CN109384277A - The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater - Google Patents
The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater Download PDFInfo
- Publication number
- CN109384277A CN109384277A CN201811320911.7A CN201811320911A CN109384277A CN 109384277 A CN109384277 A CN 109384277A CN 201811320911 A CN201811320911 A CN 201811320911A CN 109384277 A CN109384277 A CN 109384277A
- Authority
- CN
- China
- Prior art keywords
- parts
- heavy metal
- chinese medicine
- medicine slag
- bagasse
- Prior art date
- Legal status (The legal status 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 status listed.)
- Pending
Links
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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- 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
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- 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
- 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
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular 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
- C02F2101/10—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
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/16—Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
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)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention discloses a kind of composite treating agents of comprehensive removal heavy metal out of electroplating wastewater, including sodium pyrosulfite, polyepoxy sodium succinate, tetren dithiocar-bamate, Expanded rice husk powder, cross-linked rectorite, shell powder, flocculant, calcium hydroxide, modified Chinese medicine slag, ferric trichloride, bagasse, aminodithioformic acid chitosan, MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride;Heavy metal is effectively fixed by components such as aminodithioformic acid chitosans, chemistry, physical absorption and ion exchange adsorption directly occurs with heavy metal ion such as lead, cadmiums by the other components such as Expanded rice husk powder, cross-linked rectorite and shell powder, modified Chinese medicine slag, wherein modified Chinese medicine slag has larger and more absorption hole, large specific surface area, more adsorption sites are capable of providing, achieve the effect that multiple absorption.
Description
Technical field
The present invention relates to wastewater treatment, in particular to a kind of composite treating agent of comprehensive removal heavy metal out of electroplating wastewater.
Background technique
Plating is metal and nonmetallic surface to be decorated, protected and obtained certain new capabilities using the method for electrochemistry
A kind of technical process.In electroplating industry, common plating has nickel plating, copper facing, chromium plating, zinc-plated etc..In the plating process, in order to
The quality for guaranteeing electroplated product makes the coat of metal have flat and smooth good appearance and be firmly combined with plating piece, it is necessary to plate
It is preceding that dirt (oil, rust, oxide skin etc.) thorough cleaning on plating piece surface is clean, and the attachment liquid after plating plating piece surface is clear
Wash clean.Therefore, a large amount of waste water are necessarily discharged in plating production process.And the source of electroplating wastewater is generally comprised than wide
Several below: 1. plating piece cleans waste water;2. electroplating effluent;3. other waste water, including wash away mill floor, scrub floor and lead to
Wind devices condensed water and as coating bath leakage or operational administrative it is improper caused by run, drip, leak various tank liquors and draining;④
Component cooling water, component cooling water is in use in addition to cooling, the typically no pollution by heavy metal.Wherein, it plates
Part ejected wash water is the main source of electroplating wastewater, almost accounts for 80% or more of plant effluent discharge amount.Due to plating piece functional requirement
Difference, plating, bath composition, mode of operation, process conditions etc. are also different, and therefore, the pollutant of electroplating wastewater is very complicated, mainly
Contain the metal ions such as chromium, copper, nickel, lead, gold, silver, cadmium, wherein the heavy metal ion such as chromium, copper, nickel, zinc for containing and cyanide
Etc. being more toxic, some belong to carcinogenic, teratogenesis, mutagenic extremely toxic substance, do great harm to human beings.
Summary of the invention
In view of this, the purpose of the present invention is to provide a kind of combined processings of comprehensive removal heavy metal out of electroplating wastewater
Agent can accelerate the sinking speed of heavy metal ion, can preferably adsorb the heavy metal in waste water, improve the contact machine of reaction
Rate improves chelatropic reaction, redox validity, effectively to increase contact effect of the heavy metal chelating agent with heavy metal
Various heavy in removal system enables the total removal rate of comprehensive wastewater heavy metal to reach 99% or more.
