CN201390661Y - Underwater ion adsorption device - Google Patents
Underwater ion adsorption device Download PDFInfo
- Publication number
- CN201390661Y CN201390661Y CN200920105101U CN200920105101U CN201390661Y CN 201390661 Y CN201390661 Y CN 201390661Y CN 200920105101 U CN200920105101 U CN 200920105101U CN 200920105101 U CN200920105101 U CN 200920105101U CN 201390661 Y CN201390661 Y CN 201390661Y
- Authority
- CN
- China
- Prior art keywords
- ion
- ion exchange
- adsorption device
- water
- ion adsorption
- 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 - Lifetime
Links
Images
Abstract
The utility model belongs to the technical field of test analysis, in particular to a pretreatment experimental device which is used for absorbing negative ions and positive ions and testing isotopic compositions. The underwater ion adsorption device is formed by sequentially connecting a Buchner funnel, one or more ion exchange columns and a filter flask by utilizing standard grounds. The underwater ion adsorption device can connect the ion exchange columns with each other, and simultaneously absorbs various negative and positive ions in water, thereby reducing labor intensity of experiment operation. The underwater ion adsorption device further can effectively resolve a difficult problem that resin remained in the ion exchange columns is not easy to remove. Further, the under water ion adsorption device is simple in mounting and convenient in carrying, and is particularly suitable for treating field on-site water samples.
Description
Affiliated technical field
The utility model belongs to the test and analysis technology field, relates in particular to yin, yang ion in a kind of planar water, is used for simple installation, the portable pretreating device of isotopics test.
Background technology
Various yin, yang ionic element isotopics in the test analysis water are to determine these yin, yang ion sources and change the most direct and effective means, and the scientific basis of necessity can be provided for water surrounding variation and water Pollution Study.Ammonium radical ion nitrogen isotope is formed, nitrate ion nitrogen and oxygen isotope is formed, the chromate ion chromium isotope is formed, test analysis such as boron istope composition in the boric acid, usually need to adopt the moon or Zeo-karb from water, to adsorb these ions, then carry out corresponding isotopics test.For prevent that the yin, yang ion changes in the water sample in transportation, influence element isotopics wherein, ionic adsorption processing water sample is carried out at the scene in the open air.At present, be suitable for yin, yang ion in the field condition adsorbing and extracting water, the pretreating device that is used for isotopics tests mainly by separating funnel, ion exchange column and filter flask by soft rubber ball be in series (Silva et al., 2000)
*Water sample flows in the ion exchange column under the control of separating funnel valve, and the moon or cation-adsorption are on resin, and the waste water sample flows in the filter flask.
There is following technical problem in the prior art:
(1) institute's water sampling amount is limited under a lot of study conditions, still, needs absorption different kinds of ions wherein simultaneously.Existing adsorption unit can not solve the convenient problem that a plurality of ion exchange columns connect simultaneously of handling owing to adopt soft rubber ball to connect.
(2), increased the complexity and the labor intensity of operating personnel of experiment because the each experiment of existing adsorption unit only can be handled single ionic, and different ions need repeat repeatedly to test.
(3) resin is easy to remain in the exchange column in the experimentation, easy-clear not, thus influence the subsequent experimental precision.
Garten (1992)
*Once proposed the yin, yang ion exchange column and connected, adsorbed ammonium radical ion and nitrate ion in the Atmospheric precipitation simultaneously, and be used for test analysis nitrogen isotope wherein and form.But exchange column adopts soft rubber ball to be connected with sebific duct in its device, is difficult for connecting and dismounting; It is worthy of note that more this device designs for field fixed point long-term observation, each sampling point needs a covering device, and does not have portable handiness.
Chang et al. (1999)
* *Also once proposed the yin, yang ion exchange column and connected, and be used for nitrate ion nitrogen and oxygen isotope and form test.But its device mainly forms based on the described device development of Silva et al. (2000), only connects a cationic exchange coloum (not providing in connection side's French) before anion-exchange column; Its device connects the dissolved organic carbon that cationic exchange coloum is used for removing water, and purpose is not element isotopics test in the positively charged ion, so whole device is mainly used in the absorption of single ionic (nitrate ion).
Therefore, need a kind of water intermediate ion adsorption unit that is applicable to field operation that is convenient for carrying of development.On the one hand, can conveniently handle the simple and easy connection simultaneously of a plurality of ion exchange columns, single experiment absorption different kinds of ions, the labour intensity of reduction experiment operator simultaneously, need overcome the deficiency of cull removing aspect.
