CN104310676B - The method that mercury compound in waste liquid is removed under normal temperature and pressure - Google Patents
The method that mercury compound in waste liquid is removed under normal temperature and pressure Download PDFInfo
- Publication number
- CN104310676B CN104310676B CN201410539774.1A CN201410539774A CN104310676B CN 104310676 B CN104310676 B CN 104310676B CN 201410539774 A CN201410539774 A CN 201410539774A CN 104310676 B CN104310676 B CN 104310676B
- Authority
- CN
- China
- Prior art keywords
- hydrargyrum
- under normal
- waste liquid
- mercury compound
- normal temperature
- 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.)
- Active
Links
- 239000007788 liquid Substances 0.000 title claims abstract description 32
- 239000002699 waste material Substances 0.000 title claims abstract description 30
- 238000000034 method Methods 0.000 title claims abstract description 23
- 229940100892 mercury compound Drugs 0.000 title claims abstract description 22
- 150000002731 mercury compounds Chemical class 0.000 title claims abstract description 22
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 claims abstract description 61
- 239000003463 adsorbent Substances 0.000 claims abstract description 31
- 238000006243 chemical reaction Methods 0.000 claims abstract description 22
- 239000000178 monomer Substances 0.000 claims abstract description 18
- 239000011941 photocatalyst Substances 0.000 claims abstract description 11
- 239000000969 carrier Substances 0.000 claims abstract description 10
- 238000001179 sorption measurement Methods 0.000 claims abstract description 10
- 230000003197 catalytic effect Effects 0.000 claims abstract description 8
- 238000000354 decomposition reaction Methods 0.000 claims abstract description 7
- 239000002351 wastewater Substances 0.000 claims abstract description 7
- 239000003054 catalyst Substances 0.000 claims description 14
- 229910021536 Zeolite Inorganic materials 0.000 claims description 13
- 239000010457 zeolite Substances 0.000 claims description 13
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 10
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 10
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 claims description 6
- 238000010438 heat treatment Methods 0.000 claims description 6
- 238000005516 engineering process Methods 0.000 claims description 5
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 4
- 239000002250 absorbent Substances 0.000 claims description 4
- 230000002745 absorbent Effects 0.000 claims description 4
- 239000013078 crystal Substances 0.000 claims description 4
- 239000010936 titanium Substances 0.000 claims description 4
- 229910052719 titanium Inorganic materials 0.000 claims description 4
- 239000000919 ceramic Substances 0.000 claims description 3
- 239000003795 chemical substances by application Substances 0.000 claims description 3
- 239000008119 colloidal silica Substances 0.000 claims description 3
- 239000003610 charcoal Substances 0.000 claims description 2
- 239000000835 fiber Substances 0.000 claims description 2
- 230000000149 penetrating effect Effects 0.000 claims description 2
- 239000011521 glass Substances 0.000 claims 1
- 239000002594 sorbent Substances 0.000 abstract description 6
- 230000004044 response Effects 0.000 abstract description 3
- 239000012530 fluid Substances 0.000 abstract description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 30
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 11
- 230000000694 effects Effects 0.000 description 8
- -1 hydrargyrum ion Chemical class 0.000 description 8
- 229910052753 mercury Inorganic materials 0.000 description 7
- 230000008569 process Effects 0.000 description 7
- 239000007787 solid Substances 0.000 description 7
- 150000001875 compounds Chemical class 0.000 description 6
- 239000000463 material Substances 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 229910052782 aluminium Inorganic materials 0.000 description 5
- 239000007789 gas Substances 0.000 description 5
- 150000002500 ions Chemical class 0.000 description 5
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 4
- 239000004411 aluminium Substances 0.000 description 4
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 3
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 235000012239 silicon dioxide Nutrition 0.000 description 3
- 229910052709 silver Inorganic materials 0.000 description 3
- 239000004332 silver Substances 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 2
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 238000013329 compounding Methods 0.000 description 2
- 229910052593 corundum Inorganic materials 0.000 description 2
- 239000010779 crude oil Substances 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 239000002052 molecular layer Substances 0.000 description 2
- 239000005373 porous glass Substances 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- MBMLMWLHJBBADN-UHFFFAOYSA-N Ferrous sulfide Chemical compound [Fe]=S MBMLMWLHJBBADN-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- YKTSYUJCYHOUJP-UHFFFAOYSA-N [O--].[Al+3].[Al+3].[O-][Si]([O-])([O-])[O-] Chemical class [O--].[Al+3].[Al+3].[O-][Si]([O-])([O-])[O-] YKTSYUJCYHOUJP-UHFFFAOYSA-N 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229960000892 attapulgite Drugs 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000000440 bentonite Substances 0.000 description 1