The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater of the invention, the compound formulation raw material is by weight
Including following components:
10-20 parts of sodium pyrosulfites, 5-10 parts of polyepoxy sodium succinates, 1-5 parts of tetren dithiocarbamates first
Hydrochlorate, 1-3 parts of Expanded rice husk powder, 1-5 parts of cross-linked rectorite, 5-10 parts of shell powder, 1-3 parts of flocculant, calcium hydroxide 4-8
Part, modified Chinese medicine slag 4-8 parts, 1-3 parts of ferric trichloride, 1-5 parts of bagasse, 1-5 parts of aminodithioformic acid chitosan, methyl-prop
1-3 parts of alkene acyloxyethyl trimethyl ammonium chloride, the modified Chinese medicine slag are prepared by following manner:
The modified Chinese medicine slag is prepared by following manner:
A. prepare fluid matrix: by weight by 0.05 part of vitamin B1,1-5 parts of tween, 25-35 parts of potassium dihydrogen phosphate,
5-15 parts of epsom salt, 0.1-1 parts of calcium chloride dihydrate, 1-5 parts of ammonium tartrate and 100-200 parts of micro-mixed liquor are mixed
It closes;
B. it is added in fluid matrix into the Chinese medicine slag after dries pulverizing, 5.0% yellow archespore Mao Pingge is accessed after sterilizing
It is sealed after bacterium bacteria suspension, cultivates at 37 DEG C 7-10 days, then dry Chinese medicine slag at 60-70 DEG C;
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 60-80 mesh be 350-400 DEG C in temperature at calcination processing 1-2 hour, cool down
Ball-milling treatment 2-4 hours after the aqueous citric acid solution that the concentration that equivalent weight is added afterwards is 15%, slurries are collected;
D. pH to 7-8 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, stands 3- after 40-50 minutes sonicated
It 5 hours, collects cooling after sediment is calcined 1-2 hours at 600-700 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 80-100 mesh, the sodium hydroxide solution that concentration is 20% is then added, is stirred under room temperature
3-4 hours, with deionized water washes clean repeatedly after filtering, in temperature be at 60-70 DEG C it is 12-14 hours dry;
F. after bagasse processed in step e being mixed with concentration for 5% sodium hydroxide solution and epoxychloropropane
It is heated to 50-60 DEG C of stirring 5-6 hours, will generate after product filters and deionized water stirring is added, it is 27% that concentration, which is then added,
Ethylenediamine solution and concentration be 1.5% sodium bicarbonate solution, 80-100 DEG C of reaction 5-6 hours is then heated to, by gained
Being washed in turn with acetone and deionized water to product pH value after product filtering is neutrality, is finally filtered gained bagasse in temperature
It is 12-13 hours dry at 60-70 DEG C;
Further, the compound formulation raw material includes following components by weight:
15 parts of sodium pyrosulfites, 7 parts of polyepoxy sodium succinates, 3 parts of tetren dithiocar-bamates, extrudings
2 parts of powdered rice hulls, 3 parts of cross-linked rectorite, 7 parts of shell powder, 2 parts of flocculant, 6 parts of calcium hydroxide, modified 6 parts of Chinese medicine slag, trichlorine
Change 2 parts of iron, 3 parts of bagasse, 3 parts of aminodithioformic acid chitosan, 2 parts of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride;
Further, the flocculant is the mixture of polyacrylamide, dehydration polymerization ferric sulfate and polyglutamic acid, by quality
Than polyacrylamide: dehydration polymerization ferric sulfate: polyglutamic acid=2:3:1;
Further, the modified Chinese medicine slag is the mixture of Radix Isatidis and cape jasmine;
Further, the Phanerochaete chrysosporium content of the Phanerochaete chrysosporium bacteria suspension is 1.0 × 106A/mL;
Further, in step b, the Chinese medicine slag after drying is crushed to 40-60 mesh.
Beneficial effects of the present invention: the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater of the invention, Neng Goujia
The sinking speed of fast heavy metal ion, can preferably adsorb the heavy metal in waste water, improve the contact probability of reaction, to increase
Contact effect of the metal traps with heavy metal is aggravated, chelatropic reaction, redox validity is improved, effectively removes in system
Various heavy enables the total removal rate of comprehensive wastewater heavy metal to reach 99% or more.It is poly- by aminodithioformic acid shell
Heavy metal is effectively fixed in the components such as sugar, by Expanded rice husk powder, cross-linked rectorite and shell powder, modified Chinese medicine slag etc. other
Directly with heavy metal ion such as lead, cadmiums chemistry, physical absorption and ion exchange adsorption occur for component, wherein modified Chinese medicine slag tool
There is larger and more absorption hole, large specific surface area is capable of providing more adsorption sites, achieve the effect that multiple absorption,
The sludge yield of sodium pyrosulfite is low, small toxicity, acts on heavy metal ion unrestraint, calcium hydroxide, ferric trichloride, hydroxide
Calcium and sodium pyrosulfite act synergistically, and accelerate the precipitating of small molecule heavy metal particles, and processed bagasse is inhaled with multilayer
Attached effect, to Cr3+、Cu2+And Pb2+Suction-operated with super strength.
