WO1988009226A1 - Method and apparatus for cleaning freight containers as well as for treating and circulating the fluids used - Google Patents
Method and apparatus for cleaning freight containers as well as for treating and circulating the fluids used Download PDFInfo
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- WO1988009226A1 WO1988009226A1 PCT/FI1988/000071 FI8800071W WO8809226A1 WO 1988009226 A1 WO1988009226 A1 WO 1988009226A1 FI 8800071 W FI8800071 W FI 8800071W WO 8809226 A1 WO8809226 A1 WO 8809226A1
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- Prior art keywords
- filter
- unit
- accordance
- combustion
- cleansing
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Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B08—CLEANING
- B08B—CLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
- B08B9/00—Cleaning hollow articles by methods or apparatus specially adapted thereto
- B08B9/08—Cleaning containers, e.g. tanks
- B08B9/093—Cleaning containers, e.g. tanks by the force of jets or sprays
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/02—Non-contaminated water, e.g. for industrial water supply
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Definitions
- This invention concerns a method in accordance with the p amble of claim 1 for cleaning freight containers, both ra way cars and truck trailers, as well as for treating and circulating the fluids used in the cleaning operation.
- the invention also concerns an apparatus in accordance wi the preamble of claim 7 for treating liquids containing soda and water used in the cleaning of freight containers
- tank cars Freight containers on rail and on. wheel (tank cars) usual carry only one specific product, in contrast to vehicles transport-of dry goods, which after a relatively simple cleaning procedure may be loaded with almost any product.
- tank cars having to return empty for new consignment of the same goods, are that their cleanin has proved very difficult and, furthermore, that the most difficult part of the cleaning process is the appropriate treatment of the waste water formed.
- Tank cars on rail ca various nutrive fatty acids, fuel oils, heavy, medium hea and light gasoline, liquified gas, gas, chemicals such as sodium hydroxide, nitric acid, ammonia, sulphuric acid, hydrochloric acid, resinous liquids, such as urea melamin phenol resins, different latexes for the rubber, the pape and the plastics industries, organic chemicals, a large amount of more or less toxic, usually all inflammable rea to-use chemicals, mixtures such as soaps, printing colour solvents, spent liquors of the pulp industry, just to mention a few examples.
- the freight containers are cleaned with a cleansing liquid usually an alkaline liquid containing surfactants.
- Organic compounds naturally dissolve only to a small exten in these cleansing liquids; they are always -partly emulsif and thus the cleansing liquids withdrawn from the freight container may contain from a few promille up to between 10 and 15 per cent of organic compounds.
- An appropriate furth treatment of these liquids requires that the volatile orga compounds, as well as the emulsified easily volatile organ compounds, be removed from the cleansing liquid. This is most easily done by steam stripping.
- Soda which may be precipitated with lime compounds, is intentionally used as an alkaline agent in the cleansing liquid.
- Waste product lime if readily available, is naturally used for said precipitation operation, but calcium hydroxide may also be used in this context.
- fly ash with a relatively high content of incombustible carbon, is also added. It is already known in the art that incombustible carbon in fly ash very easily absorbs organic substances. In this respect, it resembles so called activated carbon. This kind of fly ash has therefore proved difficult to use i.a. in the production of cement and concrete. Moreover, i is known that fly ash can be fractioned so that the carbon contained in the fly ash is enriched in the finer fraction
- the apparatus in accordance with the invention is, in its turn, characterized by what is stated in teh characterizi part of claim 7.
- an integrated process in which all was are reused, the cleansing liquids and their heat content circulated, without causing any load to the waste waters the atmosphere.
- a unit that operates according to the met is able to treat cleansing liquids containing organic com pounds in volatile, non-volatile or emulsified form, or i any solid form suspended in water. Furthermore, no risk o fire or explosion is in any stage of the process involved the unit or the freight container.
- a liquid solution of sodium carbonate which also contain surfactants, such as sulphonated alkyl aryl compounds or lignosulphonate acids or sulphonated fatty acids, is used cleansing liquid for a freight container.
- the cleansing liquid is pumped from its container 1 to a washing means placed in the freight container 2.
- the washer may either installed in fixed position, or fitted for movement withi the container on wheels or track belts.
- the freight conta may naturally also be completely manually washed.
- the used cleansing liquid which contains dissolved inorg compounds, emulsified organic compounds and solid pre ⁇ cipitates, is then conducted via a duct to a separation tank 4, in which the organic phase lighter than water is separated upon standing.
- the aqueous phase is, in its tur pumped to a distillation column 5, in which a part of the feed water is vaporized, a large fraction of the remainin organic substances being vaporized and distilled together with the water vapour.
