CN108993435A - Superpower absorbent-type polyaluminium aluminium base flocculant - Google Patents
Superpower absorbent-type polyaluminium aluminium base flocculant Download PDFInfo
- Publication number
- CN108993435A CN108993435A CN201811051673.4A CN201811051673A CN108993435A CN 108993435 A CN108993435 A CN 108993435A CN 201811051673 A CN201811051673 A CN 201811051673A CN 108993435 A CN108993435 A CN 108993435A
- Authority
- CN
- China
- Prior art keywords
- aluminium base
- solid
- flocculant
- superpower
- absorbent
- 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
- 239000004411 aluminium Substances 0.000 title claims abstract description 42
- 229910052782 aluminium Inorganic materials 0.000 title claims abstract description 41
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 title claims abstract description 41
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 30
- 239000007787 solid Substances 0.000 claims abstract description 23
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000004021 humic acid Substances 0.000 claims abstract description 19
- 239000000843 powder Substances 0.000 claims abstract description 12
- 239000007788 liquid Substances 0.000 claims abstract description 11
- 238000000926 separation method Methods 0.000 claims abstract description 11
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 6
- 239000002002 slurry Substances 0.000 claims abstract description 6
- 239000006228 supernatant Substances 0.000 claims abstract description 6
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 4
- 238000000746 purification Methods 0.000 claims description 4
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims 1
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical compound [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 claims 1
- 229910052801 chlorine Inorganic materials 0.000 claims 1
- 239000000460 chlorine Substances 0.000 claims 1
- 238000006116 polymerization reaction Methods 0.000 claims 1
- 238000002360 preparation method Methods 0.000 claims 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 28
- 230000000694 effects Effects 0.000 abstract description 16
- 239000003463 adsorbent Substances 0.000 abstract description 9
- 159000000013 aluminium salts Chemical class 0.000 abstract description 3
- 229910000329 aluminium sulfate Inorganic materials 0.000 abstract description 3
- 239000008394 flocculating agent Substances 0.000 abstract description 2
- 239000002585 base Substances 0.000 description 13
- 239000002351 wastewater Substances 0.000 description 11
- 238000000034 method Methods 0.000 description 6
- 239000010865 sewage Substances 0.000 description 6
- 239000003795 chemical substances by application Substances 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 4
- 239000000701 coagulant Substances 0.000 description 4
- 238000009713 electroplating Methods 0.000 description 4
- 239000010842 industrial wastewater Substances 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- 239000003610 charcoal Substances 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 239000012535 impurity Substances 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 238000004065 wastewater treatment Methods 0.000 description 3
- 238000003809 water extraction Methods 0.000 description 3
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 description 2
- 230000001112 coagulating effect Effects 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000003311 flocculating effect Effects 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- RBTBFTRPCNLSDE-UHFFFAOYSA-N 3,7-bis(dimethylamino)phenothiazin-5-ium Chemical compound C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 RBTBFTRPCNLSDE-UHFFFAOYSA-N 0.000 description 1
- 241000894006 Bacteria Species 0.000 description 1
- JUQPZRLQQYSMEQ-UHFFFAOYSA-N CI Basic red 9 Chemical compound [Cl-].C1=CC(N)=CC=C1C(C=1C=CC(N)=CC=1)=C1C=CC(=[NH2+])C=C1 JUQPZRLQQYSMEQ-UHFFFAOYSA-N 0.000 description 1
- 229920000742 Cotton Polymers 0.000 description 1
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 238000005349 anion exchange Methods 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- 229940052223 basic fuchsin Drugs 0.000 description 1
- 239000012620 biological material Substances 0.000 description 1
- 230000035568 catharsis Effects 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 235000019504 cigarettes Nutrition 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000004043 dyeing Methods 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229960000907 methylthioninium chloride Drugs 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920002401 polyacrylamide Polymers 0.000 description 1
- 238000007639 printing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000013268 sustained release Methods 0.000 description 1
- 239000012730 sustained-release form Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 239000003403 water pollutant Substances 0.000 description 1
- 238000009941 weaving Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/06—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
- B01J20/08—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- 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
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- 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
- C02F1/28—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
- C02F1/52—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
- C02F1/5236—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
- C02F1/5263—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using natural chemical compounds
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Inorganic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The present invention relates to superpower absorbent-type polyaluminium aluminium base flocculants, this superpower absorbent-type polyaluminium aluminium base flocculant is by the humic acid by 20-40% based on mass fraction, the active carbon of 20-40%, the aluminium polychloride of 20-50% is prepared, the humic acid, Powdered Activated Carbon, aluminium polychloride are configured to the slurry that mass concentration is 50-80%, are vigorously stirred uniformly, quiescent setting, after its supernatant is clarified completely, it is separated by solid-liquid separation;Solid portion is dried in vacuo to obtain black powder solid, and the black powder solid is superpower absorbent-type polyaluminium aluminium base flocculant.The present invention combines the characteristics of flocculant and adsorbent, not only solves the shortcomings that becoming turbid when the alumen ustum that aluminium salt generates is light, low-temperature and low turbidity purifying water effect is poor, dosage is excessive, and alleviate adsorbent and be difficult to the shortcomings that being separated by solid-liquid separation.
