[go: up one dir, main page]

CN101492770A - Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing - Google Patents

Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing Download PDF

Info

Publication number
CN101492770A
CN101492770A CNA2009100941644A CN200910094164A CN101492770A CN 101492770 A CN101492770 A CN 101492770A CN A2009100941644 A CNA2009100941644 A CN A2009100941644A CN 200910094164 A CN200910094164 A CN 200910094164A CN 101492770 A CN101492770 A CN 101492770A
Authority
CN
China
Prior art keywords
arsenic
gold
tailings
plant
acid
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.)
Pending
Application number
CNA2009100941644A
Other languages
Chinese (zh)
Inventor
王海娟
宁平
张泽彪
曾向东
王宏镔
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kunming University of Science and Technology
Original Assignee
Kunming University of Science and Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Kunming University of Science and Technology filed Critical Kunming University of Science and Technology
Priority to CNA2009100941644A priority Critical patent/CN101492770A/en
Publication of CN101492770A publication Critical patent/CN101492770A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Cultivation Of Plants (AREA)
  • Fertilizers (AREA)

Abstract

本发明涉及一种高砷金尾矿再回收金的植物除砷预处理方法。通过种植蜈蚣草或大叶井口边草,利用其对砷的超积累特性及其喜钙、耐碱、生物量大和生长期较短且破坏氰络离子的特性,靠其根系大量吸收富集金尾矿中的砷,并将砷向上输送和转移到地上部,再通过收割地上部而除去高砷金尾矿中的砷,从而完成对金尾矿二次利用的提砷预处理。The invention relates to a plant arsenic removal pretreatment method for recovering gold from high-arsenic gold tailings. By planting centipede grass or big-leaf wellhead edge grass, using its super-accumulation characteristics of arsenic and its calcium-loving, alkali-resistant, large biomass, short growth period and destruction of cyanide ions, it absorbs and enriches gold by its roots. The arsenic in the tailings is transported upwards and transferred to the aboveground part, and then the arsenic in the high-arsenic gold tailings is removed by harvesting the aboveground part, so as to complete the arsenic extraction pretreatment for the secondary utilization of the gold tailings.