- These organic substances which co stitute the overhead product of the stripping process, ar further decanted in another separation tank (decanter) 6, and the upper layer, that is the organic fraction, is com ⁇ bined in an intermediary tank 11 with the organic fraction obtained from the separation tank 4.
- the combined fraction are fed to a combustion unit 7, where they are used as fue
- the combustion unit comprises a fluidized bed combustion unit.
- a tank 8 equipped with an impeller where said substances are precipitated.
- calcium hydroxide and fly ash with high carbon content are introduced into the mixing tank 8.
- the content of incombustible carbon in the fly ash used should be at least 3 %, preferably at least 15 %. Instead fly ash some other similar activated waste carbon product or, alternatively, ordinary activated carbon may be used.
- the mixed slurry containing precipitates is conducted from the tank 8 to a filter 9.
- the filter may comprise, e.g, a sand filter or a pressure filter.
- the sand filtering apparatus preferably consists of two separate unit, one of them being regenerated while the other one is operating.
- the sand filter may be of any type of apparatus known per se. In the process according to the invention, the cycle time of a pressure filter is rather short, typically, between 10 and 20 minutes. Even one filter unit is, in thi case, enough.
- a preferable pressure filtering apparatus is supplied by Larox Oy, Lappeenranta, Finland.
- the filterability of the precipitate-containing slurry from tank 8 is extremely goo when using a pressure filter. Comparative filtering tests have demonstrated that, for this slurry, the filtering capacity of a pressure filter is as much as 20 times as hi as the average filtering capacity of the filter, and 10 times as high as the one previously achieved when filterin a slurry of fly ash and water. We do not yet completely understand all the reasons underlying this phenomenon, bu it is possible that the small calcium carbonate crystals hinder clogging of fly ash particles and thus greatly improve the filterability.
- the jammed filter 9 is blown * with air to displace as much residual liquid as possible.
- the sand of the sand filter is fed into the combustion uni 7.
- the sand from the filter 9 is used as the material for the fluidized bed in the combustion unit.
- the combustible organic impurities in the sand are properly combusted, the sand is regenerated and the calcium carbonate in the sand is regenerated as well. Because of its fine structure, the regenerated calcium oxid may be separated from the sand in said process and, according to the invention, returned to the precipitation process.
- the sand need not be circulated between the fluidized bed combustion process an the pressure filter.
- the sodium hydroxide in the filtrate of the filtration process is then reconverted to sodium carbonate for use in the following cleaning operation.
- the conversion is ideally and integratedly done by treating said liquid in an absorber or scrubber 10 with flue gases of the above-mentioned combustion process, wher upon carbonation reoccurs. This provides also for the complete cleaning of the flue gas of said process. Only excess fly ash remains, the fly ash being free of carbon and thus more suitable for use, e.g., in the production of concrete and cement.
- the cleansing liquid circulates continuously between the cleaning-filtering-caustisation part of the process and the flue gas absorption part of the process. Further, some of the cleansing water remains in the moist sand, from whi it is evaporated during combustion, and further, some of t water is removed during flue gas absorption. Thus complete clean rinsing water, for which there is always a need, may be introduced in the water balance. This introduction of - water does not, either, cause any waste water emissions.
- furnaces and combustion apparatus may be used for combusting the solids obtained from filtration.
- Furnac using electric energy and as well as fuel-fired furnaces m be used, such as various plasma ovens and rotary kilns.
- it is important th the combustion of the organic impurities and the carbon co tained in the solids is as complete as possible.
- the cleansing liquid container ⁇ f the separation tanks 4 and 6, respectively, the distillation unit 5, the mixing tank 8 and the filter 9 may also be installed in a mobile unit, which may be driv close to the object that is to be cleaned.
- the filter cak from the filter 9 is combusted and destroyed in a separat fixed combustion unit 7. This embodiment enables the cleaning of freight containers, which cannot be transport to the process.
- An oily sludge was prepared from the following components
- This mixture was mixed in a barrel with a high-speed turb impeller and heated to 56°C for 20 minutes. After this pe 3.0 kg of soda was admixed and mixing was continued for another 5 minutes.
- the filtrate was analyzed for remaining oil with the CCI4- extraction-method.
- the oil-content was found to be less th 1 mg/1, i.e. within the limits of the measuring accuracy o the method.
- PE plastic bottles had been used. Samples taken of the bottles gave a detectable extra having an oil-content of less than 1 mg/1.
- Example 2 In accordance with the procedure of Example 1, an oily mixture was prepared having the same composition as above except for the additional components of 250 g of sunflower oil and 380 g of treacle (50 % sugar).
