CN101116865A - Method for producing and restoring vegetables growing in the heavy metal mildly-polluted soil - Google Patents

Method for producing and restoring vegetables growing in the heavy metal mildly-polluted soil Download PDF

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Publication number
CN101116865A
CN101116865A CNA2007100706221A CN200710070622A CN101116865A CN 101116865 A CN101116865 A CN 101116865A CN A2007100706221 A CNA2007100706221 A CN A2007100706221A CN 200710070622 A CN200710070622 A CN 200710070622A CN 101116865 A CN101116865 A CN 101116865A
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heavy metal
sedum alfredii
limit
elsholtzia
soil
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CN100556562C (en
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杨肖娥
李廷强
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Zhejiang University ZJU
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Abstract

The invention relates to a technique of remediation of slightly and medio- metal-contaminated vegetable soil with production. The specific steps are as follows: firstly, Sedum alfredii and Elsholtzia splendens are intercropped in vegetable soil contaminated by heavy metal such as cadmium, copper and zinc in spring with a with inter plant distance of ten to fifteen centimeters, row spacing of thirty centimeters; secondly, the Sedum alfredii is harvested periodically, a growth period of Sedum alfredii is three to four months during a first harvest, from then on, the Sedum alfredii is harvested every three months or when growing to a height of thirty to forty centimeters, stems of a height of two to three centimeters are left above the ground in harvest; the Elsholtzia splendens is harvested in October; thirdly, a cadmium-enriched rape is planted after the harvest of the Elsholtzia splendens with the spacing in the row of fifteen to twenty centimeters and is harvested in April of the next year; fourthly, a cucumber is planted after the harvest of the rape with the spacing in the row of twenty to twenty-five centimeters, a cabbage is planted after the harvest of the cucumber in September, the Elsholtzia splendens is planted after the harvest of the cabbage, then a restoring period is completed. Adopting a super accumulator plant for absorbing a plurality of heavy metal from the soil, the invention achieves reducing the heavy metal content in the vegetables and guaranteeing the safety of the farm produce.

