CN102849911A - Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud - Google Patents

Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud Download PDF

Info

Publication number
CN102849911A
CN102849911A CN2012103973367A CN201210397336A CN102849911A CN 102849911 A CN102849911 A CN 102849911A CN 2012103973367 A CN2012103973367 A CN 2012103973367A CN 201210397336 A CN201210397336 A CN 201210397336A CN 102849911 A CN102849911 A CN 102849911A
Authority
CN
China
Prior art keywords
volcanic
dammed lake
bed mud
dammed
passivation
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
Application number
CN2012103973367A
Other languages
Chinese (zh)
Inventor
曾颖
谢振华
杨臣
李博
李月兴
魏晓雪
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
INSTITUTE OF VOLCANO AND SPRING OF HEILONGJIANG ACADEMY OF SCIENCES
Original Assignee
INSTITUTE OF VOLCANO AND SPRING OF HEILONGJIANG ACADEMY OF SCIENCES
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 INSTITUTE OF VOLCANO AND SPRING OF HEILONGJIANG ACADEMY OF SCIENCES filed Critical INSTITUTE OF VOLCANO AND SPRING OF HEILONGJIANG ACADEMY OF SCIENCES
Priority to CN2012103973367A priority Critical patent/CN102849911A/en
Publication of CN102849911A publication Critical patent/CN102849911A/en
Pending legal-status Critical Current

Links

Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Filtration Of Liquid (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

A method for passivating and repairing cadmium-polluted volcano dammed lake sediment relates to the field of methods for passivating and repairing cadmium-polluted lake sediment. The invention aims to solve the technical problems that the passivation operation is complex and the repair efficiency is not high on the premise of not changing the physicochemical property of the bottom mud in the existing passivation method. A method for passivating and repairing cadmium-polluted volcano barrier lake sediment comprises the following steps: firstly, preparing volcano dammed lake bottom mud particles, secondly, preparing Wudalianchi volcano rock particles, and thirdly, passivating and repairing the volcano dammed lake bottom mud particles by utilizing the Wudalianchi volcano rock particles. The method for passivating and repairing the cadmium-polluted volcano dammed lake bottom mud is simple to operate, and the fixation rate of the volcano dammed lake bottom mud to cadmium reaches over 48 percent. The invention is applied to the field of lake sediment recycling.

