CN1303014C - Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard - Google Patents
Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard Download PDFInfo
- Publication number
- CN1303014C CN1303014C CNB2004100521077A CN200410052107A CN1303014C CN 1303014 C CN1303014 C CN 1303014C CN B2004100521077 A CNB2004100521077 A CN B2004100521077A CN 200410052107 A CN200410052107 A CN 200410052107A CN 1303014 C CN1303014 C CN 1303014C
- Authority
- CN
- China
- Prior art keywords
- soil
- zinc
- paniculata
- cadmium
- lead
- 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.)
- Expired - Fee Related
Links
- 239000002689 soil Substances 0.000 title claims abstract description 47
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 title claims abstract description 43
- 229910052793 cadmium Inorganic materials 0.000 title claims abstract description 43
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 title claims abstract description 43
- 229910052725 zinc Inorganic materials 0.000 title claims abstract description 43
- 239000011701 zinc Substances 0.000 title claims abstract description 43
- 238000000034 method Methods 0.000 title claims abstract description 23
- 241000219198 Brassica Species 0.000 title 1
- 235000003351 Brassica cretica Nutrition 0.000 title 1
- 235000003343 Brassica rupestris Nutrition 0.000 title 1
- QKSKPIVNLNLAAV-UHFFFAOYSA-N bis(2-chloroethyl) sulfide Chemical compound ClCCSCCCl QKSKPIVNLNLAAV-UHFFFAOYSA-N 0.000 title 1
- 235000010460 mustard Nutrition 0.000 title 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 41
- 241000196324 Embryophyta Species 0.000 claims abstract description 12
- 244000036975 Ambrosia artemisiifolia Species 0.000 claims description 26
- 238000003306 harvesting Methods 0.000 claims description 13
- 238000007667 floating Methods 0.000 claims description 6
- 238000005065 mining Methods 0.000 claims description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 4
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 4
- 239000004571 lime Substances 0.000 claims description 4
- 239000003337 fertilizer Substances 0.000 claims description 3
- JQJCSZOEVBFDKO-UHFFFAOYSA-N lead zinc Chemical compound [Zn].[Pb] JQJCSZOEVBFDKO-UHFFFAOYSA-N 0.000 claims description 3
- 235000015097 nutrients Nutrition 0.000 claims description 3
- 229920000742 Cotton Polymers 0.000 claims description 2
- 230000002378 acidificating effect Effects 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims description 2
- 238000005213 imbibition Methods 0.000 claims description 2
- 230000007226 seed germination Effects 0.000 claims description 2
- 241001190512 Arabis paniculata Species 0.000 abstract description 7
- 238000000605 extraction Methods 0.000 abstract description 7
- 230000007613 environmental effect Effects 0.000 abstract description 5
- 239000002028 Biomass Substances 0.000 abstract description 3
- WABPQHHGFIMREM-UHFFFAOYSA-N lead(0) Chemical compound [Pb] WABPQHHGFIMREM-UHFFFAOYSA-N 0.000 abstract 5
- 239000002131 composite material Substances 0.000 abstract 1
- 229910001385 heavy metal Inorganic materials 0.000 description 16
- 239000000126 substance Substances 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 238000005067 remediation Methods 0.000 description 3
- 241000219194 Arabidopsis Species 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 239000000284 extract Substances 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 238000011065 in-situ storage Methods 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 241000219195 Arabidopsis thaliana Species 0.000 description 1
- 241000238631 Hexapoda Species 0.000 description 1
- 238000003723 Smelting Methods 0.000 description 1
- 241000607479 Yersinia pestis Species 0.000 description 1
- 230000006978 adaptation Effects 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 231100000315 carcinogenic Toxicity 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 239000001963 growth medium Substances 0.000 description 1
- 239000007943 implant Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 230000005415 magnetization Effects 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 231100000219 mutagenic Toxicity 0.000 description 1
- 230000003505 mutagenic effect Effects 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000003900 soil pollution Methods 0.000 description 1
- 231100000378 teratogenic Toxicity 0.000 description 1
- 230000003390 teratogenic effect Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
- Cultivation Of Plants (AREA)
Abstract
Description
技术领域technical field
本发明涉及一种利用圆锥南芥(Arabis Paniculata)修复土壤和水体铅、锌、镉单一或复合污染方法。The invention relates to a method for using Arabis Paniculata to remediate single or combined pollution of lead, zinc and cadmium in soil and water.
