1. The magnetic soil remediation agent for the heavy metal pollution of soil is characterized in that: the repairing agent is prepared by taking repairing agent aggregate and a magnetic material core body as raw materials and taking a heavy metal collecting agent as a modifier;

the repairing agent aggregate is silicon dioxide subjected to strong alkali activation treatment;

the magnetic material core body comprises a magnetic material Fe₃O₄、γ-Fe₂O₃；

The modifier comprises ethylene diamine tetraacetic acid, nitrilotriacetic acid trisodium salt, (S, S) -ethylenediamine-N, N-disuccinic acid trisodium salt and mercaptoethylamine.

2. The magnetic soil remediation agent of claim 1, wherein: the mass ratio of the repairing agent aggregate to the magnetic material core body to the modifying agent is 1: 0.05-0.1: 0.005-0.01.

3. The magnetic soil remediation agent of claim 1, wherein: fe in the magnetic material core body₃O₄、γ-Fe₂O₃The mass ratio is 1.5-2: 1.

The modifier comprises EDTA, NTA, EDDS and mercaptoethylamine in a mass ratio of 1: 0.05-0.1: 0.1-0.2: 0.2-0.3.

4. The magnetic soil remediation agent of claim 1, wherein: in comparison with the unmodified magnetic material core body, in the XRD characterization pattern, the core body has characteristic peaks at 26.8 degrees, 35.3 degrees and 62.2 degrees, which correspond to SiO₂、Fe₃O₄、γ-Fe₂O₃(ii) a In the results of infrared spectroscopic analysis, it was found to be present at wave numbers of 3461, 1637, 1432, 1090 and 795cm^-1The infrared characteristic peak corresponds to a silicon-oxygen bond, a sulfhydryl group and an amino functional group.

5. The method of preparing a magnetic soil remediation agent of any one of claims 1 to 4 including the steps of:

(1) preparation of SiO₂Aggregate: with SiO₂The powder is taken as a raw material according to SiO₂Adding solid NaOH into the aggregate according to the mass ratio of 1: 0.1-0.15, roasting, cooling and crushing the discharged material, and washing off the excessive NaOH to ensure that the pH value of the aggregate is 6.5-8.5;

(2) compounding the modifier: uniformly mixing EDTA, NTA, EDDS and mercaptoethylamine according to a mass ratio, and adding water to dissolve to obtain a modifier solution;

(3) mixing SiO₂The aggregate, the magnetic material core body and the modifier solution are uniformly mixed according to the proportion, precipitated, filtered, heated, dried and crushed to obtain the magnetic material core body.

6. The method of claim 5, wherein: in the step (1), the roasting temperature is 800 ℃, the roasting is carried out for 30-60min, and excess NaOH is removed by washing to ensure that the pH value of the aggregate is 6.5-8.5.

7. As in claimThe production method according to claim 5, characterized in that: in the step (3), SiO₂The aggregate, the magnetic material core body and the modifier solution are uniformly mixed according to the proportion, precipitated and filtered, dried for 2-3h in a vacuum box at 50 ℃, and crushed to obtain the magnetic soil remediation agent.

8. Use of the magnetic soil remediation agent of any one of claims 1 to 4 for remediation of contaminated soil;

preferably, the polluted soil is heavy metal polluted soil in a mine area;

preferably, the contaminated soil is the heavy metal contaminated soil with the heavy metal content of Cd, As and Hg being 5-10 times, 15-20 times and 35-40 times of the standard of the soil for agricultural land.

9. A soil remediation method, characterized in that: applying the magnetic soil remediation agent of any one of claims 1 to 5 to contaminated soil to be treated, mixing and stirring uniformly;

the polluted soil is heavy metal polluted soil in a mine area; or the content of Cd, As and Hg in the polluted soil is 5-10 times, 15-20 times and 35-40 times of the standard of the soil for agricultural land.

