CN107500880A - A kind of sludge and mine tailing mixed method - Google Patents

A kind of sludge and mine tailing mixed method Download PDF

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Publication number
CN107500880A
CN107500880A CN201710805223.9A CN201710805223A CN107500880A CN 107500880 A CN107500880 A CN 107500880A CN 201710805223 A CN201710805223 A CN 201710805223A CN 107500880 A CN107500880 A CN 107500880A
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soil
content
mine tailing
sludge
planting
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沈向军
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DALIAN GREEN PINES ECOLOGICAL WISDOM TECHNOLOGY Co Ltd
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DALIAN GREEN PINES ECOLOGICAL WISDOM TECHNOLOGY Co Ltd
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Publication of CN107500880A publication Critical patent/CN107500880A/en
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    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05DINORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D9/00Other inorganic fertilisers
    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G24/00Growth substrates; Culture media; Apparatus or methods therefor
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05GMIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
    • C05G3/00Mixtures of one or more fertilisers with additives not having a specially fertilising activity
    • C05G3/80Soil conditioners

Abstract

A kind of sludge and mine tailing mixed method, the terminal sludge that city is handled through sewage treatment plant is mixed with mine tailing, the content of beary metal in sludge, mine tailing, conventional planting soil is detected respectively, take sludge M ㎏, mine tailing N ㎏, planting soil L ㎏, total heavy metal content Y, total heavy metal content Y divided by gross mass is calculated(M+N+L)Obtain content of beary metal in mixed planting technique soil, according to content of beary metal in obtained planting technique soil, adjust the quality of mine tailing and conventional planting soil so that content of beary metal in the planting technique soil gone out, meet standard of soil environment quality (mg/kg)(GB15618‑1995)Three-level PH>6.5.Content of beary metal is low in the mixed planting soil of the present invention, it is possible to increase the fertility of planting technique soil, solid waste is utilized effectively, turns waste into wealth.

