CS246057B2 - Method of industrial waste detoxication with heavy metals' toxic salt complexes content - Google Patents
Method of industrial waste detoxication with heavy metals' toxic salt complexes content Download PDFInfo
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- CS246057B2 CS246057B2 CS83182A CS18283A CS246057B2 CS 246057 B2 CS246057 B2 CS 246057B2 CS 83182 A CS83182 A CS 83182A CS 18283 A CS18283 A CS 18283A CS 246057 B2 CS246057 B2 CS 246057B2
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- Prior art keywords
- acid
- mixture
- sludge
- washing
- suspension
- Prior art date
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- 229910001385 heavy metal Inorganic materials 0.000 title claims description 14
- 238000000034 method Methods 0.000 title claims description 8
- 150000003839 salts Chemical class 0.000 title claims description 8
- 231100000331 toxic Toxicity 0.000 title claims description 6
- 230000002588 toxic effect Effects 0.000 title claims description 6
- 239000002440 industrial waste Substances 0.000 title description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 20
- 239000010802 sludge Substances 0.000 claims description 15
- 239000000203 mixture Substances 0.000 claims description 13
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 239000002002 slurry Substances 0.000 claims description 10
- 238000005406 washing Methods 0.000 claims description 9
- 239000002253 acid Substances 0.000 claims description 7
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 7
- 239000000725 suspension Substances 0.000 claims description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- 239000000920 calcium hydroxide Substances 0.000 claims description 6
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 6
- 235000011116 calcium hydroxide Nutrition 0.000 claims description 6
- 229910001430 chromium ion Inorganic materials 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 6
- 238000000926 separation method Methods 0.000 claims description 6
- 239000007788 liquid Substances 0.000 claims description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 4
- 229910052751 metal Inorganic materials 0.000 claims description 4
- 239000002184 metal Substances 0.000 claims description 4
- 239000011368 organic material Substances 0.000 claims description 4
- 239000002699 waste material Substances 0.000 claims description 4
- 239000010985 leather Substances 0.000 claims description 3
- 150000007522 mineralic acids Chemical class 0.000 claims description 3
- 238000006386 neutralization reaction Methods 0.000 claims description 3
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 claims description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 claims description 2
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 claims description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 2
- 238000010306 acid treatment Methods 0.000 claims description 2
- 230000002378 acidificating effect Effects 0.000 claims description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 2
- 229910001424 calcium ion Inorganic materials 0.000 claims description 2
- 229910052804 chromium Inorganic materials 0.000 claims description 2
- 239000011651 chromium Substances 0.000 claims description 2
- 150000004679 hydroxides Chemical class 0.000 claims description 2
- 229910052742 iron Inorganic materials 0.000 claims description 2
- 239000005416 organic matter Substances 0.000 claims description 2
- 238000003756 stirring Methods 0.000 claims description 2
- 229910052725 zinc Inorganic materials 0.000 claims description 2
- 239000011701 zinc Substances 0.000 claims description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L sodium carbonate Substances [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims 3
- 229910000029 sodium carbonate Inorganic materials 0.000 claims 2
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical compound [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 claims 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims 1
- 229910001431 copper ion Inorganic materials 0.000 claims 1
- 238000001784 detoxification Methods 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 claims 1
- 239000011133 lead Substances 0.000 claims 1
- 229910021645 metal ion Inorganic materials 0.000 claims 1
- 150000002739 metals Chemical class 0.000 claims 1
- 229910017604 nitric acid Inorganic materials 0.000 claims 1
- 231100000719 pollutant Toxicity 0.000 claims 1
- 239000012716 precipitator Substances 0.000 claims 1
