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CN105087194A - Detergent for antimony-polluted building wastes - Google Patents

Detergent for antimony-polluted building wastes Download PDF

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Publication number
CN105087194A
CN105087194A CN201510539745.XA CN201510539745A CN105087194A CN 105087194 A CN105087194 A CN 105087194A CN 201510539745 A CN201510539745 A CN 201510539745A CN 105087194 A CN105087194 A CN 105087194A
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antimony
parts
washing composition
waste material
carboxylic acid
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王彩霞
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Yantai Is Along Grand Chemical Industry Science Co Ltd
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Yantai Is Along Grand Chemical Industry Science Co Ltd
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Abstract

The invention relates to a detergent, in particular relates to a detergent for antimony-polluted building wastes. The detergent is prepared by the following raw materials of 4-aminocyclohexanecarboxylic acid, dimethyl-silanedio diacetate, 3-hydroxyl propane-1-sodium sulfonate, dextro-7,7-trimethylbicyclooctanone[2,2,1]heptane-2-ketone-1-methanesulfonic acid, octadecyl isothiocyanate and the like. The detergent for the antimony-polluted building wastes has the advantages that the detergent can be directly used for cleaning the building wastes, the efficiency of removing the antimony element in the antimony-polluted building is obvious, the cleaning effect is higher, the removal effect is good, and a new direction is developed for the research of the antimony metal pollution.

