CN110201994A - A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron - Google Patents

A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron Download PDF

Info

Publication number
CN110201994A
CN110201994A CN201910506805.6A CN201910506805A CN110201994A CN 110201994 A CN110201994 A CN 110201994A CN 201910506805 A CN201910506805 A CN 201910506805A CN 110201994 A CN110201994 A CN 110201994A
Authority
CN
China
Prior art keywords
soil
polycyclic aromatic
aromatic hydrocarbon
titanium powder
vinegar grain
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.)
Pending
Application number
CN201910506805.6A
Other languages
Chinese (zh)
Inventor
罗志军
王鸣俊
宋由页
郑先荣
王静
曲玲玲
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiangsu Kang Shiruijia Environmental Protection Technology Development Co Ltd
Jiangsu University
Original Assignee
Jiangsu Kang Shiruijia Environmental Protection Technology Development Co Ltd
Jiangsu University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Jiangsu Kang Shiruijia Environmental Protection Technology Development Co Ltd, Jiangsu University filed Critical Jiangsu Kang Shiruijia Environmental Protection Technology Development Co Ltd
Priority to CN201910506805.6A priority Critical patent/CN110201994A/en
Publication of CN110201994A publication Critical patent/CN110201994A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/08Reclamation of contaminated soil chemically

Abstract

The invention belongs to field of environmental technology, provide a kind of based on vinegar grain and titanium powder plant waste FeSO4·7H2The restorative procedure of the polycyclic aromatic hydrocarbon pollution of O.With vinegar grain and titanium powder plant waste FeSO4·7H2O is that raw material prepares soil remediation material I and material II.Material I is vinegar grain and titanium powder plant waste FeSO4·7H2Mixture after O co-grinding.Material II is the product obtained after roasting soil remediation material I at low temperature.When the total content of polycyclic aromatic hydrocarbon is lower than 1000mg polycyclic aromatic hydrocarbon/kg soil, the selection of material I.When the total content of polycyclic aromatic hydrocarbon is higher than 1000mg polycyclic aromatic hydrocarbon/kg soil, the selection of material II.Selected soil remediation material is stirred and shakeout with polycyclic aromatic hydrocarbon pollution, without adjusting the pH value of soil, is not necessarily to hydrogen peroxide, it is seen that, can polycyclic aromatic hydrocarbon in deep oxidation degradation soil under light irradiation.The present invention can greatly reduce the toxicity of pollutant in soil, and the coefficient of growth on soil after repair with the plant in unpolluted grown on soil does not have apparent difference.