10. The soil remediation method of claim 9 further comprising:

the application amount of the magnetic soil remediation agent ranges from 50 to 200g/m²More preferably 80 to 150g/m²More preferably 80 to 120g/m²Or 100g/m²。

Background

With the continuous acceleration of the industrialization process, various pollutants containing heavy metals continuously enter the surrounding farmland soil through various ways such As industrial waste gas, pesticide and fertilizer, sewage irrigation, waste accumulation and transfer and the like, so that serious heavy metal pollution (pollution of Cd, Pb, As, Cr and the like) of the soil is caused. Because soil heavy metals have the characteristics of being irreversible and incapable of being degraded, the heavy metals bring huge harm after entering farmland soil, have negative effects on the quantity and population structure of soil microorganisms, interfere normal metabolism of crops, and cause the yield reduction and quality reduction of the crops. In addition, after the heavy metals are absorbed and enriched by crops in soil, the heavy metal content of the heavy metals exceeds the standard, and the heavy metals finally enter a human body through a food chain and are enriched in different organs of the human body and cannot be discharged, so that various physiological functions of the human body are irreversibly damaged, and the heavy metals bring serious threats to the life and health of the human body. Therefore, the remediation and treatment of the soil environment are urgent.

However, soil heavy metal pollution is not easy to be perceived as pollution of the atmosphere, water and the like, and the harm generated by the soil heavy metal pollution is hidden to a certain extent, so that the discovery of the soil heavy metal pollution problem often has certain hysteresis, and the soil heavy metal pollution problem cannot be repaired and treated in time. Therefore, the problem of heavy metal pollution of farmland soil is prevented in advance, the heavy metal is prevented from being transferred to agricultural soil in time, and meanwhile, the capability of passivating the heavy metal in the soil is improved as much as possible aiming at the soil which is easily polluted by the heavy metal, so that the harm possibly brought by the toxicity of the heavy metal in the soil is reduced. Aiming at different soil heavy metal pollution conditions, appropriate soil remediation measures are taken, and the method is a main treatment strategy for reducing the soil treatment cost and improving the soil remediation efficiency.

The passivators commonly used at present mainly comprise calcareous materials, phosphorus-containing passivators, carbon materials, clay minerals, organic fertilizers, agricultural wastes and the like. The calcareous material is mainly used for passivating heavy metals by changing the pH value of soil, but excessive application can obviously influence the physicochemical properties of the soil, so that the yield of crops is reduced. The phosphorus-containing passivating agent is generally used for passivating lead, but high-concentration phosphorus can also cause leaching of arsenic and the like to increase the mobility of the arsenic, and as a eutrophication substance, the phosphorus-containing passivating agent is easy to pollute surrounding water, so that the application range of the phosphorus-containing passivating agent is limited to a certain extent. The carbon material is mainly characterized in that the carbon material fixes and passivates heavy metals through the adsorption action by utilizing the characteristic of large specific surface area, but the passivator is not stable enough, and the adsorbed metals can be released into soil again along with the degradation of carbon, so that secondary pollution is caused. The organic fertilizer and agricultural wastes have the problem of similar carbon materials when the heavy metal pollution of soil is treated, so the application range is narrow. The clay mineral also utilizes the characteristics of large specific surface area and charged structural layer to realize the passivation of heavy metal by means of adsorption, coordination, coprecipitation and the like, but has stronger adsorption selectivity to heavy metal, is only suitable for repairing single heavy metal pollution, needs to be matched with alkaline substances such as lime and the like for the treatment of composite heavy metal polluted soil, usually adopts modification treatment to enhance the adsorption effect, and has certain secondary pollution risk.

The silicate heavy metal passivator is an important soil heavy metal repairing agent, and can reduce the activity of heavy metals in soil and inhibit the absorption of plants by forming silicate compounds with the heavy metals, influencing the rhizosphere redox to reduce the activity of the heavy metals, improving the pH value of the soil, inhibiting the adsorption of plants to the heavy metals, changing the forms of the heavy metals, inhibiting the migration of the heavy metals to the overground parts of the plants and the like, so that the remediation of the heavy metal pollution of the soil can be realized. The market price of the prior silicate heavy metal passivator is up to 5000-10000 yuan/t, and although the heavy metal polluted farmland soil can be effectively modified, the cost is too high.