Description

A kind of antimony pollution waste material of buildings washing composition
Technical field
The present invention relates to a kind of washing composition, be specifically related to a kind of antimony pollution waste material of buildings washing composition.
Background technology
Antimony pollution is that antimony and compound thereof are to the pollution of environment.Antimony and smelting or coal mining containing antimony metal, and other process application antimony or compound time, can produce containing the waste gas of antimony element or its compound, waste water and residue contamination environment.In mineral combustion or smelting process, antimony enters air with the form of steam or dust.In water, antimony comes from the dissolving containing antimony rock, containing the discharge of antimony trade effluent, and contains the rainfall etc. of antimony.Water infiltrates soil also makes it pollute.Antimony is enriched in water and reaches 3 × 10^(-6) time start to algae produce poison, reach 12 × 10^(-6) time toxicity is produced to fish.Average containing 5.8 milligrams, antimony in human body, major part is from tableware, ceramic glaze etc.The workman Yi Fasheng stibialism be engaged in antimony ore exploitation and smelted.The personnel of contact antimony bloom (Sb2O3) are about half cardiac disorder.Antimony is similar to arsenic, and antimonious toxicity is greater than quinquevalence antimony.Trivalent antimony (SbH3) toxicity is extremely strong, can cause haemolysis and liver, nephropathy, pulmonary edema after suction.At the smog Diazolidinyl Urea mucous membrane that factory produces, causing dermatitis, rhinitis, inflammation of upper respiratory tract, and can cause tumour, is carcinogenic suspicious item.Antimony is not easily put aside in vivo, and major part is discharged from urine.
The abundance of antimony in the earth's crust is 0.2ppm.Antimony-containing mineral, based on white antimony, is secondly senarmontite.China's antimony ore rich reserves, since 20th century, antimony output often occupies first place in the world.Except antimony-containing mineral, in shale, antimony content is 1.5ppm, and in oil, antimony content reaches as high as 1ppm.Someone analyze in 13 kinds of raw coal containing antimony amount, its concentration is from being less than 0.1ppm to 2ppm.According to statistics, the antimony annual production of the current whole world has reached about 60,000 tons.Wherein half is for the manufacture of alloy, and second half is applied to the aspects such as rubber, weaving, pottery, glass, semi-conductor and medicine with antimony compounds form.
Antimony element is to the pollution of air, and the exploitation of antimony ore and smelting, the burning of mineral fuel, makes antimony enter air with the form of steam or dust.But at present, antimony is not also the principal pollutant of air.The U.S. because smelting processing, fuel combustion etc. are to airborne release about 480 tons of antimony, significantly detected antimony in the U.S.'s 7 regional air in 1978.In antarctic air in 1977, the content of antimony is 0.0008 nanogram/rice ^3.In the air in Europe, the content of antimony is 0.6 ~ 32 nanogram/rice ^3, and mean value is 8 nanograms/rice ^3.In the air of North America, the content of antimony is 0.08 ~ 55 nanogram/rice ^3, and mean value is 12 nanograms/rice ^3.Someone observed in Britain somewhere from nineteen fifty-seven to 1974 year, found that the antimony content in air has seasonal variation, and winter, in air, antimony content increased because of burning heating.
Antimony element is to the pollution of water body, and containing the rock of antimony by runoff erosion, industrial wastewater discharge, air antimony dirt, with sleet landing or natural subsidence, all can cause antimony content in water to increase.In river, the content of antimony is 0.01 ~ 5 micrograms per litre, and mean value is 0.2 micrograms per litre.Antimony exists with antimonic form in fresh water.In seawater, antimony content is 0.18 ~ 5.6 micrograms per litre, and mean value is 0.24 micrograms per litre.Antimony in seawater exists with complex form, and its main dentate is hydroxyl, and theoretic form is Sb (OH) palace.
Antimony element is to the pollution of soil, and Antimony In The Soils content is very low, containing the landing of antimony dirt in antimony atmospheric disintegration of rocks and air, is the main source of Antimony In The Soils.Per kilogram soil antimony content is 0.2 ~ 10 milligram, and mean value is 1 milligram.Antimony is enriched in the top layer of soil, variation of valence can occur in soil, is plant absorption.Plant antimony content is 0.0001 ~ 0.2ppm.
The domestic and international improvement to antimony pollution soil for some time, and has many sections of public technology bibliographical informations.Conventional clean-out system comprises water, acid, salts solution, sequestrant, tensio-active agent etc.But the disposal applications at present for antimony pollution waste material of buildings rarely has report, for the protection to environment, be necessary to study a kind of washing composition high for the cleaning performance of antimony pollution waste material of buildings
Summary of the invention
The object of the invention is to solve the existing heavy-metal contaminated soil clean-out system deficiency not good to antimony element cleaning performance, the antimony pollution waste material of buildings washing composition of antimony element on a kind of effective removing waste material of buildings is provided.
A kind of antimony pollution waste material of buildings washing composition, special character is to be prepared from by the raw material of following weight: 4-cyclohexane-carboxylic acid 8-16 part, dimethylsilane glycol diacetate 24-30 part, 3-hydroxy propane-1-sodium sulfonate 33-39 part, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 40-48 part, octadecylisocyanate 6-12 part, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13-17 part, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 27-35 part, trimethylolpropane trimethacrylate 18-24 part, 3-hydroxy-2-pyrrolidinone 38-44 part.
Preferably, the antimony pollution waste material of buildings washing composition adopting the raw material of following weight to prepare has better washing effect, 4-cyclohexane-carboxylic acid 12 parts, dimethylsilane glycol diacetate 30 parts, 3-hydroxy propane-1-sodium sulfonate 33 parts, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44 parts, octadecylisocyanate 12 parts, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13 parts, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31 parts, trimethylolpropane trimethacrylate 24 parts, 3-hydroxy-2-pyrrolidinone 38 parts.
Further, in order to obtain the higher antimony pollution waste material of buildings washing composition of cleaning efficiency, described antimony pollution waste material of buildings washing composition also comprises the raw material of following weight: N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 12-16 part, methyl o-anisate 19-27 part, 5-hydroxyl-2-diamantane ketone 30-36 part.
Preferably, antimony pollution waste material of buildings washing composition, its parts by weight of raw materials proportioning is: N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14 parts, methyl o-anisate 27 parts, 5-hydroxyl-2-diamantane ketone 30 parts.
In addition, washing composition of the present invention preferably containing tensio-active agent and/or sequestrant, improves washing effect thus.
Again preferably, described tensio-active agent and/or sequestrant weight are 2-6 part.Its content very easily bubbles time many, and time few, washing effect reduces.
Preparation method of the present invention: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
This antimony pollution waste material of buildings washing composition, directly can clean use to waste material of buildings, and have high removal effect for the antimony element in antimony pollution waste material of buildings, cleaning efficiency is high, and removal effect is good, and the research of polluting for antimony metal opens new direction.
Embodiment
Below provide the specific embodiment of the present invention, be used for being further described the present invention.In the present invention, if no special instructions, each raw material all in working substance content for 100%.
In following examples, raw material introduction:
4-cyclohexane-carboxylic acid, CAS accession number is: 1776-53-0;
Dimethylsilane glycol diacetate, CAS accession number is: 2182-66-3;
3-hydroxy propane-1-sodium sulfonate, CAS accession number is: 3542-44-7;
Dextrorotation-7,7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, CAS accession number is: 3144-16-9;