背景技术Background technique
土壤和水体毒性重金属(铅、锌、镉等)污染引起了一个主要的环境和人类健康问题。我国有着丰富的铅、锌、镉矿产资源,由于富含铅、锌、镉矿体的自然风化和相应的露天开采、冶炼等矿业活动,以及大量施用化肥、农药等化工产品,导致了我国大面积的土壤和水体铅、锌、镉等重金属污染,矿山及冶炼厂周边地带尤为严重。过量暴露的铅、锌、镉直接威胁人居环境及食品安全,通过饮水和食品,大量摄入的上述三种金属,具致癌致畸致突变以及干扰激素内分泌等作用,危及居民健康和家畜安全。Soil and water pollution with toxic heavy metals (lead, zinc, cadmium, etc.) poses a major environmental and human health concern. my country is rich in lead, zinc, and cadmium mineral resources. Due to the natural weathering of ore bodies rich in lead, zinc, and cadmium, the corresponding open-pit mining, smelting and other mining activities, as well as the extensive use of chemical fertilizers, pesticides and other chemical products, my country's large-scale Heavy metals such as lead, zinc, and cadmium pollute the soil and water bodies of the entire area, especially in areas around mines and smelters. Excessive exposure of lead, zinc, and cadmium directly threatens the living environment and food safety. The above three metals, which are ingested in large quantities through drinking water and food, have carcinogenic, teratogenic, mutagenic, and hormone-endocrine-interfering effects, endangering the health of residents and the safety of livestock. .
当前,可供治理土壤或水体重金属污染的方法主要理化修复法和生物修复法At present, the methods available to control heavy metal pollution in soil or water are mainly physical and chemical remediation and bioremediation.
理化法有客土(换土)法、沉淀法、淋洗法、电化法、磁化法。这些物理或化学方法各有其优点,但一般都存在花费高、工程量较大、易造成二次污染等问题。Physical and chemical methods include guest soil (exchange soil) method, precipitation method, leaching method, electrochemical method, and magnetization method. These physical or chemical methods have their own advantages, but generally there are problems such as high cost, large amount of engineering, and easy to cause secondary pollution.
生物法有微生物和植物修复方法,微生物生物修复的局部成功仅局限于一些有机污染物的降解,在Biological methods include microbial and phytoremediation methods. The local success of microbial bioremediation is limited to the degradation of some organic pollutants.
处理金属污染物,特别是在土壤中并非有效。植物修复(phytoremediation)是一种新兴的重金属污染原位(in situ)绿色修复技术,作为其核心技术之一的植物提取技术(phytoextraction),已发展成为环境科学领域的研究与应用热点,并引起政府、学术界和企业界的高度重视。Treatment of metal contaminants, especially in soil, is not effective. Phytoremediation is an emerging in situ green remediation technology for heavy metal pollution. As one of its core technologies, phytoextraction has developed into a research and application hotspot in the field of environmental science, and has attracted attention. The government, academia and business circles attach great importance to it.
从当前国内外植物提取技术研究与实践进展来看,尚存在并需解决以下问题:(1)可供选择的能富集重金属铅、锌和镉的植物品种较少,特别是能同时富集两种以上金属的植物极少;(2)被推荐优先使用的超富集植物(hyperaccumulator),普遍生物量偏低,重金属的总体去除效率较低,同时还存在异地气候适应等问题;(3)污染土壤中重金属生物有效性(bioavailability)有待提高;(4)从应用来看,发达国家的植物修复技术部分已投入实际应用,并获得了较好的环境、经济和社会效益,而我国尚处于起步阶段,相关技术还处于实验室或中试阶段。Judging from the current research and practical progress of plant extraction technology at home and abroad, the following problems still exist and need to be solved: (1) There are few plant species that can be selected to enrich heavy metals lead, zinc and cadmium, especially those that can enrich heavy metals at the same time. There are very few plants with more than two kinds of metals; (2) hyperaccumulators, which are recommended for priority use, generally have low biomass, low overall removal efficiency of heavy metals, and there are also problems such as climate adaptation in different places; (3) ) The bioavailability of heavy metals in contaminated soil needs to be improved; (4) In terms of application, some phytoremediation technologies in developed countries have been put into practical application and have achieved good environmental, economic and social benefits, while China has not It is in its infancy, and related technologies are still in the laboratory or pilot stage.