Description

A kind of sludge and mine tailing mixed method
Technical field
The present invention relates to planting technique soil field, and in particular to a kind of to be mixed into the sludge containing heavy metal with mine tailing Meet the planting technique soil of standard of soil environment quality.
Background technology
The terminal sludge that city is handled through sewage treatment plant contains abundant organic matter, nitrogen, phosphorus, potassium, can improve soil Fertility, granularity, pH value meet the requirement of soil, but because its content of beary metal is exceeded, it is impossible to it is used alone as planting soil.Mine tailing is Refer to the tailings that metal or nonmetallic ore leave after ore dressing, degree particle, pH value meet the requirement of soil, but some mine tailing heavy metals Content overproof, long-term accumulation, easily causes the geological disasters such as landslide, while forms dust pollution, and some tailing water liquid heavy metals contain Measure exceeded, easily underground water and surface water are polluted.But sludge and mine tailing are rationally applied, on the one hand can be eliminated Hidden danger is stated, on the other hand can save land resource.
The content of the invention
To solve the above problems, the present invention provides a kind of sludge and mine tailing mixed method, goal of the invention of the invention is logical Cross following technical scheme realization:
Sludge, mine tailing and conventional planting soil are stirred to obtain planting technique soil, its blend step by forced stirrer It is as follows:
S1:The content of beary metal in sludge, mine tailing, conventional planting soil is detected respectively, testing result be respectively X1, X2、X3;
S2:Sludge M ㎏, mine tailing N ㎏, planting soil L ㎏ are taken, preferably M, N, L mass ratio is 1:0.5-3:2.5-5.5;
S3:Total heavy metal content Y is obtained by X1*M+X2*N+X3*L;
S4:Total heavy metal content Y divided by gross mass(M+N+L)Obtain content of beary metal in mixed planting technique soil;
S5:According to content of beary metal in obtained planting technique soil, the quality of adjustment mine tailing and conventional planting soil so that go out Content of beary metal in planting technique soil, meet standard of soil environment quality (mg/kg)(GB15618-1995)Three-level PH>6.5.
Stalk, rice husk, string, chicken manure, turfy soil, adhesive, water conservation are also added into obtained planting technique soil Agent, it is adjustment soil and increase nutrient that it, which is acted on, and the indexs such as planting technique soil's water content, fertility, viscosity, pH value are changed It is kind, be advantageous to the growth of various plants.
The conventional planting soil can also be substituted by granite powder or mine tailing.The mine tailing is golden tail or Kimberley tail Or granite powder or copper tail or iron tail or quartz sand tail or oil shale tail.
The present invention draws after mixing heavy metal in planting technique soil according to the cubage of heavy metal in sludge and mine tailing Content, the content of beary metal in planting technique soil can be effectively controlled in this way, can be according to different purposes standards With require, produce meet corresponding demand planting technique soil.The invention has the advantages that by the sludge containing heavy metal with Mine tailing mixes utilization in proportion, and formation meets standard of soil environment quality(GB15618-1995)Three-level PH>6.5 greening kind Soil is planted, content of beary metal effectively reduces in planting technique soil, improves the fertility of planting technique soil, solid waste is obtained effectively Utilize, turn waste into wealth, the planting technique soil finally given is applied to urban afforestation, mine is repaired, afforestation is planted trees etc..
Embodiment
A kind of sludge and mine tailing mixed method, sludge is mixed in proportion with mine tailing, obtains the planting technique for meeting table 1 Soil.
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 1.0 1.5 40 400 500 300 500 200
Table 1:Standard of soil environment quality (mg/kg)(GB15618-1995)Three-level PH>6.5
Embodiment 1
Sludge is mixed with golden mine tailing, conventional planting soil, blend step is as follows:
S1. sludge is detected, obtained Heavy Metal Level In Sludge is as shown in table 2:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 2.7 4.9 20 280 42 173 1280 120
Table 2:Sludge heavy-metal content(mg/kg)
Golden tail is detected, content of beary metal is as shown in table 3 in obtained golden tail:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.9 0.2 442 16.5 60.7 38.1 262 20.6
Table 3:Golden mine tailing content of beary metal(mg/kg)
S 2. takes sludge 1kg, the golden kg of mine tailing 0.5, commonly uses planting soil(Can be considered content of beary metal is 0)4.5 kg.
S 3. calculates total heavy metal content, by taking cadmium as an example:2.7*1+0.9*0.5+0*4.5=3.15mg, finally gives gross weight Tenor is as shown in table 4:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Total heavy metal content 3.15 5.0 241 288.25 72.35 192.05 1411 130.3
Table 4:Total heavy metal content(mg)
The total heavy metal contents of S 4. divided by quality, by taking cadmium as an example:3.15/(1+0.5+4.5)=0.525mg/kg, after obtaining mixing Content of beary metal is as shown in table 5 in planting technique soil:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.525 0.83 40.17 48.04 12.06 32.00 235.17 21.72
Table 5:Content of beary metal in planting technique soil(mg/kg)
After S 5. contrasts table 5 and table 1, heavy metal arsenic content overproof is obtained, to the quality of the conventional planting soil in step S2 It is adjusted, is 5kg by the Mass adjust- ment of conventional planting soil, and repeat step S3, S4, obtained after calculating in planting technique soil Content of beary metal is as shown in table 6:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.48 0.77 37.06 44.35 11.13 29.55 217.08 20.05
Table 6:Content of beary metal in planting technique soil(mg/kg)
