CN107321783B - Method for improving lead-polluted soil - Google Patents

Method for improving lead-polluted soil Download PDF

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Publication number
CN107321783B
CN107321783B CN201710652948.9A CN201710652948A CN107321783B CN 107321783 B CN107321783 B CN 107321783B CN 201710652948 A CN201710652948 A CN 201710652948A CN 107321783 B CN107321783 B CN 107321783B
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lead
parts
soil
fishbone
polluted soil
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CN107321783A (en
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萧师惠
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Research Center Of Shenzhen Taihe Heart Lead Poisoning Prevention
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Research Center Of Shenzhen Taihe Heart Lead Poisoning Prevention
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    • 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

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  • Life Sciences & Earth Sciences (AREA)
  • Soil Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention relates to a method for improving lead contaminated soil, which comprises the following steps: s1: ploughing the lead-polluted soil; s2: spreading fishbone powder in the lead polluted soil treated in the step S1; s3: sprinkling water in the lead polluted soil treated in the step S2, and then uniformly mixing; s4: the surface of the lead-contaminated soil treated in step S3 is covered with a thin film, and the lead-contaminated soil covered with the thin film is fermented. The lead and the fishbone powder are combined to generate phosphorus, chlorine and lead which are harmless to human bodies, so that the active lead in the soil is reduced, and the effect of improving the lead-polluted soil is achieved; the improvement method has low cost, strong operability and wide application range.

