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CH617642A5 - Process for purifying effluents containing heavy metal compounds - Google Patents

Process for purifying effluents containing heavy metal compounds Download PDF

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Publication number
CH617642A5
CH617642A5 CH541075A CH541075A CH617642A5 CH 617642 A5 CH617642 A5 CH 617642A5 CH 541075 A CH541075 A CH 541075A CH 541075 A CH541075 A CH 541075A CH 617642 A5 CH617642 A5 CH 617642A5
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CH
Switzerland
Prior art keywords
heavy metal
metal compounds
containing heavy
effluents containing
waters
Prior art date
Application number
CH541075A
Other languages
Italian (it)
Inventor
Carlo Piccinini
Fabio Federici
Original Assignee
Tecneco Spa
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tecneco Spa filed Critical Tecneco Spa
Publication of CH617642A5 publication Critical patent/CH617642A5/en

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/70Treatment of water, waste water, or sewage by reduction
    • C02F1/705Reduction by metals
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29CSHAPING OR JOINING OF PLASTICS; SHAPING OF MATERIAL IN A PLASTIC STATE, NOT OTHERWISE PROVIDED FOR; AFTER-TREATMENT OF THE SHAPED PRODUCTS, e.g. REPAIRING
    • B29C44/00Shaping by internal pressure generated in the material, e.g. swelling or foaming ; Producing porous or cellular expanded plastics articles
    • B29C44/34Auxiliary operations
    • B29C44/36Feeding the material to be shaped
    • B29C44/46Feeding the material to be shaped into an open space or onto moving surfaces, i.e. to make articles of indefinite length
    • B29C44/467Foam spreading or levelling devices
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29CSHAPING OR JOINING OF PLASTICS; SHAPING OF MATERIAL IN A PLASTIC STATE, NOT OTHERWISE PROVIDED FOR; AFTER-TREATMENT OF THE SHAPED PRODUCTS, e.g. REPAIRING
    • B29C44/00Shaping by internal pressure generated in the material, e.g. swelling or foaming ; Producing porous or cellular expanded plastics articles
    • B29C44/34Auxiliary operations
    • B29C44/58Moulds
    • B29C44/588Moulds with means for venting, e.g. releasing foaming gas
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29CSHAPING OR JOINING OF PLASTICS; SHAPING OF MATERIAL IN A PLASTIC STATE, NOT OTHERWISE PROVIDED FOR; AFTER-TREATMENT OF THE SHAPED PRODUCTS, e.g. REPAIRING
    • B29C33/00Moulds or cores; Details thereof or accessories therefor
    • B29C33/10Moulds or cores; Details thereof or accessories therefor with incorporated venting means
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29CSHAPING OR JOINING OF PLASTICS; SHAPING OF MATERIAL IN A PLASTIC STATE, NOT OTHERWISE PROVIDED FOR; AFTER-TREATMENT OF THE SHAPED PRODUCTS, e.g. REPAIRING
    • B29C37/00Component parts, details, accessories or auxiliary operations, not covered by group B29C33/00 or B29C35/00
    • B29C37/006Degassing moulding material or draining off gas during moulding

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 Water By Oxidation Or Reduction (AREA)
  • Removal Of Specific Substances (AREA)
  • Catalysts (AREA)

Description

La presente invenzione si riferisce ad un procedimento per la depurazione delle acque di scarico nelle quali siano disciolti composti del cromo, del mercurio o di altri metalli pesanti. The present invention relates to a process for purifying waste water in which compounds of chromium, mercury or other heavy metals are dissolved.

E' noto in letteratura il processo di riduzione del Cr*-6 a Cr*3 che si avvale di Fe metallico. Il processo comunque non ha trovato larga applicazione industriale a causa soprattutto dell'elevato consumo di Fe, responsabile a sua volta dell'ottenimento di forti quantità di fanghi da smaltire e di un consumo dell'agente precipitante [Ca(OH)2 o NaOH] superiore rispetto ai processi tradizionali (S02 e bisolfito). The process of reducing Cr * -6 to Cr * 3 which uses metallic Fe is known in the literature. However, the process has not found a large industrial application mainly due to the high consumption of Fe, which in turn is responsible for obtaining large quantities of sludge to be disposed of and consumption of the precipitating agent [Ca (OH) 2 or NaOH]. higher than traditional processes (S02 and bisulfite).