Description

A kind of plant arsenic-removing pretreatment method of recycling golden from high-arsenic golden mine tailing
One, technical field
The present invention relates to a kind of plant arsenic-removing pretreatment method of recycling golden from high-arsenic golden mine tailing.Be a kind of by plantation Herba pteridis vittatae or Da Ye Herba Pteridis multifidae, utilize the tired characteristic of its ultraproduct to arsenic, by the arsenic in a large amount of absorbing enriched gold mines of its root system, and arsenic upwards carried and transfers to overground part, remove arsenic in the golden mine tailing by the harvesting overground part again, finish golden mine tailing second stage employ carried the arsenic pretreatment process.
Two, background technology
The gold mine tailing is the main solid waste that gold selects factory, and China's gold mine tailing resource is very abundant.The gold mine that built up before the seventies, traditional processing technologies such as flotation, gravity treatment, amalgamate-mercury choosing or gravity treatment-flotation are adopted in the dressing-works mostly, owing to be subjected to the restriction of factors such as industry policy, technical equipment, dressing and smelting process and fund, the rate of recovery of gold is low, therefore, in general, tailing all has quite high comprehensive utilization value.And because the second stage employ of mine tailing resource no longer needs mining, broken and corase grind ore deposit operation, production cost is low, also because price of gold rises, makes these mine tailing resources that higher recovery value arranged simultaneously.
At present, the high arsenic fine gold ore pretreatment technology has bio-oxidation, high-pressure oxidation and roasting oxidation.Bio-oxidation, roasting and high-pressure oxidation process investment are high, technical certain problem, the domestic successful experience that does not have suitability for industrialized production of still existing.Yet these method complex manufacturing, facility investment is big, also can make the arsenic-containing ores such as mispickel, orpiment, realgar of low toxicity be oxidized to the very high arsenic of toxicity, arsenate and sulfurous gas in the roasting process, causes environmental pollution.Therefore select for use cost-effective method to remove mineral such as the arsenic of gold mine, antimony, become the key factor of the extracting efficiency of raising gold, the efficient recovery that causes gold in the high arsenic difficult-treating gold mine is to study focus and difficult point at present both at home and abroad.In recent years, some special plants of a large amount of enrichment pollutents of portion on the ground--super enriching plant has become the focus of academia's research.Study the plant arsenic-removing method for this reason and remove the arsenic contain in the higher golden mine tailing of arsenic and become popular, found that the plant of enrichment arsenic mostly is the Pteris plant in a large number both at home and abroad.Herba pteridis vittatae and Da Ye Herba Pteridis multifidae all meet the standard of arsenic super enriching plant.
CN200610048663.6 relates to a kind of plant restoration method of administering lead pollution of soil, this method is by planting Pale Butterflybush Flower in the soil that is subjected to Lead contamination with direct transplanting or seeding method, make it survive growth, and upwards transport and be transported to overground part, harvesting overground part and it is removed when plant strain growth to 100~120cm or Pale Butterflybush Flower over-ground part Pb content reach 1400mg/kg, then can from soil, take away a large amount of lead, thereby reach the purpose of quick improvement lead pollution of soil.It is neutrality or slant acidity that this method will be regulated and control soil acidity or alkalinity, and plants Pale Butterflybush Flower according to the spacing in the rows of 2~4m.
CN01120519.9 relates to a kind of method of administering As polluted soil, present method relates to the method for repairing and administering As polluted soil (comprising wetland) with Herba pteridis vittatae, this method is passed through the arsenic in a large amount of absorbing environmentals of root system of Herba pteridis vittatae, and upwards carries and be transported to overground part.Gather in overground part (toothing 5~10cm height) when plant-growth to 50~80cm height or after growing 5~6 months and it is removed, then can from soil, take away a large amount of arsenic, thereby reach the purpose of quick removing arsenic contamination.For acid soil, then improve the acidity-basicity ph of contaminated soil by methods such as liming or alkaline fertilizers.
