TW201825150A - Method for removing heavy metals from soils capable of effectively removing heavy metals from soils and shortening plant rehabilitation time - Google Patents

Method for removing heavy metals from soils capable of effectively removing heavy metals from soils and shortening plant rehabilitation time Download PDF

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TW201825150A
TW201825150A TW106100845A TW106100845A TW201825150A TW 201825150 A TW201825150 A TW 201825150A TW 106100845 A TW106100845 A TW 106100845A TW 106100845 A TW106100845 A TW 106100845A TW 201825150 A TW201825150 A TW 201825150A
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soil
plant
heavy metals
fermentation broth
fern
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崔砢
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明志科技大學
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Abstract

The present invention provides a method for removing heavy metals from soils, which includes planting a plant in a soil contaminated with heavy metals; adding a fermentation broth into the soil, wherein the fermentation broth is obtained by culturing a yeast, a lactic acid bacteria, photosynthetic bacteria and Pseudomonas into a molasses culture solution until the molasses culture solution reaches a pH value of 4 or less; growing the plant to grow leaves, blossom or produce fruits; and removing the plant shoots.

Description

自土壤去除重金屬的方法Method for removing heavy metals from soil

本發明關於土壤復育的技術領域,且特別提出一種自土壤去除重金屬的方法。The invention relates to the technical field of soil rehabilitation, and particularly proposes a method for removing heavy metals from soil.

工業的快速發展雖然帶動整體經濟繁榮,反而導致環境污染,如:空氣汙染、水汙染、土地汙染。重金屬會導致土地污染,且由於汙染源相對難以去除,進入人體內後造成的傷害極大,故重金屬導致的土地汙染格外受關注。Although the rapid development of industry has promoted the overall economic prosperity, it has led to environmental pollution, such as air pollution, water pollution, and land pollution. Heavy metals can cause land pollution, and because the pollution source is relatively difficult to remove, and the damage caused by entering the human body is extremely great, land pollution caused by heavy metals is of particular concern.

目前常用之處理土壤重金屬的方法有:翻轉稀釋法、化學去除法、及植生復育法。「翻轉稀釋法」主要為將受汙染的土壤翻堆混合,但事實上土壤仍存在有重金屬並未真正自土壤去除。「化學去除法」主要為利用稀酸溶液或螯合劑與受汙染的土壤作用;經化學去除法後,重金屬雖然可自受汙染的土壤去除,但作用後土壤質地與肥力變差,從而影響土壤後續應用。「植生復育法」主要為種植植物於受汙染的土壤,而透過植物吸收重金屬;然而,重金屬與土壤顆粒分別帶有正電荷與負電荷而相互吸引,故重金屬不易移動,使得所須耗費的整治時間長。另方面,植物吸收重金屬後,重金屬多集中於植物根部,因而須移除整株植物始能自土壤去除重金屬。若土壤受汙染的程度過嚴重須多次進行植生復育法,則每次都須重新種植植物並待植物長葉、開花、或結果。如此一來,更延長多次進行整體耗費的整治時間。At present, the commonly used methods for treating heavy metals in soil are: flip dilution method, chemical removal method, and vegetative rejuvenation method. The "flip-and-dilution method" is mainly to mix and contaminate the contaminated soil, but in fact there are still heavy metals in the soil that have not really been removed from the soil. "Chemical removal method" mainly uses dilute acid solution or chelating agent to interact with the contaminated soil. After chemical removal method, although heavy metals can be removed from the contaminated soil, the soil texture and fertility become worse after the effect, which affects the soil Follow-up application. The "Plant Rejuvenation Method" is mainly for planting plants in contaminated soil and absorbing heavy metals through the plants; however, heavy metals and soil particles are attracted to each other with positive and negative charges, so the heavy metals are not easy to move, making the costly Long rectification time. On the other hand, after a plant absorbs heavy metals, most of the heavy metals are concentrated in the roots of the plants, so the entire plant must be removed before the heavy metals can be removed from the soil. If the soil is too polluted, phytorejuvenation methods must be carried out multiple times, and plants must be replanted each time and the plants need to grow leaves, flower, or bear fruit. In this way, the overall rectification time that is repeatedly carried out is extended.

職是之故,確實有必要提出一種新的植生復育法以解決目前所採用之植生復育法的問題。For this reason, it is indeed necessary to propose a new vegetative rejuvenation method to solve the problem of the currently used vegetative rejuvenation method.

