NL2033491B1 - Device and method for remediation of heavy metals in cultivated land soil by strengthening sedum plumbizincicola with biochar combined with microorganism - Google Patents
Device and method for remediation of heavy metals in cultivated land soil by strengthening sedum plumbizincicola with biochar combined with microorganism Download PDFInfo
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- B09C1/00—Reclamation of contaminated soil
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- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
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Abstract
Disclosed is a device and a method for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism, and relates to the technical field of soil remediation devices and methods, to solve the problem that there are no devices and methods for soil remediation in the market at present. Step 1: collecting calcareous soil and yellow soil; step 2: selecting lettuce and water spinach, and selecting Thiobaci/Ius ferrooxidans; step 3: removing stones and animal and plant residues, and then drying them in the shade respectively; crushing and sieving the soil by the soil crushing mechanism; step 4: filling each pot with soil and biomass charcoal to be tested, and mixing evenly for later use; step 5: cultivating three vegetable seedlings in each pot, applying corresponding proportions of bacterial solutions and three Sedum plumbizincicola to the pot, cultivating vegetable seedlings and Sedum plumbizincicola by the cultivation mechanism, and harvesting the vegetables after they grow for about 80 days; and step 6: harvesting vegetables and Sedum plumbizincicola at the same time, respectively crushing vegetables and Sedum plumbizincicola dry samples for testing; drying rhizosphere soil in the shade, sieving and testing.
Description
DEVICE AND METHOD FOR REMEDIATION OF HEAVY METALS IN CULTIVATED
LAND SOIL BY STRENGTHENING SEDUM PLUMBIZINCICOLA WITH BIOCHAR
COMBINED WITH MICROORGANISM
The invention relates to the technical field of soil remediation devices and methods, and in particular to a device and a method for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism.
Soil remediation is a technical measure to restore the polluted soil to normal functions. In the soil remediation industry, there are more than one hundred kinds of soil remediation technologies, and there are more than ten kinds of commonly used technologies; the technologies are roughly divided into three methods: physical, chemical and biological. Since 1980s, many countries in the world, especially developed countries, have formulated and carried out plans for the treatment and remediation of contaminated soil, thus forming a new soil remediation industry. At present, there are many remediation methods of heavy metals in soil theoretically, but they are all quite expensive, cause great damage to soil vegetation, soil structure and soil microbial environment, and also easily lead to “secondary pollution”. biochar combined with microorganism is a green and environment-friendly remediation method for heavy metals in cultivated soil, and has been widely recognized in recent years. biochar is a kind of highly aromatic and refractory solid material produced by pyrolysis and carbonization of biomass under complete or partial anoxic conditions. Due to its large specific surface area and surface functional groups, biochar fixes heavy metals, and has strong adsorption capacity; it adsorbs available heavy metals in the surrounding soil. At the same time, the surface space of biochar provides a habitat for microorganisms, and this is conducive to the growth of soil microorganisms. So far, it is considered as an environmental-friendly and promising green treatment technology to use microorganisms and biochar to jointly control soil heavy metals.
At present, plant intercropping remediation technology has become a hot research topic to solve the problem that single planting of hyperaccumulator affects remediation effect. Sedum plumbizincicola, a new species of Crassulaceae family plant, is also a hyperaccumulator of heavy metals found in mining areas of China. For example, using Apium graceolens and Sedum plumbizincicola intercropping to repair Cd-polluted soil, the Cd content in Apium graceolens meets the food hygiene standard, and the Cd concentration in Sedum plumbizincicola intercropping is 37.4 times that of monoculture. It is an economical and effective way to remediate heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar and microorganism, and it not only improves remediation effect, but also meets the goal of safe production of crops. The technology has low cost, little negative impact on soil fertilizer and metabolic activity, and avoids the impact of heavy metal pollutants migrating to the environment and human body. Therefore, from the perspective of pollution remediation and the quality and safety of agricultural products, it is of great significance to remediate heavy metals in cultivated soil by strengthening Sedum plumbizincicola with biochar and microorganism, and solve the problem of remediation and improvement of contaminated soil. At present, there is no remediation device and method aiming at this remediation technology in the market, so the device and method for remediation of heavy metals in cultivated land soil by strengthening
Sedum plumbizincicola with biochar combined with microorganism are urgently needed in the market to solve these problems.