D'altra parte, come è facile verificare, se la reazione avvenisse con un consumo di Fe uguale al teorico il processo risulterebbe economicamente vantaggioso. On the other hand, as it is easy to verify, if the reaction took place with a consumption of Fe equal to the theoretical one, the process would be economically advantageous.

Abbiamo ora trovato che regolando opportunamente il pH della soluzione da trattare e la velocità lineare della stessa nel sistema di riduzione, è possibile realizzare il processo con consumo di Fe molto vicino al teorico, senza che si abbiano contemporaneamente fenomeni di passivazione del metallo nel tempo; tali fenomeni sono infatti dovuti alla formazione di una pellicola passivata sulla superficie del metallo, che porta alla lunga alla completa disattivazione dello stesso; se il pH in uscita da! sistema di riduzione viene tenuto al di sotto del valore in corrispondenza del quale si ha precipitazione di Fe come idrossido, tali fenomeni vengono annullati. We have now found that by appropriately adjusting the pH of the solution to be treated and the linear speed of the same in the reduction system, it is possible to carry out the process with consumption of Fe very close to the theoretical, without simultaneously having passivation phenomena of the metal over time; these phenomena are in fact due to the formation of a passivated film on the metal surface, which in the long run leads to the complete deactivation of the same; if the pH leaving! reduction system is kept below the value at which there is precipitation of Fe as hydroxide, these phenomena are canceled.

Il procedimento per la depurazione delle acque di scarico contenenti composti di metalli pesanti dell'invenzione è definito nella rivendicazione 1. The process for purifying waste water containing heavy metal compounds of the invention is defined in claim 1.

Più particolarmente il procedimento dell'invenzione viene realizzato facendo fluire l'acqua da trattare attraverso una o più colonne riempite con l'elemento meno nobile rispetto all'idrogeno sotto forma di granuli, sfere, barrette, trucioli o qualsiasi forma compatibile con le dimensioni della colonna stessa. More particularly, the process of the invention is carried out by making the water to be treated flow through one or more columns filled with the less noble element than hydrogen in the form of granules, balls, bars, shavings or any shape compatible with the dimensions of the column itself.

La reazione che avviene al passaggio dell'acqua comporta l'ossidazione dell'elemento allo stato zero e la contemporanea riduzione dell'inquinante a stadi di ossidazione inferiori o addirittura allo stato metallico. The reaction that occurs when the water passes involves oxidation of the element in the zero state and the simultaneous reduction of the pollutant in lower oxidation stages or even in the metallic state.

Ad esempio se uno ione di un metallo multivalente appartiene ad un gruppo anionico, il procedimento dà origine ad un sale dello stesso metallo in un più basso stato di valenza, facilmente eliminabile con tecniche note. Al contrario, se l'acqua contiene il sale di un metallo nobile, il procedimento dà origine al corrispondente metallo. For example, if an ion of a multivalent metal belongs to an anionic group, the process gives rise to a salt of the same metal in a lower state of valence, which can be easily eliminated with known techniques. On the contrary, if the water contains the salt of a noble metal, the process gives rise to the corresponding metal.

Così i cromati sono ridotti a sali del cromo trivalente, ed i sali di rame o mercurio a rame o mercurio metallico rispettivamente. Thus the chromates are reduced to salts of trivalent chromium, and the salts of copper or mercury to copper or metallic mercury respectively.