本發明之目的在於改善目前用於處理土壤重金屬之植生復育法的問題,如重金屬移動性不佳所導致每次進行植生復育法耗費的整治時間過長、及/或須整株植物移除所導致多次進行植生復育法整體耗費的整治時間過長等。The purpose of the present invention is to improve the problems of current phytoremediation methods for treating heavy metals in the soil, such as the excessive remediation time required for each phytoremediation method caused by poor mobility of heavy metals, and / or the entire plant must be moved In addition, the overall time required for remediation of the phytoremediation method is too long.

於是,為達到上述及/或其他目的,本發明提出一種自土壤去除重金屬的方法,其包括:種植一植物於一受重金屬汙染的土壤;添加一發酵液至土壤中,其中發酵液為培養酵母菌、乳酸菌、光合菌、與假單胞菌至一糖蜜培養液中,直到糖蜜培養液的pH值達4以下所取得的;培養植物至其長葉、開花或結果;以及移除植物地上部。Therefore, in order to achieve the above and / or other objectives, the present invention proposes a method for removing heavy metals from soil, which includes: planting a plant in a soil contaminated with heavy metals; adding a fermentation broth to the soil, wherein the fermentation broth is cultured yeast Bacteria, lactic acid bacteria, photosynthetic bacteria, and Pseudomonas into a molasses broth until the pH of the molasses broth reaches below 4; cultivating the plant to its long leaves, flowering or fruiting; and removing the plant aerial .

根據本發明,所用的發酵液可促進植物生長,以提高植物對重金屬所造成之毒害的耐受性。而且,發酵液亦可提升植物吸收重金屬的能力,並協助重金屬自植物地下部轉移至地上部。藉此方式,植物培養後直接移除地上部便可達到自土壤去取重金屬的效果,不一定須整株植物移除。若土壤的汙染程度過嚴重,直接繼續添加發酵液即可進行下一次去除,不一定須重新種植植物。According to the present invention, the fermentation broth used can promote the growth of plants to increase the tolerance of the plants to the poisons caused by heavy metals. In addition, the fermentation broth can also enhance the ability of plants to absorb heavy metals, and assist in the transfer of heavy metals from the lower part of the plant to the upper part of the plant. In this way, the effect of removing heavy metals from the soil can be achieved by directly removing the aerial parts after the plants are cultivated, and it is not necessary to remove the entire plant. If the soil is too polluted, continue to add the fermentation broth to carry out the next removal without necessarily re-planting the plants.

為讓本發明上述及/或其他目的、功效、特徵更明顯易懂,下文特舉較佳實施方式,作詳細說明於下:In order to make the foregoing and / or other objectives, effects, and features of the present invention more comprehensible, the preferred embodiments are described below in detail as follows:

本發明之一實施方式提出一種自土壤去除重金屬的方法,此法透過植物的種植與特定發酵液的處理,以將重金屬自土壤轉移至植物地上部。之後,直接移除植物地上部便可自土壤去除重金屬。攸關此實施方式所提之方法的詳細步驟如下:An embodiment of the present invention provides a method for removing heavy metals from soil. This method transfers heavy metals from the soil to the above-ground parts of the plant through the planting of plants and the treatment of specific fermentation broth. Afterwards, heavy metals can be removed from the soil by directly removing the plant parts. The detailed steps related to the method mentioned in this embodiment are as follows:

首先,種植植物於受重金屬汙染的土壤。一般而言,草本植物的生命周期較木本植物的生命周期短,且草本植物的地上部較木本植物的地上部易移除,因此所用的植物以草本植物為宜。植物的實例可以為但不限於水稻、玉米、印度芥菜、甜菜根、向日葵、白茅、蘆葦、培地茅、美洲闊苞菊、王爺葵、多花油柑、小果葉下珠、箭葉鳳尾蕨、鳳尾蕨、鱗蓋鳳尾蕨、波斯頓蕨、腎蕨、或長葉腎蕨;而,重金屬的實例可以為但不限於鎘、鋅、汞、銅、鉛、砷、鎳、鉻、鋇、硒、或銻。另為促進植物生長,植物種植前或時可添加一肥料至土壤中,而肥料的實例可以為但不限於博西卡(Bokashi)肥料。First, grow plants in soil contaminated with heavy metals. In general, the life cycle of a herbaceous plant is shorter than that of a woody plant, and the above-ground part of an herbaceous plant is easier to remove than the above-ground part of a woody plant. Therefore, the plant used is preferably an herbaceous plant. Examples of plants can be, but are not limited to, rice, corn, Indian mustard, beetroot, sunflower, white grass, reed, prickly grass, broadleaf daisy, queen's sunflower, mandarin orange, small fruit leaf bead, arrow leaf anemone Ferns, Anchovies, Anchovies, Boston Ferns, Kidney Ferns, or Long Leaf Kidney Ferns; and examples of heavy metals can be, but are not limited to, cadmium, zinc, mercury, copper, lead, arsenic, nickel, chromium , Barium, selenium, or antimony. In addition, to promote plant growth, a fertilizer may be added to the soil before or during planting, and examples of the fertilizer may be, but not limited to, Bokashi fertilizer.