The objective of the present invention is to provide a device and a method for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism, so as to solve the problems in the background that there are no devices or methods for soil remediation in the market at present.
In order to achieve the above objective, the technical scheme provided by the invention is as follows: a device for remediation of heavy metals in cultivated land soil by strengthening
Sedum plumbizincicola with biochar combined with microorganism includes a cultivation mechanism and a soil crushing mechanism, wherein a lower end of the cultivation mechanism is provided with a support seat, and an upper part of the support seat is provided with cultivation frames at equal intervals; four corners of each cultivation frame and four corners of the upper end of each support seat are provided with fixing rod connecting sleeves, and fixing rod slots are arranged in the fixing rod connecting sleeves; fixing rods are arranged between the cultivation frame, the support seat and adjacent cultivation frames, two light-filling lamps are symmetrically arranged on both sides of a lower end of each cultivation frame, and water nozzles are arranged between adjacent light-filling lamps; a brightness sensor is arranged at one side of the water nozzle in the middle position, and the brightness sensor is electrically connected with the light-filling lamps; five cultivation pots are arranged in the upper end of the cultivation frames at equal intervals, and the cultivation pots are correspondingly arranged with the water nozzles; soil moisture sensors are arranged in the cultivation pots, one side inside the soil crushing mechanism is fixedly provided with a fixed crushing plate, the other side inside the soil crushing mechanism is slidably provided with a sliding crushing plate, opposite sides of the soil crushing mechanism and the fixed crushing plate are both provided with crushing clamping plates, and the two crushing clamping plates are meshed; a sieve tray is obliquely arranged below the fixed crushing plate of the soil crushing mechanism.
Preferably, upper and lower ends of each fixing rod are fixedly connected with the fixing rod slots through clamping grooves, a front end of one side of each cultivation frame is provided with a first magnetic block, and a rear end of the other side of the cultivation frame is provided with a second magnetic block.
Preferably, a front end of the other side of the cultivation frame is provided with a first magnetic block groove, and the first magnetic block groove is correspondingly arranged with the first magnetic block; a rear end of one side of the cultivation frame is provided with a second magnetic block groove, and the second magnetic block groove is correspondingly arranged with the second magnetic block.
Preferably, a water tank is arranged below the cultivation pots, and the water tank is communicated with the water nozzles.
Preferably, the sieve tray is fixedly connected with an inner wall of the soil crushing mechanism, a discharging conveyor belt and a material receiving basin are arranged below the sieve tray, and the discharging conveyor belt is located at one side of the material receiving basin; a filter plate is arranged inside the sieve tray; and a filter strip groove is arranged inside one side of the filter plate; the filter strip groove is positioned above the discharging conveyor belt, and another end of the filter plate is located above the material receiving basin; an outer end of the sieve tray is provided with a sieve tray frame; and one end of the sieve tray close to the material receiving basin inclines downwards.
Preferably, one side of the sliding crushing plate is provided with a crushing motor, an output end of the crushing motor is provided with a driving disc, a transmission rod is arranged between the driving disc and the sliding crushing plate, and two ends of the transmission rod are respectively connected with the driving disc and the sliding crushing plate in a rotary way.
Preferably, upper and lower ends of one side of the sliding crushing plate are provided with sliding blocks, two sides of the soil crushing mechanism are symmetrically provided with two sliding chutes, the sliding chutes are connected with the sliding blocks in a sliding way, and upper ends of the fixed crushing plate and the sliding crushing plate are provided with material guide plates.
