from an ion exchange treatment.
10. A process as claimed in any one of the preceding claims wherein the ammonia solution containing nitrates and electrochemically inactive substances such as sulphate, after the formation of ammonia in the cathode compartment is subsequently treated by using the ammonia-containing catholyte as an anolyte in the said electrochemical cell.
11. A process as claimed in claim 1 and substantially as hereinbefore described with reference to and as illustrated in the figure of the accompanying drawing.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB9211222A GB2267290A (en) | 1992-05-27 | 1992-05-27 | A Process for the electrolytic destruction of nitrate in aqueous liquids |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB9211222A GB2267290A (en) | 1992-05-27 | 1992-05-27 | A Process for the electrolytic destruction of nitrate in aqueous liquids |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| GB9211222D0 GB9211222D0 (en) | 1992-07-08 |
| GB2267290A true GB2267290A (en) | 1993-12-01 |
Family
ID=10716095
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| GB9211222A Withdrawn GB2267290A (en) | 1992-05-27 | 1992-05-27 | A Process for the electrolytic destruction of nitrate in aqueous liquids |
Country Status (1)
| Country | Link |
|---|---|
| GB (1) | GB2267290A (en) |
Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0659692A1 (en) * | 1993-12-24 | 1995-06-28 | Hahnewald GmbH | Process for electrochemical reduction of nitrate |
| FR2754251A1 (en) * | 1996-10-03 | 1998-04-10 | Step | Electrolytic treatment of an aqueous solution |
| DE19853182A1 (en) * | 1998-11-19 | 2000-05-25 | Univ Dresden Tech | Removal of ammonium and/or ammonia from saline aqueous solution, e.g. sewage or other waste liquor, involves electrolysis at constant pH in a divided cell in the presence of chloride |
| WO2002040406A1 (en) * | 2000-11-14 | 2002-05-23 | Vattenfall Ab | Process and apparatus for removal and destruction of dissolved nitrate. |
| ES2173035A1 (en) * | 2000-09-25 | 2002-10-01 | Emp Mun De Aguas Y Saneamiento | Procedure for eliminating and destroying nitrate from water |
| WO2003074430A1 (en) * | 2002-03-01 | 2003-09-12 | Vattenfall Ab (Publ) | Nitrate removal |
| EP1295853A3 (en) * | 2001-09-19 | 2003-10-01 | Sanyo Electric Co. Ltd | Method of treating water and apparatus therefor |
| WO2005097686A1 (en) * | 2004-04-07 | 2005-10-20 | Laborelec Cvba | Electrochemical device and method for the removal of ammonium and nitrate ions contained in liquid effluents |
| WO2012095659A1 (en) * | 2011-01-12 | 2012-07-19 | Future Environmental Technologies | Conditioning cell |
| CN104355369A (en) * | 2014-11-20 | 2015-02-18 | 哈尔滨工业大学 | Device for removing nitrate nitrogen in water and application method of device |
| WO2020028570A1 (en) * | 2018-08-03 | 2020-02-06 | The Board Of Trustees Of The Leland Stanford Junior University | A method for the electrochemical synthesis of ammonia from nitrates and water |
| WO2024030585A1 (en) * | 2022-08-03 | 2024-02-08 | Aclarity, Inc. | Electrochemical reduction reactor, and system and method comprising same |
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| CN113365952A (en) * | 2018-11-30 | 2021-09-07 | 帕克尔有限公司 | Method for converting total ammonia nitrogen |
| DE102021114704B3 (en) * | 2021-06-08 | 2022-09-08 | Jassen - Kunststoffzentrum Gmbh - Apparatebau, Zuschnitte Und Formung | Apparatus and method for converting ammonia from an aqueous liquid containing ammonia into molecular nitrogen |
| CN114524493B (en) * | 2022-01-25 | 2023-04-07 | 中南大学 | Ammonia recovery device and method for electrochemically treating nitrate wastewater |
| CN120504458A (en) * | 2025-07-22 | 2025-08-19 | 山东海化集团有限公司 | Nitrate wastewater treatment method |
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| GB2038872A (en) * | 1978-10-06 | 1980-07-30 | Asahi Chemical Ind | Electrolytic process for preparing nitrites |
| GB2211858A (en) * | 1987-11-05 | 1989-07-12 | Olin Corp | Electrochemical reduction of nitric acid to hydroxylamine nitrate |
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- 1992-05-27 GB GB9211222A patent/GB2267290A/en not_active Withdrawn
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2038872A (en) * | 1978-10-06 | 1980-07-30 | Asahi Chemical Ind | Electrolytic process for preparing nitrites |
| US4312722A (en) * | 1978-10-06 | 1982-01-26 | Asahi Kasei Kogyo Kabushiki Kaisha | Process for preparing nitrites |
| GB2211858A (en) * | 1987-11-05 | 1989-07-12 | Olin Corp | Electrochemical reduction of nitric acid to hydroxylamine nitrate |
Cited By (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP0659692A1 (en) * | 1993-12-24 | 1995-06-28 | Hahnewald GmbH | Process for electrochemical reduction of nitrate |
| DE4344613A1 (en) * | 1993-12-24 | 1995-06-29 | Hahnewald Gmbh | Process for the electrochemical reduction of nitrate |
| FR2754251A1 (en) * | 1996-10-03 | 1998-04-10 | Step | Electrolytic treatment of an aqueous solution |
| DE19853182A1 (en) * | 1998-11-19 | 2000-05-25 | Univ Dresden Tech | Removal of ammonium and/or ammonia from saline aqueous solution, e.g. sewage or other waste liquor, involves electrolysis at constant pH in a divided cell in the presence of chloride |
| ES2173035A1 (en) * | 2000-09-25 | 2002-10-01 | Emp Mun De Aguas Y Saneamiento | Procedure for eliminating and destroying nitrate from water |
| WO2002040406A1 (en) * | 2000-11-14 | 2002-05-23 | Vattenfall Ab | Process and apparatus for removal and destruction of dissolved nitrate. |
| US6984326B2 (en) | 2001-09-19 | 2006-01-10 | Sanyo Electric Co., Ltd. | Nitrogen treating method and nitrogen treating system |
| EP1295853A3 (en) * | 2001-09-19 | 2003-10-01 | Sanyo Electric Co. Ltd | Method of treating water and apparatus therefor |
| WO2003074430A1 (en) * | 2002-03-01 | 2003-09-12 | Vattenfall Ab (Publ) | Nitrate removal |
| WO2005097686A1 (en) * | 2004-04-07 | 2005-10-20 | Laborelec Cvba | Electrochemical device and method for the removal of ammonium and nitrate ions contained in liquid effluents |
| WO2012095659A1 (en) * | 2011-01-12 | 2012-07-19 | Future Environmental Technologies | Conditioning cell |
| CN104355369A (en) * | 2014-11-20 | 2015-02-18 | 哈尔滨工业大学 | Device for removing nitrate nitrogen in water and application method of device |
| WO2020028570A1 (en) * | 2018-08-03 | 2020-02-06 | The Board Of Trustees Of The Leland Stanford Junior University | A method for the electrochemical synthesis of ammonia from nitrates and water |
| WO2024030585A1 (en) * | 2022-08-03 | 2024-02-08 | Aclarity, Inc. | Electrochemical reduction reactor, and system and method comprising same |
Also Published As
| Publication number | Publication date |
|---|---|
| GB9211222D0 (en) | 1992-07-08 |
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| WAP | Application withdrawn, taken to be withdrawn or refused ** after publication under section 16(1) |