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CN104560461A - Washing agent for mercury-polluted building wastes - Google Patents

Washing agent for mercury-polluted building wastes Download PDF

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Publication number
CN104560461A
CN104560461A CN201510086272.2A CN201510086272A CN104560461A CN 104560461 A CN104560461 A CN 104560461A CN 201510086272 A CN201510086272 A CN 201510086272A CN 104560461 A CN104560461 A CN 104560461A
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amino
mercury
parts
acid
methyl
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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 washing agent, in particular to a washing agent for mercury-polluted building wastes. The washing agent for the mercury-polluted building wastes is prepared from the following raw materials: (R)-N-t-butyloxycarboryl-2-phenylglycinol, ethyl 3-ethoxyacrylate, 3,7-dimethyl-6-octylene-3-alcohol, 4-acetamido-2-methyl-ethoxybenzoate, 1-phenylcyclopentane-1-carboxylic acid2-(2-diethoxylaminoethyl)ethyl ester and the like. The washing agent for the mercury-polluted building wastes can be used for directly washing building wastes, operation procedures are simple, and no corrosion influence on buildings exist; furthermore, the washing agent has more than 95% removing efficiency to mercury elements in the mercury-polluted building wastes, the washing efficiency is high, the removing effect is good, and the washing agent is suitable for being widely popularized and applied in the environmental protection field of the mercury-polluted building wastes.