CN200710066021.3 the present invention relates to the plant that a kind of reduction contains high arsenic difficult-treating gold mine smelting selection cost and carries the arsenic pretreatment process.Promptly Herba pteridis vittatae or Da Ye Herba Pteridis multifidae separately or interplanting on arsenic-containing gold ore matrix, the root system by Herba pteridis vittatae or Da Ye Herba Pteridis multifidae absorbs the arsenic in the gold mine in a large number, and upwards carries and be transported to overground part.Harvesting overground part (toothing 3~5cm height) and it is removed when plant-growth to 30~50cm height then can be taken away a large amount of arsenic, thereby reach the purpose of quick removing arsenic from gold mine.
It is to utilize some self-sow or artificially breeding plant to reduce a kind of biologic pretreatment method of the arsenic content in the gold mine that plant is carried the arsenic pretreatment process, its essence is characteristic (being called the tired property of ultraproduct) by means of certain plants energy super quantity absorbing enriched arsenic, with sun power is motivating force, arsenic in a large amount of absorbing enriched cyaniding tailings matrix declines to a great extent mine tailing arsenic content by the harvesting plant.The golden plant of reclaiming again of the low-grade golden mine tailing of rich arsenic is carried the arsenic pretreatment process and utilizes some specified plant arsenic in the absorbing enriched gold mine tailing and reach the purpose that reduces mine tailing arsenic content quickly.Be applicable to through bio-oxidation, high-pressure oxidation and the pretreated various cyanidings of roasting and contain the arsenic tailings.
Three, summary of the invention
The object of the present invention is to provide a kind of plant arsenic-removing pretreatment method of recycling golden from high-arsenic golden mine tailing.By plantation Herba pteridis vittatae or Da Ye Herba Pteridis multifidae, utilize the tired characteristic of its ultraproduct to arsenic, by the arsenic in a large amount of absorbing enriched gold mines of its root system, and arsenic upwards carried and transfers to overground part, remove arsenic in the Gold Ore by the harvesting overground part again, golden mine tailing second stage employ proposed the arsenic pre-treatment thereby finish.
Regulate and control by the Agro-ecology means, its regulation measure comprises the Agro-ecology control method, as regulates its acidity-basicity ph value, moisture, Eo+ (Eh), fertilising etc.The dominant mechanism of Agro-ecology method is the arsenic in the golden mine tailing matrix of activation, increase the mobility of arsenic in the matrix, increase its rate of migration, can reduce effectively to a certain extent that arsenic reclaims the influence of lixiviate once again to gold in the golden mine tailing, and can play golden mine tailing arsenic removal repair to plant.
The present invention finishes by following steps.
1) high arsenic gold mine tailing is taken out from tailing dam through pre-treatment, the thickness of tiling 30~60cm, the pH that adjusts cyanidation tailings are 7.0~8.0 (neutral to weakly alkaline);
Can apply citric acid, oxalic acid, aspartic acid, L-glutamic acid, dilute hydrochloric acid, rare nitric acid and/or dilute sulphuric acid, adjust the pH of cyanidation tailings;
2) regulating the containing on the arsenic gold mine tailing of pH value, according to planting every 15~40cm kind or directly transplanting or spore is cultivated a strain Herba pteridis vittatae or Da Ye Herba Pteridis multifidae.Add acidic fertilizier and/or biological promotor to accelerate Da Ye Herba Pteridis multifidae or Herba pteridis vittatae root system to the absorbing enriched speed of arsenic in the CHARACTERISTICS OF TAILINGS SAND and the speed of growth of plant self;
Can introduce the success ratio that microbial preparation improves fungal infection, promote the symbiosis of mycorrhizal fungi and root system of plant, thereby strengthen the efficient of phytoremediation.
3) Herba pteridis vittatae or Da Ye Herba Pteridis multifidae gather in first and are its growth 3~5 months the time, or gather in first when arsenic content in its overground part surpasses 2500mg/kg, gather in once when arsenic content surpasses 2500mg/kg in overground part later on; Or when it grows into 40~70cm, gather in first, harvesting once during the harvesting overground part, is answered toothing 2~5cm when whenever growing into 40~70cm later on.