- 229910000278 bentonite Inorganic materials 0.000 description 1
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 1
- 239000000292 calcium oxide Substances 0.000 description 1
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 1
- LHJQIRIGXXHNLA-UHFFFAOYSA-N calcium peroxide Chemical compound [Ca+2].[O-][O-] LHJQIRIGXXHNLA-UHFFFAOYSA-N 0.000 description 1
- 235000019402 calcium peroxide Nutrition 0.000 description 1
- 238000005341 cation exchange Methods 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000005660 chlorination reaction Methods 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 239000010431 corundum Substances 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 230000000593 degrading effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 229960002089 ferrous chloride Drugs 0.000 description 1
- 229940116007 ferrous phosphate Drugs 0.000 description 1
- 239000011790 ferrous sulphate Substances 0.000 description 1
- 235000003891 ferrous sulphate Nutrition 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 238000002309 gasification Methods 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000002887 hydroxy group Chemical group [H]O* 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- NMCUIPGRVMDVDB-UHFFFAOYSA-L iron dichloride Chemical compound Cl[Fe]Cl NMCUIPGRVMDVDB-UHFFFAOYSA-L 0.000 description 1
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 1
- 229910000155 iron(II) phosphate Inorganic materials 0.000 description 1
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 1
- SDEKDNPYZOERBP-UHFFFAOYSA-H iron(ii) phosphate Chemical compound [Fe+2].[Fe+2].[Fe+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O SDEKDNPYZOERBP-UHFFFAOYSA-H 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 229910001092 metal group alloy Inorganic materials 0.000 description 1
- 229910052976 metal sulfide Inorganic materials 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 239000011733 molybdenum Substances 0.000 description 1
- 229910052901 montmorillonite Inorganic materials 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 210000003739 neck Anatomy 0.000 description 1
- 229910052759 nickel Inorganic materials 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 238000004806 packaging method and process Methods 0.000 description 1
- 229910052625 palygorskite Inorganic materials 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 238000005504 petroleum refining Methods 0.000 description 1
- 230000001699 photocatalysis Effects 0.000 description 1
- 238000007146 photocatalysis Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229920001021 polysulfide Polymers 0.000 description 1
- 239000005077 polysulfide Substances 0.000 description 1
- 150000008117 polysulfides Polymers 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000012716 precipitator Substances 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 239000010453 quartz Substances 0.000 description 1
- 230000036632 reaction speed Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000005987 sulfurization reaction Methods 0.000 description 1
- 239000004408 titanium dioxide Substances 0.000 description 1
- WFKWXMTUELFFGS-UHFFFAOYSA-N tungsten Chemical compound [W] WFKWXMTUELFFGS-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000010937 tungsten Substances 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- GPPXJZIENCGNKB-UHFFFAOYSA-N vanadium Chemical compound [V]#[V] GPPXJZIENCGNKB-UHFFFAOYSA-N 0.000 description 1
- 238000004073 vulcanization Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- 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
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- 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
- C02F1/70—Treatment of water, waste water, or sewage by reduction
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Catalysts (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
The invention discloses a kind of method that mercury compound in waste liquid is removed under normal temperature and pressure, method comprises the following steps:Step 1:Under normal temperature and pressure, the waste liquid containing mercury compound is contacted with reaction carriers, and be irradiated by 170nm~400nm length ultraviolets line or visible light;Step 2:By photocatalyst catalytic action, mercury compound is decomposed into into monomer hydrargyrum, the monomer hydrargyrum after decomposition carries out Adsorption by adsorbent.By adopting the present invention, under normal operating conditions, can continuously and efficiently easily from the various waste liquids containing hydrargyrum in the case where room temperature and normal pressure is close to while removing all kinds of form hydrargyrums, hydrargyrum concentration is less than below 5ppb in making treatment fluid.Organic pollution to containing in waste water also has high removal efficiency simultaneously, can reach draining newest standards, in addition for the clearance of hydrargyrum in spent sorbents containing hydrargyrum can reach 99%, the hydrargyrum response rate can reach 96%, the characteristics of fully demonstrating high removal efficiency, environment-friendly and green, with wide application value.
