CN103922435B - Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions - Google Patents

Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions Download PDF

Info

Publication number
CN103922435B
CN103922435B CN201410163859.4A CN201410163859A CN103922435B CN 103922435 B CN103922435 B CN 103922435B CN 201410163859 A CN201410163859 A CN 201410163859A CN 103922435 B CN103922435 B CN 103922435B
Authority
CN
China
Prior art keywords
extract
heavy metal
shaddock ped
folium camelliae
camelliae sinensis
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.)
Expired - Fee Related
Application number
CN201410163859.4A
Other languages
Chinese (zh)
Other versions
CN103922435A (en
Inventor
陈龙胜
陈世金
许舒雯
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.)
Anhui application technology research institute
Original Assignee
Anhui application technology research institute
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 Anhui application technology research institute filed Critical Anhui application technology research institute
Priority to CN201410163859.4A priority Critical patent/CN103922435B/en
Publication of CN103922435A publication Critical patent/CN103922435A/en
Application granted granted Critical
Publication of CN103922435B publication Critical patent/CN103922435B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Extraction Or Liquid Replacement (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a kind of Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions, it is characterized in that: Aqua Folium Camelliae sinensis extract or shaddock ped water extract are added water and be mixed with water extract solution and pack in bag filter, the pH that adjusts heavy metal ion solution is acid, then bag filter is immersed in described heavy metal ion solution. The present invention utilizes natural discarded object tea dust and shaddock ped, with the heavy metal ion in Aqua Folium Camelliae sinensis extract or shaddock ped water extract absorption waste water, belongs to twice laid, with low cost; And compared with other natural adsorbents, tea dust and shaddock ped do not need special processing, and the preparation process of its water extract is simple, easy to operate; And without eco-toxicity, can not produce secondary pollution; Main, Aqua Folium Camelliae sinensis extract of the present invention or shaddock ped water extract have very superior absorption property to heavy metal ion, can application and the processing of the waste water of the field discharge such as electroplating industry, plastics industry, electronics industry, mining.