Change redox potential and can make sulfide become instability and oxidation discharges heavy metal, finally increased the content of arsenic in the matrix solution, improve the enrichment transport efficacy of plant arsenic.Utilize the happiness calcium characteristic of Herba pteridis vittatae in addition, the calcium peroxide film (CaO that forms when destroying cyaniding 2), make the cyanogen complex ion resolve into nutrients such as carbon, nitrogen by the growth and the root exudates of root system of plant, from root system the arsenic the tailings is transported to part of stem leaf on the ground in the time of along with plant absorbing nutrition.In addition for the golden mine tailing matrix that is rich in iron, Mn oxide, when increasing the matrix organic content, can suitably reduce redox potential, increase the dissolving of iron, Mn oxide, just be released with the heavy metal ion of iron, Mn oxide absorption or co-precipitation, help the absorption extraction of plant, for reclaiming iron, manganese simultaneously certain effect is arranged also simultaneously arsenic.
Compare advantage and positively effect that the present invention has with known technology
Compare with known technology, provided by the invention in high arsenic gold mine tailing plantation Herba pteridis vittatae or Da Ye Herba Pteridis multifidae, utilize that its biomass is big, vegetative period is short and to arsenic in a large amount of absorbing enriched gold of the tired characteristic of the ultraproduct of the arsenic mine tailing and the calcium in the tailings, remove the arsenic of association in the golden mine tailing by the harvesting overground part.The big and arsenic migration total amount height of absorbing enriched amount height, biomagnification coefficient with arsenic does not influence the characteristics such as cyaniding leaching of follow-up auriferous ore.
Four, embodiment
Embodiment 1
The arsenic content of certain high arsenic gold mine tailing is 1%, contains gold grade 0.3g/t.High arsenic gold mine tailing is taken out from tailing dam, and the thickness of tiling 40~50cm was ploughed deeply airing after 4~8 days, on this CHARACTERISTICS OF TAILINGS SAND with plantation one strain Herba pteridis vittatae every about 20cm, the irrigation of watering as required.Auxiliary pouring leaf surface trace fertilizer, its main component are that ammonium nitrate and primary ammonium phosphate are converted the liquid fertilizer that water is formed, and promote it to survive, strengthen photosynthesis, and can increase phytomass by prolonging leaf longevity.In golden mine tailing, water rare citric acid, rare malic acid solution simultaneously.After 4 months, gather in its overground part first, toothing 2~5cm is answered in harvesting.Measure by analysis, arsenic content is reduced to 6740mg/kg by original 10086mg/kg in the mine tailing, is equivalent to make the arsenic content in the gold mine to reduce 33.17%.Later every growth was gathered in once in 3 months, and the arsenic content in the golden mine tailing then constantly reduces, and finally reduced to 85mg/kg by the arsenic of 4 harvesting back cyanidation tailings.Harvested material send the waste guaveyard landfill, or carries out the recycling of arsenic.
Embodiment 2
The gold grade of certain high arsenic gold mine tailing is 0.6g/t, on average contains arsenic 0.7%, and high arsenic gold mine tailing is taken out from tailing dam, and the thickness of the 50~60cm that tiles is ploughed deeply once every day, after 5 days, on this CHARACTERISTICS OF TAILINGS SAND with 60 strains/m 2About spacing plantation Herba pteridis vittatae, between planting season, introduce earthworm and carry out the loose of a matrix, the irrigation of watering as required every two weeks.After plantation 6 months, the harvesting overground part, toothing 2~5cm is answered in harvesting.Arsenic content in the high arsenic gold mine tailing is reduced to 1036mg/kg from 7562mg/kg.
Embodiment 3
The arsenic content mean value of certain high arsenic gold mine tailing is 2.6%, and gold grade is 0.8g/t.High arsenic gold mine tailing is taken out from tailing dam, the CHARACTERISTICS OF TAILINGS SAND that hardens is broken into the particle diameter of 0.05~0.5mm, 1~1.5mm and 2~2.5mm, and three kinds of particle diameters are with the back 40cm that tiles of 1: 1: 1 ratio combination, plough deeply every day 2 times, after 3 days on this gold CHARACTERISTICS OF TAILINGS SAND to plant a strain Da Ye Herba Pteridis multifidae every the 30cm kind.In gold mine matrix, evenly spraying the b diammonium disodium edta salt (EDTA) of 0.1mmol/L, rare tartrate, rare citric acid, rare humic acid and/or rare oxysuccinic acid after the germination every other month.The irrigation of watering as required.After 4 months, gather in its overground part first.The Da Ye Herba Pteridis multifidae that cultivates in advance, continued growth lixiviate arsenic removal are just transplanted in the harvesting back.Grow and gathered in again in 4 months, drop to 110mg/kg by 2 harvesting back high arsenic gold mine tailing arsenic contents.