Description

The method of the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud
Technical field
The present invention relates to the field of the method for the restoring cadmium polluted lakebed mud of passivation.
Background technology
Bottom mud in lake is carried out the developing direction that recycling is current scientific research, it is carried out " Fertilizer Transformed " utilizes more becomes current scientific research because meeting " resources sustainable development " focus.But because the phenomenon that current China lake ubiquity cadmium exceeds standard, using bed mud that cadmium exceeds standard can the deposits yields poisoning symptom be short and small such as: poor growth, plant to doing, atrophy and output degradation etc., and excessive cadmium can be residual in making object, harm humans is healthy, if can not get good processing, may cause secondary pollution to environment.In the various technology of current cadmium pollution in repairing bed mud, the passivation recovery technique is advantage such as easy, quick and effective and be subject to increasing attention with it, some novel materials begin to be used in the bed mud in the cadmium pollution passivation reparation research, and they have all obtained repairing effect to a certain degree under the lower level that adds.For dissimilar bottom mud in lake use identical passivator generally difficulty reach the reparation requirement, and need multiple passivator to unite use just to obtain preferably solution.In the existing passivating method, passivation operation is complicated, and the remediation efficiency under the prerequisite of the physico-chemical property that does not change bed mud is not high, and fixed rate only can reach 10% ~ 20%, can not satisfy the demand of the second stage employ of " Fertilizer Transformed ".
Summary of the invention
The present invention will solve in the existing passivating method, and passivation operation is complicated, the technical problem that the remediation efficiency under the prerequisite of the physico-chemical property that does not change bed mud is not high, and the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud is provided.
The method of the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.001mol/L ~ 0.1mol/L 3The aqueous solution is under the condition of 20 ℃ ~ 30 ℃ temperature, behind ultrasonic 2h ~ 5h under the ultrasonic frequency of 20kHz ~ 35kHz, leave standstill 20h ~ 30h, with the centrifugal 2min ~ 10min of the rotating speed of 1000r/min ~ 2000r/min, filter, obtain solid, namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:(0.005 ~ 0.03), NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is (5mL ~ 15mL): 1g.
Advantage of the present invention: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud has the following advantages:
One, the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation provided by the invention bed mud, process is simple, easy handling, cost is low, energy-conserving and environment-protective;
Two, the method of the restoring cadmium polluted volcanic dammed lake of a kind of passivation provided by the invention bed mud, what adopt is the fixedly cadmium of the attitude extracted in the bed mud of passivation cadmium pollution volcanic dammed lake of Wudalianchi Volcanic stone, because Wudalianchi Volcanic stone has huge specific surface area and abundant space on the one hand, the structures shape that it is special its have stronger adsorption and ion-exchange capacity, on the other hand, Wudalianchi Volcanic stone has strong basicity, can reduce the acidity of volcanic dammed lake bed mud, increase the pH value of volcanic dammed lake bed mud, and the adsorptive capacity of cadmium reduces with the increase of bed mud pH value in the bed mud, so that Wudalianchi Volcanic stone can effectively reduce the activity of cadmium in the bed mud;
Three, the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation provided by the invention bed mud, under the prerequisite of the physico-chemical property that does not change bed mud, fixed rate to cadmium in the bed mud of cadmium pollution volcanic dammed lake has reached more than 48%, can realize the second stage employ of volcanic dammed lake bed mud " Fertilizer Transformed ".
Embodiment
Embodiment one: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.001mol/L ~ 0.1mol/L 3The aqueous solution is under the condition of 20 ℃ ~ 30 ℃ temperature, behind ultrasonic 2h ~ 5h under the ultrasonic frequency of 20kHz ~ 35kHz, leave standstill 20h ~ 30h, with the centrifugal 2min ~ 10min of the rotating speed of 1000r/min ~ 2000r/min, filter, obtain solid, namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:(0.005 ~ 0.03), NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is (5mL ~ 15mL): 1g.
The method of the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud that present embodiment provides, when the pH of volcanic dammed lake bed mud value greater than 10 the time, because strong basicity, basic change has occured in the physico-chemical property of volcanic dammed lake bed mud, is not suitable for the second stage employ of " Fertilizer Transformed ".
The method of the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud that present embodiment provides, have the following advantages: one, process is simple, easy handling, cost is low, energy-conserving and environment-protective; Two, what adopt is the fixedly cadmium of the attitude extracted in the bed mud of passivation cadmium pollution volcanic dammed lake of Wudalianchi Volcanic stone, because Wudalianchi Volcanic stone has huge specific surface area and abundant space on the one hand, the structures shape that it is special its have stronger adsorption and ion-exchange capacity, on the other hand, Wudalianchi Volcanic stone has strong basicity, can reduce the acidity of volcanic dammed lake bed mud, increase the pH value of volcanic dammed lake bed mud, and the adsorptive capacity of cadmium reduces with the increase of bed mud pH value in the bed mud, so that Wudalianchi Volcanic stone can effectively reduce the activity of cadmium in the bed mud; Three, under the prerequisite of the physico-chemical property that does not change bed mud, (volcanized rock is to the fixed rate of cadmium=(C to the fixed rate of cadmium in the bed mud of cadmium pollution volcanic dammed lake 0-C 1)/C 0* 100%), C wherein 0The content of cadmium in the solution when not adding volcanized rock; C 1Content for cadmium in the solution behind the adding volcanized rock) reached more than 48%, can realize the second stage employ of volcanic dammed lake bed mud " Fertilizer Transformed ".