Specific embodiment
Embodiment one
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
10 parts of sodium pyrosulfites, 5 parts of polyepoxy sodium succinates, 1 part of tetren dithiocar-bamate, extruding
1 part of powdered rice hulls, 1 part of cross-linked rectorite, 5 parts of shell powder, 1 part of flocculant, 4 parts of calcium hydroxide, modified 4 parts of Chinese medicine slag, trichlorine
Change 1 part of iron, 1 part of bagasse, 1 part of aminodithioformic acid chitosan, 1 part of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride, institute
Modified Chinese medicine slag is stated to prepare by following manner:
A. fluid matrix is prepared: by weight by 0.05 part of vitamin B1,3 parts of tween, 30 parts of potassium dihydrogen phosphate, seven water sulphur
5 parts of sour magnesium, 1 part of calcium chloride dihydrate, 4 parts of ammonium tartrate and 180 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 55 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) seal afterwards, cultivate 7 days at 37 DEG C, then will in
The dregs of a decoction are dried at 64 DEG C;
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 60 mesh be 350 DEG C in temperature at calcination processing 1 hour, be added after cooling same
Ball-milling treatment 2 hours after the aqueous citric acid solution that the concentration of weight is 15%, slurries are collected;
D. pH to 7 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, it is sonicated to stand 3 hours after forty minutes,
It collects cooling after sediment is calcined 1 hour at 600 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 80 mesh, the sodium hydroxide solution that concentration is 20% (w/w) is then added, is stirred under room temperature
3 hours, with deionized water washes clean repeatedly after filtering, in temperature be at 60 DEG C it is 12 hours dry;
F. bagasse processed in step e and concentration is mixed for the sodium hydroxide solution and epoxychloropropane of 5% (w/w)
It is heated to 50 DEG C after conjunction to stir 5 hours, will generate after product filters and deionized water stirring is added, it is 27% that concentration, which is then added,
(w/w) sodium bicarbonate solution that ethylenediamine solution and concentration is 1.5% (w/w), is then heated to 80 DEG C and reacts 5 hours, will
Being washed in turn with acetone and deionized water to product pH value after products therefrom filtering is neutrality, finally filters and gained bagasse exists
Temperature is 12 hours dry at 60 DEG C.
Embodiment two
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
It is 20 parts of sodium pyrosulfites, 10 parts of polyepoxy sodium succinates, 5 parts of tetren dithiocar-bamates, swollen
Change 3 parts of powdered rice hulls, 5 parts of cross-linked rectorite, 10 parts of shell powder, 3 parts of flocculant, 8 parts of calcium hydroxide, modified 8 parts of Chinese medicine slag, three
3 parts of iron chloride, 5 parts of bagasse, 5 parts of aminodithioformic acid chitosan, 3 parts of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride,
The modified Chinese medicine slag is prepared by following manner:
A. fluid matrix is prepared: by weight by 0.08 part of vitamin B1,1 part of tween, 35 parts of potassium dihydrogen phosphate, seven water sulphur
5 parts of sour magnesium, 1 part of calcium chloride dihydrate, 1 part of ammonium tartrate and 200 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 40 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) it seals afterwards, it cultivates at 37 DEG C 10 days, then will
Chinese medicine slag is dried at 60 DEG C.