Le reazioni che avvengono in alcuni dei casi menzionati si possono così schematizzare, supponendo di impiegare il ferro quale elemento elettropositivo 3 Fe + Cr207= + 14 H+ 3 Fe2+ + 2 Cr3+ + 7 H20 The reactions that occur in some of the cases mentioned can be summarized as follows, assuming iron is used as an electropositive element 3 Fe + Cr207 = + 14 H + 3 Fe2 + + 2 Cr3 + + 7 H20

1 7 1 7

3 Fe2+ + — Cr207= + 7H+ # 3 Fe3+ + Cr3+ — H20 3 Fe2 + + - Cr207 = + 7H + # 3 Fe3 + + Cr3 + - H20

2 2 2 2

nel caso dei cromati, mentre nel caso dei metalli nobili si può schematizzare n Fe + 2 Men+ n Fe2+ + 2 Me in the case of chromates, while in the case of noble metals it is possible to schematize n Fe + 2 Men + n Fe2 + + 2 Me

Me essendo il metallo nobile, ad esempio, come detto, rame o mercurio, ed n il suo stato di ossidazione. Being the noble metal, for example, as mentioned, copper or mercury, and its oxidation state.

La reazione decorre senza rifornimento di energia dall'esterno, a pH inferiori od uguali a 3. The reaction starts without external energy supply, at pH lower than or equal to 3.

Il procedimento di depurazione secondo la presente invenzione può essere realizzato ad elevate portate di alimentazione, anzi è un aspetto particolarmente vantaggioso del procedimento lavorare alle portate più alte possibili in funzione del pH e della concentrazione dell'inquinante: infatti, a parità di quantità di inquinante ridotto, all'aumentare della portata il consumo dell'elemento elettropositivo si avvicina sensibilmente al teorico. The purification process according to the present invention can be carried out at high feed rates, indeed it is a particularly advantageous aspect of the process to work at the highest possible flows according to the pH and concentration of the pollutant: in fact, with the same quantity of pollutant reduced, as the flow rate increases, the consumption of the electropositive element approaches the theoretical significantly.

L'invenzione sarà più chiaramente comprensibile dall'esame dei seguenti esempi illustrativi, che, tuttavia, non intendono limitarne gli scopi. The invention will be more clearly understandable by examining the following illustrative examples, which, however, are not intended to limit their purposes.

Esempio 1 Influenza del PH Example 1 Influence of PH

Una colonna del diametro pari a 2,7 cm viene riempita con granuli cilindrici di Fe (0 =4 mm, h = 6 mm); attraverso tale colonna vengono fatte fluire soluzioni contenenti Cr+6, a diversi pH. A column with a diameter of 2.7 cm is filled with cylindrical granules of Fe (0 = 4 mm, h = 6 mm); through this column solutions containing Cr + 6 are made to flow, at different pH.

Tutte le prove sono state condotte a portata costante; i risultati ottenuti sono riportati nella tabella 1. All tests were conducted at a constant flow rate; the results obtained are shown in table 1.

Esempio 2 Influenza della portata Example 2 Influence of flow rate

Nella stessa colonna di cui all'esempio precedente e con lo stesso volume di riempimento, sono state condotte alcune prove a pH costante variando la portata. In the same column as in the previous example and with the same filling volume, some tests were conducted at constant pH by varying the flow rate.

I risultati sono riassunti nella tabella 2. The results are summarized in table 2.

Esempio 3 Influenza della velocità lineare Example 3 Influence of linear speed

320 cm3 di Fe sono stati collocati successivamente in tre colonne di diametro diverso, attraverso cui è stata fatta fluire una soluzione contenente Cr*6, mantenendo costante la portata ed il pH, in modo da realizzare lo stesso tempo di contatto tra soluzione e riempimento, in corrispondenza di tre velocità lineari diverse. 320 cm3 of Fe were subsequently placed in three columns of different diameters, through which a solution containing Cr * 6 was made to flow, keeping the flow rate and pH constant, so as to achieve the same contact time between solution and filling, at three different linear speeds.

I risultati sono sintetizzati nella tabella 3. The results are summarized in table 3.