Description
Technical field
The present invention relates to Pollutant Treatment recovery technology field, removes hydrargyrum in waste liquid under more particularly to a kind of normal temperature and pressure
The method of compound.
Background technology
The necks such as production, petroleum refining and petrochemistry manufacture, the production of PVC chemical products in crude oil and natural gas
Domain, for the amount and concentration of hydrargyrum can use very big difference according to the difference in the place of production, typically from several ppb to several ppm.In addition
Not only there was only monomer hydrargyrum in the disposing waste liquid of gas field, the amount of mercury compound can much unnecessary list in some cases
In body hydrargyrum, and these compounds, major part is organic mercury compound.Other containing in the waste water of PVC chlorine industries field
Mercury pollution thing major part is chlorination hydrargyrum.And most of adsorbent can only remove hydrargyrum ion, to monomer hydrargyrum and organic water
Silver does not have removal effect, does not reach newest discharge standard 5ppb of national mercurous waste liquid.For mercury compound decomposition and inversion is
Monomer hydrargyrum, needs under hydrogen gasification process reaction condition more, and high temperature and high pressure, i.e. reaction temperature must be adopted to adopt
200~400 DEG C, 2~6MPa of pressure.And the adsorption reaction speed of adsorbent is low, absorbs the process of the spent sorbents of hydrargyrum
And the recovery of hydrargyrum is also the necessary process of complexity.For in the waste liquid or waste water of petrochemical field, containing heavy
Or Ultralight crude oil liquid, the partial organic substances in the middle of them be difficult degraded, do not reach water quality discharge standard.And need single
Processing equipment.
The content of the invention
In view of this, it is an object of the invention to provide a kind of method that mercury compound in waste liquid is removed under normal temperature and pressure.
Can it is continuous and efficiently easily from the various waste liquids containing hydrargyrum in the case where room temperature and normal pressure is close to while removing all kinds of form water
Silver, reduces processing cost, and also having simultaneously for the persistent organic pollutants contained in waste water decompose well removal effect.
The purpose of the present invention is achieved through the following technical solutions:
The method that mercury compound in waste liquid is removed under the normal temperature and pressure, comprises the following steps:
Step 1:Under normal temperature and pressure, the waste liquid containing mercury compound is contacted with reaction carriers, and by 170nm~
The ultraviolet or visible light of 400nm wavelength is irradiated, irradiation time 5-10 minute;
Step 2:By photocatalyst catalytic action, mercury compound is decomposed into into monomer hydrargyrum, the monomer hydrargyrum after decomposition
Adsorption is carried out by adsorbent.
Further, also including step 3:Hydrargyrum in adsorbent is reclaimed using Low Temperature Heat Treatment technology.
Further, the reaction carriers include one or more in aluminium oxide catalyst, natural crystal, zeolite and silica gel
Combination.
Further, the adsorbent includes the adsorbent of the sulfide for main body of Mo-Fe systems.