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 80 mesh be 400 DEG C in temperature at calcination processing 2 hours, be added after cooling same
Ball-milling treatment 4 hours after the aqueous citric acid solution that the concentration of weight is 15%, slurries are collected;
D. pH to 8 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, stands 5 hours after sonicated 50 minutes,
It collects cooling after sediment is calcined 2 hours at 700 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 100 mesh, the sodium hydroxide solution that concentration is 20% (w/w) is then added, is stirred under room temperature
Mix 4 hours, with deionized water washes clean repeatedly after filtering, in temperature be at 70 DEG C it is 14 hours dry;
F. bagasse processed in step e and concentration is mixed for the sodium hydroxide solution and epoxychloropropane of 5% (w/w)
It is heated to 60 DEG C after conjunction to stir 6 hours, will generate after product filters and deionized water stirring is added, it is 27% that concentration, which is then added,
(w/w) sodium bicarbonate solution that ethylenediamine solution and concentration is 1.5% (w/w), is then heated to 100 DEG C and reacts 6 hours, will
Being washed in turn with acetone and deionized water to product pH value after products therefrom filtering is neutrality, finally filters and gained bagasse exists
Temperature is 13 hours dry at 70 DEG C.
Embodiment three
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
It is 10 parts of sodium pyrosulfites, 10 parts of polyepoxy sodium succinates, 1 part of tetren dithiocar-bamate, swollen
Change 3 parts of powdered rice hulls, 1 part of cross-linked rectorite, 10 parts of shell powder, 1 part of flocculant, 8 parts of calcium hydroxide, modified 4 parts of Chinese medicine slag, three
3 parts of iron chloride, 1 part of bagasse, 5 parts of aminodithioformic acid chitosan, 1 part of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride,
The modified Chinese medicine slag is prepared by following manner:
A. fluid matrix is prepared: by weight by 0.05 part of vitamin B1,1 part of tween, 35 parts of potassium dihydrogen phosphate, seven water sulphur
5 parts of sour magnesium, 1 part of calcium chloride dihydrate, 1 part of ammonium tartrate and 200 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 40 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) it seals afterwards, it cultivates at 37 DEG C 10 days, then will
Chinese medicine slag is dried at 60 DEG C.
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 60 mesh be 400 DEG C in temperature at calcination processing 1 hour, be added after cooling same
Ball-milling treatment 4 hours after the aqueous citric acid solution that the concentration of weight is 15%, slurries are collected;
D. pH to 7 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, stands 3 hours after sonicated 50 minutes,
It collects cooling after sediment is calcined 1 hour at 700 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 80 mesh, the sodium hydroxide solution that concentration is 20% (w/w) is then added, is stirred under room temperature
3 hours, with deionized water washes clean repeatedly after filtering, in temperature be at 70 DEG C it is 14 hours dry;
F. bagasse processed in step e and concentration is mixed for the sodium hydroxide solution and epoxychloropropane of 5% (w/w)
It is heated to 50 DEG C after conjunction to stir 6 hours, will generate after product filters and deionized water stirring is added, it is 27% that concentration, which is then added,
(w/w) sodium bicarbonate solution that ethylenediamine solution and concentration is 1.5% (w/w), is then heated to 80 DEG C and reacts 6 hours, will
Being washed in turn with acetone and deionized water to product pH value after products therefrom filtering is neutrality, finally filters and gained bagasse exists
Temperature is 13 hours dry at 60 DEG C.
Example IV
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
20 parts of sodium pyrosulfites, 5 parts of polyepoxy sodium succinates, 5 parts of tetren dithiocar-bamates, extrudings
1 part of powdered rice hulls, 5 parts of cross-linked rectorite, 5 parts of shell powder, 3 parts of flocculant, 4 parts of calcium hydroxide, modified 8 parts of Chinese medicine slag, trichlorine
Change 1 part of iron, 5 parts of bagasse, 1 part of aminodithioformic acid chitosan, 3 parts of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride, institute
Modified Chinese medicine slag is stated to prepare by following manner:
A. fluid matrix is prepared: by weight by 0.08 part of vitamin B1,5 parts of tween, 35 parts of potassium dihydrogen phosphate, seven water sulphur
15 parts of sour magnesium, 1 part of calcium chloride dihydrate, 5 parts of ammonium tartrate and 200 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 60 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) it seals afterwards, it cultivates at 37 DEG C 10 days, then will
Chinese medicine slag is dried at 70 DEG C.
