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Method for restoring soil polluted by lead by utilizing super enrichment plant-Debregeasia saeneb

A technology of lead-contaminated soil and super-accumulating plants, applied in the field of phytoremediation, can solve the problems of poor understanding of the long-term stability of soil, easy corrosion of metal electrodes, and secondary pollution of soil, etc., to achieve extensive and reliable Operability, solution to soil lead pollution, and the effect of stabilizing polluted soil

Inactive Publication Date: 2009-02-04
云南省环境科学研究院(中国昆明高原湖泊国际研究中心)
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

Soil chemical leaching is one of the effective means to effectively treat soil polluted by volatile heavy metals. Choosing a suitable extractant is the key to this technology. However, no matter what kind of extractant, there are problems such as recovery and secondary pollution that have not been solved or perfected. technical problems; electrodynamic restoration is especially suitable for low-permeability clay and silt soil, and is economically reasonable, but due to the complexity of soil system components, there are often phenomena that are contrary to the actual application and experimental results, such as the buffer performance of soil, composition , ion composition, the type of polluted metal ions, etc. will all affect the effect of electrodynamic restoration. The metal electrode itself is easily corroded, and it will also cause secondary pollution of the soil. The disadvantage of electrothermal restoration is that soil organic matter and structural water are easily destroyed. It takes a lot of energy to drive away soil moisture; the soil improvement method is effective for small areas of soil pollution, but it is not suitable for large-scale soil pollution control, and there are still problems in properly handling the replaced soil to avoid secondary pollution; Solidification technology has a certain effect, in-situ solidification of heavy metals, greatly reducing costs, but it also has certain limitations: it only changes the form of heavy metals in the soil, and does not know much about the long-term stability of the soil and its impact on the ecosystem. research in this area
However, most of the discovered lead hyperaccumulative plants have small biomass and slow growth, which greatly limits their practical application in remediating lead-contaminated soils.

Method used

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Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0021] The average lead content in a lead-contaminated soil is 800mg / kg. Apply 6000kg / hm to the soil 2 Farmyard manure was used as the base fertilizer. In March, the seeds of water hemp willow were soaked in warm water at 50°C for half an hour and then sown into the soil. They were allowed to grow naturally. After the flowering period, the aboveground parts were harvested. The lead content is 1400mg / kg, and the average lead content in the soil is reduced from the original 800mg / kg to 700mg / kg, which is equivalent to reducing the lead content in the soil by 12.5%.

Embodiment 2

[0023] The average lead content in a lead-contaminated soil is 800mg / kg. Apply 15000kg / hm to the soil 2 Farmyard manure was used as the base fertilizer. In April, the seeds of water hemp willow were soaked in warm water at 60°C for half an hour and then sown into the soil. During the growth of water hemp willow, urea was used as top dressing, and the application rate was 200kg / hm 2 , let it grow naturally, and harvest its aerial parts after it reaches the fruiting period. After analysis and determination, the lead content in the aerial part is 1850mg / kg, and the average lead content in the soil is reduced from the original 800mg / kg to 620mg / kg, which is equivalent to reducing the lead content in the soil by 22.5%. After harvesting, it can be incinerated to generate electricity.

Embodiment 3

[0025] The average lead content in a lead-contaminated soil is 800mg / kg. Apply 10000kg / hm to the soil 2 Farmyard manure was used as the base fertilizer. In March, the seeds of water hemp willow were soaked in warm water at 50°C for half an hour and then sown into the soil. They were allowed to grow naturally. After the flowering period, the aboveground parts were harvested. The lead content is 1400mg / kg, and the average lead content in the soil is reduced from the original 800mg / kg to 700mg / kg, which is equivalent to reducing the lead content in the soil by 12.5%. Metal recycling is carried out after harvesting.

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Abstract

A method for repairing the Pb polluted soil by the super-enriching plant Shuima willow includes such steps as planting the Shuima willow in the polluted soil for absorbing the Pb from the polluted soil, and removing them from the soil.

Description

technical field [0001] The invention relates to a phytoremediation technology for polluted environment, in particular to a method for remediating soil polluted by heavy metals by using hyperaccumulator phytoremediation. technical background [0002] There are usually two ways for heavy metals to pollute soil: one is the environmental pollution caused by metal mining activities. Serious soil; heavy metal polluted soil caused by leaching and other reasons during the stacking of mining waste rocks; soil pollution caused by mine wastewater containing high concentrations of heavy metals, etc. The second is heavy metal polluted soil caused by industrial sewage irrigation of farmland. The phenomenon of lead-contaminated soil is relatively common in some parts of my country, and it is especially serious in some non-ferrous metal mining areas and surrounding areas of smelters in Yunnan Province. The average lead content in the soil of a typical non-ferrous metal mining area in south...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B09C1/00B09C1/10
Inventor 刘晓海高云涛贺彬王志芸宁平曾向东王伟陈同斌廖晓勇董琨文斌
Owner 云南省环境科学研究院(中国昆明高原湖泊国际研究中心)
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