A method for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism, including the following steps: step 1: collecting calcareous soil and yellow soil widely distributed in cultivated land as test soil; step 2: selecting lettuce of leafy vegetables and water spinach of rhizomes for the experiment, selecting Thiobacillus ferrooxidans with strong tolerance to heavy metals as the test microorganism, selecting peanut hull straw as biomass charcoal raw material at carbonization temperature of 350 - 500°C, and passing through a 2 mm sieve; step 3: removing stones and animal and plant residues from the yellow soil and calcareous soil to be tested, and then drying them in the shade respectively; crushing and sieving the soil by the soil crushing mechanism; the crushing motor driving the driving disc to rotate, and a lug at the front end of the driving disc being rotationally connected with the transmission rod; when the lug rotates in a circle, the transmission rod driving the sliding crushing plate to slide inside the soil crushing mechanism, and crushing the soil by two meshing crushing clamping plates; the crushed soil falling on the discharging conveyor belt through the filter strip groove, and the unfiltered large size soil particles falling inside the material receiving basin; step 4: setting biochar at six levels, namely, 0%, 4%, 6%, 8%, 10% and 20% biomass charcoal, and they are referred to as charcoal zero, charcoal one, charcoal two, charcoal three, charcoal four and charcoal five for short; filling each pot with 4 kg of soil and biomass charcoal, and filling each pot with a corresponding amount of soil and biomass charcoal according to the experimental design, and mixing evenly for later use; step 5: placing the mixed soil in a cultivation pot of a cultivation mechanism, and cultivating three vegetable seedlings in each pot; setting Thiobacillus ferrooxidans at six levels, namely, O ml, 10 ml, 20 ml, 40 ml, 60 ml and 80 ml bacterial solutions, and they are referred to as bacteria zero, bacteria one, bacteria two, bacteria three, bacteria four and bacteria five for short; according to the experimental design, applying corresponding proportions of bacterial solutions and three Sedum plumbizincicola to the pot; cultivating vegetable seedlings and
Sedum plumbizincicola by the cultivation mechanism, planting the vegetable seedlings and
Sedum plumbizincicola in the soil of a cultivation pot, adjusting the brightness of the light-filling lamp by the brightness sensor according to the brightness of the light received by the plant to fill the light for the vegetable seedlings, monitoring the soil humidity by a soil humidity sensor, and adjusting water nozzles to spray water, and harvesting the vegetables after they grow for about 80 days; and step 6: harvesting vegetables and Sedum plumbizincicola at the same time, washing and drying at 80°C, respectively crushing vegetables and Sedum plumbizincicola dry samples for testing; drying rhizosphere soil in the shade, sieving and testing.
Compared with the prior art, the invention has the following advantages.
Firstly, the invention deals with the soil polluted by heavy metals by using several technologies of biomass charcoal, Thiobacillus ferrooxidans, Sedum plumbizincicola and combined treatment of three methods, studies the distribution characteristics, migration and transformation rules of heavy metals in the soil-vegetable system under different treatment methods, and evaluates the inhibition and control effect of biomass charcoal, microorganisms and repair plants on heavy metals in soil and their effects on biomass, nutrient elements and heavy metals Cr, As, Cd, Pb and Hg of vegetables. Finally, the invention selects an appropriate technical scheme for soil heavy metal treatment in karst areas. The charcoal-bacteria combined technology has the largest impact on vegetable biomass accumulation and total biomass, followed by soil type and vegetable type; the charcoal-bacteria combined technology has the greatest impact on total N and total P of vegetables, and biomass charcoal has the greatest impact on total K of vegetables; the charcoal-bacteria combined technology has the greatest impact on the heavy metals Cr, As, Cd, Pb, Hg in vegetables; in a word, the charcoal-bacteria combined technology has a significant impact on many indicators of vegetables, and the charcoal-bacteria combined technology is a more appropriate composite repair technology.