发明内容Contents of the invention
本发明的目的是提供一种利用圆锥南芥(Arabis Paniculata)修复土壤或水体铅、锌、镉污染的方法。The purpose of the present invention is to provide a kind of method utilizing Arabis Paniculata to remediate lead, zinc, cadmium pollution of soil or water body.
本发明通过种植圆锥南芥,持续提取并活化土壤或水体中的铅、锌、镉,同时向上转运到达地上部,待地上部形成一定的生物量,定期收割地上部,保留地下部,则可进行持续提取,持续转移土壤或水体中大量的铅、锌、镉,从而经过一定的提取周期清除土壤或水体铅、锌、镉污染。The present invention continuously extracts and activates lead, zinc, and cadmium in soil or water by planting A. paniculata, and at the same time transfers them upwards to the aboveground part. After a certain amount of biomass is formed in the aboveground part, the aboveground part is regularly harvested and the underground part is kept. Carry out continuous extraction, and continuously transfer a large amount of lead, zinc, and cadmium in the soil or water body, so as to remove lead, zinc, and cadmium pollution from the soil or water body after a certain extraction cycle.
本发明的方法的具体步骤包括:Concrete steps of the method of the present invention include:
(1)选用自然生长在我国云南省兰坪县金顶铅锌矿区的圆锥南芥(ArabisPaniculata),采集其种子进行常规育苗;(1) Select Arabis Paniculata (Arabis Paniculata) that naturally grows in the Jinding lead-zinc mining area of Lanping County, Yunnan Province, my country, and collect its seeds for conventional seedling cultivation;
用种子育苗时,种子萌发及幼苗培育的条件一般为:将圆锥南芥种子浸于Hoagland营养液中吸胀2-3小时,放置暗处发芽3-5天后,在温室正常土壤中育苗,空气相对湿度50-60%,温度22-25℃;When raising seedlings with seeds, the conditions for seed germination and seedling cultivation are generally: soak the seeds of A. paniculata in Hoagland nutrient solution for imbibition for 2-3 hours, place them in a dark place to germinate for 3-5 days, and grow seedlings in normal soil in the greenhouse. Relative humidity 50-60%, temperature 22-25 ℃;
(2)控制土壤或水体pH于5~7之间;可视生长介质实际酸碱度,通过施用酸性或碱性肥料(或石灰)加以调节;(2) Control the pH of the soil or water between 5 and 7; depending on the actual pH of the growth medium, adjust it by applying acidic or alkaline fertilizers (or lime);
(3)将生长至3~5cm(或生长4~5周)的由种子培育的上述圆锥南芥幼苗,移栽入已按前述要求调节pH的铅、锌、镉单一或复合污染的土壤或水体中;对圆锥南芥在水体生长支撑的处理为:将圆锥南芥植入浮床,根部通过浮床上钻制的小孔直接与污染水体接触,生长前期加海绵或脱脂棉于小孔中稳固植株;(3) Transplant the above-mentioned A. paniculata seedlings cultivated by seeds that have grown to 3-5 cm (or grow for 4-5 weeks) into the soil or compound polluted by lead, zinc, and cadmium whose pH has been adjusted according to the aforementioned requirements. In the water body; the treatment for the growth support of A. paniculata in the water body is: implant A. paniculata into the floating bed, and the roots directly contact the polluted water body through the small holes drilled on the floating bed, and add sponge or absorbent cotton in the small holes to stabilize the plants in the early stage of growth. ;
(4)定期收割地上部,土壤中一年两次,水体中一年三次,或当圆锥南芥长到20-30cm高度时收割一次;收割地上部时留茬3~5cm;让圆锥南芥持续生长,持续收割圆锥南芥地上部,直到土壤或水体铅、锌、镉达到安全标准。收割的圆锥南芥地上部可进行统一处理,如在垃圾填埋区安全填埋或焚烧。(4) Harvest the aboveground part regularly, twice a year in the soil, three times a year in the water body, or harvest once when A. paniculata grows to a height of 20-30cm; leave 3-5cm stubble when harvesting the above-ground part; let A. paniculata Continue to grow and harvest the shoots of A. paniculata until the lead, zinc, and cadmium in the soil or water reach the safety standards. Harvested aerial parts of A. paniculata can be disposed of uniformly, such as safe landfill or incineration in landfill areas.