- the mixture was treated as described in Example 1, an analysis of the filtrate from the pressure filter showing that the oil content was still less than 1 mg/1.
- the sugar added to the mixture had not been adsorbed, i.e. the conce tration thereof corresponded to the calculated amount.
- Example 1 The filter cake from Example 1 (moisture 20 %) was combus in a 1 MW fluidized bed furnace at 860°C. Samples of the solid matter in the flue gases contained particles of the original fly ash and finely divided particles of CaO, the diameter of the latter being about 1/4 of that of the for No traces of carbon or oil could not be found in the soli matter samples collected from the flue gases after combus
- the used cleansing liquid was fed inte the separation tan where the oil phase was separated from the liquid upon standing.
- the aqueous phase was directly conducted to the mixing tank, where 40 g/1 of fine textured fly ash conta ning ca. 14 % incombustible carbon was added, as well as equivalent amount of lime (ca. 32 g/1, when expressed as calcium oxide).
- the liquid containing precipitates and calcium carbonate was pumped to the sand filter, where th solid substances were removed.
- the impurities present in the cleansing liquid in the pre cipitation process were so efficiently sorbed onto the calcium carbonate and fly ash particles that the water in circulation after filtering was only slightly opaque. The fore, the circulating water could be reused both for a similar and a different cleaning process. 10
- the sand with its impurities was transferr to the fluidized bed combustion unit, the calcium carbonate separated from the sand was returned to the precipitation process, and the sodium hydroxide from the cleansing liquid was conducted to the scrubber (gas cleaner), where it was converted into sodium hydroxide.
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Abstract
The invention concerns a method and an apparatus for cleaning freight containers and for treating and circulating the cleansing liquids. According to the invention, an aqueous soda-containing solution is used as cleansing liquid, volatile organic substances, if any, are separated from the cleansing liquid in a separation unit (4) and in a distillation unit (5) and the liquid obtained is then treated with lime and carbon-containing fly ash in a mixing unit (8). The impurities of the cleansing liquid are sorbed to the activated carbon and precipitate onto the calcium carbonate. The slurry is filtered and the solid material retained in the filter (9) is further fed to a combustion unit (7). Flue gases formed in the combustion unit (7) are treated with the filtrate, whereby sodium hydroxide in the filtrate is transformed into carbonate form and may be used as new cleansing liquid in combination with makeup chemicals. The volatile organic compounds are used as fuel in the combustion unit. The invention provides an integrated process, in which waste products may be used for treating cleansing liquids.
Description
Method and apparatus for cleaning freight containers as w as for treating and circulating the fluids used
This invention concerns a method in accordance with the p amble of claim 1 for cleaning freight containers, both ra way cars and truck trailers, as well as for treating and circulating the fluids used in the cleaning operation.
The invention also concerns an apparatus in accordance wi the preamble of claim 7 for treating liquids containing soda and water used in the cleaning of freight containers
Freight containers on rail and on. wheel (tank cars) usual carry only one specific product, in contrast to vehicles transport-of dry goods, which after a relatively simple cleaning procedure may be loaded with almost any product. The main reasons for tank cars having to return empty for new consignment of the same goods, are that their cleanin has proved very difficult and, furthermore, that the most difficult part of the cleaning process is the appropriate treatment of the waste water formed. Tank cars on rail ca various nutrive fatty acids, fuel oils, heavy, medium hea and light gasoline, liquified gas, gas, chemicals such as sodium hydroxide, nitric acid, ammonia, sulphuric acid, hydrochloric acid, resinous liquids, such as urea melamin phenol resins, different latexes for the rubber, the pape and the plastics industries, organic chemicals, a large amount of more or less toxic, usually all inflammable rea to-use chemicals, mixtures such as soaps, printing colour solvents, spent liquors of the pulp industry, just to mention a few examples. This already shows that freight containers carry a large variety of products, and that man of these have to be heated, unloaded when hot, many being very volatile, inflammable and explosive.
The freight containers are cleaned with a cleansing liquid usually an alkaline liquid containing surfactants.
Organic compounds naturally dissolve only to a small exten in these cleansing liquids; they are always -partly emulsif and thus the cleansing liquids withdrawn from the freight container may contain from a few promille up to between 10 and 15 per cent of organic compounds. An appropriate furth treatment of these liquids requires that the volatile orga compounds, as well as the emulsified easily volatile organ compounds, be removed from the cleansing liquid. This is most easily done by steam stripping.
In connection with this invention, it was surprisingly fou that waste products may be used for the cleaning of freigh containers, that is, for the treatment of the wastes in th containers. The procedure is economical and technically operational.
Soda, which may be precipitated with lime compounds, is intentionally used as an alkaline agent in the cleansing liquid. Waste product lime, if readily available, is naturally used for said precipitation operation, but calcium hydroxide may also be used in this context.