Description

A kind of polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron Restorative procedure
Technical field
The invention belongs to field of environmental technology, are related to the resource utilization of waste and the reparation of polycyclic aromatic hydrocarbon pollution Method.
Background technique
China is vinegar production and consumption big country, and 1 ton of vinegar of every production will generate 0.8 ton of vinegar grain according to statistics, 2015 The vinegar grain of generation is as high as 3,200,000 tons.Vinegar grain water content more a height of 65%~75%, in acidity, the pH of filter liquor is acidity (3~3.5).If the problems such as annual a large amount of acid vinegar grain cannot be effectively treated, will cause environmental pollution, soil acidification.Mesh The resource utilization method of preceding vinegar grain mainly has fodder, Fertilizer Transformed, matrixing and energy etc., each method all exists Obvious disadvantage, it is difficult to promote.Urgent need finds one kind and vinegar grain is effectively treated, the method for promoting vinegar grain added value.
The production method of titanium dioxide has sulfuric acid process and two kinds of chloridising, since the production cost of chloridising is higher than sulfuric acid Method.So domestic titanium powder plant mainly uses Titanium White Production By Sulfuric Acid Process at present, can be produced in the process of production titanium dioxide Raw a large amount of ferrous sulfate, the titanium dioxide of every 1 ton of production will generate 4 tons or so of FeSO according to statistics4.7H2O, and 2017 The titanium white powder yield of China has just reached 3,550,000 tons.The byproduct FeSO generated during producing titanium dioxide4.7H2O, no Only it is in highly acid, also will cause environmental pollution if cannot be effectively treated containing a large amount of impurity.
Polycyclic aromatic hydrocarbon (Polycyclic aromatic hydrocarbons, PAHs) refers to by two or more The hydrocarbon that phenyl ring is composed by linear, horn shape or tufted, is the persistence with carcinogenic, teratogenesis, mutagenicity Organic pollutant (Persistent organic pollutants, POPs).Polycyclic aromatic hydrocarbon, which is mainly derived from petroleum, coal etc., to be had The imperfect combustion of machine pollutant is a kind of POPs being widely present in environment.Since polycyclic aromatic hydrocarbon has stronger dredge more Aqueous and stability, so that the polycyclic aromatic hydrocarbon in air and water environment finally accumulates in soil, soil is the weight of polycyclic aromatic hydrocarbon Want home to return to.
Currently, the recovery technique of polycyclic aromatic hydrocarbon pollution mainly has bioremediation technology, peripheral doses technology and chemistry Aoxidize recovery technique.Peripheral doses technology is mainly using the polycyclic aromatic hydrocarbon removal in soil between a variety of different physical processes Technology, mainly have steam extraction process, solidification stabilization method, thermal desorption method etc..The generally existing energy consumption of peripheral doses technology it is high and at This high disadvantage.It is biological prosthetic mainly to utilize plant, animal or microorganism biological species the characteristics of interior, specific Under the conditions of to polycyclic aromatic hydrocarbon carry out biodegrade.Bioremediation technology is at low cost, secondary pollution is few, but repairing effect is by periphery Environmental factor is affected, and repairing efficiency is longer.Chemical oxidation recovery technique is mainly aoxidized by adding into soil Agent realizes the reparation to organic polluted soil by the organic pollutant in oxidizing degradation soil.Common oxidation Agent mainly has ozone, hydrogen peroxide, potassium permanganate, persulfate and Fenton reagent etc..It is repaired using chemical oxidizing agent polycyclic Aromatic hydrocarbons contaminated soil, since oxidant is the medicament with strong oxidizing property, while oxidative degradation polycyclic aromatic hydrocarbon, oxidation Agent can also destroy the structure and composition of soil, result even in the secondary pollution of soil, be unfavorable for the growth of plant after repairing.
There are various disadvantages in the recovery technique of above-mentioned polycyclic aromatic hydrocarbon pollution, therefore, it is necessary to grope a kind of pair of ring Border is friendly, while removing pollutant in soil, does not destroy the soil remediation material and method of soil constitution and structure also.
Summary of the invention
Deficiency existing for recovery technique for current polycyclic aromatic hydrocarbon pollution, the present invention provides one kind to be based on vinegar Industry waste vinegar grain and titanium dioxide industry waste FeSO4.7H2The restorative procedure of the polycyclic aromatic hydrocarbon pollution of O.
What the invention is realized by the following technical scheme:
Step 1: polycyclic aromatic hydrocarbon pollution being pre-processed: including air-drying, rolling crushing, sieving processing, obtaining institute The soil particle needed;