- 239000002689 soil Substances 0.000 claims 1
- 230000003381 solubilizing effect Effects 0.000 claims 1
- 239000000126 substance Substances 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 description 3
- 150000002500 ions Chemical class 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 150000001844 chromium Chemical class 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 229910021432 inorganic complex Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 150000002736 metal compounds Chemical class 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 231100000167 toxic agent Toxicity 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
- 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
- C02F1/52—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
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- 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
- C02F1/529—Processes or devices for preparing lime water
-
- 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
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/004—Sludge detoxification
-
- 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
- C02F2101/20—Heavy metals or heavy metal compounds
-
- 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
- C02F2101/30—Organic compounds
- C02F2101/303—Complexing 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
- C02F2103/22—Nature of the water, waste water, sewage or sludge to be treated from the processing of animals, e.g. poultry, fish, or parts thereof
- C02F2103/24—Nature of the water, waste water, sewage or sludge to be treated from the processing of animals, e.g. poultry, fish, or parts thereof from tanneries
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/06—Controlling or monitoring parameters in water treatment pH
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
Landscapes
- 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)
- Inorganic Chemistry (AREA)
- Treatment Of Sludge (AREA)
- Removal Of Specific Substances (AREA)
- Processing Of Solid Wastes (AREA)
Description
246057246057
Vynález §p',tý{íá způsdhu'detóxil^ce, prů;myslovýCh 7 bdpádů ,s obsahem toxickýchkomplexů solí těžkých kovů. Jde zejména okaly, které vznikají jpři průmyslovém <P£a- cování kůží. i II* / Při yyGlppyÁní μ vydělávání kůžkvznika-jí kaly*,Vktpťé ^h|atíu]í 80 až 95 % vody.Vzhledem ke své inu vysokému obsahu or-ganických materiálů by tyto kaly bylo· mož- :no s výhodou užít jako' hnojivá v případě,že by neobsahovaly vysoce toxické iontytěžkých kovů, velmi pasti ionty chrómu,' kte<, :ré se tam dostávají; z chemických slouče-nin, užívaných při zpracování kůží. ul ·;··ή,.The invention relates to a process for the preparation of toxic compounds containing heavy metal salt complexes. In particular, it is the oceans that are produced by the industrial skin treatment. In the case of the skin-sludge extraction, 80 to 95% of water is present. Because of its otherwise high organic content, the sludge can be advantageously used as a slurry. 'Fertilizers if they do not contain highly toxic heavy metal, very trapped by chromium ions,' kte ', get there; from chemical compounds used in leather processing. ul ·;
Spalování kalů je neekonomické vzhle-dem k vysokému obsahu vody. Existuje ce- ílá řada metod, jimiž je možno zahustit ko-loidní organické materiály přidáním vloč-ikovacích činidel k Usnadnění jejich flltro-vatelnosti, čímž však není odstraněn pro-blém hospodárného odstraňování vody. ’Sludge combustion is uneconomical due to the high water content. There are a number of methods by which colloidal organic materials can be thickened by the addition of flocculants to facilitate their filterability, thereby avoiding the problem of economically removing water. '
Kaly s vysokým obsahem vody se obvykleskladují v nádržích, popřípadě ve ysaltova*cích nádržích, avšak vzhledem k velmi, přís- ,ným předpisům pyochnaně životního,·prostře-dí je velmi obtížné zvolit vhodné místo protento účel.High-water sludges are usually stored in tanks or tanks, but due to the very stringent regulations of the environment, it is very difficult to select a suitable site for this purpose.
Prozatím nebylá hrámpvy.,úvphp<ipp^nost„-i·,;odstranění toxických materiálů a využitícenných složek odpadních kalů, aniž by bylnavržen způsob, kterým by bylo možno ten-to problém vyřešit.For the time being, the elimination of toxic materials and valuable waste sludge constituents has not been done, without suggesting a way to solve this problem.