Claims (4)

1、一种高砷金尾矿再回收金的植物除砷预处理方法,其特征在于:其通过以下步骤完成,1. A plant arsenic removal pretreatment method for reclaiming gold from high-arsenic gold tailings, characterized in that: it is completed through the following steps, 1)把高砷金尾矿从尾矿坝中取出经预处理,平铺30~60cm的厚度,调整金尾矿渣的pH为7.0~8.0;1) Take the high-arsenic gold tailings out of the tailings dam and pre-treat them, spread them with a thickness of 30-60 cm, and adjust the pH of the gold tailings to 7.0-8.0; 2)在调节好pH值的含砷金尾矿上,按照每隔15~40cm种植或直接移栽或孢子培育一株蜈蚣草或大叶井口边草,加入酸性肥料和/或生物促进剂;2) On the arsenic-containing gold tailings with adjusted pH value, plant or directly transplant or spore cultivate a centipede grass or big-leaf wellhead edge grass every 15-40cm, and add acidic fertilizers and/or bioaccelerators; 3)首次收割为其生长3~5个月时,或当其地上部中砷含量超过2500mg/kg时进行首次收割,以后每当地上部中砷含量超过2500mg/kg时收割一次;或当其生长到40~70cm时首次收割,以后每生长到40~70cm时收割一次,收割地上部时,留茬2~5cm。3) Harvest for the first time when it has grown for 3 to 5 months, or when the arsenic content in the aboveground part exceeds 2500mg/kg, and then harvest once every time the arsenic content in the aboveground part exceeds 2500mg/kg; or when it grows Harvest for the first time when it grows to 40-70 cm, and harvest once every time it grows to 40-70 cm. When harvesting the aboveground part, leave 2-5 cm of stubble. 2、根据权利要求1所述的高砷金尾矿再回收金的植物除砷预处理方法,其特征在于:所述预处理为深翻晾晒4~8天后,或每天深翻一次,5天,或把板结的尾矿砂破碎成0.05~0.5mm、1~1.5mm和2~2.5mm的粒径,并且三种粒径以1∶1∶1的比例组合。2. The plant arsenic removal pretreatment method for recovering gold from high-arsenic gold tailings according to claim 1, characterized in that: the pretreatment is deep plowing and drying for 4 to 8 days, or deep plowing once a day for 5 days , or crush the compacted tailings sand into particle sizes of 0.05-0.5mm, 1-1.5mm and 2-2.5mm, and combine the three particle sizes in a ratio of 1:1:1. 3、根据权利要求1所述的高砷金尾矿再回收金的植物除砷预处理方法,其特征在于:施加柠檬酸、草酸、天冬氨酸、谷氨酸、稀盐酸、稀硝酸和/或稀硫酸,调整氰化尾渣的pH。3. The plant arsenic removal pretreatment method for recovering gold from high-arsenic gold tailings according to claim 1, characterized in that: applying citric acid, oxalic acid, aspartic acid, glutamic acid, dilute hydrochloric acid, dilute nitric acid and /or dilute sulfuric acid to adjust the pH of the cyanide tailings. 4、根据权利要求1所述的高砷金尾矿再回收金的植物除砷预处理方法,其特征在于:在种植后辅助浇灌叶面微肥,其主要成分是硝酸铵和磷酸二氢铵兑水组成的液体肥料,或在种植期间每隔半个月引入蚯蚓进行一次基质的疏松,在发芽后向金尾矿中每隔一个月均匀喷洒0.1mmol/L的乙二铵四乙酸二钠盐、稀酒石酸、稀柠檬酸、稀腐殖酸和/或稀苹果酸。4. The plant arsenic removal pretreatment method for recovering gold from high-arsenic gold tailings according to claim 1, characterized in that: after planting, foliar micro-fertilizer is assisted, and its main components are ammonium nitrate and ammonium dihydrogen phosphate Mix liquid fertilizer with water, or introduce earthworms to loosen the substrate every half a month during the planting period, and evenly spray 0.1mmol/L disodium edetate to the gold tailings every other month after germination salt, dilute tartaric acid, dilute citric acid, dilute humic acid and/or dilute malic acid.
CNA2009100941644A 2009-03-09 2009-03-09 Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing Pending CN101492770A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA2009100941644A CN101492770A (en) 2009-03-09 2009-03-09 Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA2009100941644A CN101492770A (en) 2009-03-09 2009-03-09 Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing

Publications (1)

Publication Number Publication Date
CN101492770A true CN101492770A (en) 2009-07-29

Family

ID=40923559

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA2009100941644A Pending CN101492770A (en) 2009-03-09 2009-03-09 Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing

Country Status (1)

Country Link
CN (1) CN101492770A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106111690A (en) * 2016-06-27 2016-11-16 安徽金联地矿科技有限公司 A kind of mine soil restorative procedure and repair materials
US9885095B2 (en) 2014-01-31 2018-02-06 Goldcorp Inc. Process for separation of at least one metal sulfide from a mixed sulfide ore or concentrate
CN107971335A (en) * 2017-11-28 2018-05-01 长春黄金研究院 A kind of method of gold industry cyanogen slag phytoremediation
CN109013669A (en) * 2018-09-28 2018-12-18 长春黄金研究院有限公司 A kind of cyaniding tailing library mine tailings processing method
CN113426818A (en) * 2021-07-02 2021-09-24 昆明理工大学 Method for fixing heavy metal by adding lime powder after pyrolysis of tailings