Disclosure of Invention

The invention aims to solve the problems and provides a collecting functional magnetic soil remediation agent with amino and sulfydryl for heavy metals in soil, which has a remarkable passivation and fixation effect on the heavy metals and can remarkably inhibit the absorption of plants on the heavy metals, and the specific technical scheme is as follows:

a magnetic soil remediation agent for soil heavy metal pollution is prepared by taking remediation agent aggregate and a magnetic material core body as raw materials and taking a heavy metal collecting agent as a modifier;

the repairing agent aggregate is silicon dioxide subjected to strong alkali activation treatment;

the magnetic material core body comprises a magnetic material Fe₃O₄、γ-Fe₂O₃；

The modifiers include ethylenediaminetetraacetic acid (EDTA), nitrilotriacetic acid trisodium salt (NTA), (S, S) -ethylenediamine-N, N-disuccinic acid trisodium salt (EDDS), and mercaptoethylamine.

Preferably, the mass ratio of the repairing agent aggregate to the magnetic material core body to the modifying agent is 1: 0.05-0.1: 0.005-0.01.

Preferably, Fe in the magnetic material core body₃O₄、γ-Fe₂O₃The mass ratio is 1.5-2: 1.

Preferably, the mass ratio of EDTA to NTA to EDDS to mercaptoethylamine is 1: 0.05-0.1: 0.1-0.2: 0.2-0.3.

Preferably, the magnetic soil remediation agent has characteristic peaks corresponding to SiO in XRD characterization pattern at 26.8 °, 35.3 ° and 62.2 ° compared with unmodified magnetic material core body₂、Fe₃O₄、γ-Fe₂O₃(ii) a In the results of infrared spectroscopic analysis, it was found to be present at wave numbers of 3461, 1637, 1432, 1090 and 795cm^-1The infrared characteristic peak corresponds to a silicon-oxygen bond, a sulfhydryl group and an amino functional group.

The invention also provides a preparation method of the magnetic soil remediation agent, which comprises the following steps:

(1) preparation of SiO₂Aggregate: with SiO₂The powder is taken as a raw material according to SiO₂Adding solid NaOH into the aggregate according to the mass ratio of 1: 0.1-0.15, roasting, cooling and crushing the discharged material, and washing off the excessive NaOH to ensure that the pH value of the aggregate is 6.5-8.5;

(2) compounding the modifier: uniformly mixing EDTA, NTA, EDDS and mercaptoethylamine according to a mass ratio, and adding water to dissolve to obtain a modifier solution;

(3) mixing SiO₂The aggregate, the magnetic material core body and the modifier solution are uniformly mixed according to the proportion, precipitated, filtered, heated, dried and crushed to obtain the magnetic material core body.

Preferably, in the step (1), the roasting temperature is 800 ℃, the roasting time is 30-60min, and the surplus NaOH is removed by washing with water, so that the pH value of the aggregate is 6.5-8.5.

Preferably, in the step (3), SiO₂The aggregate, the magnetic material core body and the modifier solution are uniformly mixed according to the proportion, precipitated and filtered, dried for 2-3h in a vacuum box at 50 ℃, and crushed to obtain the magnetic soil remediation agent.

The invention also provides the application of the magnetic soil remediation agent in the remediation of contaminated soil;

preferably, the polluted soil is heavy metal polluted soil in a mine area;

preferably, the contaminated soil is the heavy metal contaminated soil with the heavy metal content of Cd, As and Hg being 5-10 times, 15-20 times and 35-40 times of the standard of the soil for agricultural land.

The last aspect of the invention provides a soil remediation method, which comprises the steps of applying the magnetic soil remediation agent to the polluted soil to be treated, and uniformly mixing and stirring;

the polluted soil is heavy metal polluted soil in a mine area; or the content of Cd, As and Hg in the polluted soil is 5-10 times, 15-20 times and 35-40 times of the standard of the soil for agricultural land.