Description

Method for improving lead-polluted soil
Technical Field
The invention relates to the technical field of soil improvement, in particular to a method for improving lead-polluted soil.
Background
Soil is the main material base on which human beings rely for survival, but as the activities of mining, smelting, processing and commercial manufacturing of human beings to heavy metals are increasing, heavy metals such as lead enter the soil, and serious environmental pollution is caused. If rice, vegetables and fruits which are seriously polluted by lead are taken for a long time, and water containing excessive cadmium and lead is drunk, chronic poisoning symptoms are easy to appear, the nervous system, the hematopoietic system, the digestive system and the reproductive system of a human body are affected, and the health of the human body is damaged. The existing lead-polluted soil remediation technology mainly comprises a phytoremediation method, an electrodynamic remediation method, a leaching method, a thermal desorption method, a vitrification method, a fixation and stabilization method and the like; among them, the phytoremediation method requires a considerable time and has a problem of plant handling; the electrodynamic remediation is only suitable for small-area pollution and is not easy to operate on site; the leaching method needs to add a surfactant, so that the danger of polluting underground water exists; the thermal desorption method is a method for recovering gas by heating, and is not suitable for field operation, and has the problems of high cost, narrow application range and the like; therefore, there is also a need to develop new lead contamination improvement methods.
Disclosure of Invention
Aiming at the defects in the prior art, the invention aims to provide a method for improving lead-polluted soil, which utilizes the combination of lead and fishbone powder to generate phosphorus-chlorine-lead harmless to human bodies and reduce active lead in the soil, thereby achieving the effect of improving the lead-polluted soil; the improvement method has low cost, strong operability and wide application range.
In order to achieve the purpose, the technical scheme provided by the invention is as follows:
the invention provides a method for improving lead contaminated soil, which comprises the following steps: s1: ploughing the lead-polluted soil; s2: spreading fishbone powder in the lead polluted soil treated in the step S1; s3: sprinkling water in the lead polluted soil treated in the step S2, and then uniformly mixing; s4: the surface of the lead-contaminated soil treated in step S3 is covered with a thin film, and the lead-contaminated soil covered with the thin film is fermented. It should be noted that the plastic film only has the functions of heat preservation and moisture preservation, and is suitable for both thickness and thinness; thick and can be recycled.
In a further embodiment of the present invention, in step S4, the fermentation temperature is 32-40 ℃ and the fermentation time is 15-20 days.
In a further embodiment of the present invention, in step S3, the amount of water sprayed is 80-100 g/kg of soil.
In a further embodiment of the present invention, in step S2, the ratio of the mass of fishbone powder to the mass of lead in the soil is (0.1-0.2): 1. In step S1, the plowing is performed by a deep scarification plowing machine, and the plowing depth is 30-40 cm. It should be noted that, the lead-contaminated soil is collected, the lead-contaminated content is detected, and then the actual usage amount of the fishbone powder is calculated according to the ratio of the scattering quality of the fishbone powder to the mass of the lead in the soil.
In a further embodiment of the present invention, in step S2, the fishbone powder is obtained by pulverizing fishbone to have a particle size of less than 0.1 mm.
In a further embodiment of the present invention, in step S2, the raw material components of the fishbone powder include, by weight: 40-50 parts of fishbone, 3-5 parts of chicken bone, 10-12 parts of pig bone and 1-2 parts of boric acid.
In a further embodiment of the present invention, in step S2, the raw material composition of the fishbone powder further comprises: 5-7 parts of spirulina powder, 2-3 parts of bentonite and 1-2 parts of brown algae powder.
In a further embodiment of the present invention, in step S2, the method for preparing fish bone powder comprises the steps of: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder.
In a further embodiment of the present invention, the method of step S1 to step S4 is cyclically modified a plurality of times according to actual needs.
The technical scheme provided by the invention has the following beneficial effects: (1) the method improves the lead-polluted soil by adopting the fishbone powder, utilizes the combination of lead and the fishbone powder to generate phosphorus-chlorine-lead which is harmless to human bodies, reduces the active lead in the soil, and thus achieves the improvement effect; (2) the method for improving the lead-polluted soil provided by the invention has the advantages of low cost, strong operability and wide application range.
Additional aspects and advantages of the invention will be set forth in part in the description which follows and, in part, will be obvious from the description, or may be learned by practice of the invention.
Detailed Description
The technical solution of the present invention will be clearly and completely described below with reference to the embodiments of the present invention. The following examples are only for illustrating the technical solutions of the present invention more clearly, and therefore are only examples, and the protection scope of the present invention is not limited thereby.
The experimental procedures in the following examples are conventional unless otherwise specified. The test materials used in the following examples were purchased from a conventional store unless otherwise specified. In the quantitative tests in the following examples, three replicates were set, and the data are the mean or the mean ± standard deviation of the three replicates.
The invention provides a method for improving lead contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 30-40 cm;
s2: scattering fishbone powder with the particle size smaller than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering mass of the fishbone powder to the mass of lead in the soil is (0.1-0.2): 1;
wherein the fishbone powder is obtained by pulverizing fishbone to obtain fishbone powder with particle size less than 0.1 mm; or the fishbone powder comprises the following raw material components in parts by weight: 40-50 parts of fishbone, 3-5 parts of chicken bone, 10-12 parts of pig bone and 1-2 parts of boric acid, preferably, 5-7 parts of spirulina powder, 2-3 parts of bentonite and 1-2 parts of brown algae powder, and the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water into the lead-polluted soil treated in the step S2, wherein the sprinkling water amount is 80-100 g/kg of soil, and then uniformly mixing;
s4: and covering a film on the surface of the lead polluted soil treated in the step S3, and fermenting the lead polluted soil covered by the film at the temperature of 32-40 ℃ for 15-20 days.
The method for improving lead-contaminated soil according to the present invention will be further described with reference to the following specific examples.
Example one
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 30 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.1: 1; wherein, the fishbone powder is used for crushing fishbone to obtain fishbone powder with the particle size less than 0.1 mm;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 80g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 32 ℃ for 15 days.
