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Method for reducing cadmium content in grasses and vegetables

A vegetable and pasture technology is applied in the field of reducing the cadmium content in pasture and vegetables, which can solve the problems of unsatisfactory soil passivation repair effect, affecting the continuous application of passivating agents, unstable effect, etc. Prospects, the effect of reducing bioavailability

Active Publication Date: 2015-04-22
SOUTH CHINA BOTANICAL GARDEN CHINESE ACADEMY OF SCI
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0004] Most of the commonly used heavy metal-contaminated soil additives have defects such as unstable effects or adverse effects on soil properties and structures, so that the passivation repair effect on soil is not ideal, which directly affects the actual continuous application of passivators.

Method used

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  • Method for reducing cadmium content in grasses and vegetables
  • Method for reducing cadmium content in grasses and vegetables
  • Method for reducing cadmium content in grasses and vegetables

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0020] The soil in this example is a vegetable garden soil that has been polluted by cadmium for many years, and the cadmium content is 8.2 mg / kg. Before applying the passivation agent, 26kg of urea and 37kg of potassium nitrate were applied per mu as base fertilizer.

[0021] Before sowing, the sodium silicate (Na 2 SiO 3 ·9H 2 O) or potassium silicate (K 2 O·nSiO 2 ·H 2 O, SiO 2 The content is 48%~54%), and potassium dihydrogen phosphate is dissolved in water at the application amount of 10kg silicon and 10kg phosphorus per mu to form a mixed solution and then evenly applied to the soil. Afterwards, forage grain amaranth and leaf vegetable red amaranth were sown for routine management.

[0022] As a control, the forage grain amaranth and leaf vegetable red amaranth were sown directly in the soil without adding any additives.

[0023] Sodium silicate, 20kg silicon per acre, 20kg silicon per acre, potassium dihydrogen phosphate 20kg phosphorus per acre, were formulated into solution...

Embodiment 2

[0037] Through Example 1, the combination of sodium silicate and potassium dihydrogen phosphate with the best passivation effect was selected for further testing. The soil in this example is vegetable garden soil that has been polluted by cadmium for many years, and the cadmium content is 6.1 mg / kg. Before applying the passivation agent, 26kg of urea and 37kg of potassium nitrate were applied per mu as base fertilizer.

[0038] Before planting, mix sodium silicate and potassium dihydrogen phosphate at a rate of 9kg silicon and 10kg phosphorus (Si 1 +P 1 ), 9kg silicon and 20kg phosphorus (Si 1 +P 2 ), 17kg silicon and 10kg phosphorus (Si 2 +P 1 ), 17kg silicon and 20kg phosphorus (Si 2 +P 2 ) Are combined separately and dissolved in water to form a mixed solution, then uniformly applied to the soil, and then seeded amaranth, for routine management.

[0039] As a control, forage seed amaranth was sown directly in the soil without adding any additives.

[0040] It turns out that apply...

Embodiment 3

[0048] In order to test the best application method of this modifier, the application concentration of 9kg silicon and 10kg phosphorus per mu is specially selected, sodium silicate and potassium dihydrogen phosphate are respectively mixed into aqueous solutions, and potassium dihydrogen phosphate is first applied to the cadmium contaminated soil Solution, wait for it to fully interact with the soil, and then apply the sodium silicate solution. Afterwards, the seed amaranth is sown and routinely managed. The soil and basal fertilizer application scheme in this example is the same as in example 2.

[0049] As a control, forage seed amaranth was sown directly in the soil without adding any additives.

[0050] After implementing this example, the yield of grain amaranth has been greatly increased. Compared with the control, the yield of grain amaranth increased by 1.18 times. The Cd content in roots, stems and leaves also decreased from 80, 21 and 93 mg / kg of the control to 19, 9, an...

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Abstract

The invention discloses a method for reducing cadmium content in grasses and vegetables. The method comprises the following steps of: applying 9kg-17kg of sodium silicate or potassium silicate per mu and 10kg-20kg of monopotassium phosphate per mu to cadmium-polluted soil on the basis of normal fertilizer application; seeding grasses or / and vegetables and carrying out normal management. The method for lowering cadmium content in grasses and vegetables disclosed by the invention can be used for effectively reducing the cadmium content in the crops and improving the crop yield, so that good application prospect is achieved in the agricultural field.

Description

Technical field: [0001] The invention belongs to the field of heavy metal pollution removal, and specifically relates to a method for reducing the cadmium content in forage grass and vegetables. Background technique: [0002] Due to the acceleration of urbanization, industrial "three wastes" emissions, atmospheric deposition, sewage irrigation, irrational application of sludge and agricultural chemicals, etc., the problem of heavy metal pollution in vegetable soils in my country (especially the heavy metal cadmium) has become increasingly prominent. Cadmium in the environment is highly mobile and highly toxic in the soil. It is considered to be one of the most toxic inorganic pollutants in the environment. It is easily absorbed by plant roots and migrates to the ground. Agricultural products, especially green leafy vegetables, have a great impact on cadmium. The strong absorption and accumulation capacity has led to a serious problem of excessive cadmium content in agricultural p...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B09C1/00
Inventor 卢焕萍李志安庄萍邹碧王法明夏汉平邰义萍
Owner SOUTH CHINA BOTANICAL GARDEN CHINESE ACADEMY OF SCI