Description

A kind of mercury 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 mercury pollution waste material of buildings washing composition.
Background technology
Mercury pollution, mercury is one of heavy metal element that environment toxic is the strongest, and it has persistence, long-distance migration and bioconcentration, can change into the methyl mercury of severe toxicity at occurring in nature, and the highly enriched and amplification by food chain.As maximum mercury production in the world, use and discharge state, mercury thermometer is used in a large number by China, and China has become the most serious area of global mercury pollution.
The discharge of mercury comes from natural source and artificial source two parts, natural source comprises: volcanicity, weathering, soil discharge and vegetation release etc., the mercury emissions referred to because mankind's activity causes is discharged in artificial source, comprises in the middle of the use of mercury, material containing the mercury emissions three major types that mercury impurities and refuse process cause.
There is more conforming understanding to the source of pollution formation of mercury emissions and the relative importance of each source of pollution, mainly come from combustion of fossil fuel to the mercury emissions in air, especially the burning of coal, and coal-burning power plant is the maximum source of global mercury emissions in air.The total mercury of the artificial emission source discharge in nineteen ninety-five Europe is 341.8 tons, and the mercury of wherein coal-burning power plant's discharge accounts for 26%, occupies the first place of known source of pollution.Other source of pollution also comprise various coal-burned industrial boilers, trash burning, mercury process chlor-alkali production, manufacture of cement, nonferrous production, Iron and Steel Production etc. beyond power plant.
The burning of coal and oil, the smelting of mercurous metalliferous mineral and be the waste gas that the industrial production of raw material is discharged with mercury are the main sources of mercury in air; Using mercurous agricultural chemicals and mercury-containing sludge fertilizer, is the main source of mercury in soils; The waste water of the discharge such as chlorine industry, plastics industry, battery industry and electronic industry is the main source of Mercury in Water Body.
China is that mercury is produced and uses big country, data presentation 2005,2006, and mercury in China output accounts for about 60% of global total mercury output, and mercury demand accounts for 30% ~ 40%, all occupies first place, the whole world.Meanwhile, China is also global mercury emissions big country.End 2010, the annual human activity in the whole world has 2000 tons to the mercury emission of air, and wherein China's annual discharge mercury is about 500-600 ton, account for global mercury emissions total amount 1/4 more than.
To the process of mercury pollution, focus mostly at soil and water source, and the domestic and international improvement to mercury contaminated soil is for some time, and existing 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 mercury pollution waste material of buildings rarely has report; and when existing heavy-metal contaminated soil clean-out system is applied to waste material of buildings; cleaning performance is not good; there is the residual of mercury element more; for the protection to environment, be necessary to study the good washing composition of a kind of cleaning performance for mercury pollution waste material of buildings.
Summary of the invention
The object of the invention is to solve that above-mentioned prior art exists without mercury pollution waste material of buildings special purpose detergent, the deficiency that heavy-metal contaminated soil clean-out system is not good to waste material of buildings cleaning performance, provides a kind of, mercury pollution waste material of buildings washing composition that cleaning performance good high to mercury cleaning efficiency.
A kind of mercury pollution waste material of buildings washing composition, special character is to be prepared from by the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 40-45 part, 3-ethoxy ethyl acrylate 28-35 part, 3, 7-dimethyl-6-octene-3-alcohol 15-18 part, 4-acetamido-2-ethoxy-benzoic acid methyl ester 30-35 part, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 28-32 part, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20-23 part, acexamic acid 18-24 part, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12-15 part.
Preferably, the mercury pollution waste material of buildings washing composition adopting the raw material of following weight to prepare has better washing effect, (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42 parts, 3-ethoxy ethyl acrylate 28 parts, 3, 7-dimethyl-6-octene-3-alcohol 18 parts, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35 parts, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32 parts, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20 parts, acexamic acid 22 parts, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12 parts.
Further, in order to obtain the higher mercury pollution waste material of buildings washing composition of cleaning efficiency, described mercury pollution waste material of buildings washing composition also comprises the raw material of following weight: 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 13-17 part, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6-10 part, 3-methyl-2-amyl group-2-cyclopentene-1-one 8-12 part.
Preferably, mercury pollution waste material of buildings washing composition, its parts by weight of raw materials proportioning is: 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 15 parts, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6 parts, 3-methyl-2-amyl group-2-cyclopentene-1-one 8 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: add pure water, add (R)-N-tertbutyloxycarbonyl-2-benzene glycinol, 3-ethoxy ethyl acrylate, 3 while stirring, 7-dimethyl-6-octene-3-alcohol, continues to be stirred to and is uniformly dispersed, and is then heated to 60-70 DEG C; Slowly add 4-acetamido-2-ethoxy-benzoic acid methyl ester, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, stir and make it to dissolve; After add N-[4-[(2-amino-5-formyl radical-4-oxo-1 successively, 6,7,8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt, acexamic acid, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, stir; Be cooled to 25-30 DEG C, stir and leave standstill 45-60 minute, namely obtain required mercury pollution waste material of buildings washing composition.
This mercury pollution waste material of buildings washing composition, directly can clean use to waste material of buildings, and operation sequence is simple, to buildings without any corrosive effect.And this washing composition has the removal effect of more than 95% for the mercury element in mercury pollution waste material of buildings, cleaning efficiency is high, and removal effect is good, is suitable for wide popularization and application in mercury pollution waste material of buildings field of Environment Protection.
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:
(R)-N-tertbutyloxycarbonyl-2-benzene glycinol, CAS accession number is: 102089-74-7;
3-ethoxy ethyl acrylate, CAS accession number is: 1001-26-9;
3,7-dimethyl-6-octene-3-alcohol, CAS accession number is: 2270-57-7;
4-acetamido-2-ethoxy-benzoic acid methyl ester, CAS accession number is: 59-06-3;
1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, CAS accession number is: 77-23-6;
N-[4-[(2-amino-5-formyl radical-4-oxo-1,6,7,8-tetrahydrochysene-6-pteridyl) methyl] is amino] benzoyl-Pidolidone calcium salt, CAS accession number is: 6035-45-6;
Acexamic acid, CAS accession number is: 57-08-9;
(2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, CAS accession number is: 2566-39-4;
5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium, CAS accession number is: 569-58-4;
Tri(Hydroxymethyl) Amino Methane Hydrochloride, CAS accession number is: 1185-53-1;