* literature reference: Silva S R, Ging P B, Lee R W, ZieglerA C, Chang C C Y, and Avanzino R is new method forcollection of nitrate from fresh water and the analysis of nitrogen and oxygen isotope ratios.Journal of Hydrology J.2000.A, 228:22-36
The * literature reference: Garten C is isotope composition of ammonium and nitrate in bulk precipitation andforest throughfall.International Journal of Environment Analytical Chemistry T.1992.Nitrogen, 47:33-45
* * literature reference: Chang C C Y, Langston J, Riggs M, Campbell D H, Silva S R and Kendall is method fornitrate collection for δ 15N and δ 18O analysis from waters with low nitrate concentrations.Canadian Journal ofFisheries and Aquatic Sciences C.1999.A, 56:1856-1864
Summary of the invention
At the technical problem that exists in the above-mentioned prior art, the utility model provides a kind of device, and this device can not only effectively solve the problem of a plurality of ion exchange columns simple and easy connection simultaneously, and can solve resin residue removing problem in the exchange column.
Concrete technical scheme is as follows:
A kind of water intermediate ion adsorption unit is connected to form successively by B, single or multiple ion exchange column and filter flask;
Described connection is meant that B, ion exchange column and filter flask adopt the standard ground to be connected, and dismounting only need simply plug and unplug, and can finish;
Described B bleeding point has valve, the lower end has the standard ground;
Described ion exchange column upper and lower end all has the standard ground, and inner 0.5~1cm place mounted sieve is deposited ion exchange resin;
Described filter flask bottleneck has the standard ground, and bleeding point has valve;
The ground conformance to standard of described B, ion exchange column and filter flask is convenient to connect.
When the ion in the needs absorption water sampleConnect B, single or multiple ion exchange column and filter flask successively, close the B evacuating valve, water sample is poured in the B, naturally flow in the single or multiple ion exchange columns, open the filter flask evacuating valve, regulate the water sample flow velocity, close the filter flask evacuating valve after reaching satisfied flow velocity (1 premium on currency 2~4 hours) by vacuumizing.If connect two exchange columns be equipped with respectively hydrogen type cation exchange resin (such as, the home-made storng-acid cation exchange resin, specification: 001 * 7 (732), Hydrogen, granularity: 100~200 orders) and chlorine type anionite-exchange resin (such as, home-made strongly basic anion exchange resin, specification: 201 * 7 (717), the fluorine type, granularity: 100~200 orders), water sample can adsorb ammonium radical ion (NH wherein after by two exchange columns respectively
4 +) and nitrate ion (NO
3 -), be used for test analysis ammonium root
15N/
14N isotopics and nitrate radical
15N/
14N reaches
18O/
16The O isotopics.Connect again selection type resin-columns such as chromic acid and boron ion are housed, can also select to adsorb these ions simultaneously, be used for chromic acid
53Cr/
52Cr and boric acid
11B/
10Etc. corresponding isotopics test analysis.
When needs are removed the resin that residues in the exchange columnClose the evacuating valve of filter flask, connect single needs successively and remove the ion exchange column and the B of cull, in B, add water, filter flask is filled after water column is higher than sieve plate 1cm in water and the exchange column, with soft rubber ball sealing B upper end, opens the B evacuating valve, vacuumize repeatedly, get final product residual resin in the deionizing exchange column.
The beneficial effects of the utility model are, can solve each parts connectivity problem of experimental installation easily, be convenient to simultaneously different kinds of ions problem in the planar water, and the exchange column cull are removed problem.
Description of drawings
The existing water intermediate ion of Fig. 1 adsorption unit structural representation.
Fig. 2 the utility model apparatus structure synoptic diagram (single ionic in the planar water).
Fig. 3 the utility model apparatus structure synoptic diagram (different kinds of ions in the planar water is an example with two kinds simultaneously)
B structural representation among Fig. 4 Fig. 2 and Fig. 3.
Ion exchange column structural representation among Fig. 5 Fig. 2 and Fig. 3.
Filter flask structural representation among Fig. 6 Fig. 2 and Fig. 3.
11. separating funnels among Fig. 1,12. soft rubber balls, 13. ion exchange columns, 14. filter flasks.