Description

One heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil
Technical field
The present invention relates to the heavy metal mild or moderate and pollute the method that repair on production limit, vegetable field soil limit, belong to the improvement technical field of contaminated soil.
Background technology
At present, comparatively ripe and physical chemistry technology that be used for the heavy metal pollution of soil reparation has: soil moved in to improve the original, the technology of digging, drip washing technology, heat treatment technics, electrolysis tech, curing technology.Above-mentioned physical chemistry recovery technique respectively has its advantage, but all exists quantities big, the expense costliness, be difficult to launch the improvement of massive pollution soil, cause secondary pollution easily simultaneously and cause soil texture to destroy, ecological problems such as soil activation decline and soil fertility degeneration.Phytoremediation (phytoremediation) is that a kind of can the realization purifies the new technology that target can produce good economic benefits again and have exploitation value, compares with traditional physical chemistry technology, possesses skills and double dominant economically.China is vegetables production and consumption big country, and area reaches 1,800 ten thousand hectares.Vegetable plot multiple crop index height, agricultural chemicals and fertilizer have high input, and majority is distributed in outskirts of a town, be subjected to the urban industry pollution effect big, so soil heavy metal combined pollution are the most serious.The vegetable field soil combined pollution reduces vegetables quality, directly endanger the consumer health, influence China's Vegetables Exportation and earn foreign exchange, therefore, research and development are significant for the sustainable development that ensures agricultural, the healthy operation of promotion national economy at the bioremediation technology of China's vegetable field soil combined pollution.
Along with becoming increasingly conspicuous of environmental problem, China's agricultural production has been proposed new requirement, should reach high yield and high quality, realize the efficient utilization of resource again.China's heavy metal pollution of soil is serious day by day at present, and large tracts of land heavy metal mild or moderate polluted agricultural land is stopped farming, carries out long plant or engineering reparation, and this is unpractical under the present situation that China has a large population and a few land.There is the risk on the cultivation management on the one hand, influences normal agricultural production and farmers' income on the other hand.Therefore for the mild or moderate heavy-metal contaminated soil, adopt approach such as the low original position that drops into and do not destroy the farmland existing capability is repaired immediately, biological regulation and control, reduce the heavy metal-polluted soil biological effectiveness and, have more importantly meaning and application prospect improving agricultural product security and quality to the transportation and the accumulation at crop edible position.Hyperaccumulative plant and vegetables being done (intercropping, interplanting, crop rotation etc.) mutually, utilize hyperaccumulative plant to characteristics such as the activation of heavy metal, preferential absorption, reduce continuous cropping or content of beary metal in the interplanting vegetables with it, improve agricultural product security, will be a valid approach.
Summary of the invention
The purpose of this invention is to provide production limit, the limit restorative procedure that a heavy metal species mild or moderate pollutes vegetable field soil, both realized that the heavy metal mild or moderate polluted the original position reparation of vegetable field soil, can reduce the content of heavy metal in the vegetables again, ensure agricultural product security.
The heavy metal mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil, may further comprise the steps:
1) planted Sedum alfredii Hance and Elsholtzia haichowensis by the vegetable field soil of cadmium, copper, zinc heavy metal pollution with intercropping system spring, planting density spacing in the rows 10-15cm, line-spacing 30cm, use the nitrogen-phosphorus-potassium compound fertilizer and the fertilizer of the root growth that promotes Sedum alfredii Hance and Elsholtzia haichowensis, use the chelating agent that promotes that Sedum alfredii Hance and Elsholtzia haichowensis rhizosphere absorb heavy metal;
2) periodical reaping Sedum alfredii Hance gathers in Sedum alfredii Hance first and is growth 3-4 month, later every growth 3 months or grow into 30-40cm and highly gather in once, and overground part stays stem 2-3cm height during harvesting; Divide the results elsholtzia splendens October;
3) kind of a cadmium enrichment rape is carried in elsholtzia splendens results back, and spacing in the rows is 15-20cm, and gather in the crops April next year;
4) rape results back plantation cucumber, spacing in the rows is 20-25cm, cucumber results back plantation in September Chinese cabbage, Chinese cabbage results back plantation Elsholtzia haichowensis is finished a repairing efficiency;
5) Sedum alfredii Hance of harvesting and Elsholtzia haichowensis being transferred to other place focuses on or carries out resource processing and handle.
Among the present invention, fertilizer amount is used 20 kilograms of composite fertilizers by every mu, 500 kilograms of organic commercial fertilizers.The nitrogen-phosphorus-potassium compound fertilizer of using is N: P by weight 2O 5: K 2O=15: 15: 15.
The chelating agent that above-mentioned Sedum alfredii Hance rhizosphere is used is the DTPA of 3mmol/kg, uses in preceding 15 days in results.
The chelating agent that above-mentioned elsholtzia splendens rhizosphere is used is the EDTA of 3mmol/kg, uses in preceding 15 days in results.