Vynález šě^týká^tžpŮšdbůj^^jímŽ^jěí-fflOŽňoodstranit z uvedených odpadů soli těžkých ""kovů, zejména soli chrómu a zbytek, obsa-hující organické materiály a neodporujícípředpisům pro ochranu životního prostředíje pak možno využít v zemědělství. Vynálezje založen na zjištění, že sloučeniny těžkýchikovů, přítomné ve formě různých organic-kých nebo anorganických komplexů nebojejich sraženiny, nerozpustné ve vodě, jemožno rozložit anorganickými kyselinami aodstranit z kalů ve formě, která je rozpust-ná ve vodě. Předmětem vynálezu je způsob detoxikaceprůmyslových odpadů s obsahem toxickýchkomplexů solí těžkých kovů, zvláště odpadůprůmyslu pro> zpracování kůží, které obsa-hují komplexy toxických solí těžkých kovůa organické materiály, vyznačující se tím,že se suspenze homogenizuje vodou za stá-lého míchání za vzniku suspenze, která ob-sahuje nejvýše 100 kg/m3, s výhodou 20 až40 kg/m3 pevných látek, přidá se kyselinasírová a/nebo směs anorganických kyselinobsahující kyselinu chlorovodíkovou a/nebofosforečnou s obsahem alespoň 30 hmot-nostních % kyseliny sírové tak, že koncen-trace kyseliny nepřevýší 10 hmotnostních%, vztaženo' na celkovou hmotnost suspen-ze a pH směsi je nižší než 1 po ukončenémzpracování kyselinou, směs se alespoň ho-dinu míchá při teplotě místnosti, kyselereagující kapalina s obsahem solí těžkýchikovů se od kalu oddělí a po neutralizaci ky-selé směsi hydroxidem sodným, uhličitanem sodným nebo hydroxidem vápenatým se hyd-roxidy a/n'ebo uhličitany těžkých* kovů >vy-sráží při pH 8 až 10, čistí se promýváníma organický kal se vymývá tak dlouho, ažjft, prostý iontů kovu i kyseliny. V případě, že kyselinq nebo směs kyselin,užitých k rozkladu komplexů neobsahuje ky-selinu sírovou, je nasládne oddělení, sedi-montace a filtrace -suspenze podstatně ob-tížnější; než'. je tomu za přítomnosti kyselinysírové. ‘ ϋ ..Rychlost rozkladu komplexů je dostatečnájiž při teplotě místnosti, takže reakci je. možuo s .úspěchem provádět při původní tep-lotě suspenze, při vyšší'teplotě však dochá-zí ske kzvýšepí reakční ryfchlosti.The invention relates to the removal of heavy metal salts, in particular chromium salts, from the wastes mentioned, and the remainder containing organic materials and not to environmental regulations can then be used in agriculture. The present invention is based on the discovery that the heavy metal compounds present in the form of various organic or inorganic complexes or their water-insoluble precipitates can be decomposed by inorganic acids and removed from the sludge in a water-soluble form. SUMMARY OF THE INVENTION The present invention provides a method for detoxifying industrial wastes containing toxic heavy metal salt complexes, particularly wastes, for the treatment of skins containing complexes of heavy heavy metal salts and organic materials, characterized in that the slurry is homogenized with water to form a slurry. containing not more than 100 kg / m 3, preferably 20 to 40 kg / m 3 of solids, is added acid-acidic and / or a mixture of inorganic acids containing hydrochloric acid and / or phosphoric acid containing at least 30% by weight sulfuric acid such that the concentration the acid does not exceed 10% by weight, based on the total weight of the slurry, and the pH of the mixture is less than 1 after completion of the acid treatment, the mixture is stirred at room temperature for at least one hour, the acid-reacting liquid containing heavy metal salts is separated from the sludge and after neutralization of the ky of the mixture with sodium hydroxide, carbonate with sodium or calcium hydroxide, the hydroxides and / or heavy metal carbonates are precipitated at pH 8 to 10, the washing is cleaned, and the organic sludge is eluted for up to 10 minutes free of both metal and acid ions. If the acid or the mixture of acids used to decompose the complexes does not contain sulfuric acid, the separation, sedimentation and filtration of the suspension are considerably more difficult; than'. this is in the presence of sulfuric acid. The decomposition rate of the complexes is sufficient at room temperature, so the reaction is. at the initial temperature of the slurry, with higher temperatures, however, the reaction speed increases.