1. Bs among Fig. 2,2. ion exchange column, 3 filter flasks.
1. Bs among Fig. 3,2. ion exchange column, 3 filter flasks.
41. bleeding point valves among Fig. 4,42. standard grounds.
51. upper end standard grounds among Fig. 5,52. lower end standard grounds, 53. sieve plates.
61. bottleneck standard grounds among Fig. 6,62. bleeding point valves.
Embodiment
In Fig. 2, adopt the standard ground to connect between B (1), ion exchange column (2), the filter flask (3).
In Fig. 3, the series connection of two ion exchange columns (2) ground, two kinds of ions (is example with two kinds) in the planar water simultaneously.
In Fig. 4, B is that the centre has evacuating valve (41), the lower end has standard ground (42).
In Fig. 5, ion exchange column is that (52) end has the standard ground under last (51).
In Fig. 6, the filter flask bottleneck has standard ground (61), bleeding point has valve (62).
When the ion in the needs absorption water sampleConnect B (1), single or multiple ion exchange column (2) and filter flask (3) successively, close B evacuating valve (41), water sample is poured in the B (1), naturally flow in the single or multiple ion exchange columns (2), open filter flask evacuating valve (62), regulate the water sample flow velocity, close filter flask evacuating valve (62) after reaching satisfied flow velocity (1 premium on currency 2~4 hours) by vacuumizing.If connect be equipped with respectively on two exchange columns (2) sieve plates (53) hydrogen type cation exchange resin (such as, the home-made storng-acid cation exchange resin, specification: 001 * 7 (732), Hydrogen, granularity: 100~200 orders) and chlorine type anionite-exchange resin (such as, home-made strongly basic anion exchange resin, specification: 201 * 7 (717), the chlorine type, granularity: 100~200 orders), water sample can adsorb ammonium radical ion (NH wherein after by two exchange columns (2) respectively
4 +) and nitrate ion (NO
3 -), be used for test analysis ammonium root
15N/
14N isotopics and nitrate radical
15N/
11N reaches
18O/
16The O isotopics.Connect again selection type resin-columns such as chromic acid and boron ion are housed, can also select to adsorb these ions simultaneously, be used for chromic acid
53Cr/
52Cr and boric acid
11B/
10Corresponding isotopics test analysis such as B.
When needs are removed the resin that residues in the exchange columnClose the evacuating valve (62) of filter flask, connect single needs successively and remove the ion exchange column (2) and the B (1) of cull, at B (1) Zhong Jiashui, filter flask (3) is filled after water column is higher than sieve plate (53) 1cm in water and the exchange column (2), seals B (1) upper end with soft rubber ball, opens B evacuating valve (41), vacuumize repeatedly, get final product residual resin in the deionizing exchange column (2).
The complete assembly installation and removal are simple, only need to get final product by the simple plug of ground ((42), (51), (52), (61)); Parts ((1), (2), (3)) are easy to carry less, are fit to very much the field condition operation.
Claims (3)
1. water intermediate ion adsorption unit, by B, ion exchange column, filter flask connects successively, it is characterized in that: B, ion exchange column and filter flask adopt the standard ground to be connected.
2. water intermediate ion adsorption unit according to claim 1, it is characterized in that: B has evacuating valve, and the lower end has the standard ground; The ion exchange column upper and lower end all has the standard ground; Filter flask has standard ground and evacuating valve.