Step 2: the total content of polycyclic aromatic hydrocarbon in measurement polycyclic aromatic hydrocarbon pollution;
Step 3: to vinegar grain and titanium powder plant waste FeSO4.7H2O carries out different pretreatments method, and processing method is as follows:
(1) by vinegar grain and titanium powder plant waste FeSO4.7H2O is put into pulverizer according to certain mass ratio and is pulverized and mixed It is even to get arrive soil remediation material I;
(2) by the vinegar grain after being pulverized and mixed in step 1 and titanium powder plant waste FeSO4.7H2O is placed in Muffle furnace and roasts It burns, soil remediation material II is obtained after roasting;
Step 4: according to the content for the PAHs in soil that step 2 is measured, selecting soil remediation material made from step 3 Expect I or soil remediation material II:
When the total content of PAHs in soil is lower than 1000mg polycyclic aromatic hydrocarbon/kg soil, soil remediation material is used I;
When the total content of PAHs in soil is more than 1000mg polycyclic aromatic hydrocarbon/kg soil, soil remediation material is used II;
The soil remediation material of selection is stirred evenly in proportion with polycyclic aromatic hydrocarbon pollution, then shakeouts to form thickness Soil layer no more than 1cm;
Step 5: the soil layer shakeout being placed under visible light and is irradiated, spray water is needed during irradiation, the water content of soil is allowed to protect It holds 50%~90%;Illumination after a certain period of time, can remove the polycyclic aromatic hydrocarbon in soil.
Described to air-dry as natural drying in step 1, the time is one week;Sieving processing uses 60 mesh soil sieves.
In step 3, vinegar grain and titanium powder plant waste FeSO4.7H2The mass ratio of O is 1:1~4:1.
In step 3, the maturing temperature is 300~400 DEG C, calcining time 3h.
In step 4, the mass percent of soil remediation material and polycyclic aromatic hydrocarbon pollution is controlled 5%~10%.
Phytotoxicity evaluating method after polycyclic aromatic hydrocarbon pollution is repaired is as follows:
Phytotoxicity evaluating is by carrying out planting experiment of the lettuce in different soils.Lactuca sativa seeds are planted respectively In uncontaminated soil, in the polycyclic aromatic hydrocarbon pollution and polycyclic aromatic hydrocarbon pollution repaired, every kind of soil carry out four groups it is flat Row planting experiment.The coefficient of growth (germination percentage, root long, leaf length and fresh weight) for the lettuce planted in every kind of soil is investigated, To assess the phytotoxicity of soil.
By 5 lettuce plantings in a flowerpot equipped with soil, every kind of soil plants four flowerpots altogether namely every kind of soil is total 20 lactuca sativa seeds are planted.Flowerpot equipped with lactuca sativa seeds is put into plant incubator, in incubator when the illumination of fluorescent lamp Between and interlunation be respectively 16 hours and 8 hours, corresponding temperature is 22 degrees Celsius and 16 degrees Celsius.In incubation, soil The water content of earth is controlled 60%, therefore needs regular replenishment moisture.After lactuca sativa seeds cultivate 5 days in the soil, count at three kinds The germination percentage of seed in soil.After having counted germination percentage, two plants of lettuce rice shoots are left in each flowerpot and carry out growth experiment.After After continuous culture two weeks, lettuce is harvested, counts root long, leaf length and fresh weight in three kinds of geophilous lettuces.It will be in three kinds of soil The coefficient of growth (germination percentage, root long, leaf length and fresh weight) of the lettuce of acquisition, is arranged by software (SPSS software) Analysis, to compare the phytotoxicity after polycyclic aromatic hydrocarbon pollution is repaired.
The invention has the advantages that
(1) with Vinegar Industry waste vinegar grain and titanium dioxide industry waste FeSO4.7H2O is raw material to polycyclic aromatic hydrocarbon dirt Dye soil is repaired, and the resource utilization of solid waste is realized;
(2) vinegar grain and titanium dioxide industry waste FeSO are based on4.7H2The soil remediation material of O under visible light illumination, i.e., It can be activated to generate the superoxide radical of strong oxidizing property, thus the polycyclic aromatic hydrocarbon in deep oxidation degradation soil;
(3) vinegar grain and titanium dioxide industry waste FeSO are based on4.7H2The soil remediation material of O is in oxidative degradation soil Polycyclic aromatic hydrocarbon during the entire process of, without adjusting the pH value of soil;
(4) vinegar grain and titanium dioxide industry waste FeSO are based on4.7H2The soil remediation method of O can remove soil with depth In polycyclic aromatic hydrocarbon, the toxicity of polycyclic aromatic hydrocarbon pollution is greatly lowered.Soil after reparation, will not be to the growth of plant It has adverse effect on, the life of the plant of grown on soil after repair and the plant in unpolluted grown on soil Long coefficient (germination percentage, root long, leaf length, fresh weight) is without apparent difference.
Detailed description of the invention