Description

Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions
Technical field
The present invention relates to Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and use Aqua Folium Camelliae sinensis extract or the shaddock in Adsorption of Heavy Metal IonsThe method of severe edema due to hypofunction of the spleen extract Adsorption of Heavy Metal Ions.
Background technology
Along with the development of industrial technology, it is day by day serious that the heavy-metal pollution in industrial wastewater becomes. Its soluble-salt is along with dirtThe discharge of water and make ocean, rivers, lake and the farmland etc. of occurring in nature enjoy pollution, if do not controlled, will threatenTo the mankind's healthy and existence. Copper is the element that industrial quarters is often used, and copper ion pollutes the Important Problems that also becomes global concern.National sewage comprehensive emission standard expressly provides that the first discharge standard of copper waste water is that total copper content is less than 5.0mg/L, field irrigationWater standard is that total copper content is less than 0.5mg/L. Thereby eliminating heavy-metal pollution becomes the task of top priority.
Absorption method is to containing having demonstrated higher researching value in the wastewater treatment of heavy metal. Some are through chemical precipitations and otherThe dirty waste water containing micro heavy after treatment such as method is especially adapted to the method, makes it reach sewage drainage standard. Absorption methodThe most important thing is the selection of adsorbent. Had a lot of materials to be used to the adsorbent as heavy metal, as duck excrement (Xiang Hongzhen, oldKindly help secure the success of, Li Xiangqian, etc. the absorption-desorb research of duck excrement to Cu, Zn. Chinese agronomy circular, 2012,28 (32): 31-34),Resin cation (Zhao Shunan. resin cation is in the application of processing in effluent containing heavy metal ions. scientific and technical innovation Leader, 2012,25:144-145), (Liu Yang, waits .4A zeolite to Pb in combined pollution water body to zeolite for Jin Lanshu, Gao Xiangji2+、Cu2+And Cd2+'sRemove. environmental project journal, 2012,6 (5): 1599-1603) and other biological adsorbent (BrinzaL, DringMJ,GavrilescuM.Marinemicroandmacroalgalspeciesasbiosorbentsforheavymetals[J].EnvironmentalEngineeringandManagementJournal,2007,6(3):237-251.DasSK,DasAR,GuhaAK.AstudyontheadsorptionmechanismofmercuryonAspergillumsversicolorbiomass[J].EnvironmentalScienceandTechnology,2007,41:8281-8287.LinCC,LaiYT.AdsorptionandrecoveryofleadfromaqueoussolutionsbyimmobilizedPseudomonasaeruginosaPU21beads[J].JournalofHazardousMaterial, 2005,137 (1): 99-105) etc. But these adsorbents also exist some to ask simultaneouslyTopic, if any adsorption capacity limited, some absorption properties are not high, there is secondary pollution in what have. Therefore, for a specific huge sum of moneyBelong to, develop the society that the adsorbent high with seeking green cost performance strengthen day by day in environmental consciousness significant.
Summary of the invention
The object of the invention is, for avoiding the existing weak point of above-mentioned prior art, to utilize the water extraction of discarded natural products to getThing Adsorption of Heavy Metal Ions, provides Aqua Folium Camelliae sinensis extract and shaddock ped water extract application and the use Aqua Folium Camelliae sinensis in Adsorption of Heavy Metal IonsThe method of extract and shaddock ped water extract Adsorption of Heavy Metal Ions.
For achieving the above object, the present invention adopts following technical scheme:
Aqua Folium Camelliae sinensis extract or the application of shaddock ped water extract in Adsorption of Heavy Metal Ions, as used Aqua Folium Camelliae sinensis extract or shaddock ped water extractMake adsorbent for heavy metal, or utilize the heavy metal ion in Aqua Folium Camelliae sinensis extract or shaddock ped water extract absorption waste water, or profitBy the heavy metal ion in Aqua Folium Camelliae sinensis extract or shaddock ped water extract selective absorption solution.
Wherein, described heavy metal ion is preferably copper ion.
Described heavy metal ion exists with the form of soluble-salt, as nitrate.
The present invention uses the method for Aqua Folium Camelliae sinensis extract or shaddock ped water extract Adsorption of Heavy Metal Ions, and its feature is:
Aqua Folium Camelliae sinensis extract or shaddock ped water extract are added water and be mixed with water extract solution and pack in bag filter, adjust heavy metal ion moltenThe pH of liquid is acid, then described bag filter is immersed in described heavy metal ion solution.
The preparation method of described Aqua Folium Camelliae sinensis extract is: tea leaf powder is broken into end and adds in deionized water, extract 2~3 times at 70 DEG C,Each extraction time is 1.5~2.5 hours, and after each extraction, by centrifugal extract acquisition supernatant, merging obtains after extracting at every turnSupernatant, concentrated and freeze drying obtains Powdered Aqua Folium Camelliae sinensis extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C; InstituteStating the quality of tealeaves and the volume ratio of deionized water is 1g:30ml;