Example two
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 40 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.2: 1; wherein, the fishbone powder is used for crushing fishbone to obtain fishbone powder with the particle size less than 0.1 mm;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 100g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 40 ℃ for 20 days.
EXAMPLE III
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 35 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.15: 1; wherein, the fishbone powder is used for crushing fishbone to obtain fishbone powder with the particle size less than 0.1 mm;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 90g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 36 ℃ for 18 days.
Example four
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 30 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.1: 1; the fish bone powder comprises the following raw material components in parts by weight: 40 parts of fishbone, 5 parts of chicken bone, 10 parts of pig bone and 2 parts of boric acid, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 80g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 32 ℃ for 15 days.
EXAMPLE five
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 40 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.2: 1; the fish bone powder comprises the following raw material components in parts by weight: 50 parts of fishbone, 3 parts of chicken bone, 12 parts of pig bone and 1 part of boric acid, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 100g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 40 ℃ for 20 days.
EXAMPLE six
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 35 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.15: 1; the fish bone powder comprises the following raw material components in parts by weight: 45 parts of fishbone, 4 parts of chicken bone, 11 parts of pig bone and 1.5 parts of boric acid, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 90g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 36 ℃ for 18 days.
EXAMPLE seven
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 30 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.1: 1; the fish bone powder comprises the following raw material components in parts by weight: 40 parts of fishbone, 5 parts of chicken bone, 10 parts of pig bone, 2 parts of boric acid, 5 parts of spirulina powder, 3 parts of bentonite and 1 part of brown algae powder, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 80g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 32 ℃ for 15 days.
Example eight
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 40 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.2: 1; the fish bone powder comprises the following raw material components in parts by weight: 50 parts of fishbone, 3 parts of chicken bone, 12 parts of pig bone, 1 part of boric acid, 7 parts of spirulina powder, 2 parts of bentonite and 2 parts of brown algae powder, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 100g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 40 ℃ for 20 days.
Example nine
The embodiment provides an improvement method of lead-contaminated soil, which comprises the following steps:
s1: ploughing the lead polluted soil by adopting a deep scarification plough, wherein the ploughing depth is 35 cm;
s2: scattering fishbone powder with the particle size of less than 0.1mm in the lead-polluted soil treated in the step S1, wherein the ratio of the scattering quality of the fishbone powder to the mass of lead in the soil is 0.15: 1; the fish bone powder comprises the following raw material components in parts by weight: 45 parts of fishbone, 4 parts of chicken bone, 11 parts of pig bone, 1.5 parts of boric acid, 6 parts of spirulina powder, 2.5 parts of bentonite and 1.5 parts of brown algae powder, wherein the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain fishbone powder;
s3: sprinkling water in the lead polluted soil treated in the step S2, wherein the sprinkling water amount is 90g/kg of soil, and then uniformly mixing;
s4: and (4) covering a film on the surface of the lead-polluted soil treated in the step (S3), and fermenting the lead-polluted soil covered by the film at the temperature of 36 ℃ for 18 days.
The content of active lead in the soil before the improvement of the invention is detected, and the content of active lead in the soil after the improvement by the method provided by the first to ninth embodiments of the invention is detected, and the reduction rate of active lead is calculated, and the specific results are shown in table 1 below.
TABLE 1 statistical results of the reduction rates of active lead
Group of Example one Example two EXAMPLE III
Reduction rate of active lead in soil 57.6% 56.9% 58.2%
Group of Example four EXAMPLE five EXAMPLE six
Reduction rate of active lead in soil 70.3% 70.0% 70.9%
Group of EXAMPLE seven Example eight Example nine
Reduction rate of active lead in soil 81.7% 81.9% 82.6%
It should be noted that, in addition to the cases listed in the first to ninth embodiments, other method parameters may be selected.
The technical scheme provided by the invention has the following beneficial effects: (1) the method improves the lead-polluted soil by adopting the fishbone powder, utilizes the combination of lead and the fishbone powder to generate phosphorus-chlorine-lead which is harmless to human bodies, reduces the active lead in the soil, and thus achieves the improvement effect; (2) the method for improving the lead-polluted soil provided by the invention has the advantages of low cost, strong operability and wide application range.
It is to be noted that, unless otherwise specified, technical or scientific terms used herein shall have the ordinary meaning as understood by those skilled in the art to which the invention pertains. Unless specifically stated otherwise, the relative steps, numerical expressions, and values of the components and steps set forth in these embodiments do not limit the scope of the present invention. In all examples shown and described herein, unless otherwise specified, any particular value should be construed as merely illustrative, and not restrictive, and thus other examples of example embodiments may have different values.
In the description of the present invention, it is to be understood that the terms "first", "second" and the like are used for descriptive purposes only and are not to be construed as indicating or implying relative importance or implying any number of technical features indicated. Thus, a feature defined as "first" or "second" may explicitly or implicitly include one or more of that feature. In the description of the present invention, "a plurality" means two or more unless specifically defined otherwise.
Finally, it should be noted that: the above embodiments are only used to illustrate the technical solution of the present invention, and not to limit the same; while the invention has been described in detail and with reference to the foregoing embodiments, it will be understood by those skilled in the art that: the technical solutions described in the foregoing embodiments may still be modified, or some or all of the technical features may be equivalently replaced; the modifications or the substitutions do not make the essence of the corresponding technical solutions depart from the scope of the technical solutions of the embodiments of the present invention, and all of the technical solutions are covered in the protective scope of the present invention.