Description
Technical field
The present invention relates to water-treatment technology fields, and in particular to be superpower absorbent-type polyaluminium aluminium base flocculant.
Background technique
Due to the shortage of freshwater resources, water reuse becomes particularly important, and how impurities in water effectively removes then
It is the emphasis of research.Coagulant sedimentation has the advantages that economical and efficient, simple process and easy to operate, be widely used in water and
In wastewater treatment.Either city and industrial water supply processing or city and Industrial Wastewater Treatment, all using coagulating sedimentation as work
Indispensable sport technique segment in skill process.And the quality of coagulating treatment effect depends greatly on the product of coagulant
Matter.Coagulant belongs to the water treatment agent of high added value and high-tech content, it largely decides water treatment technology
Innovation and development, the simplification of process flow, the height of operating cost and purification of water quality quality superiority and inferiority.Traditional sewage treatment
Although method has certain catharsis to industrial wastewater, being difficult, which makes to handle water, reaches increasingly strict sewage discharge mark
It is quasi-.Therefore, development, exploiting economy, safety and efficient coagulant, to seek the effective ways of processing industrial wastewater be at water always
The pillar industry given priority in reason environmental technology field.
With the economic development and improvement of people's living standards, the water quality of city domestic sewage becomes to become increasingly complex,
Requirement to water treatment agent complex function is higher and higher.Therefore, flocculant should also kill in addition to excellent flocculating property
Bacterium, removes the multiple functions such as COD, sustained release at decoloration.There is the shortcomings that being hard to avoid in inorganic flocculating agent, including dosage is big, settling of floccus
Slowly, inconvenient to use, residual toxicity is big etc..It is inorganic mutually to compensate for deficiency with organic composite flocculant but existing inorganic
With organic flocculant collocation using can realize separation of solid and liquid to the waste water of general slight pollution, sometimes to the waste water of high density pollution
Basic separation of solid and liquid target is also difficult to reach, although in addition, the biggish aluminium polychloride of dosage is to the coloration for improving waste water
Polyacrylamide is used alone in high concentrtion, height very well but there are the remaining environmental problem of the larger brought aluminium of dosage in effect
The occasion flocculating effect of concentration industrial wastewater is poor, in current sewage treatment industry, still lacks efficient, cheap, more function so far
The flocculant of energy.
The adsorption capacity of traditional flocculant is smaller, more effective to particle biggish in absorption effluent, it is difficult to remove decontamination
Micropollutants in water.Various adsorbents such as crystalline mineral, cigarette ash, biomaterial, silica gel, sawdust, fruit shell, active carbon etc. is
Developed and for go water removal in micropollutants.But limited adsorption capacity limits the application of these adsorbents.Therefore, people
Seeking always have bigger adsorption capacity, more effective novel absorption material.
The interaction of humic acid and pollutant may include anion exchange, hydrogen bond, surface coordination exchanges, cation bridged bond
Etc. all various aspects.Humic acid large specific surface area, high surface activity, absorption property, coordination ability are also relatively high.But humic acid is easy
It is dissolved in water, it is difficult to be separated from the water.