The preparation method of described shaddock ped water extract is: shaddock ped is ground into end and adds in deionized water, extract 2~3 times at 80 DEG C,Each extraction time is 2.5~3.5 hours, and after each extraction, by centrifugal extract acquisition supernatant, merging obtains after extracting at every turnSupernatant, concentrated and freeze drying obtains Powdered shaddock ped water extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C; InstituteStating the quality of shaddock ped and the volume ratio of deionized water is 2g:30ml;
The pH of heavy metal ion solution is adjusted into acidity, and preferably pH is 2-5. Method of adjustment is by HNO3Be mixed with concentrationFor the dilute acid soln of 0.0001-0.01mol, add in heavy metal ion solution and measure heavy metal ion solution with pH meter.
After described bag filter is immersed in heavy metal ion solution, under normal temperature, can complete absorption, variations in temperature to adsorption rate slightlyImpact, keep solution temperature be 0~50 DEG C all can, preferably 20-30 DEG C.
Utilize water extract Adsorption of Heavy Metal Ions, along with the increase of the initial concentration of heavy metal ion, the suction of Unit Weight water extractAttached capacity can increase gradually, and the concentration range of water extract solution solution of the present invention is preferably 50-200mg/L. Described heavy metalIn solion, in the mole of heavy metal ion and water extract solution, the ratio of water extract quality is 3.906~15.625mol/kg.
Water extract solution is added after heavy metal ion solution, and water extract starts Adsorption of Heavy Metal Ions at once, along with the increasing of timeAdd, adsorbance increases gradually, finally reaches balance. Control adsorption time of the present invention is 10min-1440min.
The present invention uses the method for Aqua Folium Camelliae sinensis extract or shaddock ped water extract Adsorption of Heavy Metal Ions, the detection of its adsorption rate and adsorbanceStep is as follows:
Use after water extract Adsorption of Heavy Metal Ions the outer heavy metal concentration of bag filter after heavy metal ion initial concentration solution and absorptionAdopt ICP-OES (inductively coupled plasma atomic emission) method to measure, then calculate the suction of heavy metal ion according to (1) formulaAttached rate q, according to the adsorbance X of (2) formula calculating heavy metal ion.
q = C o - C e C o × 100 % - - - ( 1 ) ;
X = V × ( C o - C e ) C a × V a - - - ( 2 ) ;
Wherein, the adsorption rate that q is heavy metal ion;
CoThe metal ion solution initial concentration (mg/L) of attaching most importance to, after adjusting pH, the concentration of heavy metal ion solutionAs its initial concentration;
CeFor the outer heavy metal concentration (mg/L) of bag filter after certain a period of time is carried out in absorption;
X is the adsorbance (mg/g) that heavy metal ion after certain a period of time is carried out in absorption;
CaFor water extract solution concentration (g/L);
V is the volume of water extract solution and heavy metal ion solution and (L);
VaFor water extract liquor capacity (L).
While adsorbing certain density heavy metal ion according to water extract, adsorption rate and adsorbance, with the variation of adsorption time, can be drawn outAdsorption rate and adsorbance time dependent relation curve, thus obtained equilibration time can characterize ABSORBENTS ABSORPTION metal ionAbsorption speed degree.
Compared with the prior art, beneficial effect of the present invention is embodied in:
The present invention utilizes natural discarded object tea dust and shaddock ped, with the heavy metal in Aqua Folium Camelliae sinensis extract or shaddock ped water extract absorption waste waterIon, belongs to twice laid, with low cost; And compared with other natural adsorbents, tea dust and shaddock ped do not need special locatingReason, the preparation process of its water extract is simple, easy to operate; In addition, the present invention is using Aqua Folium Camelliae sinensis extract or shaddock ped water extract as heavyThe adsorbent of metal ion, without eco-toxicity, can not produce secondary pollution; Main, Aqua Folium Camelliae sinensis extract of the present invention or shaddock pedWater extract has very superior absorption property to heavy metal ion, can application and electroplating industry, plastics industry, electronics industry,The processing of the waste water of the field discharges such as mining, has very large potential actual application value.
Brief description of the drawings
Fig. 1 is at Cu in embodiment 1-362+When the pH=2 of solution, the copper absorption rate under measured different adsorption timesCurve map;
Fig. 2 is at Cu in embodiment 1-362+When the pH=3 of solution, the copper absorption rate under measured different adsorption timesCurve map;
Fig. 3 is at Cu in embodiment 1-362+When the pH=5 of solution, the copper absorption rate under measured different adsorption timesCurve map;
Fig. 4 is the curve map of the cupric ion adsorption under the measured different adsorption times of embodiment 37-54;
Fig. 5 is the curve map of the cupric ion adsorption under the different water extract concentration of embodiment 55-90.
Detailed description of the invention