Content of beary metal meets standard of soil environment quality (mg/kg) in the planting technique soil being calculated after adjustment (GB15618-1995)Three-level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 2
Sludge is mixed with golden mine tailing, granite powder, blend step is as follows:
S 1. detects to sludge, and obtained Heavy Metal Level In Sludge is as shown in table 2:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 2.7 4.9 20 280 42 173 1280 120
Table 2:Sludge heavy-metal content(mg/kg)
Golden tail is detected, content of beary metal is as shown in table 3 in obtained golden tail:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.9 0.2 442 16.5 60.7 38.1 262 20.6
Table 3:Golden mine tailing content of beary metal(mg/kg)
Granite is detected, content of beary metal is as shown in table 7 in obtained granite powder:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.1 0.0 1.0 40.7 18.6 2.3 54.1 4.9
Table 7:Granite powder content of beary metal(mg/kg)
S 2. takes sludge 1kg, the golden kg of mine tailing 0.5, the kg of granite powder 4.5.
S 3. calculates total heavy metal content, by taking cadmium as an example:2.7*1+0.9*0.5+0.1*4.5=3.6mg, finally give total Content of beary metal is as shown in table 8:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Total heavy metal content 3.6 5.00 245.5 371.95 156.05 202.4 1654.45 152.35
Table 8:Total heavy metal content(mg)
The total heavy metal contents of S 4. divided by quality, by taking cadmium as an example:3.6/(1+0.5+4.5)=0.6mg/kg, afforested after being mixed Content of beary metal is as shown in table 9 in planting soil:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.6 0.83 40.92 62.00 26.01 33.73 275.74 25.39
Table 9:Content of beary metal in planting technique soil(mg/kg)
After S 5. contrasts table 9 and table 1, heavy metal arsenic content overproof is obtained, the quality of granite powder in step S2 is carried out Adjustment, it is 5kg by the Mass adjust- ment of granite powder, and repeat step S3, S4, heavy metal in planting technique soil is obtained after calculating Content is as shown in table 10:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.55 0.77 37.77 57.22 24.01 31.14 254.53 23.44
Table 10:Content of beary metal in planting technique soil(mg/kg)
Content of beary metal meets standard of soil environment quality (mg/kg) in the planting technique soil being calculated after adjustment (GB15618-1995)Three-level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 3
Sludge 1kg, golden mine tailing 0.5kg, iron tailings 5kg are mixed by forced stirrer, for example preceding embodiment of blend step, passed through After calculating, content of beary metal is as shown in table 11 in iron tailings:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.1 0.0 4.3 42.2 7.2 19.7 39.4 24.2
Table 11:Iron tailings content of beary metal(mg/kg)
By step S1-S4 calculating, it is as shown in table 12 to obtain content of beary metal in planting technique soil:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.5 0.8 40.4 76.8 16.7 44.7 247.4 38.7
Table 12:Content of beary metal in planting technique soil(mg/kg)
After S 5. contrasts table 12 and table 1, heavy metal arsenic content overproof is obtained, the quality of iron tailings in step S2 is adjusted It is whole, it is 5.5kg by the Mass adjust- ment of iron tailings, and repeat step S3, S4, content of beary metal in planting technique soil is obtained after calculating As shown in table 13:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.51 0.71 37.51 71.33 15.51 41.51 229.71 35.9
Table 13:Content of beary metal in planting technique soil(mg/kg)
Content of beary metal meets standard of soil environment quality (mg/kg) in the planting technique soil being calculated after adjustment (GB15618-1995)Three-level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 4
By sludge 1kg, Kimberley mine tailing 2kg, planting soil is commonly used(Can be considered content of beary metal is 0)3kg passes through action of forced stirring Machine mixes, for example preceding embodiment of blend step, and the content of beary metal that Kimberley mine tailing is obtained by calculating measurement is as shown in table 14:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.22 0.009 4.88 36.9 24.9 662 147 476
Table 14:Kimberley mine tailing content of beary metal(mg/kg)
Content of beary metal is as shown in Table 15 in the planting technique soil obtained after mixing:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.5 0.8 5.0 59.0 15.3 249.5 262.3 178.7
Table 15:Content of beary metal in planting technique soil(mg/kg)
After table 15 and table 1 are contrasted, content of beary metal meets standard of soil environment quality (mg/kg) in obtained planting technique soil (GB15618-1995)Three-level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 5
By sludge 1kg, granite powder 5kg is stirred to obtain planting technique soil by forced stirrer, and its blend step is such as Preceding embodiment, it is as shown in table 16 that content of beary metal in planting technique soil is calculated:
Table 16:Content of beary metal in planting technique soil(mg/kg)
The planting technique soil obtained after mixing meets standard of soil environment quality (mg/kg)(GB15618-1995)Three-level PH> 6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 6
Sludge 1kg, copper tailing 3kg, commonly use planting soil(Can be considered content of beary metal is 0)2.5kg is stirred by forced stirrer Mix mixing, for example preceding embodiment of mixed process, the content of beary metal that measurement obtains copper tailing is as shown in table 17:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 1.19 0.029 39.1 527 20.6 2.66 172 10.8
Table 17:Copper tailing content of beary metal(mg/kg)
Content of beary metal is as shown in table 18 in the planting technique soil being calculated:
Table 18:Content of beary metal in planting technique soil(mg/kg)
Content of beary metal meets standard of soil environment quality (mg/kg) in mixed planting technique soil(GB15618-1995)Three Level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
Embodiment 7