Powdered Activated Carbon all has excellent adsorption capacity to methylene blue, cationic red, basic fuchsin and phenol etc..But
Powdered Activated Carbon size is small, and is easily dispersed in water, after being used as adsorbent absorption water pollutant, it is difficult to it is removed from water,
To bring secondary pollution problem.
Summary of the invention
The purpose of the present invention is superpower absorbent-type polyaluminium aluminium base flocculant, this superpower absorbent-type polyaluminium aluminium base
Flocculant is used to solve to go out when the alumen ustum that aluminium salt generates in current sewage treatment is light, low-temperature and low turbidity purifying water effect is poor, dosage is excessive
Existing muddy problem, and alleviate adsorbent and be difficult to the problem of being separated by solid-liquid separation.
The technical solution adopted by the present invention to solve the technical problems is: this superpower absorbent-type polyaluminium aluminium base flocculation
Agent is prepared by the humic acid by 20-40% based on mass fraction, the aluminium polychloride of the active carbon of 20-40%, 20-50%,
The humic acid, Powdered Activated Carbon, aluminium polychloride are configured to the slurry that mass concentration is 50-80%, are vigorously stirred uniformly,
Quiescent setting is separated by solid-liquid separation after its supernatant is clarified completely;Solid portion is dried in vacuo to obtain black powder solid, institute
Stating black powder solid is superpower absorbent-type polyaluminium aluminium base flocculant.
Content of humic acid is 30% in above scheme, activated carbon content 30%, and polyaluminium aluminium content is 40%.
Al in aluminium polychloride in above scheme2O3Content is 25-30%.
Humic acid is handled using ethanol purification in above scheme, purity 95-98%.
Active carbon is Powdered Activated Carbon in above scheme.
The invention has the following advantages:
1, the present invention provides a kind of composite flocculation for sewage treatment that can play flocculant, adsorbent surface synergistic effect
The characteristics of agent, which combines flocculant and adsorbent, the alumen ustum for not only solving aluminium salt generation is light, low-temperature and low turbidity water purification
The shortcomings that becoming turbid when effect is poor, dosage is excessive, and alleviate adsorbent and be difficult to the shortcomings that being separated by solid-liquid separation.
2, the present invention is nontoxic, reaction speed is fast, applicable pH range is wide, coagulation effect is good, in water supply, wastewater treatment, weaving
Printing and dyeing, mining, daily-use chemical industry, the especially fields such as heavy metal pollution can widely apply, and null solution is inhaled, and secondary pollution is not present.
Specific embodiment
The present invention is described further below:
Embodiment 1
This superpower absorbent-type polyaluminium aluminium base flocculant is by by 30% humic acid based on mass fraction, 30% activity
Charcoal, 40% aluminium polychloride are prepared, and above-mentioned humic acid, Powdered Activated Carbon, aluminium polychloride are configured to mass concentration and are
60% slurry is vigorously stirred uniformly, quiescent setting, after its supernatant is clarified completely, is separated by solid-liquid separation;Solid portion vacuum is dry
Dry to obtain black powder solid, the black powder solid is superpower absorbent-type polyaluminium aluminium base flocculant.
Table 1 is application of this flocculant in certain electroplating wastewater, by superpower absorbent-type polyaluminium manufactured in the present embodiment
Al-based goagulants, by 50g/m3Dosage be directly thrown into above-mentioned electroplating wastewater, above-mentioned electroplating wastewater is handled, handle
Clear water is upper afterwards, and solid is deposited in down, natural layering, clear water extraction, to objectionable impurities such as COD, heavy metal ion, SS
Removal has preferable effect.Specific such as table 1.
Application effect (mg/L) of 1 embodiment of table, 1 flocculant in certain electroplating wastewater
Embodiment 2
This superpower absorbent-type polyaluminium aluminium base flocculant is by by 20% humic acid based on mass fraction, 30% activity
Charcoal, 50% aluminium polychloride are prepared, and above-mentioned humic acid, Powdered Activated Carbon, aluminium polychloride are configured to mass concentration and are
55% slurry is vigorously stirred uniformly, quiescent setting, after its supernatant is clarified completely, is separated by solid-liquid separation;Solid portion vacuum is dry
Dry to obtain black powder solid, the black powder solid is superpower absorbent-type polyaluminium aluminium base flocculant.