All the organic, dissolved and emulsified impurities do no precipitate on the surface of the carbonate crystals forme in the precipitation process. Therefore, fly ash with a relatively high content of incombustible carbon, is also added. It is already known in the art that incombustible carbon in fly ash very easily absorbs organic substances. In this respect, it resembles so called activated carbon. This kind of fly ash has therefore proved difficult to use i.a. in the production of cement and concrete. Moreover, i is known that fly ash can be fractioned so that the carbon contained in the fly ash is enriched in the finer fraction
More specifically, the method in accordance with the inven tion is mainly characterized by what is stated in the characterizing part of claim 1.
The apparatus in accordance with the invention is, in its turn, characterized by what is stated in teh characterizi
part of claim 7.
Considerable benefits are achieved by means of the invent
Thus, an integrated process is provided, in which all was are reused, the cleansing liquids and their heat content circulated, without causing any load to the waste waters the atmosphere. A unit that operates according to the met is able to treat cleansing liquids containing organic com pounds in volatile, non-volatile or emulsified form, or i any solid form suspended in water. Furthermore, no risk o fire or explosion is in any stage of the process involved the unit or the freight container.
In the following, the invention is more closely illustrat by the following description with reference to the accomp nying drawing, which represents a schematic flow diagram the method according to the invention.
A liquid solution of sodium carbonate, which also contain surfactants, such as sulphonated alkyl aryl compounds or lignosulphonate acids or sulphonated fatty acids, is used cleansing liquid for a freight container. The cleansing liquid is pumped from its container 1 to a washing means placed in the freight container 2. The washer may either installed in fixed position, or fitted for movement withi the container on wheels or track belts. The freight conta may naturally also be completely manually washed.
The used cleansing liquid, which contains dissolved inorg compounds, emulsified organic compounds and solid pre¬ cipitates, is then conducted via a duct to a separation tank 4, in which the organic phase lighter than water is separated upon standing. The aqueous phase is, in its tur pumped to a distillation column 5, in which a part of the feed water is vaporized, a large fraction of the remainin organic substances being vaporized and distilled together with the water vapour. These organic substances, which co stitute the overhead product of the stripping process, ar
further decanted in another separation tank (decanter) 6, and the upper layer, that is the organic fraction, is com¬ bined in an intermediary tank 11 with the organic fraction obtained from the separation tank 4. The combined fraction are fed to a combustion unit 7, where they are used as fue Preferably, the combustion unit comprises a fluidized bed combustion unit.
The bottom product of the distillation column 5, containin low-volatile, that is high-molecular weight organic compounds, resins, tars, precipitates, etc., is conducted to the following treatment in a tank 8 equipped with an impeller, where said substances are precipitated. During t precipitation process, calcium hydroxide and fly ash with high carbon content are introduced into the mixing tank 8. The content of incombustible carbon in the fly ash used should be at least 3 %, preferably at least 15 %. Instead fly ash some other similar activated waste carbon product or, alternatively, ordinary activated carbon may be used.
Sodium carbonate reacts with calcium hydroxide giving calcium carbonate, which is precipitated and deposited on the bottom of the mixing tank 8, and sodium hydroxide, whi remains in the aqueous phase.
The mixed slurry containing precipitates is conducted from the tank 8 to a filter 9. The filter may comprise, e.g, a sand filter or a pressure filter. The sand filtering apparatus preferably consists of two separate unit, one of them being regenerated while the other one is operating. The sand filter may be of any type of apparatus known per se. In the process according to the invention, the cycle time of a pressure filter is rather short, typically, between 10 and 20 minutes. Even one filter unit is, in thi case, enough. A preferable pressure filtering apparatus is supplied by Larox Oy, Lappeenranta, Finland.
Unexpectedly, it was found that the filterability of the precipitate-containing slurry from tank 8 is extremely goo
when using a pressure filter. Comparative filtering tests have demonstrated that, for this slurry, the filtering capacity of a pressure filter is as much as 20 times as hi as the average filtering capacity of the filter, and 10 times as high as the one previously achieved when filterin a slurry of fly ash and water. We do not yet completely understand all the reasons underlying this phenomenon, bu it is possible that the small calcium carbonate crystals hinder clogging of fly ash particles and thus greatly improve the filterability.
According to the invention, the jammed filter 9 is blown* with air to displace as much residual liquid as possible. The sand of the sand filter is fed into the combustion uni 7. According to one mode of application, which comprises using a fluidized bed combustion unit, the sand from the filter 9 is used as the material for the fluidized bed in the combustion unit. Thus, the combustible organic impurities in the sand are properly combusted, the sand is regenerated and the calcium carbonate in the sand is regenerated as well. Because of its fine structure, the regenerated calcium oxid may be separated from the sand in said process and, according to the invention, returned to the precipitation process.