Claims (6)

1. The method for improving the lead-polluted soil is characterized by comprising the following steps of:
s1: ploughing the lead-polluted soil;
s2: spreading fishbone powder in the lead polluted soil treated in the step S1;
s3: sprinkling water in the lead polluted soil treated in the step S2, and then uniformly mixing;
s4: covering a film on the surface of the lead-polluted soil treated in the step S3, and fermenting the lead-polluted soil covered by the film;
in step S2, the fishbone powder comprises the following raw material components in parts by weight: 40-50 parts of fishbone, 3-5 parts of chicken bone, 10-12 parts of pig bone and 1-2 parts of boric acid, and the feed also comprises: 5-7 parts of spirulina powder, 2-3 parts of bentonite and 1-2 parts of brown algae powder; the ratio of the sowing quality of the fishbone powder to the quality of lead in the soil is (0.1-0.2): 1.
2. The method for improving lead-contaminated soil according to claim 1, wherein:
in the step S4, the fermentation temperature is 32-40 ℃, and the fermentation time is 15-20 days.
3. The method for improving lead-contaminated soil according to claim 1, wherein:
in step S3, the water spraying amount is 80-100 g/kg soil.
4. The method for improving lead-contaminated soil according to claim 1, wherein:
in step S1, the plowing is performed by a deep scarification plowing machine, and the plowing depth is 30-40 cm.
5. The method for improving lead-contaminated soil according to claim 1, wherein:
in step S2, the preparation method of the fishbone powder comprises the following steps: pulverizing fishbone, chicken bone and pig bone to obtain mixed powder with particle size less than 0.1mm, adding other rest raw materials, and mixing to obtain the fishbone powder.
6. The method for improving lead-contaminated soil according to claim 1, wherein:
according to actual needs, the method from step S1 to step S4 is circularly improved for a plurality of times.
CN201710652948.9A 2017-08-02 2017-08-02 Method for improving lead-polluted soil Expired - Fee Related CN107321783B (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101928179A (en) * 2009-06-19 2010-12-29 深圳市意可曼生物科技有限公司 Slow release fertilizer having soil remediation function and soil contamination remediation method
CN103740373A (en) * 2013-12-09 2014-04-23 浙江省环境保护科学设计研究院 Stabilizing agent for heavy metal contaminated soil and preparation method and application thereof
CN106085450A (en) * 2016-06-17 2016-11-09 战锡林 Heavy-metal contaminated soil repair materials
CN106345803A (en) * 2016-10-31 2017-01-25 湖南科技学院 Soil disinfection and soil restoration method
CN106391691A (en) * 2016-08-31 2017-02-15 云南能投生态环境科技有限公司 Method for efficiently remedying heavy-metal-contaminated soil
CN106825007A (en) * 2016-12-06 2017-06-13 广州富生源环保工程有限公司 A kind of method for administering heavy-metal contaminated soil

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101928179A (en) * 2009-06-19 2010-12-29 深圳市意可曼生物科技有限公司 Slow release fertilizer having soil remediation function and soil contamination remediation method
CN103740373A (en) * 2013-12-09 2014-04-23 浙江省环境保护科学设计研究院 Stabilizing agent for heavy metal contaminated soil and preparation method and application thereof
CN106085450A (en) * 2016-06-17 2016-11-09 战锡林 Heavy-metal contaminated soil repair materials
CN106391691A (en) * 2016-08-31 2017-02-15 云南能投生态环境科技有限公司 Method for efficiently remedying heavy-metal-contaminated soil
CN106345803A (en) * 2016-10-31 2017-01-25 湖南科技学院 Soil disinfection and soil restoration method
CN106825007A (en) * 2016-12-06 2017-06-13 广州富生源环保工程有限公司 A kind of method for administering heavy-metal contaminated soil

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