其次,添加一發酵液至土壤中,其中發酵液為培養酵母菌、乳酸菌、光合菌、與假單胞菌至一糖蜜培養液中,直到糖蜜培養液的pH值達4以下所取得的。另為放大發酵液體積以讓發酵液可與土壤均勻混合,添加前發酵液可先與一適當液體混合,如:水、生理食鹽水、液肥、或其他適於上述混合菌生長的培養液。此外,於本實施方式,此發酵液添加步驟於植物種植步驟後第15至45天進行。而且,為促進植物吸收重金屬的能力,本實施方式於進行此發酵液添加步驟時更可添加一螯合劑至土壤中,而螯合劑的實例可以為但不限於EDTA(ethylenediaminetetraacetic acid)、DTPA(diethylenetriaminepentaacetate)、NTA(nitrilotriacetic acid)、或EDDS(ethylenediamine-N,N'-disuccinic acid)。Secondly, a fermentation broth is added to the soil, wherein the fermentation broth is obtained by culturing yeast, lactic acid bacteria, photosynthetic bacteria, and Pseudomonas into a molasses broth until the pH of the molasses broth reaches 4 or less. In addition, in order to enlarge the volume of the fermentation broth so that the fermentation broth can be uniformly mixed with the soil, the fermentation broth can be mixed with an appropriate liquid before addition, such as water, physiological saline, liquid fertilizer, or other culture broth suitable for the growth of the mixed bacteria. In addition, in this embodiment, the fermentation broth adding step is performed on the 15th to 45th days after the plant growing step. In addition, in order to promote the ability of plants to absorb heavy metals, a chelating agent may be added to the soil when the fermentation broth is added in this embodiment, and examples of the chelating agent may be, but not limited to, EDTA (ethylenediaminetetraacetic acid), DTPA (diethylenetriaminepentaacetate) ), NTA (nitrilotriacetic acid), or EDDS (ethylenediamine-N, N'-disuccinic acid).

接著,培養植物至其長葉、開花或結果。另外,於本實施方式,培養時每隔4至14天可添加相同發酵液至土壤中以維持發酵液於土壤的濃度。同樣地,為維持螯合劑於土壤的濃度,培養時每隔4至14天可添加相同螯合劑至土壤中。Next, the plant is grown to its long leaves, flowering or fruiting. In addition, in the present embodiment, the same fermentation broth may be added to the soil every 4 to 14 days during the cultivation to maintain the concentration of the fermentation broth in the soil. Similarly, in order to maintain the concentration of the chelating agent in the soil, the same chelating agent may be added to the soil every 4 to 14 days during culture.

最後,移除植物地上部。所謂「地上部」是相對於植物地下部,主要指植物未埋於土壤的器官,如莖、葉、花、果實、或其任意組成。須說明的是,植物地上部移除步驟可直接除掉植物地上部而保留地下部於土壤中、或者直接自土壤除掉整株植物來執行。Finally, the plant ground is removed. The so-called "above-ground part" refers to the lower part of the plant, which mainly refers to the organs of the plant that are not buried in the soil, such as stems, leaves, flowers, fruits, or any composition thereof. It should be noted that the step of removing the above-ground plant can be performed by directly removing the above-ground plant and retaining the above-ground part in the soil, or directly removing the entire plant from the soil.