Further, in the step 1, it is irradiated using 185nm~365nm length ultraviolet lines;
Further, in step 2, catalytic action is carried out by titanium system photocatalyst.
The invention has the beneficial effects as follows:By adopting the present invention, under normal operating conditions, can continuously and it is efficient easily
In the case where room temperature and normal pressure is close to while removing all kinds of form hydrargyrums, hydrargyrum is dense in making treatment fluid from the various waste liquids containing hydrargyrum
Degree can reach the newest mark of draining less than below 5ppb while the organic pollution to containing in waste water also has high removal efficiency
Standard, in addition for the clearance of hydrargyrum in spent sorbents containing hydrargyrum can reach 99%, the hydrargyrum response rate can reach 96%.The present invention
The characteristics of having fully demonstrated high removal efficiency, environment-friendly and green, with wide application value.
Other advantages of the present invention, target and feature will be illustrated to a certain extent in the following description, and
And to a certain extent, based on being will be apparent to investigating hereafter to those skilled in the art, Huo Zheke
To be instructed from the practice of the present invention.The present invention target and other advantages can be realized by description below and
Obtain.
Description of the drawings
In order that the object, technical solutions and advantages of the present invention are clearer, below in conjunction with accompanying drawing the present invention is made into
The detailed description of one step, wherein:
Fig. 1 be two kinds of model aluminium oxide catalyst carrier schematic diagrams, NK124 and NKHO24;
Fig. 2 is the aluminium oxide (Al used in invention203) and knot of the zeolite mixture under high scanning electron microscope SEM
Composition;
Fig. 3 is the structure chart under high scanning electron microscope SEM of Mo-Fe systems solid sulfate in invention;
Fig. 4 is structure chart under high scanning electron microscope SEM of adsorbent in invention (a in figure:Aluminium oxide Al203And boiling
The mixed carrier of stone;b:Mo-Fe systems solid sulfate).
Specific embodiment
Hereinafter with reference to accompanying drawing, the preferred embodiments of the present invention are described in detail.It should be appreciated that preferred embodiment
Only for the explanation present invention, rather than in order to limit the scope of the invention.
The method that mercury compound in waste liquid is removed under the normal temperature and pressure of the present invention, comprises the following steps:
Step 1:Under normal temperature and pressure, the waste liquid containing mercury compound is contacted with reaction carriers, and by 170nm~
400nm length ultraviolets line or visible light are irradiated, and irradiation time is 5-10 minutes;
Step 2:By photocatalyst catalytic action, mercury compound is decomposed into into monomer hydrargyrum, the monomer hydrargyrum after decomposition
Adsorption is carried out by adsorbent.
Step 3:Hydrargyrum in adsorbent is reclaimed using Low Temperature Heat Treatment technology.
In step 1, there is provided an each form hydrargyrum organic compound for containing in said debris, with can make water
Silver-colored organic compound conversions are the monomer hydrargyrum conversion processing stage contacted by the material of monomer hydrargyrum.It is described here
The material that all kinds of hydrargyrum organic compound conversions are monomer hydrargyrum can be made to include aluminium oxide catalyst (Al2O3), as shown in figure 1, separately
Outward, zeolite catalyst carrier, ceramic catalyst carrier, colloidal silica catalyst carrier, absorbent charcoal carrier, fiber carrier, porous glass with
And natural crystal etc., for a kind of combination that can also be several in them, may be used to as reaction carriers.For natural
Ore can be any one of Kaolin, montmorillonite, attapulgite, bentonite, kieselguhr, volcanic ash, zeolite, flyash or
It is arbitrarily various to be mixed in proportion.In these decomposition catalyst carriers remove r- aluminium oxidies, beyond silicon and zeolite, as silicon-
The big porous mass of specific surface area such as this kind of complex carrier of aluminium oxide is also used.Aluminium oxide-zeolite this combination is in practice
Good reaction effect is embodied, the structure of high scanning electron microscope SEM of aluminium oxide-zeolite mixture is as shown in Figure 2.