Secondly, in the invention, the cultivation mechanism automatically replenishes water and light to promote the growth of Sedum plumbizincicola and accelerate the repair the soil polluted 5 by heavy metals, thereby improving the repair effect of the soil; the cultivation frame, support seat and fixed rod are spliced together to facilitate the loading, unloading and carrying of the device. At the same time, the correspondence of the first magnetic block and the second magnetic block with the second magnetic block groove and the first magnetic block groove realizes the splicing of multiple cultivation institutions, the soil crushing mechanism shall first crush and screen the soil before remediation, so that the remediation microorganisms, biochar and Sedum plumbizincicola fully absorb heavy metals.
Fig. 1 is a front view of the cultivation mechanism in the present invention.
Fig. 2 is a plan view of the cultivation frame in the present invention.
Fig. 3 is a bottom view of the cultivation frame in the present invention.
Fig. 4 is a cross-sectional view of Fig. 1 taken along A-A in the present invention.
Fig. 5 is a cross-sectional view of Fig. 2 taken along the B-B direction in the present invention.
Fig. 6 is a structural diagram of the soil crushing mechanism in the present invention.
Fig. 7 is a perspective view of the sieve tray of the present invention.
Fig. 8 is a side view of the sliding crushing plate in the present invention.
In the figures: 1. cultivation frame; 2. support seat; 3. fixing rod; 4. light-filling lamp; 5. cultivation pot; 6. fixing rod slot; 7. first magnetic block; 8. second magnetic block; 9. cultivation mechanism; 10. brightness sensor; 11. water nozzle; 12. water tank; 13. second magnetic block groove; 14. first magnetic block groove; 15. fixing rod connecting sleeve; 18. soil moisture sensor; 17. soil crushing mechanism; 18. fixed crushing plate; 19. sliding crushing plate; 20. crushing clamping plate; 21. driving disc; 22. crushing motor; 23. transmission rod; 24. sliding chute; 25. sieve tray; 26. discharging conveyor belt; 27. material receiving basin; 28. filter strip groove; 29. filter strip groove; 30. filter plate; 31. material guide plate; 32. sliding block.
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, but not all of them.
Referring to figures 1 - 8, the invention provides an embodiment: a device for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism includes a cultivation mechanism 9 and a soil crushing mechanism 17, wherein a lower end of the cultivation mechanism 9 is provided with a support seat 2, and an upper part of the support seat 2 is provided with cultivation frames 1 at equal intervals; four corners of each cultivation frame 1 and four corners of the upper end of each support seat 2 are provided with fixing rod connecting sleeves 15, and fixing rod slots 6 are arranged in the fixing rod connecting sleeves 15; fixing rods 3 are arranged between the cultivation frame 1, the support seat 2 and adjacent cultivation frames 1, two light-filling lamps 4 are symmetrically arranged on both sides of a lower end of each cultivation frame 1, and water nozzles 11 are arranged between adjacent light-filling lamps 4; a brightness sensor 10 is arranged at one side of the water nozzle 11 in the middle position, and the brightness sensor 10 is electrically connected with the light-filling lamps 4; five cultivation pots 5 are arranged in the upper end of the cultivation frames 1 at equal intervals, and the cultivation pots 5 are correspondingly arranged with the water nozzles 11; soil moisture sensors 16 are arranged in the cultivation pots 5, one side inside the soil crushing mechanism 17 is fixedly provided with a fixed crushing plate 18, the other side inside the soil crushing mechanism 17 is slidably provided with a sliding crushing plate 19, opposite sides of the soil crushing mechanism 17 and the fixed crushing plate 18 are both provided with crushing clamping plates 20, and the two crushing clamping plates 20 are meshed; a sieve tray 25 is obliquely arranged below the fixed crushing plate 18 of the soil crushing mechanism 17.
Further, upper and lower ends of each fixing rod 3 are fixedly connected with the fixing rod slots 6 through clamping grooves, a front end of one side of each cultivation frame 1 is provided with a first magnetic block 7, and a rear end of the other side of the cultivation frame 1 is provided with a second magnetic block 8.