Below in conjunction with embodiment, the present invention will be further described:
Embodiment 1~36
1, prepare Aqua Folium Camelliae sinensis extract: 10g tea leaf powder is broken into end and adds in 300ml deionized water, extract 3 70 DEG C of water-bathsInferior, extract 1.5 hours at every turn, after each extraction, by centrifugal extract acquisition supernatant, merge the supernatant obtaining after each extractionLiquid, concentrated and freeze drying obtains Powdered Aqua Folium Camelliae sinensis extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C;
Prepare shaddock ped water extract: 20g shaddock ped is broken into end and adds in 300ml deionized water, extract 3 times 80 DEG C of water-baths, everyInferior extraction 2.5 hours, by centrifugal extract acquisition supernatant, merges the supernatant obtaining after each extraction after each extraction, denseThe freeze drying of contracing obtains Powdered shaddock ped water extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C;
2, configuration concentration is 100mgL respectively-1Aqua Folium Camelliae sinensis extract solution and shaddock ped water extract solution;
3, taking the single element mark liquid configuration concentration of Cu as 10mgL-1Cu2+Solution, and regulate pH to be respectively 2,3 and 5,And test obtains Cu after having regulated2+Initial concentration solution;
4,10ml Aqua Folium Camelliae sinensis extract solution is put into bag filter, two ends clamp with dialysis clamp, put into the Cu of 40ml2+SolutionIn (molal weight than for 6.25mol/kg), (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, respectively at30,60,120,360,960, measure the Cu in the outer solution of bag filter when 1440min2+Concentration, averages in triplicate.
After tested, as shown in Figure 1, at the Cu of pH=22+In solution, gained adsorption rate q (AdsorptionrateofCu) complies withInferior is 4.79%, 6.16%, 7.42%, 6.94%, 6.73%, 7.15%, and maximum adsorption rate is 7.42%.
As shown in Figure 2, at the Cu of pH=32+In solution, gained adsorption rate q is followed successively by 6.45%, 8.79%, 12.08%, 12.79%,12.88%, 12.57%, maximum adsorption rate is 12.88%.
As shown in Figure 3, at the Cu of pH=52+In solution, gained adsorption rate q is followed successively by 19.69%, 34.17%, 28.11%,26.77%, 28.79%, 31.03%, maximum adsorption rate is 34.17%.
5,10ml shaddock ped water extract solution is put into bag filter, two ends clamp with dialysis clamp, put into the Cu of 40ml2+SolutionIn (molal weight than for 6.25mol/kg), (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, respectively at30,60,120,360,960, measure the Cu in the outer solution of bag filter when 1440min2+Concentration, averages in triplicate.
After tested, as shown in Figure 1, at the Cu of pH=22+In solution, gained adsorption rate q is followed successively by 5.96%, 6.92%, 7.78%,7.93%, 8.13%, 7.86%, maximum adsorption rate is 8.13%.
As shown in Figure 2, at the Cu of pH=32+In solution, gained adsorption rate q is followed successively by 6.68%, 8.72%, 10.33%, 11.23%,10.68%, 10.72%, maximum adsorption rate is 11.23%.
As shown in Figure 3, at the Cu of pH=52+In solution, gained adsorption rate q is followed successively by 11.66%, 14.95%, 20.38%,21.95%, 24.03%, 24.41%, maximum adsorption rate is 24.41%
Embodiment 37-54
1, prepare Aqua Folium Camelliae sinensis extract: 10g tea leaf powder is broken into end and adds in 300ml deionized water, extract 2 70 DEG C of water-bathsInferior, extract 2.5 hours at every turn, after each extraction, by centrifugal extract acquisition supernatant, merge the supernatant obtaining after each extractionLiquid, concentrated and freeze drying obtains Powdered Aqua Folium Camelliae sinensis extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C;
Prepare shaddock ped water extract: 20g shaddock ped is ground into end and adds in 300ml deionized water, extract 2 times 80 DEG C of water-baths,Each extraction 3.5 hours, by centrifugal extract acquisition supernatant, merges the supernatant obtaining after each extraction after each extraction,Concentrated and freeze drying obtains Powdered shaddock ped water extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C;
2, configuration concentration is 100mgL respectively-1Aqua Folium Camelliae sinensis extract solution and shaddock ped water extract solution;
3, taking the single element mark liquid configuration concentration of Cu as 10mgL-1Cu2+Solution, and to regulate pH be 5;
4,10ml Aqua Folium Camelliae sinensis extract solution is put into bag filter, two ends clamp with dialysis clamp, put into the Cu of 45ml2+SolutionIn (molal weight than for 7.03mol/kg), (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, respectively at10,30,60,100,120,240,360,720, sampling and measuring when 1440min, average in triplicate, result tableBright, the adsorbance (AdsorptionquantityofCu) of Aqua Folium Camelliae sinensis extract absorbing copper ion is respectively 49.15mg/g, 71.90mg/g,95.10mg/g,112.55mg/g,115.95mg/g,127.40mg/g,129.05mg/g,127.90mg/g,129.45mg/g。
5,10ml shaddock ped water extract solution is put into bag filter, two ends clamp with dialysis clamp, put into the Cu of 45ml2+In solution(molal weight than for 7.03mol/kg), (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, respectively at 10,30,60,100,120,240,360,720, sampling and measuring when 1440min, average in triplicate. Result shows,The adsorbance of shaddock ped water extract absorbing copper ion is respectively 41.30mg/g, 63.70mg/g, 89.10mg/g, 99.65mg/g, 103.55Mg/g, 109.60mg/g, 113.45mg/g, 115.80mg/g, 118.05mg/g. Refer to accompanying drawing 4.