When a pressure filter is used, the sand need not be circulated between the fluidized bed combustion process an the pressure filter.
The sodium hydroxide in the filtrate of the filtration process is then reconverted to sodium carbonate for use in the following cleaning operation. According to the present invention, the conversion is ideally and integratedly done by treating said liquid in an absorber or scrubber 10 with flue gases of the above-mentioned combustion process, wher upon carbonation reoccurs. This provides also for the complete cleaning of the flue gas of said process. Only excess fly ash remains, the fly ash being free of carbon
and thus more suitable for use, e.g., in the production of concrete and cement.
It is clear that substances such as glycols, sugars, soaps, etc., that are completely soluble in water, are not easily precipitated. This applies in particular to their low- molecular weight fractions. It is advisable to construct a separate cleansing liquid tank and a small evaporation uni for these substances, and to combust the evaporation resid in said combustion unit.
The cleansing liquid circulates continuously between the cleaning-filtering-caustisation part of the process and the flue gas absorption part of the process. Further, some of the cleansing water remains in the moist sand, from whi it is evaporated during combustion, and further, some of t water is removed during flue gas absorption. Thus complete clean rinsing water, for which there is always a need, may be introduced in the water balance. This introduction of - water does not, either, cause any waste water emissions.
It has been calculated that the present process is self- sufficient as regards heat, if 200 kg of essentially water insoluble organic oily substances are removed from each freight container by cleaning.
Within the scope of the present invention, several alternative embodiments of the invention differing from th one presented in the above flow diagram are conceivable. Thus, in addition to the preferred fluidized bed combustio unit, other furnaces and combustion apparatus may be used for combusting the solids obtained from filtration. Furnac using electric energy and as well as fuel-fired furnaces m be used, such as various plasma ovens and rotary kilns. In connection with the combustion process, it is important th the combustion of the organic impurities and the carbon co tained in the solids is as complete as possible.
According to the invention, the cleansing liquid container ιf the separation tanks 4 and 6, respectively, the
distillation unit 5, the mixing tank 8 and the filter 9 may also be installed in a mobile unit, which may be driv close to the object that is to be cleaned. The filter cak from the filter 9 is combusted and destroyed in a separat fixed combustion unit 7. This embodiment enables the cleaning of freight containers, which cannot be transport to the process.
Example 1
An oily sludge was prepared from the following components
Water 150 litres
Waste oil "Nefteslam, NL" 6.5 kg Heavy fuel oil (SNO-NL) 5.4 kg
Oily condensate NL 4.0 kg
This mixture was mixed in a barrel with a high-speed turb impeller and heated to 56°C for 20 minutes. After this pe 3.0 kg of soda was admixed and mixing was continued for another 5 minutes.
At the end of said time, excess oil was allowed to separa and raise to the surface. Thereafter, 95 % of the oil was removed from the surface by vacuum suction. The surface still had a thin, almost continuous oil film. The aqueous phase in the rest of the barrel contained 84 g of oil pe litre. The analysis of the oil content was performed by t chloroform-extraction method known per se and samples wer taken 2 hours after clarification.
An amount of 1.60 kg of slaked lime was admixed with the solution. Mixing was continued for 10 minutes after the addition. A sample was taken and transferred into a measuring cylinder, the calcium carbonate being allowed t precipitate and settle in the measuring cylinder for 5 minutes. A sample taken from the settled aqueous phase wa analyzed. It was found that the sample still contained 7 oil per litre; the main part of the oil was adsorbed on t surface of the precipitated and settled carbonate.
Fly ash (1.5 kg) having a carbon content of 20.3 LOI (loss of ignition) was added to the barrel that still contained the carbonate precipitate mixture, which was being mixed. Mixing was continued for 3 minutes and the mixture was filtered through a pressure filter for 10 minutes.
A completely clear filtrate free of any smell of oil was obtained. The pH of the filtrate was 11.3.
The filtrate was analyzed for remaining oil with the CCI4- extraction-method. The oil-content was found to be less th 1 mg/1, i.e. within the limits of the measuring accuracy o the method. During sampling, PE plastic bottles had been used. Samples taken of the bottles gave a detectable extra having an oil-content of less than 1 mg/1.
Example 2
In accordance with the procedure of Example 1, an oily mixture was prepared having the same composition as above except for the additional components of 250 g of sunflower oil and 380 g of treacle (50 % sugar).