Fig. 1 is the raw material for preparing soil remediation material I, and a is vinegar factory waste vinegar grain and b is titanium powder plant waste FeSO4.7H2O;
Fig. 2 is under visible light and under no light, and soil remediation material I is bent to the degradation rate of low concentration phenanthrene in contaminated soil Line;
Fig. 3 is degradation rate curve of the soil remediation material II to contaminated soil middle and high concentration phenanthrene under visible light;
Fig. 4 is under visible light that soil remediation material II is to naphthalene, anthracene, phenanthrene, the pyrene in compound polycyclic aromatic hydrocarbon pollution Degradation rate histogram;
Fig. 5 is the ESR spectrogram of soil remediation material II under visible light.
Specific embodiment
With reference to the accompanying drawings of the specification and specific embodiment the present invention is further illustrated, but protection of the invention Range is not limited to this.
The raw material for preparing soil remediation material I and soil remediation material II is that the vinegar grain of vinegar factory generation and titanium powder plant produce Raw FeSO4.7H2O, Fig. 1 are the vinegar grain that vinegar factory generates and the FeSO that titanium powder plant generates4.7H2O photo.Table 1 is FeSO4.7H2Constituent content in O, it is seen that main metallic element be Fe, Mg, Mn and Ti, wherein the content of Mg, Mn and Ti compared with It is low.
The FeSO that 1. titanium powder plant of table generates4.7H2Constituent content in O
Embodiment 1: under visible light, soil remediation material I is used for the reparation of low concentration phenanthrene-polluted soil
1. the contaminated soil sampled from pollution plot, pre-processes polycyclic aromatic hydrocarbon pollution: firstly, will fit Polycyclic aromatic hydrocarbon pollution natural air drying one week or so of amount.Then, pair soil carries out rolling crushing.Finally, 60 mesh soil Sieve carries out sieving processing to soil, obtains required soil particle;
It is phenanthrene through the major pollutants in detection soil, content is 2. a pair pretreated soil particle detects 180mg phenanthrene/kg soil;
3. by vinegar grain and titanium powder plant waste FeSO4.7H2O is put into pulverizer according to mass ratio 4:1 and is pulverized and mixed uniformly, Obtain soil remediation material I;
4. soil remediation material I is stirred evenly with polycyclic aromatic hydrocarbon pollution, wherein soil remediation material I and polycyclic virtue The mass percent of soil contaminated with hydrocarbons is 5%, then shakeouts the soil layer to form 1cm thickness;
5. the soil layer shakeout is placed in (wavelength is greater than 420nm, and average intensity is about 8100Lux) irradiation 10 hours, illumination Period water content is controlled 50%, and the degradation rate of soil China and Philippines is about 98.6% (as shown in Figure 2).
6. the plant evaluation after phenanthrene-polluted soil reparation:
Lettuce is planted in uncontaminated soil respectively, in the phenanthrene-polluted soil and phenanthrene-polluted soil repaired.By 19 days Culture, phenanthrene-polluted soil has biggish toxicity to lettuce, and the growth of lettuce is totally constrained.Phenanthrene-polluted soil is by soil After earth repair materials I is repaired, toxicity is greatly diminished, the lettuce planted above it and unpolluted grown on soil Lettuce there is no apparent difference.
Table 2 is germination percentage, root long, leaf length and fresh weight number of the lettuce in the native and luxuriant and rich with fragrance Polluted Soil after uncontaiminated soil, reparation According to.It can be seen that the phenanthrene in soil does not influence the germination percentage of lactuca sativa seeds significantly, but for root long, leaf length and fresh weight There is apparent inhibiting effect.For phenanthrene-polluted soil after soil remediation material I reparation, the lettuce of growth is long and fresh in root long, leaf Weight is not distinguished significantly with the lettuce grown in unpolluted soil, it was demonstrated that the soil based on soil remediation material I is repaired Compound method is a kind of environment friendly material and its method.
Germination percentage, root long, leaf length and fresh weight of 2. lettuce of table in different soils
Embodiment 2: under visible light, the reparation of high concentration phenanthrene-polluted soil is repaired
1. the contaminated soil sampled from pollution plot, pre-processes polycyclic aromatic hydrocarbon pollution: firstly, will fit Polycyclic aromatic hydrocarbon pollution natural air drying one week or so of amount.Then, pair soil carries out rolling crushing.Finally, 60 mesh soil Sieve carries out sieving processing to soil, obtains required soil particle;
It is phenanthrene through the major pollutants in detection soil, content contains 2. a pair pretreated soil particle detects Amount is up to 2150mg phenanthrene/kg soil;
3. by vinegar grain and titanium powder plant waste FeSO4.7H2O is put into pulverizer according to mass ratio 2:1 and is pulverized and mixed uniformly, Then smashed mixture is placed in Muffle furnace, temperature is 300 DEG C, obtains soil remediation material II after roasting 3h.