Further, a front end of the other side of the cultivation frame 1 is provided with a first magnetic block groove 14, and the first magnetic block groove 14 is correspondingly arranged with the first magnetic block 7; a rear end of one side of the cultivation frame 1 is provided with a second magnetic block groove 13, and the second magnetic block groove 13 is correspondingly arranged with the second magnetic block 8.
Further, a water tank 12 is arranged below the cultivation pots 5, and the water tank 12 is communicated with the water nozzles 11.
Further, the sieve tray 25 is fixedly connected with an inner wall of the soil crushing mechanism 17, a discharging conveyor belt 26 and a material receiving basin 27 are arranged below the sieve tray 25, and the discharging conveyor belt 26 is located at one side of the material receiving basin 27; a filter plate 30 is arranged inside the sieve tray 25; and a filter strip groove 29 is arranged inside one side of the filter plate 30; the filter strip groove 29 is positioned above the discharging conveyor belt 26, and another end of the filter plate 30 is located above the material receiving basin 27; an outer end of the sieve tray 25 is provided with a sieve tray frame 28; and one end of the sieve tray 25 close to the material receiving basin 27 inclines downwards.
Further, one side of the sliding crushing plate 19 is provided with a crushing motor 22, an output end of the crushing motor 22 is provided with a driving disc 21, a transmission rod 23 is arranged between the driving disc 21 and the sliding crushing plate 19, and two ends of the transmission rod 23 are respectively connected with the driving disc 21 and the sliding crushing plate 19 in a rotary way.
Further, upper and lower ends of one side of the sliding crushing plate 19 are provided with sliding blocks 32, two sides of the soil crushing mechanism 17 are symmetrically provided with two sliding chutes 24, the sliding chutes 24 are connected with the sliding blocks 32 in a sliding way, and upper ends of the fixed crushing plate 18 and the sliding crushing plate 19 are provided with material guide plates 31.
A method of the device for remediation of heavy metals in cultivated land soil by strengthening Sedum plumbizincicola with biochar combined with microorganism includes the following steps: step 1: collecting calcareous soil and yellow soil widely distributed in cultivated land as test soil; physical and chemical properties of tested soil are shown in the following table:
Types Cr(mg/kg) As{(mg/kg) Cd(mg/kg) Pb(mg/kg) Hg(mg/kg) ‘calcareous soil 34.12 16.68 0.12 23.60 0.13
Yellow soil 64.12 56.68 0.32 52.60 0.33 step 2: selecting lettuce of leafy vegetables and water spinach of rhizomes for the experiment, selecting Thiobacillus ferrooxidans with strong tolerance to heavy metals as the test microorganism, selecting peanut hull straw as biomass charcoal raw material at carbonization temperature of 350 - 500°C, and passing through a 2 mm sieve; the strains provided by Shanghai Biological Network Microbial Culture Collection Center (RCCC) are described as follows:
Name of Date of Preservation Validity Incubation Incubation
Thiobacillus Storing at - physical and chemical properties of biomass charcoal are shown in the following table:
charcoal potassium step 3: removing stones and animal and plant residues from the yellow soil and calcareous soil to be tested, and then drying them in the shade respectively; crushing and sieving the soil by the soil crushing mechanism 17; the crushing motor 22 driving the driving disc 21 to rotate, and a lug at the front end of the driving disc 21 being rotationally connected with the transmission rod 23; when the lug rotates in a circle, the transmission rod 23 driving the sliding crushing plate 19 to slide inside the soil crushing mechanism 17, and crushing the soil by two meshing crushing clamping plates 20; the crushed soil falling on the discharging conveyor belt 26 through the filter strip groove 29, and the unfiltered large size soil particles falling inside the receiving basin 27; step 4: setting biochar at six levels, namely, 0%, 4%, 6%, 8%, 10% and 20% biomass charcoal, and they are referred to as charcoal zero, charcoal one, charcoal two, charcoal three, charcoal four and charcoal five for short; filling each pot with 4 kg of soil and biomass charcoal, and filling each pot with a corresponding amount of soil and biomass charcoal according to the experimental design, and mixing evenly for later use; step 5: placing the mixed soil in a cultivation pot 5 of a cultivation mechanism 9, and cultivating three vegetable seedlings in each pot; setting Thiobacillus ferrooxidans at six levels, namely, O ml, 10 ml, 20 ml, 40 ml, 60 ml and 80 ml bacterial solutions, and they are referred to as bacteria zero, bacteria one, bacteria two, bacteria three, bacteria four and bacteria five for short; according to the experimental design, applying corresponding proportions of bacterial solutions and three Sedum plumbizincicola to the pot; cultivating vegetable seedlings and
Sedum plumbizincicola by the cultivation mechanism 9, planting the vegetable seedlings and
Sedum plumbizincicola in the soil of a cultivation pot 5, adjusting the brightness of the light- filling lamp 4 by the brightness sensor 10 according to the brightness of the light received by the plant to fill the light for the vegetable seedlings, monitoring the soil humidity by a soil humidity sensor 16, and adjusting water nozzles 11 to spray water, and harvesting the vegetables after they grow for about 80 days;
The experimental orthogonal design of biomass charcoal- Thiobacillus ferrooxidans-Sedum plumbizincicola combined application to control heavy metals in soil is shown in the following table:
van tin
Appli- 9 / quan cation
Whether tity Plan-
Bio- Biomass amount to inter- of Vege- ting
Soil pot mass charcoal of
Treat Soil crop Sedu table amount loading char- pot Thioba- / ment type / / Sedum m varie- of vege- kg coal loading/ cillus == / / plumbizi plum ties tables/ ratio/% kg ferro- / ncicola ~~ bizin plant oxidans / cicol /ml a/pla nt
Calcare 1 / 3.76 6 0.24 10 Yes 3 Lettuce 3 ous soil
Yellow Water 2 3.68 8 0.32 10 Yes 3 3 soil spinach
Calcare 3 / 4 0 -- 0.5 No -- Lettuce 3 ous soil
Yellow Water 4 3.6 10 0.4 0.5 Yes 3 3 soil spinach
Yellow Water 3.2 20 0.8 20 Yes 3 3 soil spinach
Yellow Water 6 3.84 4 0.16 0 Yes 3 3 soil spinach
Yellow 7 / 3.2 20 0.8 0 Yes 3 Lettuce 3 soil
Calcare 8 / 3.68 8 0.32 c No -- Lettuce 3 ous sail
Yellow 9 / 3.84 4 0.16 1 No -- Lettuce 3 soil
Yellow / 4 0 -- c No -- Lettuce 3 sail
Yellow Water 11 3.76 6 0.24 0 No -- 3 soil spinach
Calcare Water 12 4 0 -- 1 Yes 3 3 ous soil spinach
Calcare 13 / 4 0 -- 5 Yes 3 Lettuce 3 ous soil
Calcare 14 / 3.84 4 0.16 0 Yes 3 Lettuce 3 ous soil
Calcare / 3.6 10 0.4 0 Yes 3 Lettuce 3 ous soil
Calcare Water 16 3.68 8 0.32 1 Yes 3 3 ous soil spinach
Yellow 17 / 3.76 6 0.24 1 No -- Lettuce 3 soil
Yellow Water 18 3.6 10 0.4 10 No -- 3 soil spinach
Yellow 19 / 4 0 -- 5 Yes 3 Lettuce 3 soil
Calcare Water 4 0 -- 20 Yes 3 3 ous soil spinach