本发明所用的铅、锌和镉超富集植物圆锥南芥(Arabis Paniculata),为十字花科南芥属植物,在我国云南省兰坪县金顶铅锌矿区自然生长,常年可采集到,其种子也较易发芽繁殖。The lead, zinc and cadmium super-enrichment plant Arabis Paniculata used in the present invention is a plant of the genus Arabidopsis thaliana, which grows naturally in Jinding lead-zinc mining area, Lanping County, Yunnan Province, my country, and can be collected all year round. Its seeds are also easier to germinate and reproduce.
自然条件下其多金属富集特征如下:The polymetallic enrichment characteristics under natural conditions are as follows:
圆锥南芥地上部铅、锌、镉的平均含量分别为2484,20749和457mg/kg(干重,下同),地下部铅、锌、镉的平均含量分别为1578,18149,452mg/kg.地上部含量均大于地下部,富集指标达到超富集水平。The average contents of lead, zinc and cadmium in the aerial parts of A. paniculata were 2484, 20749 and 457 mg/kg (dry weight, the same below), and the average contents of lead, zinc and cadmium in the underground were 1578, 18149 and 452 mg/kg, respectively. The contents in the aboveground parts were greater than those in the underground parts, and the enrichment index reached the super-enrichment level.
本发明具以下突出效果:The present invention has the following outstanding effects:
1.本发明所选用的圆锥南芥,可超富集重金属铅、锌和镉,应用于植物修复污染土壤或水体中的铅、锌和镉,成本低,对环境友好,修复效率高,潜在经济效益可观;1. The selected Arabidopsis paniculata in the present invention can hyper-accumulate heavy metals lead, zinc and cadmium, and can be applied to phytoremediation of lead, zinc and cadmium in polluted soil or water bodies, with low cost, environmental friendliness, high repair efficiency and potential considerable economic benefits;
2.本发明所选用的圆锥南芥,具有易繁殖、能同时耐受并富集多种重金属(主要为铅、锌、镉)、抗病虫害、多年生长等特点,适合于污染土壤或水体的铅、锌、镉植物提取;2. the selected Arabidopsis paniculata of the present invention has characteristics such as easy reproduction, can tolerate and enrich multiple heavy metals (mainly lead, zinc, cadmium), resistance to diseases and insect pests, and perennial growth, and is suitable for polluting soil or water bodies Lead, zinc, cadmium plant extraction;
3.按照本发明方法的持续提取模式,简化了修复土壤或水体铅、锌、镉污染的程序,适合于推广应用;3. According to the continuous extraction mode of the method of the present invention, the procedure for remediating soil or water body lead, zinc, and cadmium pollution is simplified, which is suitable for popularization and application;
4.本发明建立的修复模式系绿色原位修复,所收获的地上部进行集中安全填埋或焚烧,不会造成二次污染,同时修复进程不会破坏土壤或水体生态环境,并有助于改善土壤因重金属污染而引起的土壤退化和生产力下降,恢复并提高土壤生物多样性,对水体的修复可明显改善水质。4. The restoration mode established by the present invention is green in-situ restoration, and the harvested above-ground parts are safely buried or incinerated, which will not cause secondary pollution. At the same time, the restoration process will not damage the soil or water body ecological environment, and contribute to Improve soil degradation and productivity decline caused by heavy metal pollution, restore and increase soil biodiversity, and restore water bodies can significantly improve water quality.