Sedum alfredii Hance (Sedum alfredii Hance) is a herbaceos perennial, stem, mesophyll matter shape; Root-like stock is horizontal to be walked, the leaf alternate, and bottom Ye Chang comes off.Different with general plant, Sedum alfredii Hance is a kind of new zinc, cadmium hyperaccumulative plant, simultaneously lead is had very strong accumulation ability, cadmium, zinc, the lead of high-load in the soil is had very strong restrain oneself, absorption and accumulation ability.Under the field condition, the overground part dry weight can reach 3219kg/hm 2, overground part Zn content range is 4134~5000mg/kg, and mean value is 4515mg/kg, and the cadmium content scope is at 247~381mg/kg, and lead content is 177mg/kg.Under the lower situation of zinc in soil, cadmium, lead content, also can a large amount of zinc, cadmium, the lead of enrichment in the Sedum alfredii Hance body, so it can repair the soil of serious pollution and slight pollution.
Elsholtzia splendens is the annual herb plant, and stem is upright, in the open air up to 50~150cm.According to estimates, the dry matter production of elsholtzia splendens can reach 4.5t/hm in the open air 2Elsholtzia splendens has extremely strong patience to copper, and external enwergy out of office is a normal growth in 1645~8950mg/kg soil environment in copper content, and the copper content of its root system and aerial part can be up to 2288mg/kg and 304mg/kg, far above general plant (0~30mg/kg).In the with serious pollution soil of Cu, elsholtzia splendens can and be restrained oneself high-caliber copper by powerful and intensive root system absorption and enrichment, and the copper content of overground part can reach 0.89~1.42kg/hm 2, can reduce the copper content in the soil behind the results overground part.
Compare with traditional contaminated soil improvement method, the present invention is by zinc cadmium hyperaccumulative plant Sedum alfredii Hance, crop rotation of copper enriching plant Elsholtzia haichowensis and cadmium enrichment rape and vegetables or intercropping plant, in conjunction with different agronomy regulation measures, utilize hyperaccumulative plant that the preferential absorption of heavy metal is extracted on the one hand, the overground part cutting is carried out the strange land to be handled, reduce the soil available content of beary metal, on the other hand by making effect mutually between plant, the heavy metal that reduces the vegetables that do mutually with it absorbs and accumulation, do not destroying under farmland ecological environment and the existing plantation function prerequisite, reach the original position reparation of heavy metal mild or moderate contaminated soil, ensure the purpose of agricultural product security, do not influence normal vegetables simultaneously and produce and peasant's extra earning.This method small investment, administrative skill is less demanding, does not destroy soil physico-chemical property, and non-secondary pollution is a kind of applied range, small investment, " production limit, limit recovery technique " simple to operate.The invention solves the problem that contaminated soil reparation of mild or moderate vegetable plot and agricultural production are difficult to take into account, have good social benefit, economic benefit and environmental benefit.
Description of drawings
Fig. 1 is repairing efficiency of the present invention, and heavy metal content in soil changes, and among the figure, a changes for heavy metal-polluted soil full dose before and after repairing, and b changes for heavy metal-polluted soil available state before and after repairing.
The specific embodiment
Following example will further specify the feasibility and the good effect of the inventive method.
Hope new garden spot carry out two-year repairing test at the Shanghai City Jiading District.This garden spot heavy metal content in soil generally exceeds standard, belong to the mild or moderate contaminated soil, wherein soil cadmium, zinc, copper, plumbous full dose are distinguished 0.65mg/kg, 207.35mg/kg, 52.20mg/kg and 58.14mg/kg, and available state is respectively 0.16mg/kg, 7.08mg/kg, 5.45mg/kg and 1.64mg/kg.Begin test in March, 2005, soil is used composite fertilizer (N: P for every mu 2O 5: K 2O=15: 15: 15) 20kg, organic commercial fertilizer 500kg applies with base manure.In a repairing efficiency, Sedum alfredii Hance results 4 times, dry output is 448kg/667m 2, the overground part cadmium content is 22.6mg/kg, and zinc content is 5680.2mg/kg, and lead content is 94.6mg/kg, and the cadmium of taking away from soil, zinc, lead are respectively 10.0g/667m 2, 2009.5g/667m 2And 42.1g/667m 2Elsholtzia splendens results 1 time, overground part dry output 320kg/667m 2, copper content is 282.2mg/kg, and lead content is 68.6mg/kg, and zinc content is 117.4mg/kg, and the copper of taking away from soil, lead, zinc are respectively and are 73.3g/667m 2, 7.8g/667m 2, 32.7g/667m 2Rape results 1 time, overground part rape cauline leaf dry output can reach 360kg/667m 2, cadmium, the zinc taken away from soil are respectively 1.4g/667m 2And 37.5g/667m 2Cucumber results 1 time, output 1480kg/667m 2, Chinese cabbage results 2 times, output 1986kg/667m 2, two kinds of vegetables heavy metal of body content all do not exceed standard, and meet pollution-free vegetable content of beary metal standard (table 1).After finishing a repairing efficiency, the remediation efficiency that calculates with soil cadmium, zinc, copper, plumbous full dose reduction amount is respectively 13.8%, 8.7%, 2.9% and 1.5%; The remediation efficiency that calculates with soil cadmium, zinc, copper, plumbous available state reduction amount is respectively 50.7%, 39.9%, 43.1% and 21.9% (see figure 1).
Table 1 test vegetables heavy metal of body content (mg/kg)
Vegetables Cadmium Plumbous Mercury Chromium Arsenic
Cucumber 0.04 0.14 nd 0.11 0.08
Chinese cabbage 0.05 0.18 nd 0.23 0.13
Standard ≤0.05 ≤0.2 ≤0.01 ≤0.5 ≤0.5