Po ukončení reakce, jejíž rychlost je zá-vislá;·na teplotě, se suspenze zahusti,, napří-klad tak, že se ionty těžkého kovu vymyjívodou nebo zředěnou kyselinou sírovou, zby-tek se neutralizuje hašeným vápnem a pakse z roztoku oddělí. . .··,,βοΐΐ. těžkého,. kovu, .oddělené od kalu, sěkoncentrují! vysrážením a pak se skladujijako' taková na. určeném místě nebo se poočistění znovu použijí. Způsob podle vyná-lezu je znázorněn blokovým diagramem naobr·..!. . , Příklad iUpon completion of the temperature-dependent reaction, the suspension is concentrated, for example, by washing heavy metal ions with dilute sulfuric acid, neutralizing the residue with slaked lime, and then separating it from the solution. . . ·· ,, βοΐΐ. heavy ,. metal, separated from the sludge, concentrate! by precipitation and then folding like that. the specified location or reuse. The method according to the invention is shown in the block diagram. . , Example i
Ionty chrómu se odstraní z fermentova-uého odpadbíhó ‘kalu po zpracování kůží snásledujícím složením:' osah sušiny , 200 kg/m3 obsah organických látek 100 kg/m3 obsah iontů chrómu ‘ ·">- 12 kg/m3 Káiy ηιίηίοίο obsahu jí 'ionty zinku a kad-mia a větší množství iontů železa a vápníku.Kál a se' smísí s Vedou b V objemovém po*rněru 1-6 v Momogenizátoru1 nebo se vtomto homogenizátord ‘ smísí s okyselenouvodou s obsahem iontů chrómu, která se vy-pouští z promývacího separačního systému.Získaná homogenní suspenze se přivádí dorekatoru 2, do něhož se rovněž přidává 150kilogramů’ kyseliny sírové co koncentraci96'% na 1 m3 suspenze a reakce se provádípři teplotě kalu za energického míchání’ 60minut. Pevný podíl suspenze se zahustí vseparátoru 3 a koncentrovaná suspenze sepřivádí do systému 4 prd promývání a sepa-raci a pak do systému 5 pro neutralizaci aSeparaci, jako výsledný produkt sé získávákal g, který je prostý iontů těžkých kovů akterý5 se neutra lizuje hašeným vápnem e.Zc systému 4 so promývací voda f přivádízpět do homogenizátoru 1. Ze separátoru 3se roztok s obsahem chrómu vede do Srá-žecího' zařízení 6, v němž se vysráží kovovésoli při pH 8 až 10, které se upraví působe-ním hašeného vápna. Sraženina i s obsahemiontů těžkého kovu se oddělí od alkalickyreagující vody v druhém separátoru 7.The chromium ions are removed from the fermented sludge after treatment with the following skin composition: dry solids content, 200 kg / m 3 organic matter content 100 kg / m 3 chromium ion content · · 12 kg / m 3 kai ηιίηίοίο its content ions zinc and cadmium and a greater amount of iron and calcium ions. The calcium and admixture are mixed with the vapor b in volume 1-6 in the Momogenizer 1 or mixed with the acidic water containing chromium ions from the homogenizer. The resulting homogeneous slurry is fed to dorekatore 2, to which 150 kilograms of sulfuric acid is also added at a concentration of 96% per m 3 of slurry, and the reaction is carried out at the sludge temperature with vigorous stirring for 60 minutes. the slurry feeds into the system 4 washing and separation, and then into the system 5 for neutralization and separation, as a result of the obtaining a heavy metal ion-free g, which is neutralized with slaked lime from the system 4, the washing water f is fed to the homogenizer 1. From the separator 3, the chromium-containing solution is fed to a precipitation apparatus 6 in which metal salts are precipitated at pH 8 to 10 which are treated with slaked lime. The heavy metal-containing precipitate is separated from the alkaline-reacting water in the second separator 7.