Embodiment two: the difference of present embodiment and embodiment one is: the temperature condition in the described step 3 is 23 ℃ ~ 27 ℃.Other is identical with embodiment one.
Embodiment three: present embodiment and embodiment one or twos' difference is: the temperature condition in the described step 3 is 25 ℃.Other is identical with embodiment one or two.
Embodiment four: the difference of one of present embodiment and embodiment one to three is: the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that the step 1 in the described step 3 obtains and step 2 obtain is 1:0.01.Other is identical with embodiment one to three.
Adopt following verification experimental verification effect of the present invention:
Test one: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with cadmium pollution volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.01mol/L 3The aqueous solution under the condition of 25 ℃ temperature, behind ultrasonic 3h under the ultrasonic frequency of 28kHz, leaves standstill 24h, with the centrifugal 5min of the rotating speed of 1500r/min, filters, and obtains the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:0.005, NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is 10mL:1g.
Other gets cadmium pollution volcanic dammed lake bed mud natural air drying, is screened to particle diameter and is not more than 2mm, obtains the volcanic dammed lake sediment particles, and adding concentration in the sediment particles of volcanic dammed lake is the NaNO of 0.01mol/L 3Aqueous solution 10mL under the condition of 25 ℃ temperature, behind ultrasonic 3h under the ultrasonic frequency of 28kHz, leaves standstill 24h, with the centrifugal 5min of the rotating speed of 1500r/min, filters, and obtains the volcanic dammed lake bed mud of not passivation.
Volcanic dammed lake bed mud to not passivation carries out the measurement of pH value, and getting not, the pH value of the volcanic dammed lake bed mud of passivation is 6.15.
To test in one after filtering resulting supernatant liquor of step 3, adopt the concentration of cadmium in the graphite furnace atomic absorption spectrometry supernatant liquor, calculate the fixed rate of cadmium, can obtain, when the mass ratio of the Wudalianchi Volcanic stone granulate that obtains when volcanic dammed lake sediment particles that step 1 obtains and step 2 is 1:0.005, be 48% through the restoring cadmium polluted volcanic dammed lake of passivation bed mud to the fixed rate of cadmium, at this moment, 6.15 before by the passivation of the pH value of volcanic dammed lake bed mud is increased to 7.30 after the passivation, the physico-chemical property of volcanic dammed lake bed mud does not change, and the volcanic dammed lake bed mud under this pH value is fit to the second stage employ of " Fertilizer Transformed ".
Test two: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.01mol/L 3The aqueous solution under the condition of 25 ℃ temperature, behind ultrasonic 3h under the ultrasonic frequency of 28kHz, leaves standstill 24h, with the centrifugal 5min of the rotating speed of 1500r/min, filters, and obtains solid, has namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:0.01, NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is 10mL:1g.
To test in two after filtering resulting supernatant liquor of step 3, adopt the concentration of cadmium in the graphite furnace atomic absorption spectrometry supernatant liquor, calculate the fixed rate of cadmium, can obtain, when the mass ratio of the Wudalianchi Volcanic stone granulate that obtains when volcanic dammed lake sediment particles that step 1 obtains and step 2 is 1:0.01, be 83% through the restoring cadmium polluted volcanic dammed lake of passivation bed mud to the fixed rate of cadmium, at this moment, 6.15 before by the passivation of the pH value of volcanic dammed lake bed mud is increased to 7.86 after the passivation, the physico-chemical property of volcanic dammed lake bed mud does not change, and the volcanic dammed lake bed mud under this pH value is fit to the second stage employ of " Fertilizer Transformed ".
Test three: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.01mol/L 3The aqueous solution under the condition of 25 ℃ temperature, behind ultrasonic 3h under the ultrasonic frequency of 28kHz, leaves standstill 24h, with the centrifugal 5min of the rotating speed of 1500r/min, filters, and obtains solid, has namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:0.03, NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is 10mL:1g.
To test in three after filtering resulting supernatant liquor of step 3, adopt the concentration of cadmium in the graphite furnace atomic absorption spectrometry supernatant liquor, calculate the fixed rate of cadmium, can obtain, when the mass ratio of the Wudalianchi Volcanic stone granulate that obtains when volcanic dammed lake sediment particles that step 1 obtains and step 2 is 1:0.03, be 92% through the restoring cadmium polluted volcanic dammed lake of passivation bed mud to the fixed rate of cadmium, at this moment, 6.15 before by the passivation of the pH value of volcanic dammed lake bed mud is increased to 9.07 after the passivation, the pH value is higher, make the physico-chemical property of volcanic dammed lake bed mud produce little change, this pH value is higher for the second stage employ of " Fertilizer Transformed " of volcanic dammed lake bed mud.
Test four: the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation bed mud, specifically finish according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.01mol/L 3The aqueous solution under the condition of 25 ℃ temperature, behind ultrasonic 3h under the ultrasonic frequency of 28kHz, leaves standstill 24h, with the centrifugal 5min of the rotating speed of 1500r/min, filters, and obtains solid, has namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:0.05, NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is 10mL:1g.
To test in four after filtering resulting supernatant liquor of step 3, adopt the concentration of cadmium in the graphite furnace atomic absorption spectrometry supernatant liquor, calculate the fixed rate of cadmium, can obtain, when the mass ratio of the Wudalianchi Volcanic stone granulate that obtains when volcanic dammed lake sediment particles that step 1 obtains and step 2 is 1:0.05, be 100% through the restoring cadmium polluted volcanic dammed lake of passivation bed mud to the fixed rate of cadmium.But the pH value of the volcanic dammed lake bed mud of this moment surpasses 10, and basic change has occured the physico-chemical property of volcanic dammed lake bed mud, and this pH value is so that the volcanic dammed lake bed mud is not suitable for the second stage employ of " Fertilizer Transformed ".