Sludge 1kg, iron tail 5kg are stirred by forced stirrer, for example preceding embodiment of blend step, measure obtained iron tail The content of beary metal of ore deposit is as shown in table 19:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content 0.087 0.008 4.32 42.2 7.24 19.7 39.4 24.2
Table 19:Copper tailing content of beary metal(mg/kg)
Content of beary metal is as shown in table 20 in the planting technique soil being calculated after mixing:
Heavy metal title Cadmium Mercury Arsenic Copper Lead Chromium Zinc Nickel
Content of beary metal in planting technique soil 0.5 0.8 6.9 81.8 13.0 45.3 246.2 40.2
Table 20:Content of beary metal in planting technique soil(mg/kg)
Content of beary metal meets standard of soil environment quality (mg/kg) in mixed planting technique soil(GB15618-1995)Three Level PH>6.5, planted trees available for urban afforestation, mine reparation, afforestation etc..
The ratio of sludge and mine tailing is not limited to the ratio in above-described embodiment in the present invention, it is contemplated that green after mixing Change the nutritional ingredient and the factor such as content of beary metal of planting soil, preferably take 1 part of sludge, other materials proportioning summation take 4-5 parts with On.
And mixed method of the present invention is safety and environmental protection, and planting technique soil is in the aqueous solution or Urban Acid Rain shape Under state, meet《Urban wastewater treatment firm pollutant emission standard》GB18918-2016 or《Standards for drinking water quality》 GB5749-2006,《Urban wastewater treatment firm pollutant emission standard》GB18918-2016 is as shown in table 21:
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 50 100 10 100 1 1000 500 50
Table 21:Solution heavy metal standard index(ug/L)GB18918-2016
《Standards for drinking water quality》GB5749-2006 is as shown in table 22:
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 50 10 5 10 1 1000 1000 20
Table 22:Solution heavy metal standard index(ug/L)GB5749-2006
The mixed planting technique soil aqueous solution is detected, as shown in table 23,24,25,26,27,28,29,30,31,32:
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 0.3 11.1 0.4 8.7 0.0 78.2 35.6 58.4
After 3 immersions 1.6 3.9 0.1 3.4 0.0 60.7 40.7 10.8
Table 23:Sludge water solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 0.3 16.5 0.4 6.8 0.0 58.3 27.1 53.4
After 3 immersions 15.1 3.3 0.1 2.0 0.1 24.5 24.2 10.3
Table 24:Sludge weak acid solution index(ug/L)PH=3.8
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 25.9 3.6 0.3 5.3 0.1 1.9 3.5 5.3
Table 25:Golden tail water solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 26.5 5.1 0.4 2.7 0.1 0.7 2.9 7.4
Table 26:Golden tail weak acid solution index(ug/L)PH=3.8
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 38.7 4.6 0.3 15.2 0.1 15.8 3.4 52.3
After 3 immersions 13.5 2.1 0.0 1.1 0.1 5.6 3.8 4.0
Table 27:Kimberley aqueous solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 46.5 2.8 0.4 20.3 0.1 17.9 3.9 72.8
After 3 immersions 18.2 2.3 0.2 0.6 0.1 18.3 4.3 13.4
Table 28:Kimberley weak acid solution index(ug/L)PH=3.8
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 29.2 5.4 0.3 2.8 0.0 2.8 29.3 2.5
Table 29:Granite powder aqueous solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 38.7 4.9 0.4 3.0 0.0 61.0 185.5 13.1
Table 30:Granite powder weak acid solution index(ug/L)PH=3.8
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 33.1 5.3 0.3 2.3 0.1 0.3 1.7 2.0
Table 31:Iron tail water solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 30.9 6.0 0.4 3.6 0.1 1.1 3.2 4.4
Table 32:Iron tailings weak acid solution index(ug/L)PH=3.8
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 35.4 5.6 0.3 5.6 0.1 4.0 15.4 3.1
Table 33:Copper tailing aqueous solution index(ug/L)PH=6.7
Heavy metal title Chromium Arsenic Cadmium Lead Mercury Zinc Copper Nickel
Content 33.7 5.2 0.4 9.4 0.1 10.1 32.0 5.3
Table 34:Copper tailing weak acid solution index(ug/L)PH=3.8
Table 23,25,27,29,31,33 is that sludge, golden mine tailing, Kimberley, granite, iron tailings, the copper tailing aqueous solution refer to respectively Mark, table 24,26,28,30,32,34 are that sludge, golden mine tailing, Kimberley, granite, iron tailings, copper tailing weak acid solution refer to respectively Mark, it meets urban wastewater treatment firm pollutant emission standard》GB18918-2016 standards, the sludge solution ph after immersion =6.0, golden mine tailing solution ph=8.0 after immersion, Kimberley solution ph=7.7 after immersion, the granite powder after immersion Solution ph=7.7, iron tail water solution PH=7.9 after immersion, copper tailing solution ph=7.7 after immersion.
The sludge aqueous solution and weak acid solution, the Kimberley aqueous solution and weak acid solution are not met《Standards for drinking water quality》 GB5749-2006 standards, other solution meet《Standards for drinking water quality》GB5749-2006 standards.It is water-soluble to sludge Liquid and weak acid solution, the Kimberley aqueous solution and weak acid solution carry out 3 immersions, and the aqueous solution and weak acid solution after immersion meet 《Standards for drinking water quality》GB5749-2006 standards.Exceeded solution can be received using heavy metal-polluted dye liquor recovery technology Collection.
Shown by many experiments and experimental data, the method applied in the present invention safety and environmental protection, can will discard, not conform to The sludge and mine tailing of lattice are turned waste into wealth, and are mixed in proportion, are rationally utilized, planted trees available for urban afforestation, mine reparation, afforestation etc. Aspect, improve environment, economize on resources.Organic matter, full nitrogen, full phosphorus in planting technique soil meet technical indicator, in dispensing, Stalk, rice husk, string, chicken manure, turfy soil, adhesive, water-loss reducer etc. are mixed in planting technique soil, to planting technique soil The indexs such as moisture content, fertility, viscosity, pH value are improved, and are advantageous to the growth of various plants.