Table 2 is application of this flocculant in landscape water, and superpower absorbent-type polyaluminium aluminium base manufactured in the present embodiment is wadded a quilt with cotton
Solidifying agent, by 50g/m3Dosage be directly thrown into above-mentioned landscape water, above-mentioned landscape water is handled, clear water exists after processing
On, solid is deposited in down, natural layering, clear water extraction, to reduction COD, BOD5, permanganate index etc. have it is preferable
Effect.Specific such as table 2.
Application effect (mg/L) of 2 embodiment of table, 2 flocculant in certain landscape water
Embodiment 3
This superpower absorbent-type polyaluminium aluminium base flocculant is by by 30% humic acid based on mass fraction, 20% activity
Charcoal, 50% aluminium polychloride are prepared, and above-mentioned humic acid, Powdered Activated Carbon, aluminium polychloride are configured to mass concentration and are
65% slurry is vigorously stirred uniformly, quiescent setting, after its supernatant is clarified completely, is separated by solid-liquid separation;Solid portion vacuum is dry
Dry to obtain black powder solid, the black powder solid is superpower absorbent-type polyaluminium aluminium base flocculant.
Table 3 is application of this flocculant in certain high concentrated organic wastewater, and superpower absorbent-type manufactured in the present embodiment is gathered
Aluminum chloride-based flocculant is closed, by 90g/m3Dosage be directly thrown into above-mentioned high concentrated organic wastewater, have to above-mentioned high concentration
Machine waste water is handled, and clear water is upper after processing, and solid is deposited in down, natural layering, clear water extraction, to COD, SS,
NH3The removal of the objectionable impurities such as-N has preferable effect.Specific such as table 3.
Application effect (mg/L) of 3 embodiment of table, 3 flocculant in certain high concentrated organic wastewater
Claims (5)
1. a kind of superpower absorbent-type polyaluminium aluminium base flocculant, it is characterised in that: this superpower absorbent-type polyaluminium aluminium base
Flocculant is by the humic acid by 20-40% based on mass fraction, the active carbon of 20-40%, the aluminium polychloride preparation of 20-50%
It forms, the humic acid, Powdered Activated Carbon, aluminium polychloride is configured to the slurry that mass concentration is 50-80%, are vigorously stirred
Uniformly, quiescent setting is separated by solid-liquid separation after its supernatant is clarified completely;It is solid that solid portion is dried in vacuo to obtain black powder
Body, the black powder solid are superpower absorbent-type polyaluminium aluminium base flocculant.
2. superpower absorbent-type polyaluminium aluminium base flocculant according to claim 1, it is characterised in that: the humic acid
Content is 30%, activated carbon content 30%, and polyaluminium aluminium content is 40%.
3. superpower absorbent-type polyaluminium aluminium base flocculant according to claim 2, it is characterised in that: the polymerization chlorine
Change Al in aluminium2O3Content is 25-30%.
4. superpower absorbent-type polyaluminium aluminium base flocculant according to claim 3, it is characterised in that: the humic acid
It is handled using ethanol purification, purity 95-98%.