茲以下列實施例,例示說明本發明:The following examples illustrate the invention:

<鎘金屬汙染土壤的製備>< Preparation of cadmium metal contaminated soil >

先加入去離子水至一土壤中並混合約1周,以維持土壤田間容水量(field capacity)約50%。加入硝酸鎘溶液至土壤後,以石灰調整土壤pH值,並混合2周,以維持土壤田間容水量約50%。然後,對土壤進行3次乾溼交替,以取得鎘金屬汙染的土壤。若有必要,可預先添加200g博西卡肥料與土壤混合。First add deionized water to a soil and mix for about 1 week to maintain the soil field capacity of about 50%. After adding the cadmium nitrate solution to the soil, adjust the pH of the soil with lime and mix for 2 weeks to maintain the water capacity of the soil field at about 50%. Then, the soil was alternated between wet and dry 3 times to obtain soil contaminated with cadmium metal. If necessary, 200g of bosica fertilizer can be added in advance and mixed with the soil.

<水稻的種植與有益混合菌之發酵液的添加>< The cultivation of rice and the addition of fermentation broth of beneficial bacteria >

水稻栽種於鎘金屬汙染的土壤中1個月後,先pH為4以下之有益混合菌的發酵液與水以1:50至1:200的比例混合,以得到稀釋發酵液,再將稀釋發酵液添加至土壤中;而有益混合菌之發酵液的製備為:培養酵母菌、乳酸菌、光合菌、與假單胞菌(於下文,四菌種總稱為「有益混合菌」)至一糖蜜培養液中,直到糖蜜培養液的pH值達4以下。接著,依水稻生理特性培養,培養時每隔1周添加相同稀釋發酵液至土壤中,直到水稻結穗。若有必要,添加稀釋發酵液時,可添加含量2mmol/kg土壤的EDTA溶液至土壤中;且於培養時每隔1周可添加相同量的EDTA溶液至土壤中,共3周。After rice was planted in cadmium-contaminated soil for one month, the fermentation broth of beneficial mixed bacteria with pH below 4 was first mixed with water at a ratio of 1:50 to 1: 200 to obtain a diluted fermentation broth, and the diluted fermentation was then performed. Liquid is added to the soil; and the fermentation broth of beneficial mixed bacteria is prepared by culturing yeast, lactic acid bacteria, photosynthetic bacteria, and pseudomonas (hereinafter, the four strains are collectively referred to as "beneficial mixed bacteria") to a molasses culture Until the pH of the molasses broth reaches 4 or less. Next, culture according to the physiological characteristics of rice, and the same diluted fermentation broth is added to the soil every one week during the cultivation until the rice panicles are formed. If necessary, when adding a diluted fermentation broth, an EDTA solution with a content of 2 mmol / kg soil can be added to the soil; and the same amount of EDTA solution can be added to the soil every other week during the cultivation for a total of 3 weeks.

<水稻的外觀>< Appearance of rice >

結穗後,連根拔起整株水稻,並量測水稻高度與重量。如表1所示,鎘金屬確實會影響水稻生長;但於同樣受鎘金屬汙染下,添加有稀釋發酵液的土壤較無添加的土壤有助於水稻生長。 表1、水稻於含不同添加物之土壤培養後的生長狀況 After earing, the whole rice was uprooted and the height and weight of the rice were measured. As shown in Table 1, cadmium metal does affect rice growth; but under the same contamination with cadmium metal, soil added with diluted fermentation broth is better for soil growth than non-added soil. Table 1. Growth status of rice after cultivation in soil with different additives

<鎘金屬含量的分析>< Analysis of Cadmium Metal Content >

結穗後,取1g水稻各器官。加入10mL硝酸至各器官後,靜置1小時。接著,對所得的硝酸溶液依序進行微波處理、過濾、與分析,以取得水稻各器官的鎘金屬含量。After earing, 1 g of rice organs were taken. After adding 10 mL of nitric acid to each organ, let stand for 1 hour. Next, the obtained nitric acid solution was sequentially subjected to microwave treatment, filtration, and analysis to obtain the cadmium metal content of each organ of rice.

結穗後,另取1g土壤。加入9mL硝酸與3mL氫氟酸至土壤後,靜置1小時。之後,對所取得的酸溶液進行微波處理;於加入15mL的4%硼酸溶液至酸溶液後,再對酸溶液進行微波處理、過濾、與分析,以取得土壤的鎘金屬含量。After earing, another 1 g of soil was taken. After adding 9 mL of nitric acid and 3 mL of hydrofluoric acid to the soil, let stand for 1 hour. After that, the obtained acid solution is subjected to microwave treatment; after adding 15 mL of a 4% boric acid solution to the acid solution, the acid solution is subjected to microwave treatment, filtration, and analysis to obtain the cadmium metal content of the soil.