Embodiment 55-90
The present embodiment is prepared Aqua Folium Camelliae sinensis extract and shaddock ped water extract by the identical mode of embodiment 37-54;
Tealeaves and shaddock ped water extract solution concentration are 100mgL-1,Cu2+The pH of solution is 5, and concentration is 10mgL-1, get 10mLWater extract solution is put into bag filter, and two ends clamp with dialysis clamp, put into 50mlCu2+In solution, (molal weight ratio is7.8125mol/kg), (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, the sampling and measuring time is respectively 10,30,60,100,120,240,360,720,1440min, in triplicate. Result shows, tealeaves water extraction in such casesThing is respectively 107.50mg/g to the adsorbance of copper ion, 156.55mg/g, and 145.95mg/g, 139.65mg/g, 151.50mg/g,153.22mg/g. Shaddock ped water extract is respectively 68.85mg/g to the adsorbance of copper ion, 91.80mg/g, 112.35mg/g, 119.50Mg/g, 116.34mg/g, 131.35mg/g. Other conditions are identical, change the concentration of Aqua Folium Camelliae sinensis extract and shaddock ped water extract, allFor 50mgL-1, put into 50mlCu2+In solution (molal weight is than being 15.625mol/kg), Aqua Folium Camelliae sinensis extract in such casesAdsorbance to copper ion is respectively 69.4mg/g, 89.1mg/g, 93.6mg/g, 97.5mg/g, 98.1mg/g, 97.8mg/g.Shaddock ped water extract is respectively 57.7mg/g to the adsorbance of copper ion, 80.1mg/g, and 79.8mg/g, 92.3mg/g, 88.1mg/g,91.2mg/g. Other conditions are identical, change the concentration of Aqua Folium Camelliae sinensis extract and shaddock ped water extract, are 200mgL-1, put into50mlCu2+In solution (molal weight is than being 3.906mol/kg), Aqua Folium Camelliae sinensis extract is divided the adsorbance of copper ion in such casesWei 49.25mg/g, 72.78mg/g, 103.65mg/g, 107.70mg/g, 105.93mg/g, 99.03mg/g. Shaddock ped waterExtract is respectively 32.80mg/g to the adsorbance of copper ion, 39.83mg/g, and 52.70mg/g, 62.03mg/g, 60.55mg/g,61.35mg/g. Refer to accompanying drawing 5.
Embodiment 91-92
Prepare Aqua Folium Camelliae sinensis extract and shaddock ped water extract by the identical mode of embodiment 37-54;
Get the water sample of tributary, the Fei river in Anhui Province, Hefei City section, with clearing up after Filter paper filtering, regulating its pH value is 5, gets this water sample of 40mLAs heavy metal ion solution;
Getting 10mL concentration is 100mgL-1Aqua Folium Camelliae sinensis extract solution is put into bag filter, and two ends clamp with dialysis clamp, put into waterIn sample, (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, the sampling and measuring time is 720min, repeats threeInferior. Result shows, Aqua Folium Camelliae sinensis extract is in the time processing Fei river in Anhui Province water sample, best to the treatment effect of Cu in 6 heavy metal species ions, inhalesAttached amount maximum, is 151.50mg/g, and other 5 heavy metal species are also had to higher adsorbance. Concrete data are in table 1.
Table 1 is processed tributary, Fei river in Anhui Province water sample result by Aqua Folium Camelliae sinensis extract
Under the same terms, Aqua Folium Camelliae sinensis extract is changed into the shaddock ped water extract of same concentration, result shows, the adsorption effect of Cu and AsBest, adsorbance is respectively 116.33mg/g and 102.67. Concrete data are in table 2.
Table 2 is processed tributary, Fei river in Anhui Province water sample result with shaddock ped water extract
Embodiment 93-94
Prepare Aqua Folium Camelliae sinensis extract and shaddock ped water extract by the identical mode of embodiment 37-54;
Get Hefei City's waste water from plating plant, with clearing up after Filter paper filtering, regulating its pH value is 5, gets this water sample of 40mL;
Getting 10mL concentration is 100mgL-1Aqua Folium Camelliae sinensis extract solution is put into bag filter, and two ends clamp with dialysis clamp, put into waterIn sample, (220r/min) constant temperature (25 DEG C) vibration on reciprocation type vibrating machine, the sampling and measuring time is 720min, repeats threeInferior. Result shows, Aqua Folium Camelliae sinensis extract is in the time processing certain waste water from plating plant, and best to the absorption of Cu, adsorbance is 103.65mg/g,Other heavy metal ion are also possessed to certain adsorption capacity. Concrete data are in table 3.
Table 3 is processed certain waste water from plating plant result by Aqua Folium Camelliae sinensis extract
Under the same terms, Aqua Folium Camelliae sinensis extract is changed into the shaddock ped water extract of same concentration, result shows, shaddock ped water extract is to these six kindsThe adsorption effect of heavy metal ion is similar. Concrete data are in table 4.
Table 4 is processed certain waste water from plating plant result with shaddock ped water extract
Above-described embodiment, only for the present invention will be described, does not form the restriction to claim scope, art technology peopleOther alternative means that member can expect, all within the scope of the claims in the present invention.