5. superpower absorbent-type polyaluminium aluminium base flocculant according to claim 4, it is characterised in that: the active carbon
For Powdered Activated Carbon.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811051673.4A CN108993435A (en) | 2018-09-10 | 2018-09-10 | Superpower absorbent-type polyaluminium aluminium base flocculant |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811051673.4A CN108993435A (en) | 2018-09-10 | 2018-09-10 | Superpower absorbent-type polyaluminium aluminium base flocculant |
Publications (1)
Publication Number | Publication Date |
---|---|
CN108993435A true CN108993435A (en) | 2018-12-14 |
Family
ID=64591306
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811051673.4A Pending CN108993435A (en) | 2018-09-10 | 2018-09-10 | Superpower absorbent-type polyaluminium aluminium base flocculant |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN108993435A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113880158A (en) * | 2021-10-26 | 2022-01-04 | 广州市芦苇环保科技有限责任公司 | Polyacrylamide water purifying agent and production method thereof |
CN117861621A (en) * | 2024-01-24 | 2024-04-12 | 安徽科凌沃特水处理技术有限公司 | Biochar/polyaluminum chloride composite adsorbent |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105692823A (en) * | 2016-01-19 | 2016-06-22 | 赵东星 | Environment-friendly efficient biological flocculant and preparing method thereof |
CN106732434A (en) * | 2017-01-24 | 2017-05-31 | 福州大学 | A kind of method that acticarbon is prepared based on humic acid dipping |
-
2018
- 2018-09-10 CN CN201811051673.4A patent/CN108993435A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105692823A (en) * | 2016-01-19 | 2016-06-22 | 赵东星 | Environment-friendly efficient biological flocculant and preparing method thereof |
CN106732434A (en) * | 2017-01-24 | 2017-05-31 | 福州大学 | A kind of method that acticarbon is prepared based on humic acid dipping |
Non-Patent Citations (4)
Title |
---|
厉衡隆 等编: "《铝冶炼生产技术手册(上册)》", 31 July 2011, 冶金工业出版社 * |
李旭东等: "《废水处理技术及工程应用》", 30 June 2003, 机械工业出版社 * |
谢昆 等编: "《纳米技术在水污染控制中的应用》", 30 June 2014, 武汉大学出版社 * |
郑文翰: "《军事大辞典》", 31 December 1992, 上海辞书出版社 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113880158A (en) * | 2021-10-26 | 2022-01-04 | 广州市芦苇环保科技有限责任公司 | Polyacrylamide water purifying agent and production method thereof |
CN117861621A (en) * | 2024-01-24 | 2024-04-12 | 安徽科凌沃特水处理技术有限公司 | Biochar/polyaluminum chloride composite adsorbent |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107188330B (en) | A kind of method for adsorption and purification of acid waste water | |
CN101327976B (en) | Water treatment flocculant | |
CN101386424B (en) | Method for preparing modification forming magnalium hydrotalcite and application | |
CN105060579A (en) | Advanced treatment method of fluoride-containing wastewater | |
CN105217842A (en) | A kind of waste water treatment process | |
WO2020010678A1 (en) | Novel material for in-situ decontamination of turbid river water and preparation method thereof | |
CN102040301A (en) | Method for treating municipal waste leachate membrane concentrated solution | |
CN105366788A (en) | Water purification agent composition and application thereof | |
Otal et al. | Ammonium ion adsorption and settleability improvement achieved in a synthetic zeolite-amended activated sludge | |
CN102040309A (en) | Combined treatment process for urban garbage percolate | |
CN105540987A (en) | Water deep purification method | |
CN106336038B (en) | A kind of processing method containing heavy metal polluted waste water | |
CN108993435A (en) | Superpower absorbent-type polyaluminium aluminium base flocculant | |
CN107010690B (en) | A kind of city domestic sewage dephosphorization agent and preparation method thereof | |
CN104478055A (en) | Sewage treatment complexing agent as well as preparation method and application method thereof | |
CN100463868C (en) | A kind of eco-environmental protection composite water treatment agent | |
CN101734746A (en) | Method for adsorbing and removing phycobiliprotein and microcystin-LR by modified attapulgite | |
CN103253725A (en) | A method for removing organic matter in reclaimed water by using in situ generation of iron hydroxyhydroxide In situ FeOxHy | |
CN103553245B (en) | A kind of efficient adsorption process is containing the method for lower concentration roxarsone waste water | |
CN105600892A (en) | Water purifying agent composition and application thereof | |
CN106746475B (en) | Composite polymer sludge dewatering flocculant and preparation method thereof | |
CN1212979C (en) | Organic sewage treatment complexing agent | |
CN106379955A (en) | Waste water treating agent and application thereof | |
CN1321073C (en) | Safety and ecological natural built-up flocculant, its production and use | |
CN101381142A (en) | A kind of cyanobacteria scavenging agent taking mineral material as carrier and preparation method thereof |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20181214 |