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 PDFInfo
- 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
- Authority
- CN
- China
- Prior art keywords
- heavy metal
- sedum alfredii
- limit
- elsholtzia
- soil
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000002689 soil Substances 0.000 title claims abstract description 52
- 235000013311 vegetables Nutrition 0.000 title claims abstract description 33
- 229910001385 heavy metal Inorganic materials 0.000 title claims abstract description 32
- 238000004519 manufacturing process Methods 0.000 title claims abstract description 14
- 241000124844 Sedum alfredii Species 0.000 claims abstract description 24
- 229910052793 cadmium Inorganic materials 0.000 claims abstract description 19
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000010949 copper Substances 0.000 claims abstract description 16
- 239000011701 zinc Substances 0.000 claims abstract description 16
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 15
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims abstract description 15
- 229910052802 copper Inorganic materials 0.000 claims abstract description 15
- 238000000034 method Methods 0.000 claims abstract description 15
- 229910052725 zinc Inorganic materials 0.000 claims abstract description 15
- 241001549572 Elsholtzia splendens Species 0.000 claims abstract description 13
- 238000003306 harvesting Methods 0.000 claims abstract description 10
- 240000008067 Cucumis sativus Species 0.000 claims abstract description 7
- 235000010799 Cucumis sativus var sativus Nutrition 0.000 claims abstract description 7
- 230000012010 growth Effects 0.000 claims abstract description 6
- 239000003337 fertilizer Substances 0.000 claims description 15
- 241000311345 Elsholtzia haichowensis Species 0.000 claims description 11
- 235000010149 Brassica rapa subsp chinensis Nutrition 0.000 claims description 6
- 235000000536 Brassica rapa subsp pekinensis Nutrition 0.000 claims description 6
- 241000499436 Brassica rapa subsp. pekinensis Species 0.000 claims description 6
- 239000002738 chelating agent Substances 0.000 claims description 6
- WZLMXYBCAZZIRQ-UHFFFAOYSA-N [N].[P].[K] Chemical compound [N].[P].[K] WZLMXYBCAZZIRQ-UHFFFAOYSA-N 0.000 claims description 4
- 238000009342 intercropping Methods 0.000 claims description 4
- 239000002131 composite material Substances 0.000 claims description 3
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 claims description 2
- QPCDCPDFJACHGM-UHFFFAOYSA-N N,N-bis{2-[bis(carboxymethyl)amino]ethyl}glycine Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(=O)O)CCN(CC(O)=O)CC(O)=O QPCDCPDFJACHGM-UHFFFAOYSA-N 0.000 claims description 2
- 238000012545 processing Methods 0.000 claims description 2
- 230000002786 root growth Effects 0.000 claims description 2
- 241000196324 Embryophyta Species 0.000 abstract description 12
- 238000005067 remediation Methods 0.000 abstract description 3
- 240000007124 Brassica oleracea Species 0.000 abstract 2
- 235000003899 Brassica oleracea var acephala Nutrition 0.000 abstract 2
- 235000011301 Brassica oleracea var capitata Nutrition 0.000 abstract 2
- 235000001169 Brassica oleracea var oleracea Nutrition 0.000 abstract 2
- 238000005516 engineering process Methods 0.000 description 8
- 230000008901 benefit Effects 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 4
- 238000009825 accumulation Methods 0.000 description 4
- 238000012271 agricultural production Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000006872 improvement Effects 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- 230000004913 activation Effects 0.000 description 2
- 238000013459 approach Methods 0.000 description 2
- 230000033228 biological regulation Effects 0.000 description 2
- 238000003967 crop rotation Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000011133 lead Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 230000008439 repair process Effects 0.000 description 2
- ASDVPEFDBFOVRF-UHFFFAOYSA-N [Cr].[As].[Hg] Chemical compound [Cr].[As].[Hg] ASDVPEFDBFOVRF-UHFFFAOYSA-N 0.000 description 1
- 239000003905 agrochemical Substances 0.000 description 1
- CEKJAYFBQARQNG-UHFFFAOYSA-N cadmium zinc Chemical compound [Zn].[Cd] CEKJAYFBQARQNG-UHFFFAOYSA-N 0.000 description 1