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 80 mesh be 350 DEG C in temperature at calcination processing 2 hours, be added after cooling same
Ball-milling treatment 2 hours after the aqueous citric acid solution that the concentration of weight is 15%, slurries are collected;
D. pH to 8 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, it is sonicated to stand 5 hours after forty minutes,
It collects cooling after sediment is calcined 2 hours at 600 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 100 mesh, the sodium hydroxide solution that concentration is 20% (w/w) is then added, is stirred under room temperature
Mix 4 hours, with deionized water washes clean repeatedly after filtering, in temperature be at 60 DEG C it is 12-14 hours dry;
F. bagasse processed in step e and concentration is mixed for the sodium hydroxide solution and epoxychloropropane of 5% (w/w)
It is heated to 60 DEG C after conjunction to stir 5 hours, will generate after product filters and deionized water stirring is added, it is 27% that concentration, which is then added,
(w/w) sodium bicarbonate solution that ethylenediamine solution and concentration is 1.5% (w/w), is then heated to 100 DEG C and reacts 5 hours, will
Being washed in turn with acetone and deionized water to product pH value after products therefrom filtering is neutrality, finally filters and gained bagasse exists
Temperature is 12 hours dry at 70 DEG C.
Embodiment five
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
15 parts of sodium pyrosulfites, 5 parts of polyepoxy sodium succinates, 5 parts of tetren dithiocar-bamates, extrudings
2 parts of powdered rice hulls, 1 part of cross-linked rectorite, 10 parts of shell powder, 2 parts of flocculant, 6 parts of calcium hydroxide, modified 4 parts of Chinese medicine slag, trichlorine
Change 3 parts of iron, 4 parts of bagasse, 2 parts of aminodithioformic acid chitosan, 1 part of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride, institute
Modified Chinese medicine slag is stated to prepare by following manner:
A. fluid matrix is prepared: by weight by 0.05 part of vitamin B1,1 part of tween, 25 parts of potassium dihydrogen phosphate, seven water sulphur
5 parts of sour magnesium, 0.1 part of calcium chloride dihydrate, 1 part of ammonium tartrate and 100 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 40 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) seal afterwards, cultivate 7 days at 37 DEG C, then will in
The dregs of a decoction are dried at 60 DEG C.
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 70 mesh be 380 DEG C in temperature at calcination processing 1.5 hours, be added after cooling same
Etc. weight concentration be 15% aqueous citric acid solution after ball-milling treatment 2.5 hours, collect slurries;
D. pH to 7 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, stands 4 hours after sonicated 45 minutes,
It collects cooling after sediment is calcined 1.5 hours at 620 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 90 mesh, the sodium hydroxide solution that concentration is 20% is then added, stirring 3.5 is small under room temperature
When, with deionized water washes clean repeatedly after filtering, in temperature be at 65 DEG C it is 13 hours dry;
F. after bagasse processed in step e being mixed with concentration for 5% sodium hydroxide solution and epoxychloropropane
It is heated to 55 DEG C to stir 5.5 hours, will generate after product filters and deionized water stirring is added, the second that concentration is 27% is then added
The sodium bicarbonate solution that diamine solution and concentration are 1.5% is then heated to 90 DEG C and reacts 5.5 hours, products therefrom is filtered
It is neutral for being washed in turn with acetone and deionized water to product pH value afterwards, is finally filtered gained bagasse in the case where temperature is 65 DEG C
It is 12.5 hours dry.