For aluminium oxide catalyst carrier can be divided into the γ types of the α types and activated alumina of corundum etc. etc., possess here
Contact degrading activity is γ types.The specific surface area of the γ type activated alumina catalyst carriers for being used here be 50~
500m2/ g, preferably with 120~250m2/ g, 0.1~1.5cm of pore volume3/ g, preferably with 0.4~1.4cm3/g。
For zeolite or natural minerals, they are all crystalline aluminum silicate compounds so possessing various crystallization structure
Make.H types, cation exchange and layer structure etc. are used and are all possible, but sometimes need to consider to decompose hydrocarbon solution
Property activity control, so compared with other adopt layer structure more.The layered zeolite for using or the principal shape of natural minerals
It is specific surface area in 150~700m2/ g, preferably with 350~500m2/ g, 0.1~0.5cm of pore volume3/ g, preferably with
0.2~0.4cm3/g。
In step 2) in, the present invention adopt middle-ultraviolet lamp or visible photocatalysis conversion energy, wavelength of light be 170nm~
400nm, preferably with 185nm~365nm, in the present invention in uviol lamp or the tube outer wall of visible light, is entered with titanium photocatalyst
The transparent adherence overlay film of row.In whole course of reaction, photocatalyst rises and decomposes catalytic action.In the present embodiment, using visible ray titanium light
Wavelength can be adopted during catalyst to be irradiated for the visible ray of more than 300nm, carried out using the quartz burner of 185nm~365nm
During irradiation, the preferential ultraviolet photocatalyst using titanium dioxide so can just react at normal temperatures and pressures, reduce operation
Cost.
For the selection of adsorbent, in the present embodiment, adsorbent mainly adopts sulfide including Mo-Fe systems for main body
Adsorbent.Adsorbent is mainly used in the solid absorbent with insoluble and slightly solubility metal sulfide for main body and is contacted, and makes list
Body hydrargyrum occur vulcanizable cures reaction the sulfide removal stage, the adsorbent elements for using can be molybdenum, tungsten, vanadium, copper, ferrum,
At least select in the metals such as nickel, zinc, cadmium it is a kind of can also be this metal alloy or two kinds and two or more metals, then
Vulcanizing treatment is carried out to them, adsorbent product is obtained, such as Mo-Fe mixing is led to alumina carrier surface OH groups with species
The control of excess temperature and pressure forms molecular layer, Fe3+Ionic replacement Al3+Ion occupies alumina surface position, and Mo6+From
It is sub then combined with the oxonium ion in molecular layer, using newly-generated presoma by the oxidation state of its active component by temperature, pressure
Power controls to be converted into sulphided state, and Mo with vulcanizing agent is added6+Ion and Fe3+Ion is changed into active specy by vulcanizing treatment;
Can also use in the oxide of those metals, chloride, sulfide or polysulfide one or two and it is two or more mixed
Compound, carries out process and obtains adsorbent product.During adsorbent use, carrier can be adopted, it is also possible to do not use carrier,
Adsorbent can make the form such as powder, broken shape, cylindric, spherical, fibrous, cellular, according to practical service environment
Carry out selection use.
In the present embodiment, adsorbent is allowed to be dispersed on carrier, with the increase of dispersibility, the effect of adsorbent in the present invention
Become more preferable.Carrier is mixed into aluminium oxide-zeolite system particularly, and molten dispersion Mo-Fe systems solid of penetrating vulcanizes on this support
Thing is optimal for the method for adsorbent.Structure such as Fig. 3 of high scanning electron microscope SEM of Mo-Fe systems solid sulfate
It is shown.The structure of high scanning electron microscope SEM of the adsorbent on carrier with vulcanization reaction thing is as shown in Figure 4.