- 238000005520 cutting process Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007850 degeneration Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 230000035558 fertility Effects 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000009335 monocropping Methods 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Images
Landscapes
- Processing Of Solid Wastes (AREA)
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
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.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100706221A CN100556562C (en) | 2007-08-31 | 2007-08-31 | One heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100706221A CN100556562C (en) | 2007-08-31 | 2007-08-31 | One heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil |
Publications (2)
Publication Number | Publication Date |
---|---|
CN101116865A true CN101116865A (en) | 2008-02-06 |
CN100556562C CN100556562C (en) | 2009-11-04 |
Family
ID=39053212
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB2007100706221A Expired - Fee Related CN100556562C (en) | 2007-08-31 | 2007-08-31 | One heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN100556562C (en) |
Cited By (43)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101670360B (en) * | 2009-10-30 | 2011-04-27 | 四川农业大学 | Application of sinosenecio oldhamianus in restoring copper pollution of mining soil and sludge |
CN102125927A (en) * | 2010-12-29 | 2011-07-20 | 上海市环境科学研究院 | Method for repairing heavy metal polluted soil |
CN102144467A (en) * | 2010-12-16 | 2011-08-10 | 中国计量学院 | Method for remedying soil polluted with cadmium by using interplanting |
CN101704016B (en) * | 2009-11-17 | 2012-01-18 | 上海市农业科学院 | Phytochemically combined remediation technology for soil contaminated by heavy metals, Mn, Pb, Cr and Zn |
CN101992208B (en) * | 2009-08-14 | 2012-05-30 | 中国科学院沈阳应用生态研究所 | Method for restoring and using vegetable field soil combinedly polluted by cadmium and polycyclic aromatic hydrocarbon |
CN102896142A (en) * | 2012-10-22 | 2013-01-30 | 杭州固洁环保工程有限公司 | Soil remediation method |
CN102989750A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DBP (dibutyl phthalate) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN102989749A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DNP (2, 4-dinitropheno) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN102989751A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DEHP (di-(2-ethylhexyl)phthalate) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN103109651A (en) * | 2011-11-16 | 2013-05-22 | 中国科学院沈阳应用生态研究所 | Method of producing while recovering for cadmium-polluted vegetable field |
CN103125472A (en) * | 2013-03-09 | 2013-06-05 | 广西大学 | Method of preventing gramineous weeds in southeast orpines field |
CN103270869A (en) * | 2013-05-15 | 2013-09-04 | 天津师范大学 | Method for repairing sludge heavy metal by combination of DTPA and ryegrass |
CN104025913A (en) * | 2014-06-17 | 2014-09-10 | 四川农业大学 | Method for improving capacity of descendants of Capsella bursa-pastoris to remedy cadmium-contaminated orchid soil by grafting |
CN104070057A (en) * | 2014-06-20 | 2014-10-01 | 杭州蓝天园林生态科技股份有限公司 | Treatment method for improving repair effect on cadmium-contaminated soil |
CN104475434A (en) * | 2014-11-21 | 2015-04-01 | 沈阳工业大学 | Technological method for directionally separating heavy metal in soil and sludge |
CN104620804A (en) * | 2014-12-20 | 2015-05-20 | 湖南科技大学 | Method for reducing absorbed and accumulated heavy metal of Brass napus |
CN104718836A (en) * | 2015-03-18 | 2015-06-24 | 青岛农业大学 | Method for treating metal cadmium contaminated soil through cotton plants |
CN104772327A (en) * | 2015-03-07 | 2015-07-15 | 湖南农业大学 | Method for repairing heavy metal-contaminated soil by using oilseed rape-oil sunflower crop rotation technology |
CN105170619A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Method for remediating and modifying heavy metal contaminated soil |
CN105290092A (en) * | 2014-10-21 | 2016-02-03 | 苗庆龄 | Method for remediating heavy metal polluted soil comprehensively |
CN105665441A (en) * | 2016-03-18 | 2016-06-15 | 浙江大学 | Remediation method for cadmium-nitrate combined pollution of facility agriculture soil |
CN105817471A (en) * | 2016-05-24 | 2016-08-03 | 湖南农业大学 | Method for repairing heavy metal contaminated soil by rape-peanut crop rotation mode |