Embodiment six
The composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of the present embodiment, the compound formulation raw material is by weight
Part includes following components:
15 parts of sodium pyrosulfites, 7 parts of polyepoxy sodium succinates, 3 parts of tetren dithiocar-bamates, extrudings
2 parts of powdered rice hulls, 3 parts of cross-linked rectorite, 7 parts of shell powder, 2 parts of flocculant, 6 parts of calcium hydroxide, modified 6 parts of Chinese medicine slag, trichlorine
Change 2 parts of iron, 3 parts of bagasse, 3 parts of aminodithioformic acid chitosan, 2 parts of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride;Institute
Modified Chinese medicine slag is stated to prepare by following manner:
A. fluid matrix is prepared: by weight by 0.06 part of vitamin B1, tween 3,30 parts of potassium dihydrogen phosphate, seven water sulfuric acid
10 parts of magnesium, 0.61 part of calcium chloride dihydrate, 3 parts of ammonium tartrate and 150 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix to dries pulverizing into the cape jasmine of 50 mesh and the Radix Isatidis dregs of a decoction, 5.0% is accessed after sterilizingPhanerochaete chrysosporium bacteria suspension (content be 1.0 × 106A/mL) seal afterwards, cultivate 8 days at 37 DEG C, then will in
The dregs of a decoction are dried at 65 DEG C;
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 75 mesh be 360 DEG C in temperature at calcination processing 1.8 hours, be added after cooling same
Etc. weight concentration be 15% aqueous citric acid solution after ball-milling treatment 2.5 hours, collect slurries;
D. pH to 8 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, it is small that 3.8 are stood after sonicated 48 minutes
When, it collects cooling after sediment is calcined 1.8 hours at 680 DEG C of temperature;
The bagasse is through following process:
E. bagasse powder is broken to 90 mesh, the sodium hydroxide solution that concentration is 20% is then added, stirring 3 is small under room temperature
When, with deionized water washes clean repeatedly after filtering, in temperature be at 68 DEG C it is 12 hours dry;
F. after bagasse processed in step e being mixed with concentration for 5% sodium hydroxide solution and epoxychloropropane
It is heated to 58 DEG C to stir 5.5 hours, will generate after product filters and deionized water stirring is added, the second that concentration is 27% is then added
The sodium bicarbonate solution that diamine solution and concentration are 1.5% is then heated to 95 DEG C and reacts 5.5 hours, products therefrom is filtered
It is neutral for being washed in turn with acetone and deionized water to product pH value afterwards, is finally filtered gained bagasse in the case where temperature is 68 DEG C
It is 12 hours dry.
In above-described embodiment, the flocculant is the mixture of polyacrylamide, dehydration polymerization ferric sulfate and polyglutamic acid,
Polyacrylamide in mass ratio: dehydration polymerization ferric sulfate: polyglutamic acid=2:3:1;The molecular weight of polyacrylamide is 4,000,000,
The modified Chinese medicine slag is the mixture of Radix Isatidis and cape jasmine;The Phanerochaete chrysosporium of the Phanerochaete chrysosporium bacteria suspension
Content is 1.0 × 106A/mL.
Electroplating wastewater processing is carried out using the composite treating agent of the comprehensive removal heavy metal out of electroplating wastewater of this method compounding,
Treatment effect is as follows, unit mg/L:
Finally, it is stated that the above examples are only used to illustrate the technical scheme of the present invention and are not limiting, although referring to compared with
Good embodiment describes the invention in detail, those skilled in the art should understand that, it can be to skill of the invention
Art scheme is modified or replaced equivalently, and without departing from the objective and range of technical solution of the present invention, should all be covered at this
In the scope of the claims of invention.
Claims (6)
1. a kind of composite treating agent of comprehensive removal heavy metal out of electroplating wastewater, it is characterised in that: the compound formulation raw material is pressed
Parts by weight include following components:
10-20 parts of sodium pyrosulfites, 5-10 parts of polyepoxy sodium succinates, 1-5 parts of tetren dithiocar-bamates,
1-3 parts of Expanded rice husk powder, 5-10 parts of shell powder, 1-3 parts of flocculant, 4-8 parts of calcium hydroxide, is modified 1-5 parts of cross-linked rectorite