Yellow Water 21 3.84 4 0.16 0.5 Yes 3 3 soil spinach
Calcare 22 / 3.68 8 0.32 20 No -- Lettuce 3 ous soil
Yellow 23 / 4 0 -- 0.5 Yes 3 Lettuce 3 soil
Yellow 24 / 3.78 6 0.24 0 Yes 3 Lettuce 3 soil
Calcare Water 3.2 20 0.8 0.5 No -- 3 ous soil spinach
Yellow 26 / 4 0 -- 20 No -- Lettuce 3 soil
Calcare Water 27 3.84 4 0.16 5 No -- 3 ous soil spinach
Yellow 28 / 3.68 8 0.32 5 Yes 3 Lettuce 3 soil
Calcare Water 29 4 0 -- 1 No -- 3 ous soil spinach
Yellow / 3.2 20 0.8 1 No -- Lettuce 3 soil
Yellow 31 / 3.84 4 0.16 20 No -- Lettuce 3 soil
Calcare Water 32 4 0 -- 0 No -- 3 ous soil spinach
Yellow 33 / 3.6 10 0.4 1 Yes 3 Lettuce 3 soil
Yellow 34 / 3.68 8 0.32 0.5 No -- Lettuce 3 soil
Calcare / 3.2 20 0.8 0 Yes 3 Lettuce 3 ous soil
Yellow Water 36 3.2 20 0.8 5 No -- 3 soil spinach
Yellow 37 / 3.6 10 0.4 20 No -- Lettuce 3 soil
Yellow Water 38 3.68 8 0.32 0 No -- 3 soil spinach
Yellow Water 39 3.76 6 24 5 No -- 3 soil spinach
Yellow / 4 0 -- 0 No -- Lettuce 3 soil
Yellow Water 41 4 0 == 0 No -- 3 soil spinach
Yellow Water 42 4 0 -- 10 No -- 3 soil spinach
Yellow 43 4 0 -- 10 Yes 3 Lettuce 3 soil
Calcare 44 3.76 6 0.24 0.5 No -- Lettuce 3 ous soil
Calcare 45 3.6 10 0.4 5 No -- Lettuce 3 ous soil
Calcare Water 46 3.6 10 0.4 0 No -- 3 ous soil spinach
Calcare 47 3.84 4 0.16 10 No -- Lettuce 3 ous soil
Calcare Water 48 3.76 6 0.24 20 Yes 3 3 ous soil spinach
Calcare 49 3.2 20 0.8 10 No -- Lettuce 3 ous soil step 6: harvesting vegetables and Sedum plumbizincicola at the same time, washing and drying at 60°C, respectively crushing vegetables and Sedum plumbizincicola dry samples for testing; drying rhizosphere soil in the shade, sieving and testing.
Experimental results of combined application of biomass charcoal- Thiobacillus ferrooxidans-Sedum plumbizincicola to control heavy metals in soil
Analysis of the effects of different compound remediation technologies on vegetable biomass
Taking charcoal (Tan), bacteria (Jun) and Sedum plumbizincicola (JT) indicators as fixed factors, soil type (Tu) and vegetable type (ZW) indicators as covariates, and vegetable dry weight and total biomass (vegetables+Sedum plumbizincicola) indicators as dependent variables, carrying out the multivariate general linear model analysis by SPSS19.0 to study the effects of charcoal, bacteria and Sedum plumbizincicola compound technology on the dry weight and total biomass of vegetables.
From the test results of inter-body effect, it can be seen that the significant P values of soil type, vegetable type, different proportion of charcoal, intercropping Sedum plumbizincicola or not and charcoal-bacteria combination on the dry weight of vegetables are all less than 0.05,
indicating that these items have significant effects on the dry weight of vegetables; soil type, vegetable type, different proportion of bacteria, Sedum plumbizincicola or not and bacteria-
Sedum plumbizincicola combination have a significant P value of less than 0.05, indicating that these factors have a significant impact on the total biomass.
Analysis of the effects of each index shows that the charcoal-bacteria combination technology has the greatest impact on vegetable biomass and total biomass, with its effects of 28.45% and 23.82% respectively, followed by the soil type index with its effects of 20% and 13.53% respectively. However, on the whole, the combined technologies of bacteria-Sedum plumbizincicola, charcoal-Sedum plumbizincicola and charcoal-bacteria-Sedum plumbizincicola have little effect on vegetables and total biomass.