Claims (2)
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
HU82100A HU185194B (en) | 1982-01-14 | 1982-01-14 | Method for detoxication mixing tannery sewage sludges |
Publications (1)
Publication Number | Publication Date |
---|---|
CS246057B2 true CS246057B2 (en) | 1986-10-16 |
Family
ID=10947909
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CS83182A CS246057B2 (en) | 1982-01-14 | 1983-01-11 | Method of industrial waste detoxication with heavy metals' toxic salt complexes content |
Country Status (10)
Country | Link |
---|---|
CS (1) | CS246057B2 (en) |
DD (1) | DD209430A5 (en) |
DE (1) | DE3301120A1 (en) |
ES (1) | ES518907A0 (en) |
GB (1) | GB2113199B (en) |
HU (1) | HU185194B (en) |
IT (1) | IT1160174B (en) |
PL (1) | PL139584B1 (en) |
RO (1) | RO86780B (en) |
YU (1) | YU6383A (en) |
Families Citing this family (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE3428535A1 (en) * | 1984-08-02 | 1986-02-13 | Siekmann, Helmut E., Prof.Dr.-Ing., 1000 Berlin | METHOD AND DEVICE, IN PARTICULAR FOR THE CONDITIONING OF SEWAGE SLUDGE |
DE3503199C2 (en) * | 1985-01-31 | 1987-03-19 | Hölter, Heinz, Dipl.-Ing., 4390 Gladbeck | Process for producing a soil improver or a fertilizer from sewage sludge |
DE3627253C2 (en) * | 1986-08-12 | 1995-06-22 | Linde Ag | Process for the biological treatment of substrates containing organic substances |
DE3919788C1 (en) * | 1989-06-16 | 1990-07-05 | Siebtechnik Gmbh, 4330 Muelheim, De | |
FI97288C (en) * | 1993-08-26 | 1996-11-25 | Kemira Oy | Procedure for treatment of wastewater sludge |
ITRM20010671A1 (en) * | 2001-11-12 | 2003-05-12 | Sicit Chemitech S P A | CHROME-BASED PRODUCT IN COMPOSITION WITH HYDROLYZED PROTEINS AND PROCESS FOR ITS OBTAINING. |
AU2003900241A0 (en) * | 2003-01-21 | 2003-02-06 | Australian Organic Resources Pty Ltd | The extraction and treatment of heavy metals in sewage sludge |
ITRM20050425A1 (en) * | 2005-08-05 | 2007-02-06 | Sicit Chemitech S P A | PROCESS FOR THE PRODUCTION OF PRODUCTS BASED ON HYDRAULIC PROTEINS IN COMPOSITION WITH MANGANESE. |
JP5985925B2 (en) * | 2012-08-20 | 2016-09-06 | 水ing株式会社 | Method and apparatus for treating waste liquid containing heavy metal |
-
1982
- 1982-01-14 HU HU82100A patent/HU185194B/en not_active IP Right Cessation
-
1983
- 1983-01-10 RO RO109659A patent/RO86780B/en unknown
- 1983-01-11 ES ES518907A patent/ES518907A0/en active Granted
- 1983-01-11 CS CS83182A patent/CS246057B2/en unknown
- 1983-01-12 PL PL1983240123A patent/PL139584B1/en unknown
- 1983-01-12 YU YU00063/83A patent/YU6383A/en unknown
- 1983-01-12 DD DD83247194A patent/DD209430A5/en unknown
- 1983-01-13 IT IT19091/83A patent/IT1160174B/en active
- 1983-01-14 DE DE19833301120 patent/DE3301120A1/en not_active Withdrawn
- 1983-01-14 GB GB08300987A patent/GB2113199B/en not_active Expired
Also Published As
Publication number | Publication date |
---|---|
ES8402549A1 (en) | 1984-03-01 |
GB8300987D0 (en) | 1983-02-16 |
GB2113199B (en) | 1985-07-10 |
HU185194B (en) | 1984-12-28 |
YU6383A (en) | 1985-10-31 |
RO86780B (en) | 1985-05-31 |
GB2113199A (en) | 1983-08-03 |
PL139584B1 (en) | 1987-02-28 |
DE3301120A1 (en) | 1983-07-28 |
DD209430A5 (en) | 1984-05-09 |
IT8319091A0 (en) | 1983-01-13 |
RO86780A (en) | 1985-05-20 |
ES518907A0 (en) | 1984-03-01 |
IT1160174B (en) | 1987-03-04 |
PL240123A1 (en) | 1984-06-18 |
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