具体实施方式Detailed ways
以下通过实施例对本发明作进一步说明。The present invention will be further described below through embodiment.
实施例1:土壤修复Example 1: Soil Remediation
圆锥南芥种子,于Hoagland营养液中吸胀3小时,放置暗处4天发芽后,于温室正常土壤中培育,空气相对湿度60%,温度25℃。待圆锥南芥幼苗生长至3~5cm,移栽入重金属污染土壤,土壤重金属本底含量:铅>500mg/kg,锌>1000mg/kg,镉>10mg/kg,施石灰调节pH至6~7,行距15cm,株距10cm。生长6个月收获地上部,留茬4~5cm。第一次收获的圆锥南芥,测定地上部干重中各重金属含量为:Pb>100mg/kg,锌>3000mg/kg,镉>100mg/kg;圆锥南芥持续生长、持续提取土壤铅、锌、镉,持续收割圆锥南芥地上部,土壤中的铅、锌、镉含量不断减少,直到污染土壤铅、锌、镉含量减少到正常土壤水平,土壤铅、锌、镉污染消除。Seeds of A. paniculata were imbibed in Hoagland nutrient solution for 3 hours, placed in a dark place for 4 days to germinate, and then cultivated in normal soil in a greenhouse with a relative air humidity of 60% and a temperature of 25°C. When the seedlings of A. paniculata grow to 3-5cm, transplant them into heavy metal-contaminated soil. The background content of heavy metals in the soil: lead> 500mg/kg, zinc> 1000mg/kg, cadmium> 10mg/kg, apply lime to adjust the pH to 6-7 , row spacing 15cm, plant spacing 10cm. Harvest the aboveground part after 6 months of growth, and leave stubble of 4 to 5 cm. For the first harvest of A. paniculata, the content of heavy metals in the dry weight of the aboveground part was determined as follows: Pb>100mg/kg, zinc>3000mg/kg, cadmium>100mg/kg; A. paniculata continues to grow and continuously extracts soil lead and zinc , cadmium, continuous harvesting of the shoots of A. paniculata, the content of lead, zinc, and cadmium in the soil continued to decrease, until the content of lead, zinc, and cadmium in the polluted soil decreased to the normal soil level, and the pollution of soil lead, zinc, and cadmium was eliminated.
实施例2:水体修复Example 2: Water restoration
野外移栽的幼苗于温室正常土壤中培育,空气相对湿度60%,温度25℃,待幼苗生长至3~5cm,移栽入设置于重金属污染水体的浮床,根部通过在浮床上钻制的小孔,直接与污染水体接触,生长前期加海绵于小孔中稳固植株;水体重金属本底含量:铅>20mg/L,锌>100mg/L,镉>10mg/L,加石灰调节pH至6~7;行距15cm,株距15cm。生长四个月收获地上部,留茬3~4cm。经测定,收获的圆锥南芥地上部干重中各重金属含量:铅>2000mg/kg,锌>5000mg/kg,镉>100mg/kg;圆锥南芥持续提取铅、锌、镉,持续收割其地上部,水体中的铅、锌、镉含量不断减少,直到污染水体中的铅、锌、镉含量减少到正常水体水平,水体铅、锌、镉污染消除。The seedlings transplanted in the field are cultivated in the normal soil of the greenhouse, the relative air humidity is 60%, and the temperature is 25°C. After the seedlings grow to 3-5cm, they are transplanted into the floating bed set in the heavy metal polluted water body, and the roots pass through the small holes drilled on the floating bed. Hole, directly in contact with polluted water, add sponge in the small hole to stabilize the plant in the early stage of growth; the background content of heavy metals in the water: lead> 20mg/L, zinc> 100mg/L, cadmium> 10mg/L, add lime to adjust the pH to 6~ 7; row spacing 15cm, plant spacing 15cm. Harvest the aboveground part after growing for four months, leaving 3 to 4 cm stubble. After determination, the content of heavy metals in the dry weight of the harvested A. paniculata: lead > 2000mg/kg, zinc > 5000mg/kg, cadmium > 100mg/kg; continuous extraction of lead, zinc and cadmium from A. paniculata, continuous harvesting of its aboveground Ministry, the content of lead, zinc and cadmium in the water body is continuously reduced until the content of lead, zinc and cadmium in the polluted water body is reduced to the level of the normal water body, and the pollution of lead, zinc and cadmium in the water body is eliminated.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2004100521077A CN1303014C (en) | 2004-11-09 | 2004-11-09 | Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2004100521077A CN1303014C (en) | 2004-11-09 | 2004-11-09 | Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1623933A CN1623933A (en) | 2005-06-08 |