CN105921513A (en) * | 2016-06-12 | 2016-09-07 | 武汉理工大学 | Method of accelerating accumulation of heavy metals cadmium and zinc by sedum alfredii hance |
CN105921502A (en) * | 2016-05-20 | 2016-09-07 | 中国科学院地理科学与资源研究所 | Method for utilizing cold-resistant winter rape variety for repairing cadmium and lead polluted farmland in winter |
CN106238446A (en) * | 2016-07-01 | 2016-12-21 | 河南化工职业学院 | The method utilizing herbaceous plant catch cropping restoration of soil polluted by heavy metal |
CN106734182A (en) * | 2016-12-16 | 2017-05-31 | 四川省文景环保工程有限公司 | A kind of method that utilization plant promotes plant absorption heavy metal |
CN106817946A (en) * | 2017-02-24 | 2017-06-13 | 中国科学院南京土壤研究所 | A kind of production of south jiangxi rare-earth mining area cadmium exceeded soil safety and reparation synchronously the cropping pattern that carries out |
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 |
CN107052031A (en) * | 2016-12-06 | 2017-08-18 | 广州富生源环保工程有限公司 | A kind of restorative procedure of heavy-metal contaminated soil |
CN107716535A (en) * | 2017-11-23 | 2018-02-23 | 湖北文理学院 | The plant of phthalate ester polycyclic aromatic hydrocarbon heavy-metal contaminated soil mixes up restorative procedure |
CN108326022A (en) * | 2018-02-02 | 2018-07-27 | 浙江农林大学 | A kind of plant restoration method of soil of zinc-cadmium combined pollution |
CN109328916A (en) * | 2018-11-23 | 2019-02-15 | 湖南科技大学 | A method of Absorption of Rape heavy metal is reduced using miscegenation flowers |
CN109699225A (en) * | 2018-12-16 | 2019-05-03 | 安徽省巢湖铸造厂有限责任公司 | A kind of preparation method of Nutrition Soil |
CN110052485A (en) * | 2019-04-16 | 2019-07-26 | 浙江大学 | A method of strengthen to extract using rape-Sedum alfredii Hance intercropping and interplanting and repairs cadmium mild or moderate polluted agricultural land |
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 |
CN110496857A (en) * | 2019-09-25 | 2019-11-26 | 苏州碧青环境科技有限公司 | A kind of soil remediation technique |
CN110523772A (en) * | 2019-08-29 | 2019-12-03 | 安徽禾美环保集团有限公司 | A kind of chromium-copper combined pollution plant restoration method |
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 |
CN111108839A (en) * | 2019-11-22 | 2020-05-08 | 华南农业大学 | Method for repairing cadmium-polluted rice field by intercropping sedum alfredii and broad beans |
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 |
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 |
CN115780505A (en) * | 2022-11-21 | 2023-03-14 | 煜环环境科技有限公司 | Combined remediation method for heavy metal contaminated soil |
-
2007
- 2007-08-31 CN CNB2007100706221A patent/CN100556562C/en not_active Expired - Fee Related
Cited By (54)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101992208B (en) * | 2009-08-14 | 2012-05-30 | 中国科学院沈阳应用生态研究所 | Method for restoring and using vegetable field soil combinedly polluted by cadmium and polycyclic aromatic hydrocarbon |
CN101670360B (en) * | 2009-10-30 | 2011-04-27 | 四川农业大学 | Application of sinosenecio oldhamianus in restoring copper pollution of mining soil and sludge |
CN101704016B (en) * | 2009-11-17 | 2012-01-18 | 上海市农业科学院 | Phytochemically combined remediation technology for soil contaminated by heavy metals, Mn, Pb, Cr and Zn |
CN102144467B (en) * | 2010-12-16 | 2012-07-25 | 中国计量学院 | Method for remedying soil polluted with cadmium by using interplanting |
CN102144467A (en) * | 2010-12-16 | 2011-08-10 | 中国计量学院 | Method for remedying soil polluted with cadmium by using interplanting |
CN102125927B (en) * | 2010-12-29 | 2012-07-04 | 上海市环境科学研究院 | Method for repairing heavy metal polluted soil |
CN102125927A (en) * | 2010-12-29 | 2011-07-20 | 上海市环境科学研究院 | Method for repairing heavy metal polluted soil |
CN103109651A (en) * | 2011-11-16 | 2013-05-22 | 中国科学院沈阳应用生态研究所 | Method of producing while recovering for cadmium-polluted vegetable field |
CN102896142A (en) * | 2012-10-22 | 2013-01-30 | 杭州固洁环保工程有限公司 | Soil remediation method |
CN102989750A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DBP (dibutyl phthalate) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN102989749A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DNP (2, 4-dinitropheno) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN102989751A (en) * | 2012-12-04 | 2013-03-27 | 常州大学 | Method for restoring and controlling Cd (cadmium) and DEHP (di-(2-ethylhexyl)phthalate) compound polluted soil by using large-biomass non-hyperaccumulation vegetables |