Octadecylisocyanate, CAS accession number is: 2877-26-1;
N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, CAS accession number is: 967-80-6;
(2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, CAS accession number is: 3398-22-9;
Trimethylolpropane trimethacrylate, CAS accession number is: 3290-92-4;
3-hydroxy-2-pyrrolidinone, CAS accession number is: 15166-68-4;
N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt, CAS accession number is: 4261-67-0;
Methyl o-anisate, CAS accession number is: 606-45-1;
5-hydroxyl-2-diamantane ketone, CAS accession number is: 20098-14-0.
As the tensio-active agent preferably used in washing composition of the present invention, preferred anionic system tensio-active agent, can enumerate carboxylic acid type, sulfonic acid type, sulfuric acid ester type, phosphate type etc., preferably have C 11-20the tensio-active agent of the alkyl (preferred straight-chain) of left and right, the particularly preferably tensio-active agent of sulfonic acid type.
This occasion also can be the mixture of the different tensio-active agent of the carbonatoms of alkyl.In addition, the counterion as sulfonic acid is not particularly limited, but preferred ammonium ion etc.
Such as, preferably using is be mixed with C 11-16the negatively charged ion system tensio-active agent of the sulfonic acid type of the alkyl straight-chain of scope, ammonium ion are the tensio-active agents etc. of counterion.
Tensio-active agent only can use a kind, also can 2 kinds or more kinds of and use.
As the sequestrant that the present invention uses, the nitrogenous carboxylic-acid of preferred ethylenediamine tetraacetic acid (EDTA), diethylene triaminepentaacetic acid(DTPA), triethylenetetraaminehexaacetic acid, hydroxyethylethylene diamine tri-acetic acid, nitrilotriacetic acid(NTA) etc., the nitrogenous phosphonic acid based of EDTMP, propylene diamine four (methylene phosphonic acid) etc., quadrol two o-hydroxy guanidine-acetic acid and derivative thereof, N, N '-bis-(2-hydroxybenzyl) quadrol-N, N '-oxalic acid etc.
These sequestrants can use as the acid, also can the salt form of ammonium salt etc. use.
Sequestrant only can use a kind, also can 2 kinds or more kinds of and use.
Embodiment 1
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 8kg, dimethylsilane glycol diacetate 27kg, 3-hydroxy propane-1-sodium sulfonate 39kg, dextrorotation-7,7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 40kg, octadecylisocyanate 9kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 17kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 27kg, trimethylolpropane trimethacrylate 21kg, 3-hydroxy-2-pyrrolidinone 44kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
Embodiment 2
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7,7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition is with embodiment 1.
Embodiment 3
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 16kg, dimethylsilane glycol diacetate 24kg, 3-hydroxy propane-1-sodium sulfonate 36kg, dextrorotation-7,7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 48kg, octadecylisocyanate 6kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 15kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 35kg, trimethylolpropane trimethacrylate 18kg, 3-hydroxy-2-pyrrolidinone 41kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition is with embodiment 1.
Embodiment 4
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 12kg, methyl o-anisate 23kg, 5-hydroxyl-2-diamantane ketone 36kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt, methyl o-anisate, 5-hydroxyl-2-diamantane ketone in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
Embodiment 5
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14kg, methyl o-anisate 27kg, 5-hydroxyl-2-diamantane ketone 30kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition is with embodiment 4.
Embodiment 6
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 16kg, methyl o-anisate 19kg, 5-hydroxyl-2-diamantane ketone 33kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition is with embodiment 4.
Embodiment 7
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14kg, methyl o-anisate 27kg, 5-hydroxyl-2-diamantane ketone 30kg, tensio-active agent and sequestrant 2kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt, methyl o-anisate, 5-hydroxyl-2-diamantane ketone, tensio-active agent and sequestrant in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
Embodiment 8
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14kg, methyl o-anisate 27kg, 5-hydroxyl-2-diamantane ketone 30kg, tensio-active agent 4kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt, methyl o-anisate, 5-hydroxyl-2-diamantane ketone, tensio-active agent in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
Embodiment 9
Weigh the raw material of following weight: 4-cyclohexane-carboxylic acid 12kg, dimethylsilane glycol diacetate 30kg, 3-hydroxy propane-1-sodium sulfonate 33kg, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44kg, octadecylisocyanate 12kg, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13kg, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31kg, trimethylolpropane trimethacrylate 24kg, 3-hydroxy-2-pyrrolidinone 38kg, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14kg, methyl o-anisate 27kg, 5-hydroxyl-2-diamantane ketone 30kg, sequestrant 6kg.
The preparation method of the present embodiment antimony pollution waste material of buildings washing composition: by deionized water, 4-cyclohexane-carboxylic acid, dimethylsilane glycol diacetate, 3-hydroxy propane-1-sodium sulfonate, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid, octadecylisocyanate to add in reactor 1 stirring and dissolving at 60-85 DEG C, by N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid, trimethylolpropane trimethacrylate, 3-hydroxy-2-pyrrolidinone, N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt, methyl o-anisate, 5-hydroxyl-2-diamantane ketone, sequestrant in reactor 2 at 45-60 DEG C stirring and dissolving, mixture in reactor 2 is joined gradually in reactor 1, fully 15-25 minute is stirred in 45 DEG C of waters bath with thermostatic control, leave standstill 1.5-2 hour, namely required antimony pollution waste material of buildings washing composition is obtained.
The test of antimony residue removal rate is carried out with embodiment 1-9 gained finished product
With the conventional washing composition of heavy-metal contaminated soil as a control group, the EDTA-Na of 0.1mol/L 2the citric acid (top grade is pure) of (analytical pure), 0.5mol/L, the HC1 (top grade is pure) of 0.5mol/L.
(1) antimony pollution preparation of samples
Choose that earth's surface in certain chemical plant antimonic salt production plant factory building lays by the concrete blocks of antimony pollution, with this concrete blocks waste material of buildings for tested object, concrete blocks is crushed to 0.9mm, sieves, sealing saves backup.
In control group, first clean-out system adopts deionized water wash, removes water-soluble state antimony.Accurately take 100g sample in plastic bucket, carry out washing 40min with deionized water according to solid-to-liquid ratio 1:10, after solid-liquid separation, sample is air-dry, save backup.
Accurately take the sample after 5g once washing in 250ml Erlenmeyer flask, 50ml control group clean-out system is added respectively by solid-to-liquid ratio 1:10, take the non-washing sample of 5g in 250ml Erlenmeyer flask simultaneously, 50ml embodiment 1-4 washing composition is added respectively by solid-to-liquid ratio 1:10, induction stirring cleaning 40min, suction filtration, collect filtrate and solid sample by cleaning afterwards sample air-dry, save backup.
(2) sample antimony is residual calculates
(3) interpretation of result
Different embodiment washing composition and commercially available heavy-metal contaminated soil are commonly used the cleaning performance of washing composition to antimony pollution waste material of buildings and are seen the following form.
Contrasted from upper table, antimony pollution waste material of buildings washing composition cleaning performance of the present invention is obviously better than the conventional washing composition of commercially available heavy-metal contaminated soil, more than 97.5% is reached to chemical combination state trivalent antimony clearance, chemical combination state quinquevalence antimony clearance reaches more than 95.8%, wherein, compared to the washing composition that commercially available heavy-metal contaminated soil is conventional, washing composition of the present invention is particularly evident to the antimonious removal effect of chemical combination state, has high marketable value.