The application amount of the magnetic soil remediation agent ranges from 50 to 200g/m²More preferably 80 to 150g/m²More preferably 80 to 120g/m²Or 100g/m²。

The invention has the beneficial effects that: the magnetic soil remediation agent for soil polluted by heavy metals can effectively change the oxidation-reduction potential of the soil and increase the migration capacity of the heavy metals in the soil by aiming at the magnetic function of the heavy metals in the soil; the amino and the sulfydryl of the repairing material can effectively capture various heavy metal elements, so that a heavy metal complex is formed on the surface of the magnetic soil repairing agent material; the active silicon-oxygen bond of the silicon dioxide after the alkali activation treatment can further form a heavy metal silicate structure with heavy metal, so that the adsorption capacity of the material is increased, the formed stable heavy metal silicate structure has a remarkable passivation and fixing effect on the heavy metal, the effective state content of the stable heavy metal silicate structure is reduced, and the absorption of plants on the heavy metal can be remarkably inhibited.

Drawings

Fig. 1 is an XRD characterization diagram of a magnetic iron concentrate product.

FIG. 2 is an XRD characterization of the magnetic soil remediation agent of the present invention.

FIG. 3 is an infrared map of the magnetic soil remediation agent of the present invention.

Detailed Description

The invention is further illustrated by the following examples, which are not intended to be limiting.

The experimental methods in the following examples are all conventional methods unless otherwise specified; the chemical reagents used in the examples are commercially available conventional ones, unless otherwise specified, and are commercially available.

The main reagents are as follows:

ethylenediaminetetraacetic acid (EDTA): CAS number 60-00-4;

(S, S) -ethylenediamine-N, N-disuccinic acid trisodium salt (EDDS): CAS number 178949-82-1;

nitrilotriacetic acid trisodium salt (NTA): CAS number 5064-31-3;

mercaptoethylamine: CAS number 60-23-1.

Example 1 preparation of a magnetic soil remediation agent of the invention

Firstly, the magnetic soil remediation agent of the invention is prepared

Selecting magnetic material Fe₃O₄、γ-Fe₂O₃As core body, heavy metal collector ethylenediaminetetraacetic acid (EDTA), nitrilotriacetic acid trisodium salt (NTA), (S, S) -ethylenediamine-N, N-disuccinic acid trisodium salt (EDD)S) and mercaptoethylamine are used as modifiers, and silicon dioxide subjected to strong base activation treatment is used as a repairing agent aggregate to prepare the collecting functional magnetic soil repairing agent with amino and mercapto.

The preparation method of the magnetic soil remediation agent comprises the following steps:

(1) preparation of SiO₂Aggregate: with SiO 97% purity₂The powder is taken as a raw material according to SiO₂Adding solid NaOH (with the purity of 99%) into NaOH with the mass ratio of 1: 0.1-0.15, roasting at 800 ℃ for 30-60min, discharging, cooling, ball-milling, sieving with a 200-mesh sieve, and washing off excessive NaOH with pure water (or tap water) to enable the pH of the aggregate to be 6.5-8.5.

(2) Preparation of magnetic Fe₃O₄: prepared by a conventional simple coprecipitation method and by FeCl₃And FeCl₂·4H₂O being an iron precursor, FeCl₃:FeCl₂·4H₂The mass ratio of O is 1.63:1, and the main process is as follows: first, 40mL of a dispersion was prepared, and an aqueous solution containing a certain amount of an iron precursor was added thereto under constant stirring, after stirring for 30min, methylamine was added thereto until pH reached 11, and stirring was continued for 30min at a predetermined reaction temperature of 30 ℃ to precipitate iron oxide particles (i.e., Fe)₃O₄) (ii) a Cooling the solution to room temperature, centrifuging at high speed to separate precipitate, and drying in a vacuum oven at 50 deg.C for 1-2 hr. Magnetic Fe₃O₄Or commercially available conventional magnetic Fe₃O₄Commercial powders, commercially available.

(3) Preparation of gamma-Fe₂O₃The steps of (1): 10.01g of FeSO₄·7H₂O and 8.08g Fe (NO)₃)₃·9H₂O was dissolved in 50mL of water previously bubbled with nitrogen to eliminate oxygen dissolved in water, and Fe²⁺/Fe³⁺The molar ratio was fixed at 1: 1.8. The iron salt solution was slowly added to deoxygenated 400mL NH₄Adding into OH solution, homogenizing with magnetic stirrer, adding ferric salt solution, reacting under magnetic stirring and nitrogen gas for 5 hr, adjusting pH to 2, adding 4g sodium citrate, heating to 80 deg.C, stirring, maintaining for 30min, adding sodium citrate, stirring, and stirringEliminating large agglomerates at 2500rpm, and centrifuging several times at 5650rpm to purify and separate impurities of the sample. Can also directly purchase the commercial gamma-Fe₂O₃Commercial powder, such as nano-gamma-Fe₂O₃。

(4) Compounding the modifier: mixing EDTA, NTA, EDDS and mercaptoethylamine at a mass ratio of 1: 0.05-0.1: 0.1-0.2: 0.2-0.3 uniformly, and dissolving into an aqueous solution to obtain a modifier solution.