3. water intermediate ion adsorption unit according to claim 1, it is characterized in that: the ion exchange column that is connected is single or multiple.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN200920105101U CN201390661Y (en) | 2009-01-14 | 2009-01-14 | Underwater ion adsorption device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN200920105101U CN201390661Y (en) | 2009-01-14 | 2009-01-14 | Underwater ion adsorption device |
Publications (1)
Publication Number | Publication Date |
---|---|
CN201390661Y true CN201390661Y (en) | 2010-01-27 |
Family
ID=41597483
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN200920105101U Expired - Lifetime CN201390661Y (en) | 2009-01-14 | 2009-01-14 | Underwater ion adsorption device |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN201390661Y (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102008842A (en) * | 2010-09-21 | 2011-04-13 | 重庆文理学院 | Multipurpose filter bottle and use method |
CN102466576A (en) * | 2010-11-10 | 2012-05-23 | 中国科学院地质与地球物理研究所 | Apparatus used for gas collection in solid-liquid/liquid-liquid reactions |
CN101776536B (en) * | 2009-01-14 | 2014-02-19 | 中国科学院地理科学与资源研究所 | Apparatus for absorbing ion in water |
CN105242032A (en) * | 2015-09-25 | 2016-01-13 | 国网山东省电力公司电力科学研究院 | Apparatus for determining maximum regeneration capacity of hydrogen-oxygen type anion exchange resin |
-
2009
- 2009-01-14 CN CN200920105101U patent/CN201390661Y/en not_active Expired - Lifetime
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101776536B (en) * | 2009-01-14 | 2014-02-19 | 中国科学院地理科学与资源研究所 | Apparatus for absorbing ion in water |
CN102008842A (en) * | 2010-09-21 | 2011-04-13 | 重庆文理学院 | Multipurpose filter bottle and use method |
CN102466576A (en) * | 2010-11-10 | 2012-05-23 | 中国科学院地质与地球物理研究所 | Apparatus used for gas collection in solid-liquid/liquid-liquid reactions |
CN105242032A (en) * | 2015-09-25 | 2016-01-13 | 国网山东省电力公司电力科学研究院 | Apparatus for determining maximum regeneration capacity of hydrogen-oxygen type anion exchange resin |
CN105242032B (en) * | 2015-09-25 | 2017-10-31 | 国网山东省电力公司电力科学研究院 | A kind of device for determining hydrogen-oxygen type anion exchange resin maximum regeneration capacity |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN201390661Y (en) | Underwater ion adsorption device | |
CN105259011B (en) | A kind of Soil fulvic acid subfraction fractional extraction method | |
CN109596809B (en) | Simulation system for monitoring and analyzing dynamic release of pollutants in soil filler under leaching state | |
US11656207B2 (en) | Material and its method for rapid eluting in an ionic rare earth ore leaching site | |
CN111562354A (en) | Method and device for evaluating long-acting property of heavy metal contaminated soil remediation agent based on solidification/stabilization | |
CN112496024A (en) | Decontamination separation method of uranium-contaminated soil based on chemical leaching | |
Guo et al. | Partition and characterization of cadmium on different particle-size aggregates in Chinese Phaeozem | |
Yoshida et al. | Determination of the chemical forms of iodine with IC-ICP-MS and its application to environmental samples | |
CN105688828B (en) | A method of extraction of uranium from seawater plant-inorganic compounding adsorbent is prepared using phosphoric acid modification folium cycas | |
Van Benschoten et al. | A nonelectrostatic surface complexation model for lead sorption on soils and mineral surfaces | |
CN101776536B (en) | Apparatus for absorbing ion in water | |
CN102478468A (en) | Apparatus for determination of water soluble ions in solid sample and determination method | |
CN101637693A (en) | NO2 absorbent, absorption tube and application thereof | |
Lins et al. | Removal of ammonia nitrogen from leachate of Muribeca municipal solid waste landfill, Pernambuco, Brazil, using natural zeolite as part of a biochemical system | |
CN201753173U (en) | Apparatus for treating hydrogen sulfide | |
LIU et al. | Development of a first-order kinetics-based model for the adsorption of nickel onto peat | |
CN102527088B (en) | Pressure-reducing type asphalt four-component separating device | |
CN109300386B (en) | Experimental device for treating polluted karst underground water of leachate in phosphogypsum yard | |
CN102967574A (en) | Method for fast enriching and detecting trace amount of As (V) and Cr (VI) contained in water by filling microcolumn by utilizing fiber | |
CN106950301B (en) | Determination method of dioxin in sediment and rapid pretreatment method of sediment | |
CN206116033U (en) | Low -level radioactive wastewater's processing apparatus | |
CN212646686U (en) | Coal-fired power plant fly ash leaching test device | |
CN215262744U (en) | Seawater heavy metal element multi-unit collaborative online enrichment and self-cleaning device | |
CN206321611U (en) | A kind of mercury ion detecting separator | |
CN212633835U (en) | Cadmium-polluted soil restorer |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
AV01 | Patent right actively abandoned |
Granted publication date: 20100127 Effective date of abandoning: 20090114 |
|
AV01 | Patent right actively abandoned |
Granted publication date: 20100127 Effective date of abandoning: 20090114 |
|
RGAV | Abandon patent right to avoid regrant | ||
DD01 | Delivery of document by public notice |
Addressee: Wang Zhimin Document name: Notification of Passing Examination on Formalities |