4-8 parts of Chinese medicine slag, 1-3 parts of ferric trichloride, 1-5 parts of bagasse, 1-5 parts of aminodithioformic acid chitosan, methacryloxypropyl
1-3 parts of ethyl-trimethyl salmiac;
The modified Chinese medicine slag is prepared by following manner:
A. fluid matrix is prepared: by weight by 0.05 part of vitamin B1,1-5 parts of tween, 25-35 parts of potassium dihydrogen phosphate, seven water
5-15 parts of magnesium sulfate, 0.1-1 parts of calcium chloride dihydrate, 1-5 parts of ammonium tartrate and 100-200 parts of micro-mixed liquor mixing;
B. it is added in fluid matrix into the Chinese medicine slag after dries pulverizing, 5.0% Phanerochaete chrysosporium bacterium is accessed after sterilizing
It is sealed after suspension, cultivates at 37 DEG C 7-10 days, then dry Chinese medicine slag at 60-70 DEG C;
The cross-linked rectorite is handled by following manner:
C. by cross-linked rectorite be crushed to after 60-80 mesh be 350-400 DEG C in temperature at calcination processing 1-2 hour, add after cooling
Ball-milling treatment 2-4 hours after the aqueous citric acid solution that the concentration for entering equivalent weight is 15%, slurries are collected;
D. pH to 7-8 is adjusted after sodium hydrate aqueous solution is added dropwise into slurries, it is small to stand 3-5 after 40-50 minutes sonicated
When, it collects cooling after sediment is calcined 1-2 hours at 600-700 DEG C of temperature
The bagasse is through following process:
E. bagasse powder is broken to 80-100 mesh, the sodium hydroxide solution that concentration is 20% is then added, stirring 3-4 is small under room temperature
When, with deionized water washes clean repeatedly after filtering, in temperature be at 60-70 DEG C it is 12-14 hours dry;
F. it is heated after bagasse processed in step e being mixed with concentration for 5% sodium hydroxide solution and epoxychloropropane
To 50-60 DEG C stirring 5-6 hours, will generate product filter after be added deionized water stirring, then be added concentration be 27% second
The sodium bicarbonate solution that diamine solution and concentration are 1.5%, is then heated to 80-100 DEG C of reaction 5-6 hours, by products therefrom
It is neutral for being washed in turn to product pH value after filtering with acetone and deionized water, finally filters and is in temperature by gained bagasse
It is 12-13 hours dry at 60-70 DEG C.
2. the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater according to claim 1, it is characterised in that: described
Compound formulation raw material includes following components by weight:
15 parts of sodium pyrosulfites, 7 parts of polyepoxy sodium succinates, 3 parts of tetren dithiocar-bamates, extruding rice husk
2 parts of powder, 3 parts of cross-linked rectorite, 7 parts of shell powder, 2 parts of flocculant, 6 parts of calcium hydroxide, modified 6 parts of Chinese medicine slag, ferric trichloride 2
Part, 3 parts of bagasse, 3 parts of aminodithioformic acid chitosan, 2 parts of MethacryloyloxyethylTrimethyl Trimethyl Ammonium Chloride.
3. the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater according to claim 1, it is characterised in that: described
Flocculant is the mixture of polyacrylamide, dehydration polymerization ferric sulfate and polyglutamic acid, in mass ratio polyacrylamide: dehydration is poly-
Close ferric sulfate: polyglutamic acid=2:3:1.
4. the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater according to claim 3, it is characterised in that: described
Modified Chinese medicine slag is the mixture of Radix Isatidis and cape jasmine.
5. the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater according to claim 4, it is characterised in that: described
The Phanerochaete chrysosporium content of Phanerochaete chrysosporium bacteria suspension is 1.0 × 106A/mL.
6. the composite treating agent of comprehensive removal heavy metal out of electroplating wastewater according to claim 5, it is characterised in that: step
In b, the Chinese medicine slag after drying is crushed to 40-60 mesh.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811320911.7A CN109384277A (en) | 2018-11-07 | 2018-11-07 | The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811320911.7A CN109384277A (en) | 2018-11-07 | 2018-11-07 | The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109384277A true CN109384277A (en) | 2019-02-26 |
Family
ID=65427076
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811320911.7A Pending CN109384277A (en) | 2018-11-07 | 2018-11-07 | The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109384277A (en) |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101357798A (en) * | 2007-07-31 | 2009-02-04 | 深圳市邦友通科技有限公司 | Heavy metal wastewater purificant |