(5) Prepared SiO₂Aggregate and magnetic Fe₃O₄And gamma-Fe₂O₃Magnetic material core body (Fe) composed of material₃O₄、γ-Fe₂O₃Mixing according to the mass ratio of 1.5-2: 1, namely Fe³⁺With Fe²⁺The molar ratio of 4:1), uniformly mixing modifier solution according to a certain proportion, precipitating, filtering, drying in a vacuum oven at 50 deg.C for 2-3h, pulverizing (particle diameter)<2mm) to obtain the magnetic soil repairing agent. The mass ratio of the aggregate, the magnetic material core body and the modifier contained in the obtained magnetic soil repairing agent product is 1: 0.05-0.1: 0.005-0.01.

The 4 experimental groups of magnetic soil remediation agent products of the invention were prepared according to the above method, and the specific components and the use amounts of each experimental group are shown in table 1.

TABLE 1

Experimental group	SiO2(g)	Fe3O4(g)	γ-Fe2O3(g)	EDTA(g)	NTA(g)	EDDS(g)	Mercaptoethylamine (g)
								Experimental group 1	100	3	2	0.74	0.04	0.07	0.15
Experimental group 2	100	3.3	1.7	0.69	0.03	0.07	0.21
								Experimental group 3	100	6	4	0.36	0.04	0.04	0.07
Experimental group 4	100	6.6	3.4	0.33	0.03	0.07	0.07

Secondly, analyzing the product components and characterizing XRD

The products prepared in experimental groups 1-4 were subjected to composition analysis and XRD characterization, and the composition analysis results are shown in Table 2:

table 2 composition analysis of magnetic soil remediation agent of the present invention (%)

Experimental group	Fe	CaO	Al2O3	SiO2	Na	K	TOC
								Experimental group 1	4.02	0.82	0.22	90.31	2.52	0.37	1.93
Experimental group 2	3.88	0.79	0.22	90.55	3.15	0.22	1.85
								Experimental group 3	3.95	1.05	0.19	82.49	2.77	0.18	0.96
Experimental group 4	4.30	1.02	0.22	81.50	4.02	0.55	0.95

As can be seen from Table 2, part of organic matters are attached to the product, and the TOC content of the organic matters is about 1-2%, which shows that the amino and the mercapto contained in the modified material are compounded in the magnetic material through modification.

The XRD characteristics of the product are shown in figures 1 and 2, and the experimental parameters/conditions of XRD are as follows: using Cu-KaIrradiating, and analyzing by an X-ray diffractometer to obtain the X-ray diffraction (XRD) peak profile of the magnetic soil remediation agent, and recording an X-ray diffraction pattern at a scanning rate of 0.5 DEG/min within the range of 5-85 deg.

Figure 1 is a drawing of a magnetic iron concentrate product,

fig. 2 shows the magnetic soil remediation agent product of experimental group 1, which is characterized by XRD, and the lattice structure of the product is greatly changed, and compared with the magnetic iron ore concentrate raw material, the magnetic soil remediation agent product of the present invention has representative changes as follows: the peak heights at 26.8 °, 35.3 °, 62.2 ° have significant reductions due to some Fe₃O₄Converted to gamma-Fe₂O₃As a result, 25.1 °, 35.3 ° and 62.2 ° were Fe₃O₄Reaction peak of crystal. gamma-Fe₂O₃Respectively appear at 24.0 °, 26.8 °, 33.1 °, 35.3 °, 35.6 °, 40.8 °, 49.4 °, 62.2 ° and 63.9 °, Fe₃O₄The peaks of (a) appear at 30.1 °, 35.3 °, 43.3 °, 57.1 ° and 62.2 °, respectively. The corresponding hematite and magnetite phases appear in figure 2, indicating the coexistence of these two phases in the material.