3-methyl-2-amyl group-2-cyclopentene-1-one, CAS accession number is: 1128-08-1.
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: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 40kg, 3-ethoxy ethyl acrylate 35kg, 3, 7-dimethyl-6-octene-3-alcohol 15kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 32kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 28kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 23kg, acexamic acid 18kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 13kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition: add pure water, add (R)-N-tertbutyloxycarbonyl-2-benzene glycinol, 3-ethoxy ethyl acrylate, 3 while stirring, 7-dimethyl-6-octene-3-alcohol, continue to be stirred to and be uniformly dispersed, be then heated to 60-70 DEG C; Slowly add 4-acetamido-2-ethoxy-benzoic acid methyl ester, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, stir and make it to dissolve; After add N-[4-[(2-amino-5-formyl radical-4-oxo-1 successively, 6,7,8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt, acexamic acid, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, stir; Be cooled to 25-30 DEG C, stir and leave standstill 45-60 minute, namely obtain required mercury pollution waste material of buildings washing composition.
Embodiment 2
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition is with embodiment 1.
Embodiment 3
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 45kg, 3-ethoxy ethyl acrylate 30kg, 3, 7-dimethyl-6-octene-3-alcohol 17kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 30kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 30kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 21kg, acexamic acid 24kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 15kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition is with embodiment 1.
Embodiment 4
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 17kg, Tri(Hydroxymethyl) Amino Methane Hydrochloride 8kg, 3-methyl-2-amyl group-2-cyclopentene-1-one 10kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition: add pure water, add (R)-N-tertbutyloxycarbonyl-2-benzene glycinol, 3-ethoxy ethyl acrylate, 3 while stirring, 7-dimethyl-6-octene-3-alcohol, continue to be stirred to and be uniformly dispersed, be then heated to 60-70 DEG C; Slowly add 4-acetamido-2-ethoxy-benzoic acid methyl ester, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, stir and make it to dissolve; After add N-[4-[(2-amino-5-formyl radical-4-oxo-1 successively, 6,7,8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt, acexamic acid, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium, Tri(Hydroxymethyl) Amino Methane Hydrochloride, 3-methyl-2-amyl group-2-cyclopentene-1-one, stir; Be cooled to 25-30 DEG C, stir and leave standstill 45-60 minute, namely obtain required mercury pollution waste material of buildings washing composition.
Embodiment 5
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 15kg, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6kg, 3-methyl-2-amyl group-2-cyclopentene-1-one 8kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition is with embodiment 4.
Embodiment 6
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 13kg, Tri(Hydroxymethyl) Amino Methane Hydrochloride 10kg, 3-methyl-2-amyl group-2-cyclopentene-1-one 12kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition is with embodiment 4.
Embodiment 7
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, tensio-active agent and sequestrant 6kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition: add pure water, add (R)-N-tertbutyloxycarbonyl-2-benzene glycinol, 3-ethoxy ethyl acrylate, 3 while stirring, 7-dimethyl-6-octene-3-alcohol, continue to be stirred to and be uniformly dispersed, be then heated to 60-70 DEG C; Slowly add 4-acetamido-2-ethoxy-benzoic acid methyl ester, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, stir and make it to dissolve; After add N-[4-[(2-amino-5-formyl radical-4-oxo-1 successively, 6,7,8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt, acexamic acid, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, tensio-active agent and sequestrant, stir; Be cooled to 25-30 DEG C, stir and leave standstill 45-60 minute, namely obtain required mercury pollution waste material of buildings washing composition.
Embodiment 8
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 15kg, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6kg, 3-methyl-2-amyl group-2-cyclopentene-1-one 8kg, sequestrant 4kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition: add pure water, add (R)-N-tertbutyloxycarbonyl-2-benzene glycinol, 3-ethoxy ethyl acrylate, 3 while stirring, 7-dimethyl-6-octene-3-alcohol, continue to be stirred to and be uniformly dispersed, be then heated to 60-70 DEG C, slowly add 4-acetamido-2-ethoxy-benzoic acid methyl ester, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester, stir and make it to dissolve, after add N-[4-[(2-amino-5-formyl radical-4-oxo-1 successively, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt, acexamic acid, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium, Tri(Hydroxymethyl) Amino Methane Hydrochloride, 3-methyl-2-amyl group-2-cyclopentene-1-one, sequestrant, stir, be cooled to 25-30 DEG C, stir and leave standstill 45-60 minute, namely obtain required mercury pollution waste material of buildings washing composition.
Embodiment 9
Weigh the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42kg, 3-ethoxy ethyl acrylate 28kg, 3, 7-dimethyl-6-octene-3-alcohol 18kg, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35kg, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32kg, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20kg, acexamic acid 22kg, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12kg, 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2, 5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 17kg, Tri(Hydroxymethyl) Amino Methane Hydrochloride 8kg, 3-methyl-2-amyl group-2-cyclopentene-1-one 10kg, tensio-active agent 2kg.
The preparation method of the present embodiment mercury pollution waste material of buildings washing composition is with embodiment 8.
The test of mercury 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 0.1 mol/L 2the citric acid (top grade is pure) of (analytical pure), 0.5 mol/L, the HC1 (top grade is pure) of 0.5 mol/L.
(1) mercury pollution preparation of samples
Choose the mercury-contaminated concrete blocks that in certain chemical plant mercury salt production plant factory building, earth's surface is laid, 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 mercury.Accurately take 100 g samples in plastic bucket, carry out washing 40 min 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 5 g once washings in 250 ml Erlenmeyer flasks, 50 ml control group clean-out systems are added respectively by solid-to-liquid ratio 1:10, take the non-washing sample of 5 g in 250 ml Erlenmeyer flasks simultaneously, 50 ml embodiment 1-4 washing composition are added respectively by solid-to-liquid ratio 1:10, induction stirring cleans 40 min, suction filtration, collect filtrate and solid sample by cleaning afterwards sample air-dry, save backup.
(2) sample mercury is residual calculates
By alkali degestion by the water-soluble state mercury stripping in solid sample, atomic absorption spectroscopy determination dissolution fluid ρ; With microwave-assisted Acid digestion method by the exchange state mercury in solid sample, the stripping of residual form mercury, atomic absorption spectroscopy determination dissolution fluid ρ.
Hg clearance %=
(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 mercury pollution waste material of buildings and are seen the following form.
Contrasted from upper table, mercury 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 95.2% is reached to water-soluble state Hg clearance, exchange state Hg clearance reaches more than 95.1%, residual form Hg clearance reaches more than 96.1%, wherein, compared to the washing composition that commercially available heavy-metal contaminated soil is conventional, the removal effect of washing composition of the present invention to exchange state Hg is particularly evident, has high marketable value.