CN1303014C true CN1303014C (en) | 2007-03-07 |
Family
ID=34764099
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNB2004100521077A Expired - Fee Related CN1303014C (en) | 2004-11-09 | 2004-11-09 | Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1303014C (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2013150197A1 (en) | 2012-03-06 | 2013-10-10 | Centre National De La Recherche Scientifique | Use of certain metal-accumulating plants for the performance of organic chemistry reactions |
Families Citing this family (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100457300C (en) * | 2006-07-27 | 2009-02-04 | 云南省环境科学研究院 | Method for repairing lead polluted soil using super enriching plant Tephrosia candida |
CN100457301C (en) * | 2006-07-31 | 2009-02-04 | 云南省环境科学研究院 | Method for restoring soil polluted by lead by utilizing super enrichment plant-Debregeasia saeneb |
CN101125338B (en) * | 2007-09-29 | 2010-05-26 | 中山大学 | A method for controlling soil or water body cadmium pollution |
CN104607448B (en) * | 2014-12-10 | 2017-01-11 | 韩山师范学院 | Method for restoring Cd-polluted soil or water body |
CN104710016B (en) * | 2015-04-02 | 2017-03-01 | 广西科学院 | A kind of method going heavy metal in eliminating water using Properties of Mangrove Seedlings |
CN108906875A (en) * | 2018-07-05 | 2018-11-30 | 安徽袁粮水稻产业有限公司 | A kind of method for comprehensive repairing of lead contamination rice soil |
CN109365494B (en) * | 2018-11-30 | 2021-06-01 | 江门市邑凯环保服务有限公司 | Phytoremediation method for treating cadmium-manganese-chromium composite polluted soil |
CN109467194A (en) * | 2018-12-29 | 2019-03-15 | 广西壮族自治区农业科学院农产品质量安全与检测技术研究所 | A method of utilizing the restoring cadmium polluted water body of brill leaf aster and wetland |
CN109772881B (en) * | 2019-03-06 | 2021-11-05 | 韶关学院 | A method for using aromatic plants to remediate and efficiently utilize cadmium-contaminated farmland soil |
CN112404122A (en) * | 2020-10-28 | 2021-02-26 | 武汉市秀谷科技有限公司 | Planting and cultivating method for farmland heavy metal-enriched plants |
CN114602969A (en) * | 2022-04-22 | 2022-06-10 | 泉州师范学院 | Method for restoring lead pollution of water body and soil by utilizing spice plants |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61171597A (en) * | 1985-01-11 | 1986-08-02 | Tsutomu Arimizu | Method for purifying water of lake and marsh by aquatic plant |
DE19643364A1 (en) * | 1996-10-09 | 1998-04-16 | Umweltforschung Grosbeeren Gmb | Process to liberate especially heavy metals from polluted soil in modular bed |
CN1397390A (en) * | 2001-07-18 | 2003-02-19 | 中国科学院地理科学与资源研究所 | Method for treating As polluted soil |
CN1480411A (en) * | 2003-07-18 | 2004-03-10 | 中山大学 | A kind of phytoremediation method of eutrophic water body |
CN1502423A (en) * | 2002-11-27 | 2004-06-09 | 中国科学院地理科学与资源研究所 | A method for repairing arsenic polluted environment |
-
2004
- 2004-11-09 CN CNB2004100521077A patent/CN1303014C/en not_active Expired - Fee Related
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS61171597A (en) * | 1985-01-11 | 1986-08-02 | Tsutomu Arimizu | Method for purifying water of lake and marsh by aquatic plant |
DE19643364A1 (en) * | 1996-10-09 | 1998-04-16 | Umweltforschung Grosbeeren Gmb | Process to liberate especially heavy metals from polluted soil in modular bed |
CN1397390A (en) * | 2001-07-18 | 2003-02-19 | 中国科学院地理科学与资源研究所 | Method for treating As polluted soil |