WO2014012134A1 (en) * | 2012-07-18 | 2014-01-23 | University Of Technology, Sydney | Biosorbent for heavy metal removal |
CN105233458A (en) * | 2015-10-19 | 2016-01-13 | 桂林理工大学 | Method for degrading bisphenol A through white-rot fungus crude enzyme |
CN105417652A (en) * | 2015-11-16 | 2016-03-23 | 台州学院 | Treatment method for removing copper ions in electroplating wastewater |
CN107311248A (en) * | 2017-07-19 | 2017-11-03 | 湖南沃邦环保科技有限公司 | A kind of electroplating wastewater with heavy metal ions processing inorganic agent and preparation method thereof |
CN108753309A (en) * | 2018-07-11 | 2018-11-06 | 重庆工程职业技术学院 | Efficiently remove the soil in-situ repair composite material of removing heavy metals |
-
2018
- 2018-11-07 CN CN201811320911.7A patent/CN109384277A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101357798A (en) * | 2007-07-31 | 2009-02-04 | 深圳市邦友通科技有限公司 | Heavy metal wastewater purificant |
WO2014012134A1 (en) * | 2012-07-18 | 2014-01-23 | University Of Technology, Sydney | Biosorbent for heavy metal removal |
CN105233458A (en) * | 2015-10-19 | 2016-01-13 | 桂林理工大学 | Method for degrading bisphenol A through white-rot fungus crude enzyme |
CN105417652A (en) * | 2015-11-16 | 2016-03-23 | 台州学院 | Treatment method for removing copper ions in electroplating wastewater |
CN107311248A (en) * | 2017-07-19 | 2017-11-03 | 湖南沃邦环保科技有限公司 | A kind of electroplating wastewater with heavy metal ions processing inorganic agent and preparation method thereof |
CN108753309A (en) * | 2018-07-11 | 2018-11-06 | 重庆工程职业技术学院 | Efficiently remove the soil in-situ repair composite material of removing heavy metals |
Non-Patent Citations (4)
Title |
---|
姜思俭等: "《生活实用小化工》", 31 January 1986, 浙江科学技术出版社 * |
柴博华: "改性甘蔗渣吸附剂的制备及其对糖液脱色作用的研究", 《中国优秀硕士学位论文全文数据库 工程科技Ⅰ辑》 * |
沈旭: "《化学选矿技术》", 31 July 2011, 冶金工业出版社 * |
马伟光等: "《天然植物药的生物转化研究》", 31 May 2013, 云南科技出版社 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107952416B (en) | Shell powder chitosan composite microsphere for adsorbing heavy metals and preparation method thereof | |
CN103381316B (en) | Air filter screen with functions of sterilization and bacteriostasis and preparation method | |
CN102935352B (en) | Method for absorbing and removing heavy metal and hexavalent chromium from waste liquid by using mangosteen slag | |
CN105439314A (en) | Treatment method for removing heavy metals from comprehensive electroplating wastewater | |
CN107585918A (en) | A kind of efficient water treatment agent | |
CN106673165A (en) | High-molecular chitosan composite flocculant | |
CN106365287A (en) | Wastewater treating agent for electroplating | |
CN107285431A (en) | A kind of modified cation-exchange resin filter element of water purifier | |
CN107128999A (en) | It is a kind of for medicament of municipal sewage treatment and preparation method thereof | |
CN106186423A (en) | A kind of phosphorized waste water intermediate water reuse system | |
CN106167304A (en) | A kind of heavy metal-polluted water treatment agent and processing method | |
CN104556522A (en) | Method for treating waste water containing vanadium and chromium | |
CN102153177B (en) | Efficient dephosphorization agent for waste water treatment | |
CN109502804A (en) | The method for removing heavy metal out of electroplating wastewater | |
CN104211225A (en) | Multiple complex treatment method for heavy metal sewage | |
CN109502716A (en) | Heavy metal in electroplating wastewater inorganic agent | |
CN109384277A (en) | The composite treating agent of comprehensive removal heavy metal out of electroplating wastewater | |
CN109354309A (en) | Heavy metal MULTIPLE COMPOSITE treatment process for industrial wastewater | |
CN105217765A (en) | A kind of composite macromolecular flocculant and preparation method thereof | |
CN109717358B (en) | Efficient energy-saving whole-meter circulating cadmium removal method | |
CN106006890A (en) | Preparation method of chitosan coagulant | |
CN108483713A (en) | The treatment process and system of total zinc and total lead in electrobrightening waste water are removed simultaneously | |
CN107986419A (en) | The method that removing heavy metals are removed in a kind of chelating-coagulation collaboration | |
CN110790417B (en) | Treatment method of hardware and electronic electroplating wastewater | |
CN1116611A (en) | Treatment of waste galvanized water with its treating agent and method for recovery of precipitate |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190226 |
|
RJ01 | Rejection of invention patent application after publication |