The mixture was treated as described in Example 1, an analysis of the filtrate from the pressure filter showing that the oil content was still less than 1 mg/1. The sugar added to the mixture had not been adsorbed, i.e. the conce tration thereof corresponded to the calculated amount.
Example 3
Hydrogen peroxide having a concentration of 30 %, was admixed with the remaining 115 litres of the solution pre¬ pared according to Example 2, in order to oxidize the sugars. The hydrogen peroxide was added in an amount exceeding the theoretically calculated equivalent amount b 10 %. Upon filtration samples were taken and the oil and sugar contents determined. The analysis showed that the total amount of sugars in the filtrate was half the origin amount, the oil content still being less than 1 mg/1.
Example 4
Fluidized bed combustion
The filter cake from Example 1 (moisture 20 %) was combus in a 1 MW fluidized bed furnace at 860°C. Samples of the solid matter in the flue gases contained particles of the original fly ash and finely divided particles of CaO, the diameter of the latter being about 1/4 of that of the for No traces of carbon or oil could not be found in the soli matter samples collected from the flue gases after combus
Example 5
Cleaning of a freight container
A railway car, which had transported soya oil, was cleane with a cleansing liquid containing 0.3 g/1 alkyl aryl sulphonates and 20 g/1 soda (sodium carbonate). Approxima 3,000 1/h of liquid was used, at a temperature of ca 90°C About 50 kg of soya oil, which had been emulsified in the presence of surfactants, was obtained from the car, as we as ca. 40 kg of various unidentified precipitates.
The used cleansing liquid was fed inte the separation tan where the oil phase was separated from the liquid upon standing. The aqueous phase was directly conducted to the mixing tank, where 40 g/1 of fine textured fly ash conta ning ca. 14 % incombustible carbon was added, as well as equivalent amount of lime (ca. 32 g/1, when expressed as calcium oxide). The liquid containing precipitates and calcium carbonate was pumped to the sand filter, where th solid substances were removed.
The impurities present in the cleansing liquid in the pre cipitation process were so efficiently sorbed onto the calcium carbonate and fly ash particles that the water in circulation after filtering was only slightly opaque. The fore, the circulating water could be reused both for a similar and a different cleaning process.
10
After filtering, the sand with its impurities was transferr to the fluidized bed combustion unit, the calcium carbonate separated from the sand was returned to the precipitation process, and the sodium hydroxide from the cleansing liquid was conducted to the scrubber (gas cleaner), where it was converted into sodium hydroxide.
Claims
1. A method for cleaning freight containers and for trea and circulating the liquids used in the cleansing operati c h a r a c t e r i z e d by the steps of a) using an aqueous solution containing soda as clean liquid, b) separating the organic volatile compounds and substances lighter than water, if any, from the us cleansing liquid by decanting and/or distilling, c) treating the liquid thus obtained with lime and an activated carbon product, d) filtering the slurry obtained from step c, e) subjecting the solids retained in the filter to combustion in order to remove organic impurities a carbon, f) treating the filtrate of step d with the flue gas formed in the combustion operation of step e in or to convert sodium hydroxide in the filtrate to sod carbonate, and g) circulating the liquid obtained from step f and us it, possibly in combination with makeup chemicals, as cleansing liquid in step a.
2. A method in accordance with claim 1, c h a r a c t e i z e d by collecting calcium oxide which is regenerated during combustion in step e and recirculating it for use the precipitation process.
3. A method in accordance with claim 1 or 2, c h a r a t e r i z e d in that the slurry obtained from step c is filtered by means of sand, the solids-containing sand bei combusted in step e.
4. A method in accordance with claim 1 or 2, c h a r a t e r i z e d in that the slurry obtained from step c is filtered by means of a pressure filter, the filter cake obtained from the filtration being combusted in step e. 12
5. A method in accordance with one of claims 1 to 4, c h a r a c t e r i z e d by combusting the solids retain in the filter in a fluidized bed combustion unit.
6. A method in accordance with any preceeding claim, c h a r a c t e r i z e d in that the activated carbon product comprises either activated carbon separated from fly ash originating in coal combustion, or fly ash that in itself contains at least 3 %, preferably at least 15 % incombustible carbon.
7. An apparatus for treating soda-containing aqueous liquids to be used in the cleaning of freight containers, c h a r a c t e r i z e d in that it comprises - a first separation tank (4) for separating a fractio lighter than water from the cleansing liquid used fo cleaning the freight container (2),
- a distillation unit (5) for removing water-emulsifie compounds, if any, ~ a precipitation unit (8) equipped with means for feeding lime as well as an activated carbon product,
- a filter (9) for filtering the slurry obtained from the precipitation unit (8),
- a combustion unit (7) for treating the solid matter containing precipitates from the filter (9),
- a scrubber (10) for cleaning the flue gases of the combustion unit (7) by using the filtrate obtained from the filter (9), as well as
- means for connecting in series the first separation tank (4), the distillation unit (5), the precipitati unit (8) and the filter (9), and means for connectin the combustion unit (7) and the scrubber (10) in parallel with the filter (9).