Claims (6)

1. an antimony pollution waste material of buildings washing composition, it is characterized in that being prepared from by the raw material of following weight: 4-cyclohexane-carboxylic acid 8-16 part, dimethylsilane glycol diacetate 24-30 part, 3-hydroxy propane-1-sodium sulfonate 33-39 part, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 40-48 part, octadecylisocyanate 6-12 part, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13-17 part, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 27-35 part, trimethylolpropane trimethacrylate 18-24 part, 3-hydroxy-2-pyrrolidinone 38-44 part.
2. antimony pollution waste material of buildings washing composition as claimed in claim 1, it is characterized in that parts by weight of raw materials proportioning is: 4-cyclohexane-carboxylic acid 12 parts, dimethylsilane glycol diacetate 30 parts, 3-hydroxy propane-1-sodium sulfonate 33 parts, dextrorotation-7, 7-trimethylammonium two ring [2.2.1] heptane-2-ketone-1-methylsulfonic acid 44 parts, octadecylisocyanate 12 parts, N-2-quinoxalinyl-4-aminobenzene sulfonamide sodium salt 13 parts, (2R, 4S)-4-hydroxyl pyrrolidine-2-carboxylic acid 31 parts, trimethylolpropane trimethacrylate 24 parts, 3-hydroxy-2-pyrrolidinone 38 parts.
3. antimony pollution waste material of buildings washing composition as claimed in claim 1 or 2, it is characterized in that described antimony pollution waste material of buildings washing composition also comprises the raw material of following weight: N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 12-16 part, methyl o-anisate 19-27 part, 5-hydroxyl-2-diamantane ketone 30-36 part.
4. antimony pollution waste material of buildings washing composition as claimed in claim 3, is characterized in that its parts by weight of raw materials proportioning is: N, N-dimethylamino-3-chloro-2-methyl propane hydrochloride salt 14 parts, methyl o-anisate 27 parts, 5-hydroxyl-2-diamantane ketone 30 parts.
5. antimony pollution waste material of buildings washing composition as claimed in claim 4, is characterized in that also containing tensio-active agent and/or sequestrant.
6. antimony pollution waste material of buildings washing composition as claimed in claim 5, is characterized in that described tensio-active agent and/or sequestrant weight are 2-6 part.
CN201510539745.XA 2015-08-28 2015-08-28 Detergent for antimony-polluted building wastes Pending CN105087194A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109528711A (en) * 2019-01-11 2019-03-29 苏州大学 The application of pyrrolidones

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102080024A (en) * 2009-11-30 2011-06-01 杭州正博新型建筑材料有限公司 High-performance mild cleanser for cleansing wall face brick

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102080024A (en) * 2009-11-30 2011-06-01 杭州正博新型建筑材料有限公司 High-performance mild cleanser for cleansing wall face brick

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109528711A (en) * 2019-01-11 2019-03-29 苏州大学 The application of pyrrolidones

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