Claims (6)

1. a mercury pollution waste material of buildings washing composition, it is characterized in that being prepared from by the raw material of following weight: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 40-45 part, 3-ethoxy ethyl acrylate 28-35 part, 3, 7-dimethyl-6-octene-3-alcohol 15-18 part, 4-acetamido-2-ethoxy-benzoic acid methyl ester 30-35 part, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 28-32 part, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20-23 part, acexamic acid 18-24 part, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12-15 part.
2. mercury 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: (R)-N-tertbutyloxycarbonyl-2-benzene glycinol 42 parts, 3-ethoxy ethyl acrylate 28 parts, 3, 7-dimethyl-6-octene-3-alcohol 18 parts, 4-acetamido-2-ethoxy-benzoic acid methyl ester 35 parts, 1-benzyl ring pentane-1-carboxylic acid 2-(2-diethylin oxyethyl group) ethyl ester 32 parts, N-[4-[(2-amino-5-formyl radical-4-oxo-1, 6, 7, 8-tetrahydrochysene-6-pteridyl) methyl] amino] benzoyl-Pidolidone calcium salt 20 parts, acexamic acid 22 parts, (2S)-2-[[(4S)-4-amino-5-hydroxyl-5-oxo valeryl] is amino]-4-methylvaleric acid 12 parts.
3. mercury pollution waste material of buildings washing composition as claimed in claim 1 or 2, characterized by further comprising the raw material of following weight: 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 13-17 part, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6-10 part, 3-methyl-2-amyl group-2-cyclopentene-1-one 8-12 part.
4. mercury pollution waste material of buildings washing composition as claimed in claim 3, it is characterized in that its parts by weight of raw materials proportioning is: 5-[(3-carboxyl-4-hydroxy phenyl) (3-carboxyl-4-oxo-2,5-cyclohexadiene-1-subunit) methyl]-2 hydroxybenzoic acid three ammonium 15 parts, Tri(Hydroxymethyl) Amino Methane Hydrochloride 6 parts, 3-methyl-2-amyl group-2-cyclopentene-1-one 8 parts.
5. mercury 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. as claim 5 mercury pollution waste material of buildings washing composition, it is characterized in that described tensio-active agent and/or sequestrant weight are 2-6 part.
CN201510086272.2A 2015-02-24 2015-02-24 Washing agent for mercury-polluted building wastes Pending CN104560461A (en)

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Publication number Priority date Publication date Assignee Title
CN105532688A (en) * 2016-01-14 2016-05-04 烟台顺隆化工科技有限公司 Herbicide for apple orchard

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JPH03228327A (en) * 1990-02-02 1991-10-09 Nec Corp Cleaning method of semiconductor wafer
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CN105532688A (en) * 2016-01-14 2016-05-04 烟台顺隆化工科技有限公司 Herbicide for apple orchard

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