Claims (4)

1. the method that uses Aqua Folium Camelliae sinensis extract or shaddock ped water extract Adsorption of Heavy Metal Ions, is characterized in that:
Aqua Folium Camelliae sinensis extract or shaddock ped water extract are added water and be mixed with water extract solution and pack in bag filter, adjust heavy metal ion moltenThe pH of liquid is 5, then described bag filter is immersed in described heavy metal ion solution.
2. the method for use Aqua Folium Camelliae sinensis extract according to claim 1 or shaddock ped water extract Adsorption of Heavy Metal Ions, its featureBe:
The preparation method of described Aqua Folium Camelliae sinensis extract is: tea leaf powder is broken into end and adds in deionized water, extract 2~3 times at 70 DEG C,Each extraction time is 1.5~2.5 hours, and after each extraction, by centrifugal extract acquisition supernatant, merging obtains after extracting at every turnSupernatant, concentrated and freeze drying obtains Powdered Aqua Folium Camelliae sinensis extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C; InstituteStating the quality of tealeaves and the volume ratio of deionized water is 1g:30ml;
The preparation method of described shaddock ped water extract is: shaddock ped is ground into end and adds in deionized water, extract 2~3 times at 80 DEG C,Each extraction time is 2.5~3.5 hours, and after each extraction, by centrifugal extract acquisition supernatant, merging obtains after extracting at every turnSupernatant, concentrated and freeze drying obtains Powdered shaddock ped water extract, and sublimation drying is 16h, and condenser temperature is-40 DEG C; InstituteStating the quality of shaddock ped and the volume ratio of deionized water is 2g:30ml.
3. the method for use Aqua Folium Camelliae sinensis extract according to claim 1 or shaddock ped water extract Adsorption of Heavy Metal Ions, its featureBe: after described bag filter is immersed in heavy metal ion solution, keeping heavy metal ion solution temperature is 0~50 DEG C.
4. the method for use Aqua Folium Camelliae sinensis extract according to claim 1 or shaddock ped water extract Adsorption of Heavy Metal Ions, its featureBe: described water extract solution concentration is 50mg/L~200mg/L; The mole of heavy metal ion in described heavy metal ion solutionWith the ratio of water extract quality in water extract solution be 3.906~15.625mol/kg.
CN201410163859.4A 2014-04-22 2014-04-22 Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions Expired - Fee Related CN103922435B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410163859.4A CN103922435B (en) 2014-04-22 2014-04-22 Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410163859.4A CN103922435B (en) 2014-04-22 2014-04-22 Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions

Publications (2)

Publication Number Publication Date
CN103922435A CN103922435A (en) 2014-07-16
CN103922435B true CN103922435B (en) 2016-05-25

Family

ID=51140870

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410163859.4A Expired - Fee Related CN103922435B (en) 2014-04-22 2014-04-22 Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions

Country Status (1)

Country Link
CN (1) CN103922435B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109730296B (en) * 2019-03-08 2022-05-06 徐丽春 Preparation method of purple bamboo salt
CN114988944A (en) * 2022-05-31 2022-09-02 中科华瑞(深圳)生态科技有限公司 Heavy metal blocking agent and preparation method, use method and application thereof
CN115075055B (en) * 2022-06-15 2023-04-18 石家庄铁道大学 Nano magnetic oxide composite tea paper and preparation method thereof

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101062165A (en) * 2007-06-18 2007-10-31 石任兵 Citrus aurantium total flavone extract and the preparing method thereof
CN101224411A (en) * 2007-10-17 2008-07-23 南京大学 Natural plant material of processing cationic dye in industrial wastewater and method thereof
CN101507914A (en) * 2009-02-10 2009-08-19 浙江大学 Preparation method of tea-leaf power capable of processing lead-containing waste water and use method thereof
KR100924914B1 (en) * 2009-04-17 2009-11-03 아쿠아골드 주식회사 Slow release granules including natural plant extracts and the preparation of the same
CN102202815A (en) * 2008-05-16 2011-09-28 维鲁泰克技术股份有限公司 Green synthesis of nanometals using plant extracts and use thereof
CN103484257A (en) * 2013-10-14 2014-01-01 厦门大学 Comprehensive utilization method for pomelo peels
CN103657595A (en) * 2013-11-27 2014-03-26 杭州电子科技大学 Method for preparing adsorption bag for removing chromium from wastewater

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8394739B2 (en) * 2010-07-14 2013-03-12 Technology Development Center, King Abdulaziz City For Science And Technology Adsorbent for adsorption of heavy metals in waste water