The product was tested by infrared analysis under the following conditions (FTIR, Nicolet 6700): mixing magnetic soil repairing agent and KBr particles, tabletting, and scanning resolution ratio of 0.4cm^-1The scanning range is 4000-650 cm^-1. FIG. 3 is an infrared map of the product of Experimental group 1, as seen with the feedstock (i.e., SiO)₂) In contrast, the modified product of the invention has an increased structure of functional groups at wave numbers of 3461, 1637, 1432, 1090 and 795cm^-1Has obvious characteristic peaks of 3461 and 1637cm^-1Tensile peaks at 1432cm for-OH and for the carboxyl group COO- (C ═ O), respectively^-1For the folding peaks of the Fe (III) -modified material complex, 1090 and 795cm^-1The peaks of (A) are respectively expressed as a characteristic absorption peak of silicate and a silicon-oxygen octahedronTensile vibration peak of body, gamma-Fe₂O₃And Fe₃O₄The characteristic peak of (A) appears at 468cm^-1Nearby, mainly Fe-O bond vibration peaks.

Example 2 application of the soil remediation agent of the present invention

First, the study of the pot experiment of the soil repairing agent product of the invention

In order to research the remediation effect of the soil remediation agent on the heavy metal pollution of soil and the influence of the soil remediation agent on the absorption of heavy metals by plants, farmland experiments are carried out by taking pakchoi As an object, and morphological change analysis of heavy metals Pb, Cu, Cr, Cd, Hg and As in soil and the influence on the growth of crops are mainly carried out.

The test method comprises the following steps:

a polluted farmland in a certain large lead-zinc ore mining area is selected to carry out a field plot test, and soil is collected to carry out a culture test and a pot experiment. This experiment prepared two treatments: the control group (without adding the magnetic soil repairing agent of the invention) and the magnetic soil repairing agent treatment group (with different application rates, respectively 50 g/m)²、80g/m²、100g/m²、120g/m²、150g/m²、200g/m²). Each treatment comprises 4 repeating cells, each cell having an area of 20m²(4m × 5m), cells are randomly arranged. The magnetic soil remediation agent (particle diameter) of the experimental group 1 of example 1 was added to the treatment group experimental field 1 week before sowing<2mm) is added into the soil, and is fully mixed with the surface soil (0-10 cm in depth) through manual cultivation, the Chinese cabbage variety 'April Slow' is sowed after one week, and the daily management is carried out according to the conventional field management method of the Chinese cabbage. The fertilization management comprises the following steps: before planting the pakchoi, nitrogen-phosphorus compound fertilizer is applied at a ratio of 225 kg/hectare as base fertilizer, and nitrogen fertilizer is applied within 1 month after planting. And the soil sample collection is respectively carried out before the magnetic soil remediation agent is applied and after the pakchoi is mature, and the pakchoi sample is collected after the pakchoi is mature.

Secondly, the influence of the application of the soil remediation agent on the heavy metals in the soil

(1) Change of soil heavy metal available state and residue state

Detecting the effective states and residue states of heavy metals Pb, Cu, Cr, Cd, Hg and As in the soil after different soil remediation agent application amounts:

the method for detecting the effective state of the heavy metal in the soil comprises the following steps: the effective Pb, Cu, Cr, Cd, Hg and As in soil are measured by leaching with DTPA solution (0.005mol/L DTPA +0.01mol/L CaCl)₂+0.1mol/L triethanolamine TEA), adjusting the pH of the solution to 7.3 +/-0.05, oscillating at 180rpm for 2h at room temperature, fixing the volume of the leaching solution by using 5g/L tartaric acid, filtering by using a 0.45um water system film, measuring the contents of Pb, Cu, Cr and Cd by using a flame atomic absorption spectrophotometer, and measuring the contents of Hg and As by using an atomic fluorescence spectrophotometer.