In practical operation, on carrier, the amount scope of Mo-Fe systems solid sulfate is 0.1~30wt%, especially with
It is ideal in the case of 10~20wt%.If it exceeds this amount, the effect of carrier will reduce dispersibility to be reduced.If amount
Very little, then the adsorption treatment effect of adsorbent will be deteriorated.
In the waste liquid that the present invention is adopted, the processing method containing each form hydrargyrum can substantially be divided into two stages:First
Stage is each form hydrargyrum organic compound for containing in said debris, with can make hydrargyrum organic compound conversions be monomer
The monomer hydrargyrum conversion processing stage contacted by the material of hydrargyrum;Second stage is vulcanized with insoluble and slightly solubility metal
Thing is contacted for the solid absorbent of main body, makes monomer hydrargyrum that the sulfide removal stage of vulcanizable cures reaction to occur.This
It is bright contain in the various waste liquids of efficient process whole form hydrargyrums while, the hardly degraded organic substance in waste water ultraviolet with
And be decomposed in the presence of photocatalyst, the material after decomposition has the carrier adsorptions such as oxidized aluminum or activated carbon to remove.By adopting
The method, the whole form hydrargyrums contained in various waste liquids after being separated with liquid effectively can be removed, and reach 5ppb standards with
It is interior.
Low Temperature Heat Treatment can be carried out by the hydrargyrum solidfied material after solid-liquid separation in the present invention, hydrargyrum resource is reclaimed.Process
In spent sorbents, residual water silver concentration is less than 0.1% afterwards, and the response rate of hydrargyrum can reach more than 96%.
In the present invention for the sulfuration hydrargyrum after solidification reclaims hydrargyrum therein using low-temperature heat, comprise the concrete steps that
It is 200~300 DEG C that heating-up temperature is controlled in rotary kiln roasting smelting device, heating treatment time 40~60 minutes, and device is intrinsic pressure
Power is 90~100kPa, and sufficient air will be provided when heating, and air velocity is 500~600ml/min.Material adsorbent
In composition there must be ferrous compound, silicon dioxide and calcium dioxide.For ferrous compound can be oxygen
Change ferrous, Iron sulfuret., ferrous chloride, ferrous sulfate, ferrous nitrate, in ferrous phosphate, and ferrous other compounds
One kind, and two or more mixture, it is preferred to use iron sulfide.For silicon dioxide, mainly there is conduct
The clay of adsorbent elements, zeolite, ceramics, porous glass, colloidal silica catalyst, a kind of thing in natural crystal and soil etc.
Matter, or two kinds and two or more compounding substances.The combination of zeolite and aluminium oxide is used preferably as carrier.For calcium
What compound was conventional is two kinds and two or more in calcium oxide, calcium hydroxide or Calcium Carbonate etc., and these compounds
Compounding substances.In this condition with a temperature of, HgS is broken down into hydrargyrum simple substance through a series of reaction of catalytic chemistries, and with gaseous state shape
Formula is escaped with tail gas, and other metallicses are then remained in waste residue.Jing rotations are distinguished at high temperature with the steam hydrargyrum that tail gas is escaped
Wind dust-precipitator and bagroom gather dust after removal mercurial soot, then cooler, tubulation cooler and surge tank are cold in scripture mound respectively
Congeal into liquid mercury, Jing water seals are slipped mercury tank and collected and enter collection mercury tank, then the packaging and storage by washing after mercury tank washes clean.It is buffered
Tail gas after tank condensation demercuration Jing after the further demercuration of packed absorber introduces full factory's vent gas treatment workshop by blower fan again and processes.It is de-
Waste residue after hydrargyrum is pumped to vacuum rewinding tank by vacuum pump Jing after the cooling of slag cooler, finally keeps in collection slag bath, according to demercuration
Composition in slag is processed afterwards.