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9885095B2 (en) 2014-01-31 2018-02-06 Goldcorp Inc. Process for separation of at least one metal sulfide from a mixed sulfide ore or concentrate
US10370739B2 (en) 2014-01-31 2019-08-06 Goldcorp, Inc. Stabilization process for an arsenic solution
US11124857B2 (en) 2014-01-31 2021-09-21 Goldcorp Inc. Process for separation of antimony and arsenic from a leach solution
CN106111690A (en) * 2016-06-27 2016-11-16 安徽金联地矿科技有限公司 A kind of mine soil restorative procedure and repair materials
CN107971335A (en) * 2017-11-28 2018-05-01 长春黄金研究院 A kind of method of gold industry cyanogen slag phytoremediation
CN109013669A (en) * 2018-09-28 2018-12-18 长春黄金研究院有限公司 A kind of cyaniding tailing library mine tailings processing method
CN109013669B (en) * 2018-09-28 2021-07-06 长春黄金研究院有限公司 Method for treating tailings of cyanided tailing pond
CN113426818A (en) * 2021-07-02 2021-09-24 昆明理工大学 Method for fixing heavy metal by adding lime powder after pyrolysis of tailings

Similar Documents

Publication Publication Date Title
Li et al. Fe (III) reduction due to low pe+ pH contributes to reducing Cd transfer within a soil-rice system
Xian et al. Steel slag as an iron fertilizer for corn growth and soil improvement in a pot experiment
CN103785679B (en) A kind of method improving the phytoremediation efficiency of copper polluted soil
CN106797820B (en) Mine ecological restoration nutrient covering soil with municipal sludge as main matrix and preparation method thereof
El-Hassanin et al. Effect of foliar application with humic acid substances under nitrogen fertilization levels on quality and yields of sugar beet plant
CN104529668A (en) Metal mine soil conditioner, and mine ecological remediation method using metal mine soil conditioner.
CN100500890C (en) A plant-extracting arsenic pretreatment method for reducing the cost of beneficiation and smelting of high-arsenic-containing gold ore
CN102399111A (en) Greening matrix and phytoremediation technology method of pulverized coal gangue
CN101492770A (en) Plant arsenic-removing pretreatment method for recycling golden from high-arsenic golden mine tailing
CN101695711B (en) A chemical immobilization material suitable for soil arsenic and its application
CN110771464A (en) Culture solution for reducing rice cadmium accumulation in cadmium-polluted soil and rice planting method
CN108541522A (en) A kind of acidity mining area refuse dump method for recovering vegetation
CN101597182B (en) Application of ammonium sulfate mixed liquor in extracting heavy metals from waste composts with lawn plants
CN114367532A (en) Using phosphogypsum and fungus residue to improve lead-zinc mine wasteland and promote the method of replanting
CN108668552A (en) A kind of ion type rareearth tailings ground modifying agent and its restorative procedure
CN102775218A (en) Method for preparing plant nutrient solution from sludge microproteins
Heba et al. Effect of some organic extracts on essential nutrients uptake of sugar beet under saline conditions
CN101491724B (en) Method for quickening plant degrading cyanide complex of cyanidation tailings
CN106222110A (en) A kind of microbial product administering heavy metal pollution sandy soil and manufacture method thereof
Najafi et al. Effects of soil water conditions, sewage sludge, poultry manure and chemical fertilizers on macronutrients concentrations in rice plant.
Humaria Impact of iron and steel slag on crop cultivation: a review
Mahrous et al. Effect of applying some soil amendments and distance between drains on quality and productivity of soybean grown under saline conditions
CN106903148B (en) Method for repairing vanadium ore polluted soil by utilizing bacillus subtilis to strengthen rorifolia
Sebastian et al. Rice plants for cleanup of trace elements—Bioeconomic perspectives
CN111515242A (en) Method for repairing rare earth mine by using slash pine and iron dicranopteris pedata

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Open date: 20090729