如圖1所示,相較於培養於無添加之土壤的水稻,培養於僅添加稀釋發酵液之土壤的水稻能吸收較多量的重金屬,且多數存在於地上部,尤其莖的重金屬濃度大於根的重金屬濃度。另外,相較於無添加的土壤,添加稀釋發酵液與螯合劑的土壤促進水稻吸收重金屬的量略多。雖然相較於無添加的土壤,添加稀釋發酵液與博卡西肥料之土壤及添加稀釋發酵液、螯合劑、與博卡西肥料之土壤促進水稻吸收重金屬的量較少,但後二者對植物生長較前者有助益(表1)。As shown in Figure 1, compared to rice cultivated in soil without addition, rice cultivated in soil with only diluted fermentation broth can absorb a larger amount of heavy metals, and most of them are above ground, especially the stem has a higher concentration of heavy metals than roots. Heavy metal concentration. In addition, compared with the non-added soil, the amount of heavy metals absorbed by rice was slightly increased in the soil with diluted fermentation broth and chelating agent. Although the soils with diluted fermentation broth and bocasi fertilizer and the soils with diluted fermentation broth, chelating agent, and bocasi fertilizer promoted less absorption of heavy metals compared to soils without added fertilizer, the latter two were opposite. Plant growth is more beneficial than the former (Table 1).

於此,介紹以下術語:BCF,全名為bioconcentration factor,中文稱作「生物濃縮因子」,指植物根部的重金屬濃度除以土壤之重金屬濃度所得的值;TF,全名為translocation factor,中文稱作「植物傳輸因子」,指植物地上部的重金屬濃度除以植物根部之重金屬濃度所得的值;BAF,全名為bioaccumulation factor,中文稱作「生物累積因子」,指植物地上部的重金屬濃度除以土壤之重金屬濃度所得的值,亦即BCF乘以TF所得的值。Here, the following terms are introduced: BCF, full name bioconcentration factor, Chinese term "biological concentration factor", refers to the value obtained by dividing the concentration of heavy metals in the roots of plants by the concentration of heavy metals in the soil; TF, the full name is translocation factor, in Chinese As "plant transmission factor", it refers to the value obtained by dividing the concentration of heavy metals above the plant by the concentration of heavy metals at the root of the plant; BAF, full name is bioaccumulation factor, which is called "bioaccumulation factor" in Chinese, refers to the concentration of heavy metals above the plant The value obtained by the concentration of heavy metals in the soil, that is, the value obtained by multiplying BCF by TF.

由上述定義可知,BCF代表重金屬自土壤轉移至根部的能力,TF代表重金屬自根部轉移至地上部的能力,BAF代表重金屬自土壤轉移至地上部的能力。由表2可知,無論是否與其他物質混合,添加稀釋發酵液之土壤的TF與BAF均優於無添加的土壤。這表示稀釋發酵液可促進重金屬自土壤轉移至地上部。 表2、鎘金屬於含不同添加物之土壤培養水稻後的分布 From the above definition, BCF represents the ability of heavy metals to transfer from the soil to the roots, TF represents the ability of heavy metals to transfer from the roots to the ground, and BAF represents the ability of heavy metals to transfer from the soil to the ground. It can be known from Table 2 that TF and BAF of the soil with the diluted fermentation broth are better than those without the addition of the soil, whether mixed with other substances or not. This means that dilute fermentation broth can promote the transfer of heavy metals from soil to above ground. Table 2. Distribution of cadmium metal after rice cultivation in soil with different additives

綜上所述,本實施方式的發酵液可促進植物生長,以提高植物對重金屬所造成之毒害的耐受性。而且,此發酵液亦可提升植物吸收重金屬的能力,並協助重金屬自植物地下部轉移至地上部。藉此方式,植物培養後直接移除地上部便可達到自土壤去取重金屬的效果,不一定須整株植物移除。若土壤的汙染程度過嚴重,直接繼續添加發酵液即可進行下一次去除,不一定須重新種植植物。In summary, the fermentation broth of this embodiment can promote the growth of plants, so as to improve the tolerance of plants to poisons caused by heavy metals. In addition, the fermentation broth can also enhance the ability of plants to absorb heavy metals, and assist in the transfer of heavy metals from the lower part of the plant to the upper part of the plant. In this way, the effect of removing heavy metals from the soil can be achieved by directly removing the aerial parts after the plants are cultivated, and it is not necessary to remove the entire plant. If the soil is too polluted, continue to add the fermentation broth to carry out the next removal without necessarily re-planting the plants.