Effect quantity analysis of different compound remediation technologies on heavy metal content in vegetables
Taking charcoal (Tan), bacteria (Jun) and Sedum plumbizincicola (JT) indicators as fixed factors, soil type (Tu) and vegetable type (ZW) indicators as covariates, and vegetable heavy metals (Cr, As, Cd, Pb, Hg) as dependent variables, and carrying out the multivariate general linear model analysis by SPSS19.0 to study the effects of charcoal, bacteria and Sedum plumbizincicola compound technology on heavy metals Cr, As, Cd, Pb and Hg in vegetables.
From the test results of inter-body effect, it can be seen that the significant P values of vegetable types, biomass charcoal, Thiobacillus ferrooxidans, charcoal-bacteria, charcoal-
Sedum plumbizincicola and bacteria-Sedum plumbizincicola combination on Cr in vegetables are all less than 0.05, indicating that these items have significant effects on Cr enrichment in vegetables; soil type, biomass charcoal, Thiobacillus ferrooxidans, intercropping Sedum plumbizincicola or not, charcoal-bacteria, charcoal-Sedum plumbizincicola and bacteria-Sedum plumbizincicola combination all have significant P values less than 0.05, indicating that these factors have significant effects on the enrichment of As in vegetables; the significant P values of vegetable types, biomass charcoal, Thiobacillus ferrooxidans, intercropping Sedum plumbizincicola or not and charcoal-bacteria on Cd in vegetables are all less than 0.05, indicating that these factors have significant effects on Cd enrichment in vegetables; the significant P values of soil type, biomass charcoal, Thiobacillus ferrooxidans, intercropping
Sedum plumbizincicola or not, charcoal-bacteria, charcoal-Sedum plumbizincicola and bacteria-
Sedum plumbizincicola combination are all less than 0.05, indicating that these factors have significant effects on Pb enrichment in vegetables; the significant P values of soil type, biomass charcoal, Thiobacillus ferrooxidans, charcoal-bacteria and charcoal-Sedum plumbizincicola on
Hg in vegetables are all less than 0.05, indicating that these factors have significant effects on
Hg enrichment in vegetables.
Through the analysis of the effects of each index, it is found that carbon-bacteria combined technology has the greatest impact on heavy metals Cr, As, Cd, Pb and Hg in vegetables, and the effects are 78%, 74%, 50%, 66% and 54% respectively. Among other combined technologies, the combination of bacteria and Sedum plumbizincicola has a great influence on the Cr of vegetables, with an effective amount of 49%, and the combination of carbon and
Sedum plumbizincicola has a great influence on the Cr, As, Pb and Hg of vegetables. It can be seen that the combined application of several technologies greatly affects the enrichment of heavy metals in vegetables.
Experimental conclusion
Experimental conclusion of combined application of biomass charcoal- Thiobacillus ferrooxidans-Sedum plumbizincicola
Charcoal-bacteria combination technology has the greatest influence on the biomass accumulation and total biomass of vegetables, followed by soil types and vegetable types; charcoal-bacteria combination technology has the greatest influence on total N and total P of vegetables, and biomass charcoal has the greatest influence on total K of vegetables; charcoal- bacteria combination technology has the greatest influence on heavy metals Cr, As, Cd, Pb and
Hg in vegetables; on the whole, the charcoal-bacteria combination technology has a significant impact on many indexes of vegetables, and the charcoal-bacteria combination technology is a suitable compound remediation technology.
It is obvious to those skilled in the art that the present invention is not limited to the details of the above exemplary embodiments, but is implemented in other specific forms without departing from the spirit or essential characteristics of the present invention. Therefore, the embodiments should be regarded as illustrative and non-restrictive in all respects. The scope of the invention is defined by the appended claims rather than the above description, and therefore all changes that fall within the meaning and range of equivalents of the claims are intended to be embraced by the invention. Any reference signs in the claims should not be regarded as limiting the claims involved.
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