CN103125472A (en) * | 2013-03-09 | 2013-06-05 | 广西大学 | Method of preventing gramineous weeds in southeast orpines field |
CN103270869B (en) * | 2013-05-15 | 2016-02-17 | 天津师范大学 | DTPA combines perennial ryegrass and repairs sludge heavy-metal method |
CN103270869A (en) * | 2013-05-15 | 2013-09-04 | 天津师范大学 | Method for repairing sludge heavy metal by combination of DTPA and ryegrass |
CN104025913A (en) * | 2014-06-17 | 2014-09-10 | 四川农业大学 | Method for improving capacity of descendants of Capsella bursa-pastoris to remedy cadmium-contaminated orchid soil by grafting |
CN104025913B (en) * | 2014-06-17 | 2015-11-18 | 四川农业大学 | A kind of grafting improves the method that shepherd's purse offspring repairs orchard cadmium pollution soil ability |
CN104070057A (en) * | 2014-06-20 | 2014-10-01 | 杭州蓝天园林生态科技股份有限公司 | Treatment method for improving repair effect on cadmium-contaminated soil |
CN105290092A (en) * | 2014-10-21 | 2016-02-03 | 苗庆龄 | Method for remediating heavy metal polluted soil comprehensively |
CN104475434A (en) * | 2014-11-21 | 2015-04-01 | 沈阳工业大学 | Technological method for directionally separating heavy metal in soil and sludge |
CN104620804B (en) * | 2014-12-20 | 2017-01-11 | 湖南科技大学 | Method for reducing absorbed and accumulated heavy metal of Brass napus |
CN104620804A (en) * | 2014-12-20 | 2015-05-20 | 湖南科技大学 | Method for reducing absorbed and accumulated heavy metal of Brass napus |
CN104772327A (en) * | 2015-03-07 | 2015-07-15 | 湖南农业大学 | Method for repairing heavy metal-contaminated soil by using oilseed rape-oil sunflower crop rotation technology |
CN104718836A (en) * | 2015-03-18 | 2015-06-24 | 青岛农业大学 | Method for treating metal cadmium contaminated soil through cotton plants |
CN105170619A (en) * | 2015-09-30 | 2015-12-23 | 河南行知专利服务有限公司 | Method for remediating and modifying heavy metal contaminated soil |
CN105170619B (en) * | 2015-09-30 | 2018-07-17 | 河南行知专利服务有限公司 | A method of repairing and improve heavy-metal contaminated soil |
CN105665441A (en) * | 2016-03-18 | 2016-06-15 | 浙江大学 | Remediation method for cadmium-nitrate combined pollution of facility agriculture soil |
CN105921502B (en) * | 2016-05-20 | 2019-04-12 | 中国科学院地理科学与资源研究所 | A method of cadmium lead contamination farmland is repaired using cold-resistant winter rape variety winter |
CN105921502A (en) * | 2016-05-20 | 2016-09-07 | 中国科学院地理科学与资源研究所 | Method for utilizing cold-resistant winter rape variety for repairing cadmium and lead polluted farmland in winter |
CN105817471A (en) * | 2016-05-24 | 2016-08-03 | 湖南农业大学 | Method for repairing heavy metal contaminated soil by rape-peanut crop rotation mode |
CN105921513A (en) * | 2016-06-12 | 2016-09-07 | 武汉理工大学 | Method of accelerating accumulation of heavy metals cadmium and zinc by sedum alfredii hance |
CN106238446A (en) * | 2016-07-01 | 2016-12-21 | 河南化工职业学院 | The method utilizing herbaceous plant catch cropping restoration of soil polluted by heavy metal |
CN107052031A (en) * | 2016-12-06 | 2017-08-18 | 广州富生源环保工程有限公司 | A kind of restorative procedure of heavy-metal contaminated soil |
CN107052031B (en) * | 2016-12-06 | 2019-10-18 | 广州富生源环保工程有限公司 | A kind of restorative procedure of heavy-metal contaminated soil |
CN106734182B (en) * | 2016-12-16 | 2020-05-29 | 四川省文景环保工程有限公司 | Method for promoting plants to absorb heavy metals by using plants |
CN106734182A (en) * | 2016-12-16 | 2017-05-31 | 四川省文景环保工程有限公司 | A kind of method that utilization plant promotes plant absorption heavy metal |
CN106817946B (en) * | 2017-02-24 | 2018-12-28 | 中国科学院南京土壤研究所 | A kind of cadmium exceeded soil safety in south jiangxi rare-earth mining area produces the cropping pattern of progress synchronous with reparation |
CN106817946A (en) * | 2017-02-24 | 2017-06-13 | 中国科学院南京土壤研究所 | A kind of production of south jiangxi rare-earth mining area cadmium exceeded soil safety and reparation synchronously the cropping pattern that carries out |
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 |
CN107716535A (en) * | 2017-11-23 | 2018-02-23 | 湖北文理学院 | The plant of phthalate ester polycyclic aromatic hydrocarbon heavy-metal contaminated soil mixes up restorative procedure |
CN108326022A (en) * | 2018-02-02 | 2018-07-27 | 浙江农林大学 | A kind of plant restoration method of soil of zinc-cadmium combined pollution |