惟以上所述者,僅為本發明之較佳實施例,但不能以此限定本發明實施之範圍;故,凡依本發明申請專利範圍及發明說明書內容所作之簡單的等效改變與修飾,皆仍屬本發明專利涵蓋之範圍內。However, the above are merely preferred embodiments of the present invention, but cannot limit the scope of implementation of the present invention; therefore, any simple equivalent changes and modifications made in accordance with the scope of patent application and the contents of the invention specification of the present invention, All are still within the scope of the invention patent.

no

圖1為一長條圖,說明水稻各器官於不同方式處理土壤後的鎘金屬吸收量。Figure 1 is a bar graph illustrating the amount of cadmium metal absorbed by various organs of rice after treating the soil in different ways.

Claims (10)

一種自土壤去除重金屬的方法,係包括: 種植一植物於一受重金屬汙染的土壤; 添加一發酵液至該土壤中,其中該發酵液為培養酵母菌、乳酸菌、光合菌、與假單胞菌至一糖蜜培養液中,直到該糖蜜培養液的pH值達4以下所取得的; 培養該植物至其長葉、開花或結果;以及 移除該植物地上部。A method for removing heavy metals from soil, comprising: planting a plant in soil contaminated by heavy metals; adding a fermentation broth to the soil, wherein the fermentation broth is cultured yeast, lactic acid bacteria, photosynthetic bacteria, and pseudomonas Into a molasses broth until the pH of the molasses broth reaches below 4; growing the plant to its long leaves, flowering or fruiting; and removing the above-ground part of the plant. 如請求項第1項所述之方法,其中該植物為草本植物。The method according to claim 1, wherein the plant is a herbaceous plant. 如請求項第1項所述之方法,其中該植物為選自於由水稻、玉米、印度芥菜、甜菜根、向日葵、白茅、蘆葦、培地茅、美洲闊苞菊、王爺葵、多花油柑、小果葉下珠、箭葉鳳尾蕨、鳳尾蕨、鱗蓋鳳尾蕨、波斯頓蕨、腎蕨、及長葉腎蕨所組成的群組。The method according to claim 1, wherein the plant is selected from the group consisting of rice, corn, Indian mustard, beetroot, sunflower, white grass, reeds, pelagow grass, American broadleaf, queen kwai, and oleander , Small fruit leaves under beads, arrowleaf anchovy fern, anchovies fern, anemone fern, Boston fern, kidney fern, and longleaf kidney fern. 如請求項第1項所述之方法,其中該重金屬為選自於由鎘、鋅、汞、銅、鉛、砷、鎳、鉻、鋇、硒、及銻所組成的群組。The method according to claim 1, wherein the heavy metal is selected from the group consisting of cadmium, zinc, mercury, copper, lead, arsenic, nickel, chromium, barium, selenium, and antimony. 如請求項第1項所述之方法,其中該植物種植步驟前或時,更包括: 添加一肥料至該土壤中。The method according to claim 1, wherein before or during the step of planting, the method further comprises: adding a fertilizer to the soil. 如請求項第5項所述之方法,其中該肥料為博卡西(Bokashi)肥料。The method according to claim 5, wherein the fertilizer is Bokashi fertilizer. 如請求項第1項所述之方法,其中該植物的地上部為莖、葉、花、或果實。The method according to claim 1, wherein the above-ground part of the plant is a stem, a leaf, a flower, or a fruit. 如請求項第1項所述之方法,其中該發酵液添加步驟為於該植物種植步驟後第15至45天進行。The method according to item 1 of the claim, wherein the fermentation broth adding step is performed 15 to 45 days after the plant growing step. 如請求項第1項所述之方法,其中該植物培養步驟包括: 添加同一發酵液至該土壤中。The method of claim 1, wherein the step of cultivating the plant comprises: adding the same fermentation broth to the soil. 如請求項第1項所述之方法,其中該發酵液添加步驟更包括: 添加一螯合劑至該土壤中。The method according to claim 1, wherein the step of adding the fermentation broth further comprises: adding a chelating agent to the soil.
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