Claims (5)

1. a heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil, it is characterized in that may further comprise the steps:
1) planted Sedum alfredii Hance and Elsholtzia haichowensis by the vegetable field soil of cadmium, copper, zinc heavy metal pollution with intercropping system spring, planting density spacing in the rows 10-15cm, line-spacing 30cm, use the nitrogen-phosphorus-potassium compound fertilizer and the fertilizer of the root growth that promotes Sedum alfredii Hance and Elsholtzia haichowensis, use the chelating agent that promotes that Sedum alfredii Hance and Elsholtzia haichowensis absorb heavy metal;
2) periodical reaping Sedum alfredii Hance gathers in Sedum alfredii Hance first and is growth 3-4 month, later every growth 3 months or grow into 30-40cm and highly gather in once, and overground part stays stem 2-3cm height during harvesting; Gather in the crops elsholtzia splendens October;
3) kind of a cadmium enrichment rape is carried in elsholtzia splendens results back, and spacing in the rows is 15-20cm, and gather in the crops April next year;
4) rape results back plantation cucumber, spacing in the rows is 20-25cm, cucumber results back plantation in September Chinese cabbage, Chinese cabbage results back plantation Elsholtzia haichowensis is finished a repairing efficiency;
5) Sedum alfredii Hance of harvesting and Elsholtzia haichowensis being transferred to other place focuses on or carries out resource processing and handle.
2. heavy metal mild or moderate according to claim 1 pollutes production limit, the limit restorative procedure of vegetable field soil, it is characterized in that fertilizer amount uses 20 kilograms of composite fertilizers by every mu, 500 kilograms of fertilizers.
3. heavy metal mild or moderate according to claim 1 and 2 pollutes production limit, the limit restorative procedure of vegetable field soil, it is characterized in that the nitrogen-phosphorus-potassium compound fertilizer used, by weight being N: P 2O 5: K 2O=15: 15: 15.
4. heavy metal mild or moderate according to claim 1 pollutes production limit, the limit restorative procedure of vegetable field soil, it is characterized in that the chelating agent that the Sedum alfredii Hance rhizosphere is used is the DTPA of 3mmol/kg, uses in preceding 15 days in results.
5. heavy metal mild or moderate according to claim 1 pollutes production limit, the limit restorative procedure of vegetable field soil, it is characterized in that the chelating agent that the elsholtzia splendens rhizosphere is used is the EDTA of 3mmol/kg, uses in preceding 15 days in results.
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CN106982630A (en) * 2017-04-06 2017-07-28 贵州省蚕业研究所 Persistently kept the safety in production using low cadmium capsicum/companion's ore deposit red-spotted stonecrop strip cropping the method for capsicum
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CN110280584A (en) * 2019-07-12 2019-09-27 江西洁地环境治理生态科技有限公司 A kind of heavy metal in soil biology removing method
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CN111108838A (en) * 2019-11-22 2020-05-08 广州草木蕃环境科技有限公司 Method for repairing cadmium-polluted rice field by intercropping sedum alfredii and astragalus sinicus
CN111097795A (en) * 2019-12-20 2020-05-05 浙江大学 Method for simultaneously producing and repairing cadmium-polluted continuous cropping obstacle facility agricultural soil
CN111602561A (en) * 2020-06-09 2020-09-01 农业农村部环境保护科研监测所 Method for intercropping grain amaranth and wheat on cadmium-polluted soil
CN112934949A (en) * 2021-02-18 2021-06-11 上海交通大学 Lawn restoration method based on heavy metal contaminated soil obtained by harvesting withered and old leaves

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