8. An apparatus in accordance with claim 7, c h a r a c t e r i z e d by a second separation tank (6) connected t the upper end of the distillation unit (5) for separating that fraction of the distillate which is lighter than wate
9. An apparatus in accordance with claim 7 or 8, c h a r a c t e r i z e d by means for feeding the orga fractions obtained from the first and second separation tanks (4, 6) as fuel to the combustion unit (7).
10. An apparatus in accordance with any one of claims 7 c h a r a c t e r i z e d in that the filter (9) compri a pressure filter.
11. An apparatus in accordance with any one of claims 7 c h a r a c t e r i z e d in that the filter (9) compri a sand filter.
12. An apparatus in accordance with any preceeding claim c h a r a c t e r i z e d in that the combustion unit ( comprises 'a fluidized bed combustion unit.
Priority Applications (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT88904408T ATE79571T1 (en) | 1987-05-22 | 1988-05-11 | METHOD AND APPARATUS FOR CLEANING CONTAINERS AND FOR THE TREATMENT AND CIRCULATION OF THE LIQUIDS USED. |
DE8888904408T DE3873925T2 (en) | 1987-05-22 | 1988-05-11 | METHOD AND DEVICE FOR CLEANING CONTAINERS AND TREATING AND CIRCULATING THE LIQUIDS USED. |
NO890256A NO890256D0 (en) | 1987-05-22 | 1989-01-20 | PROCEDURE AND APPARATUS FOR CLEANING TRANSPORT CONTAINERS AND FOR TREATMENT AND CIRCULATION OF USED LIQUIDS. |
SU894742625A RU1814567C (en) | 1987-05-22 | 1989-11-21 | Method of washing freight containers |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
FI872279 | 1987-05-22 | ||
FI872279A FI78405C (en) | 1987-05-22 | 1987-05-22 | FOERFARANDE OCH ANLAEGGNING FOER TVAETTNING AV TRANSPORTBEHAOLLARE SAMT FOER BEHANDLING OCH CIRKULERING AV VAETSKOR ANVAENDA VID TVAETTNINGEN. |
Publications (1)
Publication Number | Publication Date |
---|---|
WO1988009226A1 true WO1988009226A1 (en) | 1988-12-01 |
Family
ID=8524529
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/FI1988/000071 WO1988009226A1 (en) | 1987-05-22 | 1988-05-11 | Method and apparatus for cleaning freight containers as well as for treating and circulating the fluids used |
Country Status (11)
Country | Link |
---|---|
US (1) | US4984593A (en) |
EP (1) | EP0375683B1 (en) |
AT (1) | ATE79571T1 (en) |
CA (1) | CA1307717C (en) |
DD (1) | DD270020A5 (en) |
DE (1) | DE3873925T2 (en) |
FI (1) | FI78405C (en) |
HU (1) | HU207006B (en) |
NO (1) | NO890256D0 (en) |
RU (1) | RU1814567C (en) |
WO (1) | WO1988009226A1 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1996013343A1 (en) * | 1994-10-28 | 1996-05-09 | Astra Aktiebolag | Cleaning system |
US6475459B1 (en) | 1997-09-08 | 2002-11-05 | Fp-Pigments Oy | Process for preparing calcium carbonate particles |
RU2610748C1 (en) * | 2016-02-02 | 2017-02-15 | Федеральное автономное учреждение "25 Государственный научно-исследовательский институт химмотологии Министерства обороны Российской Федерации" | Technological complex for decontamination of reservoirs after propellant fuel drainage |
CN111977993A (en) * | 2019-05-21 | 2020-11-24 | 江苏苏盐井神股份有限公司 | Device and method for performing desulfurization or ash melting on returned stone and returned sand pulping in soda production |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4040944C2 (en) * | 1990-12-20 | 1995-09-07 | Wacker Chemie Gmbh | Process for cleaning containers |
DE4127975A1 (en) * | 1991-08-23 | 1993-02-25 | Wue Umwelt Engineering Gmbh | Cleaning system for rinsing waste containers - treats different containers according to contents for subsequent reuse for identical waste |
DE4216383A1 (en) * | 1992-05-18 | 1993-11-25 | Siemens Ag | Process for cleaning a closed container |
DE19823899A1 (en) * | 1998-05-28 | 1999-12-02 | Basf Ag | Cleaning device for road and rail tankers using thermal degradation of vapor and off-gases before discharging to atmosphere |