The detection method of the soil heavy metal effective state residue state comprises the following steps: weighing 0.2000-0.5000 g of residue soil which is air-dried and sieved by a 100-mesh sieve, sequentially adding concentrated nitric acid (6mL), concentrated hydrochloric acid (2mL) and 30% hydrogen peroxide (2mL) into a digestion tank, covering and screwing after bubbles in the digestion tank are eliminated, and putting into a microwave digestion instrument. Heating according to a program, digesting for 30min at 200 ℃, after heating, cooling the digestion tank to room temperature, opening, transferring the digestion solution into a 50mL colorimetric tube, fixing the volume with 5g/L tartaric acid, shaking up, standing, respectively measuring the contents of Pb, Cu, Cr and Cd by a flame atomic absorption spectrophotometer through a 0.45um water system filter membrane, and measuring the contents of Hg and As by an atomic fluorescence spectrophotometer.

The experimental results show that the effective states of Pb, Cu, Cr, Cd, Hg and As in six different metals are added with the soil repairing agent, and the application amount of the repairing agent is 50-150g/m²Within the range, the content of the additive is in a descending trend along with the increase of the application amount, and the descending amplitude of the effective state is gradually increased; the content of the residue state is gradually increased along with the increase of the addition amount of the repairing agent, and the larger the addition amount is, the larger the amplification is. It can be seen that the repairing agent has a remarkable passivation and fixing effect on heavy metals.

At the same time, the application amount of the repairing agent is found to be 150g/m²In the above case, the passivation and fixation effect is not improved any more, but rather, the effect tends to decrease slowly. Therefore, the application amount of the repairing agent can be in the range of 50-200 g/m²More preferably 80 to 150g/m²From cost and effectComprehensively considered, the optimal range is 80-120 g/m²Or 100g/m²。

Wherein the application amount is 0, 50g/m²，100g/m²，200g/m²The test results of the experimental groups are shown in tables 3-8.

TABLE 3 Effect of remediation Agents on the available and residual states of lead in soil

TABLE 4 Effect of remediation Agents on the available and residual copper states in soil

TABLE 5 Effect of remediation Agents on the available and residual states of chromium in soil

TABLE 6 Effect of remediation Agents on the available and residual states of cadmium in soil

TABLE 7 Effect of remediation Agents on the available and residual states of Mercury in soils

TABLE 8 Effect of remediation Agents on the available and residual status of arsenic in soil

As can be seen from tables 3-8, the effective states of Pb, Cu, Cr, Cd, Hg and As in the six different metals are in a descending trend along with the addition of the soil remediation agent within a certain application amount range, and the larger the addition amount of the soil remediation agent is, the larger the reduction is. The content of the residue is gradually increased along with the addition of the repairing agent, and the larger the addition amount is, the larger the amplification is; wherein 100g/m²The effect is best. Therefore, the repairing agent has obvious passivation and fixation effects on heavy metals.

(2) Changes in the form of heavy metals in soil

In order to further research the form change conditions of heavy metals Pb, Cu, Cr, Cd, Hg and As in soil after different application amounts of the repairing agent are applied, the forms of the heavy metals are detected:

the method for analyzing each form of the heavy metal comprises the following steps: the morphological analysis of Pb, Cu, Cr, Cd and Hg in soil is determined by a Tessier method, and the exchangeable state is MgCl with 1mol/L and pH of 7₂Oscillating at room temperature for 1h for leaching; the carbonate combined state is extracted by oscillating NaAc solution with 1mol/L pH value of 5 at room temperature for 6 h; the oxidation state of the ferro-manganese adopts 0.04mol/L NH₂Oscillating the mixed solution of OH & HCl and 25% (v/v) HOAc at 96 +/-3 ℃ for 6h for leaching; the organic combination state adopts 0.02mol/L HNO₃+30％H₂O₂(pH 2) shaking at 85 + -2 deg.C for 2H, and adding 30% H₂O₂Oscillating for 3h at the temperature of 85 +/-2 ℃, and then adding 3.2mol/L of 20% (v/v) HNO₃Oscillating for 30 min; the residue was digested with 3mL of nitric acid and 9mL of hydrochloric acid by microwave.