4. soil remediation material II is stirred evenly with polycyclic aromatic hydrocarbon pollution, wherein soil remediation material II with it is polycyclic The mass percent of aromatic hydrocarbons contaminated soil is 10%, then shakeouts the soil layer to form 0.5cm thickness;
5. the soil layer shakeout is placed in (wavelength is greater than 420nm, and average intensity is about 8100Lux) irradiation 10 hours, illumination Period water content is controlled 70%, and luxuriant and rich with fragrance degradation rate is about 91% (as shown in Figure 3).
6. the plant evaluation after phenanthrene-polluted soil reparation:
Lettuce is planted in uncontaminated soil respectively, in the phenanthrene-polluted soil and phenanthrene-polluted soil repaired, by 19 days Culture, coefficient of growth such as the following table 3.Different from low concentration phenanthrene-polluted soil, in the soil of high concentration phenanthrene, the hair of lactuca sativa seeds Bud rate receives apparent inhibition, but soil is after soil remediation material II reparation, the germination of germination percentage and not comtaminated soil Rate is not distinguished significantly.The lettuce grown in root long, leaf length and fresh weight and unpolluted soil is also without apparent area Not.
Germination percentage, root long, leaf length and fresh weight of 3. lettuce of table in the soil repaired
Germination percentage (%) Root long (centimetre) Leaf is long (centimetre) Fresh weight (gram)
Uncontaiminated soil 90.1 3.05 2.6 0.042
Soil after reparation 89.8 3.01 2.58 0.040
High concentration phenanthrene Polluted Soil 63.1 0.51 0.61 0.031
Embodiment 3: under visible light, the compound polycyclic aromatic hydrocarbon pollution of high concentration is repaired
1. the contaminated soil sampled from pollution plot, pre-processes polycyclic aromatic hydrocarbon pollution: firstly, will fit Polycyclic aromatic hydrocarbon pollution natural air drying one week or so of amount.Then, pair soil carries out rolling crushing.Finally, 60 mesh soil Sieve carries out sieving processing to soil, obtains required soil particle;
It is naphthalene, anthracene, phenanthrene, pyrene through the major pollutants in detection soil 2. a pair pretreated soil particle detects, Concentration is respectively 350mg naphthalene/kg soil, 1350mg anthracene/kg soil, 531mg phenanthrene/kg soil and 768mg pyrene/kg soil;
3. by vinegar grain and titanium powder plant waste FeSO4.7H2O is put into pulverizer according to mass ratio 1:1 and is pulverized and mixed uniformly, Then smashed mixture is placed in Muffle furnace, temperature is 350 DEG C, obtains soil remediation material II after roasting 3h.
4. soil remediation material II is stirred evenly with polycyclic aromatic hydrocarbon pollution, wherein soil remediation material II with it is polycyclic The mass percent of aromatic hydrocarbons contaminated soil is 10%, then shakeouts the soil layer to form 0.5cm thickness;
5. the soil layer shakeout is placed in (wavelength is greater than 420nm, and average intensity is about 8100Lux) irradiation 10 hours, illumination The control of period water content in 90%, soil naphthalene, anthracene, phenanthrene, pyrene degradation rate be respectively 98%, 90%, 93% and 91% (such as Shown in Fig. 4).
Fig. 5 is the DMPO-O under dark and radiation of visible light respectively of soil remediation material II2 ·-ESR spectrogram.Visible Light irradiation is lower it can be observed that DMPO-O2 ·-Six characteristic peaks of spin adduct, but do not detect in the dark obvious Signal.In addition, can not detect DMPO-OH spin adduct under visible light illumination.ESR spectral results show can Under light-exposed irradiation condition, soil remediation material II can produce the O of a large amount of strong oxidizing properties2 ·-, thus having in oxidative degradation soil Machine pollutant, here it is be based on vinegar grain and titanium powder plant waste FeSO4.7H2The soil remediation material of O can repair polycyclic virtue The reason of soil contaminated with hydrocarbons.
6. the plant evaluation after compound polycyclic aromatic hydrocarbon pollution reparation:
Lettuce is planted in uncontaminated soil respectively, the polycyclic aromatic hydrocarbon pollution repaired and compound polycyclic aromatic hydrocarbon are dirty It contaminates in soil, was cultivated by 19 days, coefficient of growth such as the following table 4.The toxicity of compound polycyclic aromatic hydrocarbon pollution is apparently higher than list The toxicity of one Phenanthrene, lettuce can not germinating growths in this compound polycyclic aromatic hydrocarbon pollution.But it is compound Polycyclic aromatic hydrocarbon pollution after soil remediation material II reparation, the lettuce of growth is in root long, leaf is long and fresh weight with it is not dirty The lettuce grown in the soil of dye do not distinguish significantly, it was demonstrated that the toxicity of polycyclic aromatic hydrocarbon pollution is reduced significantly ?.
Germination percentage, root long, leaf length and fresh weight of 4. lettuce of table in the soil repaired
Germination percentage (%) Root long (centimetre) Leaf is long (centimetre) Fresh weight (gram)
Uncontaiminated soil 90.1 3.05 2.6 0.042
Soil after reparation 89.3 3.03 2.61 0.043