TABELLA 1 TABLE 1

Cr+6 ingresso mg/1 Cr + 6 mg / 1 input

Cr*6 uscita mg/1 Cr * 6 mg / 1 output

PH PH

Consumo di Fe Kg Fe/Kg Cr ridotto Reduced consumption of Fe Kg Fe / Kg Cr

30 30

< 0,02 <0.02

0,3 0.3

10 10

30 30

<0,02 <0.02

1 1

7 7

30 30

<0,02 <0.02

2 2

2 2

30 30

<0,02 <0.02

2,5 2.5

1,1 1.1

5 5

10 10

15 15

20 20

25 25

30 30

35 35

40 40

45 45

50 50

55 55

60 60

65 65

3 3

617642 617642

TABELLA 2 TABLE 2

„ . Q Cr« uscita „ Co"sucm° Fe: ". Q Cr «exit" Co "sucm ° Fe:

Cr+e ingresso ,, pH KgFe/Kg Cr + and input ,, pH KgFe / Kg

1/h mg/1 Cr ridotto 1 / h mg / 1 Cr reduced

300 300

6 6

<0,02 <0.02

1 1

2,2 2.2

300 300

8 8

< 0,02 <0.02

1 1

2,0 2.0

300 300

10 10

<0,02 <0.02

1 1

1,8 1.8

300 300

16 16

<0,02 <0.02

1 1

1,26 1.26

TABELLA 3 TABLE 3

Cr1-6 ingresso „ Q 0 colonna Cr+6 uscita mg/1 p 1/h cm mg/1 Cr1-6 inlet "Q 0 column Cr + 6 outlet mg / 1 p 1 / h cm mg / 1

168 1 32 2 3,2 168 1 32 2 3.2

168 1 32 2,7 17,5 168 1 32 2.7 17.5

168 1 32 4,1 42,5 168 1 32 4.1 42.5

Esempio 4 Influenza del diametro della colonna Example 4 Influence of the column diameter

Operando su colonne di diametro diverso, si è osservato, 5 come mostrato in tabella 4, che, a parità di portata di alimentazione, la quantità di Fe necessaria per la riduzione totale del Cr0+ a Cr3+ è tanto più piccola quanto minore è il diametro della colonna stessa. Operating on columns of different diameters, it has been observed, 5 as shown in table 4, that, for the same flow rate, the amount of Fe necessary for the total reduction of Cr0 + to Cr3 + is much smaller the smaller the diameter of the column itself.

io TABELLA 4 i TABLE 4

Cr+6 ingresso mg/1 Cr + 6 mg / 1 input

PH PH

Q Q

1/h 1 / h

Fe (g) Fe (g)

cm 9,7 9.7 cm

cm 4,1 4.1 cm

15 32 15 32

2,03 2.03

40 40

1050 1050

1500 1500

32 32

2,03 2.03

80 80

1550 1550

2050 2050

32 32

2,03 2.03

120 120

1800 1800

2600 2600

20 32 20 32

2,03 2.03

160 160

1950 1950

3050 3050

25 25

V V

Claims (3)

617642617642 1. Procedimento per la depurazione delle acque di scarico contenenti composti di metalli pesanti consistente nel mettere in contatto tali acque con un elemento scelto tra quelli meno nobili rispetto all'idrogeno, caratterizzato dal fatto che l'acqua da trattare viene fatta fluire attraverso una o più colonne riempite con l'elemento meno nobile sotto forma di granuli, sfere, barrette, trucioli o qualsiasi forma compatibile con le dimensioni della colonna stessa e che la reazione avviene a pH inferiori o uguali a 3. 1. A process for the purification of waste water containing heavy metal compounds consisting of putting these waters in contact with an element chosen from among those less noble than hydrogen, characterized in that the water to be treated is made to flow through one or more columns filled with the less noble element in the form of granules, spheres, bars, shavings or any shape compatible with the dimensions of the column itself and that the reaction takes place at pH lower than or equal to 3. 2. Procedlimento secondo la rivendicazione 1, caratterizzato dal fatto che le acque da trattare contengono cromati e l'elemento impiegato è il ferro. 2. Process according to claim 1, characterized in that the waters to be treated contain chromates and the element used is iron. 2 2 RIVENDICAZIONI 3. Procedimento secondo la rivendicazione 2, caratterizzato dal fatto che il pH in uscita dal sistema di riduzione viene tenuto al di sotto del valore in corrispondenza del quale si ha la precipitazione del ferro come idrossido. 3. Process according to claim 2, characterized in that the pH output from the reduction system is kept below the value at which the precipitation of iron as hydroxide occurs.
CH541075A 1974-05-08 1975-04-28 Process for purifying effluents containing heavy metal compounds CH617642A5 (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
IT22396/74A IT1010486B (en) 1974-05-08 1974-05-08 PROCEDURE FOR THE PURIFICATION OF WASTE WATER