The As form analysis in the soil adopts Wenel continuous extraction method, and the non-specific adsorption As adopts 0.05mol/L (NH)₄)₂SO₄Oscillating the solution for 4h for leaching; 0.05mol/L (NH) is adopted As the obligate adsorption As₄)H₂PO₄Oscillating the solution for 16h for leaching; amorphous and weakly crystalline water and iron-aluminium oxide As in a bound state is 0.2mol/L (NH4)₂C₂O₄The buffer (pH 3.25) was extracted with shaking in the dark for 4h, centrifuged, filtered, washed with 0.2mol/L (NH4)₂C₂O₄Shaking the buffer (pH 3.25) in dark for 10min, and collecting the supernatant; the crystalline hydrated iron-aluminum oxide binding state As is 0.2mol/L (NH)₄)₂C₂O₄Heating 0.1mol/L ascorbic acid solution in water bath at 96 deg.C for 30min, centrifuging, filtering, and adding 0.2mol/L (NH)₄)₂C₂O₄Washing with buffer (pH 3.25), and extracting under shaking in dark for 10 min; the As residue was digested with 3mL of nitric acid and 9mL of hydrochloric acid by microwave.

The experimental result shows that in the six different metals, the heavy metals of Pb, Cu, Cr, Cd, Hg and As can be transferred and converted, and can be easily absorbed by plants in exchangeable state and carbonate binding state, and the application amount of the repairing agent is 50-150g/m²In the range, the distribution rate of the additive is in a descending trend along with the increase of the addition amount, and the larger the addition amount is, the larger the descending amplitude of the distribution rate is;

at the same time, the application amount of the repairing agent is found to be 150g/m²In the above process, the distribution rate of exchangeable heavy metal and carbonate combined heavy metal is not reduced any more, so the same conclusion is obtained by the same experiment as the change experiment of the effective state and residue state of the heavy metal in the soil, and the application amount range of the repairing agent can be 50-200 g/m²More preferably 80 to 150g/m²In consideration of cost and effect, the optimal range is 80-120 g/m²Or 100g/m². Wherein the application amount is 0, 50g/m²，100g/m²，200g/m²The results of the tests in the experimental groups are shown in tables 9-14.

TABLE 9 Effect of soil remediation Agents on morphological changes in lead

TABLE 10 Effect of soil remediation Agents on copper morphological changes

TABLE 11 Effect of soil remediation Agents on chromium morphological changes

TABLE 12 Effect of soil remediation Agents on morphological changes of cadmium

TABLE 13 Effect of soil remediation Agents on Mercury morphological changes

TABLE 14 Effect of soil remediation Agents on arsenic morphological changes

As can be seen from tables 9-14, among the six different metals, exchangeable states and carbonate binding states capable of being migrated and transformed and easily absorbed by plants in heavy metal forms of Pb, Cu, Cr, Cd, Hg and As show a trend of decreasing distribution rates with the addition of the repairing agent within a certain application rate range, and the larger the addition amount, the larger the decrease of the distribution rate, wherein 100g/m²The effect is best.

Therefore, the repairing agent disclosed by the invention has a remarkable passivation and fixation effect on heavy metals, and can repair the heavy metal contaminated soil. Influence of repairing agent on heavy metal content of crops

The method for detecting the contents of heavy metals Pb, Cr, Cd, Hg and As of plants with different application amounts of the repairing agent comprises the following steps: at nitric acid and 30% H₂O₂Microwave digestion, cooling to room temperature, and diluting to 50m with 5g/L tartaric acidAnd L, measuring the contents of Pb, Cr and Cd by using a flame atomic absorption photometer, and measuring the contents of Hg and As by using a fluorescence photometer.

The results are shown in Table 15.

TABLE 15 influence of amount of soil remediation agent added on the reduction of heavy metal content of plants

Injecting: the "standard" in the table refers to the pollutant limit in national food Standard for food safety (GB 2762-

As can be seen from Table 15, after the soil remediation agent is added, the contents of Pb, Cr, Cd, Hg and As in the pakchoi are all obviously reduced, and the reduction range is gradually increased within a certain application amount range along with the increase of the addition amount of the remediation agent; the application amount is 100g/m²In the left and right experimental groups, the heavy metal content of the plants is reduced below the qualified limit value. The soil remediation agent can obviously inhibit the absorption of heavy metals by plants.