Claims (5)

1. a kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron, feature exist In including the following steps:
Step 1: polycyclic aromatic hydrocarbon pollution being pre-processed: including air-drying, rolling crushing, sieving processing, being obtained required Soil particle;
Step 2: the total content of polycyclic aromatic hydrocarbon in measurement polycyclic aromatic hydrocarbon pollution;
Step 3: to vinegar grain and titanium powder plant waste FeSO4.7H2O carries out different pretreatments method, and processing method is as follows:
(1) by vinegar grain and titanium powder plant waste FeSO4.7H2O is put into pulverizer according to certain mass ratio and is pulverized and mixed uniformly, i.e., Obtain soil remediation material I;
(2) by the vinegar grain after being pulverized and mixed in step 1 and titanium powder plant waste FeSO4.7H2O is placed in Muffle kiln roasting, roasting Soil remediation material II is obtained after burning;
Step 4: according to the content for the PAHs in soil that step 2 is measured, selecting soil remediation material I made from step 3 Or soil remediation material II:
When the total content of PAHs in soil is lower than 1000mg polycyclic aromatic hydrocarbon/kg soil, soil remediation material I is used;
When the total content of PAHs in soil is more than 1000mg polycyclic aromatic hydrocarbon/kg soil, soil remediation material II is used;
The soil remediation material of selection is stirred evenly in proportion with polycyclic aromatic hydrocarbon pollution, then shakeouts to form thickness and do not surpass Cross the soil layer of 1cm;
Step 5: the soil layer shakeout being placed under visible light and is irradiated, spray water is needed during irradiation, the water content of soil is allowed to be maintained at 50%~90%;Illumination after a certain period of time, can remove the polycyclic aromatic hydrocarbon in soil.
2. restorative procedure as described in claim 1, which is characterized in that described to air-dry as natural drying in step 1, the time is One week;Sieving processing uses 60 mesh soil sieves.
3. restorative procedure as described in claim 1, which is characterized in that in step 3, vinegar grain and titanium powder plant waste FeSO4.7H2The mass ratio of O is 1:1~4:1.
4. restorative procedure as described in claim 1, which is characterized in that in step 3, the maturing temperature is 300~400 DEG C, Calcining time is 3h.
5. restorative procedure as described in claim 1, which is characterized in that in step 4, soil remediation material with it is polycyclic aromatic hydrocarbons contaminated The mass percent of soil is controlled 5%~10%.
CN201910506805.6A 2019-06-12 2019-06-12 A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron Pending CN110201994A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910506805.6A CN110201994A (en) 2019-06-12 2019-06-12 A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910506805.6A CN110201994A (en) 2019-06-12 2019-06-12 A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron

Publications (1)

Publication Number Publication Date
CN110201994A true CN110201994A (en) 2019-09-06

Family

ID=67792255

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910506805.6A Pending CN110201994A (en) 2019-06-12 2019-06-12 A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron

Country Status (1)

Country Link
CN (1) CN110201994A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111411103A (en) * 2020-03-25 2020-07-14 南京师范大学 Microorganism immobilization carrier prepared based on vinegar residue waste and preparation method and application thereof
CN113702623A (en) * 2021-08-27 2021-11-26 河北科技大学 Microwave leaching type soil remediation evaluation device and evaluation method
CN114907855A (en) * 2022-07-07 2022-08-16 华东理工大学 Method for preparing soil conditioner by using by-product in titanium dioxide production

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102085529A (en) * 2009-12-04 2011-06-08 中国科学院生态环境研究中心 Method for repairing polycyclic aromatic hydrocarbon polluted soil by using residual active sludge
CN103878172A (en) * 2014-04-14 2014-06-25 北京建筑材料科学研究总院有限公司 Method for jointly treating polycyclic aromatic hydrocarbon polluted soil and urban organic waste
CN108641721A (en) * 2018-03-14 2018-10-12 江苏大学 One kind being based on mesoporous Fe3O4The preparation method and applications of the polycyclic aromatic hydrocarbon pollution repair materials of/carbon composite
CN108655168A (en) * 2018-04-13 2018-10-16 江苏大学 g-C3N4/Fe3O4Purposes of the composite material in repairing polycyclic aromatic hydrocarbon pollution

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102085529A (en) * 2009-12-04 2011-06-08 中国科学院生态环境研究中心 Method for repairing polycyclic aromatic hydrocarbon polluted soil by using residual active sludge
CN103878172A (en) * 2014-04-14 2014-06-25 北京建筑材料科学研究总院有限公司 Method for jointly treating polycyclic aromatic hydrocarbon polluted soil and urban organic waste
CN108641721A (en) * 2018-03-14 2018-10-12 江苏大学 One kind being based on mesoporous Fe3O4The preparation method and applications of the polycyclic aromatic hydrocarbon pollution repair materials of/carbon composite
CN108655168A (en) * 2018-04-13 2018-10-16 江苏大学 g-C3N4/Fe3O4Purposes of the composite material in repairing polycyclic aromatic hydrocarbon pollution