Publications (1)

Publication Number Publication Date
CH617642A5 true CH617642A5 (en) 1980-06-13

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ID=11195718

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CH541075A CH617642A5 (en) 1974-05-08 1975-04-28 Process for purifying effluents containing heavy metal compounds

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JP (1) JPS50152557A (en)
AT (2) AT346253B (en)
BE (1) BE828570A (en)
CH (1) CH617642A5 (en)
CS (1) CS202546B2 (en)
DD (1) DD118051A5 (en)
DE (1) DE2520531A1 (en)
DK (1) DK196775A (en)
ES (1) ES437875A1 (en)
FI (1) FI751142A (en)
FR (1) FR2270209B1 (en)
GB (1) GB1474145A (en)
IE (1) IE41336B1 (en)
IL (1) IL47073A (en)
IT (1) IT1010486B (en)
LU (1) LU72427A1 (en)
NL (1) NL7505514A (en)
NO (1) NO751626L (en)
PL (1) PL111038B1 (en)
RO (1) RO69366A (en)
SE (1) SE7505290L (en)
TR (1) TR19213A (en)
YU (1) YU103975A (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2613128C2 (en) * 1976-03-27 1982-03-04 Hoechst Ag, 6000 Frankfurt Process for reducing the mercury content of industrial wastewater
DE3321451A1 (en) * 1982-06-16 1983-12-22 Occidental Chemical Corp., 48089 Warren, Mich. DEVICE AND METHOD FOR REMOVING COPPERIONS FROM AQUEOUS SOLUTIONS
DE3411228C1 (en) * 1984-03-27 1985-05-30 Du Pont de Nemours (Deutschland) GmbH, 4000 Düsseldorf Process for the environmentally friendly purification of photographic wash water from film processing machines and apparatus for carrying out the process
DE4217987A1 (en) * 1992-05-30 1993-12-02 Battelle Institut E V Removal and recovery of heavy metals from earth, sludges and waterways - by amalgamation and sedimentation of esp. mercury@, nickel@ and cobalt@ and their cpds., by addn. of powered zinc@ or aluminium@
DE69308311T2 (en) * 1992-09-18 1997-09-11 Krueger As I METHOD FOR PURIFYING METAL-CONTAINING AQUEOUS LIQUIDS AND METHOD FOR PRODUCING AN ADSORBENT
DE102007045337B4 (en) * 2007-09-22 2021-01-07 Bayerische Motoren Werke Aktiengesellschaft Procedure for protection against dust containing chromium (VI)

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2177656B1 (en) * 1972-03-31 1979-02-16 Lewandowski Raymond

Also Published As

Publication number Publication date
CS202546B2 (en) 1981-01-30
NO751626L (en) 1975-11-11
AT346253B (en) 1978-11-10
LU72427A1 (en) 1975-08-26
DK196775A (en) 1975-11-09
SE7505290L (en) 1975-11-10
IE41336B1 (en) 1979-12-05
GB1474145A (en) 1977-05-18
FR2270209A1 (en) 1975-12-05
FR2270209B1 (en) 1980-04-18
ATA390876A (en) 1979-01-15
YU103975A (en) 1982-02-28
AU8013875A (en) 1976-10-21
JPS50152557A (en) 1975-12-08
IL47073A (en) 1978-07-31
IT1010486B (en) 1977-01-10
ATA351775A (en) 1978-02-15
AT351775B (en) 1978-02-15
BE828570A (en) 1975-08-18
DD118051A5 (en) 1976-02-12
RO69366A (en) 1981-07-30
TR19213A (en) 1978-06-07
ES437875A1 (en) 1977-01-01
PL111038B1 (en) 1980-08-30
IL47073A0 (en) 1975-06-25
FI751142A (en) 1975-11-09
NL7505514A (en) 1975-11-11
DE2520531A1 (en) 1975-11-13
IE41336L (en) 1975-11-08

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