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101062165A (en) * 2007-06-18 2007-10-31 石任兵 Citrus aurantium total flavone extract and the preparing method thereof
CN101224411A (en) * 2007-10-17 2008-07-23 南京大学 Natural plant material of processing cationic dye in industrial wastewater and method thereof
CN102202815A (en) * 2008-05-16 2011-09-28 维鲁泰克技术股份有限公司 Green synthesis of nanometals using plant extracts and use thereof
CN101507914A (en) * 2009-02-10 2009-08-19 浙江大学 Preparation method of tea-leaf power capable of processing lead-containing waste water and use method thereof
KR100924914B1 (en) * 2009-04-17 2009-11-03 아쿠아골드 주식회사 Slow release granules including natural plant extracts and the preparation of the same
CN103484257A (en) * 2013-10-14 2014-01-01 厦门大学 Comprehensive utilization method for pomelo peels
CN103657595A (en) * 2013-11-27 2014-03-26 杭州电子科技大学 Method for preparing adsorption bag for removing chromium from wastewater

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
有效地用生物质废弃物除去有害的金属和回收有价金属的工艺进展;井上胜利,等;《国外金属矿选矿》;20071031;36-44 *
柚皮纤维素的提取工艺研究;罗均,等;《食品工业科技》;20101231;第31卷(第4期);273-276 *

Also Published As

Publication number Publication date
CN103922435A (en) 2014-07-16

Similar Documents

Publication Publication Date Title
Jin et al. Phosphorus fractions and phosphate sorption-release characteristics of the sediment in the Yangtze River estuary reservoir
Pédrot et al. Upper soil horizons control the rare earth element patterns in shallow groundwater
CN103922435B (en) Aqua Folium Camelliae sinensis extract or shaddock ped water extract application and the adsorption method in Adsorption of Heavy Metal Ions
Pettine et al. Soluble and particulate metals in the Po River: factors affecting concentrations and partitioning
Byrd et al. The behavior of trace metals in the Geum Estuary, Korea
Yang et al. Modeling and visualizing the transport and retention of cationic and oxyanionic metals (Cd and Cr) in saturated soil under various hydrochemical and hydrodynamic conditions
Yan et al. Effects of inorganic and organic acids on heavy metals leaching in contaminated sediment
Gao et al. Coagulation efficiency and residual aluminum content of polyaluminum silicate chloride in water treatment
Bolan et al. Effect of pH on the adsorption of phosphate and potassium in batch and in column experiments
Tian et al. Phosphorus fractions and adsorption characteristics of floodplain sediments in the lower reaches of the Hanjiang River, China
Hua et al. Soil metal contamination and fractionation of tea plantations: case studies in a normal tea garden and in a restored mineland tea stand
Rashad et al. Effect of dissolved organic matter derived from waste amendments on the mobility of inorganic arsenic (III) in the Egyptian alluvial soil
Litynska et al. Neutralization of arsenic pollutants of natural waters by converting them into insoluble form
Sanou et al. Dynamic Study and Modelling of Arsenic Removal from Groundwater Using Ferromagnetic Carbon as Fixed Bed Adsorbent in Column
Zhang et al. Arsenic pollution characteristics and variation trends in Yangzonghai Lake, China.
CN112730650B (en) Method for enriching ultra-trace organic matters in large-volume water
Alcaine et al. Distribution and mobility of geogenic arsenic in the shallow aquifers of the northeast of La Pampa, Argentina
ミャンガンオルギルボルド Impact of land uses on dynamics of pollutants along the Selenga River system in the Lake Baikal basin
Knox et al. In-Situ U Stabilization by Microbial Metabolites; Sequestration of U by Melanin and its Sorption to Minerals.
Islama et al. Seasonal Variations of Arsenic in the Ganges and Brahmaputra River, Bangladesh.
Sinwar et al. Influence of organic matter on retention and release of lead in a semi-arid soil from India
Persson et al. Combining Chemical Flocculation and Disc Filtration with Managed Aquifer Recharge.
Gao et al. Arsenic in saline groundwater in the Yuncheng Basin, northern China
Wong et al. The effects of increasing salinity on exchange processes in coastal lowland acid sulfate soils.
Savenko et al. Migration of dissolved matter at Serebryanka R. Mouth, the basin of the Sea of Japan (Sikhote Alin Reserve)

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160525

Termination date: 20200422