Claims (4)

1. a kind of sludge and mine tailing mixed method, it is characterised in that:Sludge and mine tailing, conventional planting soil are passed through into action of forced stirring Machine, which is mixed to get, meets standard of soil environment quality(GB15618-1995)Three-level PH>6.5 planting technique soil, its blend step It is as follows:
S1:Detect that the content of beary metal in sludge, mine tailing, conventional planting soil is X1, X2, X3 respectively;
S2:Sludge M ㎏, mine tailing N ㎏, planting soil L ㎏ are taken, preferably M, N, L mass ratio is 1:0.5-3:2.5-5.5;
S3:Total heavy metal content Y is obtained by X1*M+X2*N+X3*L;
S4:Total heavy metal content Y divided by gross mass(M+N+L)Obtain content of beary metal in mixed planting technique soil;
S5:According to content of beary metal in obtained planting technique soil, the quality of adjustment mine tailing and conventional planting soil so that go out Content of beary metal in planting technique soil, meet standard of soil environment quality (mg/kg)(GB15618-1995)Three-level PH>6.5.
2. a kind of sludge as claimed in claim 1 and mine tailing mixed method, it is characterised in that:There are straw in planting technique soil Stalk, rice husk, string, chicken manure, turfy soil, adhesive, water-loss reducer.
3. a kind of sludge as claimed in claim 1 and mine tailing mixed method, it is characterised in that:The conventional planting soil can be with Substituted by granite powder or mine tailing.
4. a kind of sludge and mine tailing mixed method as described in claim 1 or 3, it is characterised in that:The mine tailing be golden tail or Kimberley tail or granite powder or copper tail or iron tail or quartz sand tail or oil shale tail.
CN201710805223.9A 2017-09-08 2017-09-08 A kind of sludge and mine tailing mixed method Pending CN107500880A (en)