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
ZHIJUN LUO等: "Remediation of Phenanthrene Contaminated Soil by a Solid State Photo-Fenton Reagent Based on Mesoporous Magnetite/Carboxylate-Rich Carbon Composites and Its Phytotoxicity Evaluation", 《ACS SUSTAINABLE CHEMISTRY AND ENGINEERING》 *
周琦等: "生物质吸附去除水环境中多环芳烃的研究进展", 《上海应用技术学院学报(自然科学版)》 *
张晶等: "多环芳烃污染土壤修复技术研究进展", 《安徽农业科学》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111411103A (en) * 2020-03-25 2020-07-14 南京师范大学 Microorganism immobilization carrier prepared based on vinegar residue waste and preparation method and application thereof
CN113702623A (en) * 2021-08-27 2021-11-26 河北科技大学 Microwave leaching type soil remediation evaluation device and evaluation method
CN114907855A (en) * 2022-07-07 2022-08-16 华东理工大学 Method for preparing soil conditioner by using by-product in titanium dioxide production

Similar Documents

Publication Publication Date Title
Cui et al. Biochar and effective microorganisms promote Sesbania cannabina growth and soil quality in the coastal saline-alkali soil of the Yellow River Delta, China
Luo et al. Effect of co-application of wood vinegar and biochar on seed germination and seedling growth
Sani et al. Impact of application of Trichoderma and biochar on growth, productivity and nutritional quality of tomato under reduced NPK fertilization
CN110201994A (en) A kind of restorative procedure of the polycyclic aromatic hydrocarbon pollution based on vinegar grain and titanium powder plant waste sulfate ferrous iron
CN108655168A (en) g-C3N4/Fe3O4Purposes of the composite material in repairing polycyclic aromatic hydrocarbon pollution
Montemurro et al. MSW compost application on tomato crops in Mediterranean conditions: effects on agronomic performance and nitrogen utilization
CN109847750B (en) Preparation method and application of iron-enriched biological carbon of cattail roots
CN104957009A (en) Method for regulating turfgrass heavy metal accumulation by using OTC and carbon nano-tube interlayer
CN108637005A (en) It is a kind of to repair polycyclic aromatic hydrocarbons contaminated composite material, preparation method and the usage
Naresh et al. Organic matter fractions and soil carbon sequestration after 15-years of integrated nutrient management and tillage systems in an annual double cropping system in northern India
CN110999751A (en) Biochar prepared from facility agricultural wastes, preparation method of biochar, soilless culture substrate and application of substrate
Li et al. Altered transfer of heavy metals from soil to Chinese cabbage with film mulching
Munongo et al. Production and characterization of compost manure and biochar from cocoa pod husks
Ball et al. Assessment of the potential of a novel newspaper/horse manure-based compost
Kanakaraju et al. Uptake of heavy metals from palm oil mill effluent sludge amended soils in water spinach
Hu et al. Performance and mechanism of high-speed vermicomposting of dewatered sludge using a new type of laboratory earthworm reactor
Regni et al. The sustainable reuse of compost from a new type of olive mill pomace in replacing peat for potted olive tree
CN115918319B (en) Method for reducing arsenic content in rice in paddy field polluted by acidic arsenic and application
Ashrafi et al. The interactions of Cr (VI) concentrations and amendments (biochar and manure) on growth and metal accumulation of two species of Salicornia in contaminated soil
Qin et al. Regrow Napier grass–Chinese milk vetch relay intercropping system: A cleaner production strategy in Cd-contaminated farmland
CN108641721B (en) Based on mesoporous Fe3O4Preparation method and application of polycyclic aromatic hydrocarbon contaminated soil remediation material of/carbon composite material
CN116493405A (en) Method for repairing tailings by combining blue algae-moss crust and biochar-semi-carbonized sludge modifier
CN109721423A (en) A kind of pakchoi is compound fertilizer dedicated and its preparation method and application
Marathe et al. Influence of different potting media on soil properties, plant nutrient content and nutrient uptake by pomegranate (Punica granatum) seedlings
Ali et al. Potential of organic and inorganic amendments for stabilizing nickel in acidic soil, and improving the nutritional quality of spinach

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190906

RJ01 Rejection of invention patent application after publication