Claims (4)

1. the method for the restoring cadmium polluted volcanic dammed lake of a passivation bed mud is characterized in that the method for the restoring cadmium polluted volcanic dammed lake of passivation bed mud, specifically finishes according to the following steps:
One, with volcanic dammed lake bed mud natural air drying, then, be screened to particle diameter and be not more than 2mm, obtain the volcanic dammed lake sediment particles;
Two, get Wudalianchi Volcanic stone, pulverize, then, be screened to particle diameter and be not more than 80 orders, obtain the Wudalianchi Volcanic stone granulate;
Three, the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 is obtained and step 2 obtain mixes, and obtains mixture, and adding concentration in the mixture is the NaNO of 0.001mol/L ~ 0.1mol/L 3The aqueous solution is under the condition of 20 ℃ ~ 30 ℃ temperature, behind ultrasonic 2h ~ 5h under the ultrasonic frequency of 20kHz ~ 35kHz, leave standstill 20h ~ 30h, with the centrifugal 2min ~ 10min of the rotating speed of 1000r/min ~ 2000r/min, filter, obtain solid, namely finished the restoring cadmium polluted volcanic dammed lake of passivation bed mud; Wherein, the mass ratio of the Wudalianchi Volcanic stone granulate that the volcanic dammed lake sediment particles that step 1 obtains and step 2 obtain is 1:(0.005 ~ 0.03), NaNO 3The ratio of the quality of the volcanic dammed lake sediment particles that the volume of the aqueous solution and step 1 obtain is (5mL ~ 15mL): 1g.
2. the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation according to claim 1 bed mud is characterized in that the temperature condition in the described step 3 is 23 ℃ ~ 27 ℃.
3. the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation according to claim 1 and 2 bed mud is characterized in that the temperature condition in the described step 3 is 25 ℃.
4. the method for the restoring cadmium polluted volcanic dammed lake of a kind of passivation according to claim 1 and 2 bed mud is characterized in that the mass ratio of the Wudalianchi Volcanic stone granulate that volcanic dammed lake sediment particles that the step 1 in the described step 3 obtains and step 2 obtain is 1:0.01.
CN2012103973367A 2012-10-18 2012-10-18 Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud Pending CN102849911A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2012103973367A CN102849911A (en) 2012-10-18 2012-10-18 Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2012103973367A CN102849911A (en) 2012-10-18 2012-10-18 Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud

Publications (1)

Publication Number Publication Date
CN102849911A true CN102849911A (en) 2013-01-02

Family

ID=47396961

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2012103973367A Pending CN102849911A (en) 2012-10-18 2012-10-18 Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud

Country Status (1)

Country Link
CN (1) CN102849911A (en)

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006080587A1 (en) * 2005-01-31 2006-08-03 Egs Company, Limited Immobilizing agent and immobilization method for harmful component
JP2006263509A (en) * 2005-03-22 2006-10-05 Chugoku Electric Power Co Inc:The Method for fixing substance easily eluted in water, and material obtained by it
CN101811133A (en) * 2010-04-27 2010-08-25 河海大学 Ultrasonic remediating method for heavy metal polluted soil/slurry
CN102432144A (en) * 2011-11-01 2012-05-02 华南再生资源(中山)有限公司 Method for preparing microporous adsorbent from sludge, product and special equipment

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2006080587A1 (en) * 2005-01-31 2006-08-03 Egs Company, Limited Immobilizing agent and immobilization method for harmful component
JP2006263509A (en) * 2005-03-22 2006-10-05 Chugoku Electric Power Co Inc:The Method for fixing substance easily eluted in water, and material obtained by it
CN101811133A (en) * 2010-04-27 2010-08-25 河海大学 Ultrasonic remediating method for heavy metal polluted soil/slurry
CN102432144A (en) * 2011-11-01 2012-05-02 华南再生资源(中山)有限公司 Method for preparing microporous adsorbent from sludge, product and special equipment

Similar Documents

Publication Publication Date Title
Zabihi et al. Removal of mercury from water by carbonaceous sorbents derived from walnut shell
Jeon Adsorption of silver ions from industrial wastewater using waste coffee grounds
Zhang et al. Removing copper and cadmium from water and sediment by magnetic microspheres-MnFe2O4/chitosan prepared by waste shrimp shells
CN104069814A (en) Method for preparing modified wood chip hydrothermal charcoal by adopting KOH
CN102626607A (en) Preparation method and application of residual activated sludge adsorbent
CN103433011B (en) Preparation method of wheat straw modified material for removing lead ions in waste water
CN103071463A (en) Modified peanut shell Pb(II) adsorbent, and preparation method and application thereof
CN110548490A (en) Preparation method and application of recyclable lanthanum modified bentonite phosphorus removal material
CN110508243B (en) Preparation method and application of biomass-based porous carbon loaded iron floc adsorption material
Zhu et al. Hazelnut shell activated carbon: a potential adsorbent material for the decontamination of uranium (VI) from aqueous solutions
Prapagdee et al. Activation of cassava stem biochar by physico-chemical method for stimulating cadmium removal efficiency from aqueous solution.
CN108435135A (en) A kind of preparation method of watermelon peel charcoal and its in removing waste water thallium application
CN112076727A (en) Heavy metal pollution repairing agent and preparation method thereof
CN109173999A (en) A kind of preparation method and applications of biology carbon microspheres
CN103752286B (en) Composite adsorbing material of a kind of heavy-metal ion removal and its preparation method and application
Das et al. Removal of Ag (I) and Zn (II) ions from single and binary solution using sulfonated form of gum arabic-powdered mushroom composite hollow semispheres: Equilibrium, kinetic, thermodynamic and ex-situ studies
Xu et al. Adsorption of acid fuchsin onto LTA-type zeolite derived from fly ash
Kushwaha et al. Equilibrium, kinetics and thermodynamic studies for adsorption of Hg (II) on palm shell powder
Siswoyo et al. Agar-encapsulated adsorbent based on leaf of platanus sp. to adsorb cadmium ion in water
CN108126655A (en) A kind of preparation method of the Jujun grasses charcoal of iron oxide modified
Shah et al. Waste water treatment-bed of coal fly ash for dyes and pigments industry
CN102849911A (en) Method for passivating and repairing cadmium-polluted volcano barrier lake bottom mud
CN113813930B (en) Modified biomass-based composite adsorption material for treating radioactive pollutants
Cai et al. Bagasse-based adsorbent with nitric acid esterification and Fe (iii) chelation for the highly efficient removal of low concentration phosphate from water
Farasati et al. Use of agricultural nano adsorbents for nitrate removal from aqueous solutions

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20130102