WO2001090290A1 (en) * | 2000-05-21 | 2001-11-29 | Leda's - Deutschland | Water-soluble cleaning agent and cleaning method for product recovery |
CN110563235A (en) * | 2019-09-06 | 2019-12-13 | 山东理工大学 | Liquid tank truck evaporation and washing tank body waste water-waste gas combined treatment equipment and process |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4566912A (en) * | 1983-05-13 | 1986-01-28 | Seitz Enzinger Noll Maschinenbau Aktiengesellschaft | Method of regenerating alkali-containing wash solutions utilized for cleaning containers |
GB2179243A (en) * | 1985-08-19 | 1987-03-04 | William G Urbani | Tank cleaning system |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US1920626A (en) * | 1931-09-09 | 1933-08-01 | Koppers Co Inc | Separation and purification of gaseous mixtures |
US2324804A (en) * | 1942-07-11 | 1943-07-20 | John Van Gelderen | Apparatus for cleaning tanks |
US3607482A (en) * | 1969-08-11 | 1971-09-21 | Wilson & Co | Process of regeneration of metal treating solutions |
US4434069A (en) * | 1982-07-28 | 1984-02-28 | Purex Corporation | Plastic bottle cleaner |
-
1987
- 1987-05-22 FI FI872279A patent/FI78405C/en not_active IP Right Cessation
-
1988
- 1988-05-11 AT AT88904408T patent/ATE79571T1/en not_active IP Right Cessation
- 1988-05-11 HU HU883245A patent/HU207006B/en not_active IP Right Cessation
- 1988-05-11 DE DE8888904408T patent/DE3873925T2/en not_active Expired - Fee Related
- 1988-05-11 EP EP88904408A patent/EP0375683B1/en not_active Expired - Lifetime
- 1988-05-11 WO PCT/FI1988/000071 patent/WO1988009226A1/en active IP Right Grant
- 1988-05-13 CA CA000566825A patent/CA1307717C/en not_active Expired - Lifetime
- 1988-05-19 US US07/195,887 patent/US4984593A/en not_active Expired - Fee Related
- 1988-05-19 DD DD88315906A patent/DD270020A5/en not_active IP Right Cessation
-
1989
- 1989-01-20 NO NO890256A patent/NO890256D0/en unknown
- 1989-11-21 RU SU894742625A patent/RU1814567C/en active
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4566912A (en) * | 1983-05-13 | 1986-01-28 | Seitz Enzinger Noll Maschinenbau Aktiengesellschaft | Method of regenerating alkali-containing wash solutions utilized for cleaning containers |
GB2179243A (en) * | 1985-08-19 | 1987-03-04 | William G Urbani | Tank cleaning system |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1996013343A1 (en) * | 1994-10-28 | 1996-05-09 | Astra Aktiebolag | Cleaning system |
AU706299B2 (en) * | 1994-10-28 | 1999-06-10 | Astra Aktiebolag | Cleaning system |
US6202654B1 (en) * | 1994-10-28 | 2001-03-20 | Astra Aktiebolag | Cleaning system |
US6475459B1 (en) | 1997-09-08 | 2002-11-05 | Fp-Pigments Oy | Process for preparing calcium carbonate particles |
RU2610748C1 (en) * | 2016-02-02 | 2017-02-15 | Федеральное автономное учреждение "25 Государственный научно-исследовательский институт химмотологии Министерства обороны Российской Федерации" | Technological complex for decontamination of reservoirs after propellant fuel drainage |
CN111977993A (en) * | 2019-05-21 | 2020-11-24 | 江苏苏盐井神股份有限公司 | Device and method for performing desulfurization or ash melting on returned stone and returned sand pulping in soda production |
Also Published As
Publication number | Publication date |
---|---|
FI78405C (en) | 1989-08-10 |
CA1307717C (en) | 1992-09-22 |
DE3873925D1 (en) | 1992-09-24 |
FI78405B (en) | 1989-04-28 |
FI872279A0 (en) | 1987-05-22 |
FI872279A (en) | 1988-11-23 |
ATE79571T1 (en) | 1992-09-15 |
US4984593A (en) | 1991-01-15 |
NO890256L (en) | 1989-01-20 |
EP0375683B1 (en) | 1992-08-19 |
DE3873925T2 (en) | 1993-04-08 |
HU207006B (en) | 1993-03-01 |
DD270020A5 (en) | 1989-07-19 |
EP0375683A1 (en) | 1990-07-04 |
NO890256D0 (en) | 1989-01-20 |
RU1814567C (en) | 1993-05-07 |
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