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* Cited by examiner, † Cited by third party
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CN107821090A (en) * 2017-12-27 2018-03-23 大连地拓环境科技有限公司 A kind of planting soil and preparation method thereof
CN108064662A (en) * 2017-12-27 2018-05-25 大连地拓环境科技有限公司 A kind of organic magnetic planting soil and preparation method thereof
CN109127114A (en) * 2018-09-21 2019-01-04 大连地拓环境科技有限公司 A kind of low-grade magnesite method of comprehensive utilization
CN109392655A (en) * 2018-11-19 2019-03-01 大连青松智慧生态科技有限公司 A method of sludge and metallurgical slag are mixed to get planting soil
CN110454165A (en) * 2019-07-26 2019-11-15 武汉理工大学 One kind repairing matrix and preparation method thereof and burying method for lime stone stone pit abandoned mine pit
CN113372920A (en) * 2021-06-09 2021-09-10 华南师范大学 Composite conditioner for soil cadmium pollution remediation and preparation method and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101810130A (en) * 2010-04-30 2010-08-25 张夫道 Method for using major metal tailings after harmless treatment as culture medium
CN103039297A (en) * 2013-01-11 2013-04-17 南京信息工程大学 Plant culture mediums and preparation method thereof
CN104987260A (en) * 2015-06-11 2015-10-21 北京矿冶研究总院 Ecological restoration matrix for lead-zinc tailing pond and preparation method and application thereof
CN105061001A (en) * 2015-04-17 2015-11-18 北京林业大学 Acidic copper tailing matrix improver, improving matrix, preparation method of improver and application of improving matrix

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101810130A (en) * 2010-04-30 2010-08-25 张夫道 Method for using major metal tailings after harmless treatment as culture medium
CN103039297A (en) * 2013-01-11 2013-04-17 南京信息工程大学 Plant culture mediums and preparation method thereof
CN105061001A (en) * 2015-04-17 2015-11-18 北京林业大学 Acidic copper tailing matrix improver, improving matrix, preparation method of improver and application of improving matrix
CN104987260A (en) * 2015-06-11 2015-10-21 北京矿冶研究总院 Ecological restoration matrix for lead-zinc tailing pond and preparation method and application thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
刘国飞等: "添加剂用量对人工土壤生态特征影响的研究", 《环境科学与技术》 *
张鸿龄等: "粉煤灰、城市污泥、尾矿砂配施用于无土排岩场生态修复人工土壤的持水性能研究", 《农业环境科学学报》 *

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107821090A (en) * 2017-12-27 2018-03-23 大连地拓环境科技有限公司 A kind of planting soil and preparation method thereof
CN108064662A (en) * 2017-12-27 2018-05-25 大连地拓环境科技有限公司 A kind of organic magnetic planting soil and preparation method thereof
CN109127114A (en) * 2018-09-21 2019-01-04 大连地拓环境科技有限公司 A kind of low-grade magnesite method of comprehensive utilization
CN109392655A (en) * 2018-11-19 2019-03-01 大连青松智慧生态科技有限公司 A method of sludge and metallurgical slag are mixed to get planting soil
CN110454165A (en) * 2019-07-26 2019-11-15 武汉理工大学 One kind repairing matrix and preparation method thereof and burying method for lime stone stone pit abandoned mine pit
CN110454165B (en) * 2019-07-26 2020-07-28 武汉理工大学 Repair matrix for abandoned mine pits of limestone quarry and preparation method and landfill method thereof
CN113372920A (en) * 2021-06-09 2021-09-10 华南师范大学 Composite conditioner for soil cadmium pollution remediation and preparation method and application thereof
CN113372920B (en) * 2021-06-09 2022-03-04 华南师范大学 Composite conditioner for soil cadmium pollution remediation and preparation method and application thereof

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Application publication date: 20171222