CN109328916A (en) * | 2018-11-23 | 2019-02-15 | 湖南科技大学 | A method of Absorption of Rape heavy metal is reduced using miscegenation flowers |
CN109699225A (en) * | 2018-12-16 | 2019-05-03 | 安徽省巢湖铸造厂有限责任公司 | A kind of preparation method of Nutrition Soil |
CN110052485A (en) * | 2019-04-16 | 2019-07-26 | 浙江大学 | A method of strengthen to extract using rape-Sedum alfredii Hance intercropping and interplanting and repairs cadmium mild or moderate polluted agricultural land |
CN110052485B (en) * | 2019-04-16 | 2021-03-30 | 浙江大学 | Method for repairing cadmium moderately and slightly polluted farmland by intercropping and enhanced extraction |
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 |
CN110523772A (en) * | 2019-08-29 | 2019-12-03 | 安徽禾美环保集团有限公司 | A kind of chromium-copper combined pollution plant restoration method |
CN110496857A (en) * | 2019-09-25 | 2019-11-26 | 苏州碧青环境科技有限公司 | A kind of soil remediation technique |
CN111108839A (en) * | 2019-11-22 | 2020-05-08 | 华南农业大学 | Method for repairing cadmium-polluted rice field by intercropping sedum alfredii and broad beans |
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 |
CN115780505A (en) * | 2022-11-21 | 2023-03-14 | 煜环环境科技有限公司 | Combined remediation method for heavy metal contaminated soil |
Also Published As
Publication number | Publication date |
---|---|
CN100556562C (en) | 2009-11-04 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100556562C (en) | One heavy metal species mild or moderate pollutes production limit, the limit restorative procedure of vegetable field soil | |
CN104550208B (en) | A kind of farmland soil heavy metals pollution amelioration method of coupling activation and passivation | |
CN104813885B (en) | Production method for cadmium-polluted rice land governing and rice cadmium reduction | |
CN103238440B (en) | Method for reducing cadmium pollution risk for rape | |
CN108856282B (en) | Composite remediation method for heavy metal contaminated farmland soil | |
CN108633650B (en) | Biogas slurry, water and fertilizer integrated safe application method of watermelons and muskmelons | |
CN107836303B (en) | Cadmium-polluted farmland safe utilization method based on multifunctional crop sweet sorghum | |
CN101279325A (en) | Method for repairing heavy metal polluted soil using combined technology of interacted plants and chemical leaching | |
CN109746255A (en) | A kind of method of activator joint Phytoremediation of Soils Contaminated by Heavy Metals | |
CN103109651A (en) | Method of producing while recovering for cadmium-polluted vegetable field | |
CN101617595A (en) | Method for safe production in cadmium polluted soil by utilizing low cadmium accumulation type celery cabbage | |
CN102349373A (en) | Method for repairing soil polluted by heavy metal in situ by mixed planting of plant | |
CN105290103A (en) | Method for utilizing cadmium-resisting fungus aspergillus aculeatus for promoting festuca arundinacea to remedy cadmium contaminated soil | |
CN104429850A (en) | Method for soilless culture of tomatoes | |
CN111408618B (en) | Method for restoring cadmium-polluted soil by utilizing black nightshade and corn intercropping plants | |
CN112974492A (en) | Strongly acidic high-heavy-metal-content mining wasteland combined ecological restoration method | |
CN108817069A (en) | A kind of heavy metallic activation agent and its application in soil joint is repaired | |
CN113058984B (en) | Phytoremediation method for heavily cadmium-lead polluted farmland | |
CN107774705A (en) | A kind of crop restorative procedure for cutting down agricultural land soil cadmium pollution | |
CN109168846A (en) | The ecology planting method in tea place | |
CN115889448B (en) | Method for promoting safe production of medium rice-rape rotation in Cd polluted farmland | |
CN111014279A (en) | Method for restoring lead-cadmium combined polluted soil by using corn straws and rhodiola rosea intercropping energy plants | |
CN103238439B (en) | Method for screening cadmium rejection varieties of leaf-edible rapes | |
CN109513733B (en) | Soil remediation method | |
CN113366945B (en) | Intercropping method for safely planting corn while repairing farmland with moderate and mild cadmium pollution |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20091104 |