Specific embodiment:
1 Xinjiang of the experimental example treating waste liquid of hydrargyrum containing monomer
Total hydrargyrum amount (mg/L) | |
Before processing | 1200 |
After adsorption treatment | 0.00021 |
2 Shaanxi of the embodiment treating waste liquid of mercury pollution containing ion
Total hydrargyrum amount (mg/L) | |
Before processing | 1.92 |
After adsorption treatment | 0.0003 |
Embodiment 3
For the recovery of the hydrargyrum for wherein adsorbing after processing for spent sorbents low-temperature heat.Spent sorbents for testing come
The adsorbent after absorption hydrargyrum from experiment, measures its content for 67g/kg
4 zunyi, guizhou mercury pollution containing ion waste liquid of embodiment
Total hydrargyrum amount (mg/L) | |
Before processing | 1.52 |
After adsorption treatment | 0.0045 |
Finally illustrate, above example is only unrestricted to illustrate technical scheme, although with reference to compared with
Good embodiment has been described in detail to the present invention, it will be understood by those within the art that, can be to the skill of the present invention
Art scheme is modified or equivalent, and without deviating from the objective and scope of the technical program, which all should be covered in the present invention
Right in the middle of.
Claims (5)
1. the method that mercury compound in waste liquid is removed under normal temperature and pressure, it is characterised in that:The method comprising the steps of:
Step 1:Under normal temperature and pressure, the waste liquid containing mercury compound is contacted with reaction carriers, and by 170nm~
The ultraviolet or visible light of 400nm wavelength is irradiated, irradiation time 5-10 minute;
Step 2:By the photocatalyst catalytic action of the molten photocatalyst for penetrating attachment on reaction carriers, mercury compound is decomposed into into list
Body hydrargyrum, the scattered adsorption agent on carrier, the adsorbed agent of the monomer hydrargyrum after decomposition absorb and are attached on carrier with adsorbent,
Monomer hydrargyrum in waste water is removed;
Also include step 3:Hydrargyrum in adsorbent is reclaimed using Low Temperature Heat Treatment technology.
2. the method that mercury compound in waste liquid is removed under normal temperature and pressure according to claim 1, it is characterised in that:It is described
Reaction carriers include zeolite catalyst carrier, ceramic catalyst carrier, colloidal silica catalyst carrier, absorbent charcoal carrier, fiber carrier, porous
The combination of one or more in property glass and natural crystal.
3. the method that mercury compound in waste liquid is removed under normal temperature and pressure according to claim 1 and 2, it is characterised in that:
The adsorbent includes the adsorbent of the sulfide for main body of Mo-Fe systems.
4. the method that mercury compound in waste liquid is removed under normal temperature and pressure according to claim 1, it is characterised in that:It is described
In step 1, it is irradiated using 185nm~365nm length ultraviolet lines.
5. the method that mercury compound in waste liquid is removed under normal temperature and pressure according to claim 1, it is characterised in that:In step
In rapid 2, catalytic action is carried out by titanium system photocatalyst.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201410539774.1A CN104310676B (en) | 2014-10-13 | 2014-10-13 | The method that mercury compound in waste liquid is removed under normal temperature and pressure |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201410539774.1A CN104310676B (en) | 2014-10-13 | 2014-10-13 | The method that mercury compound in waste liquid is removed under normal temperature and pressure |
Publications (2)
Publication Number | Publication Date |
---|---|
CN104310676A CN104310676A (en) | 2015-01-28 |
CN104310676B true CN104310676B (en) | 2017-03-29 |
Family
ID=52366029
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201410539774.1A Active CN104310676B (en) | 2014-10-13 | 2014-10-13 | The method that mercury compound in waste liquid is removed under normal temperature and pressure |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104310676B (en) |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6858147B2 (en) * | 2001-08-03 | 2005-02-22 | Dispersion Technology, Inc. | Method for the removal of heavy metals from aqueous solution by means of silica as an adsorbent in counter-flow selective dialysis |