CN1502423A (en) * | 2002-11-27 | 2004-06-09 | 中国科学院地理科学与资源研究所 | A method for repairing arsenic polluted environment |
CN1480411A (en) * | 2003-07-18 | 2004-03-10 | 中山大学 | A kind of phytoremediation method of eutrophic water body |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2013150197A1 (en) | 2012-03-06 | 2013-10-10 | Centre National De La Recherche Scientifique | Use of certain metal-accumulating plants for the performance of organic chemistry reactions |
Also Published As
Publication number | Publication date |
---|---|
CN1623933A (en) | 2005-06-08 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
de-Bashan et al. | The potential contribution of plant growth-promoting bacteria to reduce environmental degradation–A comprehensive evaluation | |
CN102172608B (en) | Application of artemisia stolonifera in repairing of heavy metal cadmium polluted soil | |
US6302942B1 (en) | Methods for removing pollutants from contaminated soil materials with a fern plant | |
CN100427227C (en) | A phytoremediation method for controlling lead-contaminated soil | |
CN1303014C (en) | Method for treating soil and aquatic lead, zinc, cadmium pollution by cone south mustard | |
CN1724184A (en) | A kind of method of utilizing the plant of Solanaceae cadmium pollution soil repair | |
CN102172607A (en) | Use of Debregeasia orientalis C. J. Chen in remediation of cadmium heavy metal contaminated soil | |
CN101249501A (en) | Phytoremediation method based on uranium tailings slag contaminated soil | |
CN103143559A (en) | Method for remediation of heavy metal contaminated soil | |
CN102806227A (en) | Method of restoring soil polluted by heavy metal | |
CN101670362A (en) | Application of grain amaranth in repairing mine soil and sludge polluted by heavy metal cadmium | |
CN102513341A (en) | Chemical-giant reed combined ecological recovery method of polymetal polluted soil in mining and metallurgy zones | |
CN103111460A (en) | Method for restoring heavy metal pollution soil | |
CN101332466A (en) | Method for repairing heavy metal pollution in mine soil and sludge | |
CN101693252A (en) | Application of siegesbeckia herb in remediation of soil contaminated with heavy metal cadmium | |
CN101125338B (en) | A method for controlling soil or water body cadmium pollution | |
CN106269845A (en) | The method of phytomicroorganism combine d bioremediation DDT contaminated soil and application | |
CN102515939A (en) | Method for converting heavy metal-enriched plant into miscellaneous fertilizer containing biological carbon special for mine vegetation recovery | |
CN102303040A (en) | Remediation method for acid heavy metal contaminated soil | |
CN102489498B (en) | Application of ruellia brittoniana in repairing soil and/or water body cadmium pollution | |
CN100441325C (en) | A method for promoting phytoremediation of nickel-contaminated soil by using Pseudomonas vesicularis | |
CN1281345C (en) | Method for repairing soil and zinc and cadmium nollution in water b using Arrow leaf violet | |
CN1303015C (en) | Method for treating soil and aquatic lead, zinc, cadmium pollution by long pubescence potentilla chinensis | |
CN101670361A (en) | Application of nicandra physalodes in repairing mine soil and sludge polluted by heavy metal cadmium | |
CN100371092C (en) | A method for remediating cadmium-contaminated soil using cruciferous plants |
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 | ||
C17 | Cessation of patent right | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20070307 Termination date: 20111109 |