CA2694949A1 (en) * | 2007-07-31 | 2009-02-05 | Perry Equipment Corporation | Systems and methods for removal of heavy metal contaminants from fluids |
TWI441783B (en) * | 2010-12-14 | 2014-06-21 | Super Dragon Technology Co Ltd | Method of removing heavy metals from wastewater |
CN103623771B (en) * | 2013-12-02 | 2016-02-10 | 上海交通大学 | A kind of waste liquid mercury-removing adsorbent and preparation method thereof and using method |
-
2014
- 2014-10-13 CN CN201410539774.1A patent/CN104310676B/en active Active
Also Published As
Publication number | Publication date |
---|---|
CN104310676A (en) | 2015-01-28 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US5080799A (en) | Hg removal from wastewater by regenerative adsorption | |
US8771519B2 (en) | Method of reducing a level of metallic species contamination of a fluid | |
Habeeb et al. | Isothermal modelling based experimental study of dissolved hydrogen sulfide adsorption from waste water using eggshell based activated carbon | |
JP4648977B2 (en) | Halide scavenger for high temperature applications | |
CN104445498B (en) | Device and method for treating mercury-containing wastewater through photocatalytic adsorption | |
KR101680610B1 (en) | Activated carbon adsorbent for acidic gas removal and manufacturing method the same | |
CN203916677U (en) | A kind of water and gas dual-purpose Graphene absorption and reclaim equiment | |
CN104310676B (en) | The method that mercury compound in waste liquid is removed under normal temperature and pressure | |
BRPI0719977A2 (en) | METHOD OF FORMATION OF AN AGENT AND ITS USE IN DISULFURIZATION | |
JP4465190B2 (en) | Method and apparatus for removing contaminants | |
Subeshan et al. | Mercury recycling technologies in its’ end-of-life management: a review | |
CN114887587A (en) | Porous adsorbent for heavy metal in wastewater prepared by using lithium ore waste residue as raw material and preparation method thereof | |
AU2017247530B2 (en) | Process for the removal of heavy metals from fluids | |
JP5106721B2 (en) | Method for producing photocatalyst and method for treating hydrogen sulfide using the photocatalyst | |
RU2807840C1 (en) | Method for preparing hydrogen chloride absorbent from gas mixtures | |
JP2796754B2 (en) | Mercury removal from liquid hydrocarbons | |
CN104645929A (en) | Method for preparing water-quenched slag-rectorite particle adsorption material | |
Muksin et al. | Enhancing Diatomaceous Earth Characteristics for Adsorption of Heavy Metals from Acid Mine Drainage: The Impact of Dual Activation Process | |
RU2829370C1 (en) | Methods for reducing presence of environmental pollutants in environment | |
JP2005169370A (en) | Dehydrosulfurization treatment agent of gas containing hydrogen sulfide, treatment method and treatment apparatus | |
CN211159284U (en) | Underground garage exhaust treatment device | |
KR100564359B1 (en) | Method for preparing adsorbents for removing acid gases and method for removing acid gases with the adsorbent prepared by the same | |
Chiani et al. | Adsorption of cationic dye from aqueous solution using SBA-15 nano particles synthesized by stem sweep ash as the source of silica | |
CN206131015U (en) | VOCs's processing apparatus among industrial waste gas | |
Yenial et al. | Investigation of arsenic removal parameters by a new nano-hybrid adsorbent produced from red mud and fly ash |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
TR01 | Transfer of patent right |
Effective date of registration: 20230522 Address after: Room 402, Supply and Marketing Cooperative Office Building, No. 38 Jiaotong Road, Baicheng County, Aksu Prefecture, Xinjiang Uygur Autonomous Region, 848008 Patentee after: Xinjiang Chengrun Environmental Protection Technology Co.,Ltd. Address before: No. 1, 10th Floor, Unit 1, Jinjiang International, No. 13 Jinjiang South Road, Bijiang District, Tongren Prefecture, Guizhou Province, 554300 Patentee before: GUIZHOU MEIRUITE ENVIRONMENTAL PROTECTION TECHNOLOGY Co.,Ltd. |
|
TR01 | Transfer of patent right |