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CN102154142B - Microorganism for promoting black nightshade to remove trace cadmium pollution in water and method for removing cadmium pollution - Google Patents

Microorganism for promoting black nightshade to remove trace cadmium pollution in water and method for removing cadmium pollution Download PDF

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CN102154142B
CN102154142B CN2010105131400A CN201010513140A CN102154142B CN 102154142 B CN102154142 B CN 102154142B CN 2010105131400 A CN2010105131400 A CN 2010105131400A CN 201010513140 A CN201010513140 A CN 201010513140A CN 102154142 B CN102154142 B CN 102154142B
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罗胜联
陈觉梁
陈亮
饶婵
李波
刘承斌
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Hunan University
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Abstract

本发明提供了一种促进龙葵去除水中微量镉污染的微生物及其去除镉污染的方法,利用超累积植物龙葵对镉的高效吸收特性来净化受到镉污染的饮用水。采用水培方式培养龙葵,通过接种金黄杆菌Chryseobacterium sp.LKS03促进其根部生长。净化饮用水时将龙葵植株的根部浸入含有镉污染的饮用水中,每株龙葵在一个净化周期内对应净化约1-1.2升饮用水,根据水样中镉离子浓度的高低(不高于200μg/L),所需的净化时间从2小时至12小时不等,龙葵植株在其培养周期的第45-80天内净化水样的能力最佳。该方法针对饮用水中镉污染的去除效果好、操作简便、适用范围广,在饮用水净化方面具有很大的应用潜力。The invention provides a microorganism that promotes nightshade nightshade to remove trace cadmium pollution in water and a method for removing cadmium pollution, and uses the high-efficiency absorption characteristic of cadmium of the superaccumulative plant nightshade to purify drinking water polluted by cadmium. Solanum solanum was cultivated in hydroponics, and its root growth was promoted by inoculating Chryseobacterium sp.LKS03. When purifying drinking water, immerse the roots of Solanum nigrum plants in drinking water containing cadmium pollution. Each plant of Solanum nigrum will purify about 1-1.2 liters of drinking water in one purification cycle, depending on the concentration of cadmium ions in the water sample (not high 200μg/L), the required purification time ranges from 2 hours to 12 hours, and the ability of Solanum nigrum plants to purify water samples is the best in the 45th-80th day of its culture cycle. The method has the advantages of good removal effect of cadmium pollution in drinking water, simple operation and wide application range, and has great application potential in drinking water purification.

Description

一种促进龙葵去除水中微量镉污染的微生物及其去除镉污染的方法A kind of microorganism that promotes nightshade to remove trace cadmium pollution in water and method for removing cadmium pollution

技术领域 technical field

本发明涉及微量镉污染饮用水的生物学净化方法,具体涉及利用龙葵去除水中微量镉污染的方法及其采用的微生物。The invention relates to a biological purification method for drinking water polluted by trace amounts of cadmium, in particular to a method for removing trace amounts of cadmium pollution in water by using black nightshade and the microorganisms used.

背景技术 Background technique

工业发展往往伴随的环境污染的产生,“工业三废”中的废水废渣排放引起的水体重金属污染问题越来越严重,不仅破坏生态环境,而且直接或间接危害人们的身体健康。重金属镉污染主要来自印染、农药、矿石开采、冶炼等行业,长期摄入微量镉,会严重损害人体的肝、肾等器官,进而引发多种疾病。欧洲和日本因镉污染引发的骨痛病,是镉污染区域镉中毒的常见病。Industrial development is often accompanied by environmental pollution. The problem of heavy metal pollution in water caused by the discharge of waste water and residue in the "three industrial wastes" is becoming more and more serious, which not only destroys the ecological environment, but also directly or indirectly endangers people's health. Heavy metal cadmium pollution mainly comes from printing and dyeing, pesticides, ore mining, smelting and other industries. Long-term intake of trace amounts of cadmium will seriously damage the liver, kidney and other organs of the human body, and cause various diseases. Osteopathy caused by cadmium pollution in Europe and Japan is a common disease caused by cadmium poisoning in cadmium-polluted areas.

常用的去除饮用水中镉污染的方法主要有:絮凝剂过滤法、石灰沉淀法、离子交换法、电解法等,但这些方法在处理过程中存在着产生二次污染、费用过高、重复利用性不强、工艺复杂等缺陷。因此研究出一种高效,环保,低成本的方法是目前科技发展的趋势,本发明采用的生物学净化方法,就会解决现有方法出现的一系列问题。Commonly used methods to remove cadmium pollution in drinking water mainly include: flocculant filtration method, lime precipitation method, ion exchange method, electrolysis method, etc., but these methods have secondary pollution, high cost, and repeated use during the treatment process. Poor performance, complex process and other defects. Therefore researching out a kind of efficient, environment-friendly, low-cost method is the trend of current technological development, the biological purification method that the present invention adopts, will solve a series of problems that existing method occurs.

发明内容: Invention content:

本发明要解决的技术问题是克服现有技术的不足,提供一种促进龙葵去除水中微量镉污染的微生物及其去除镉污染方法,该方法操作简单、经济高效、环境友好。The technical problem to be solved by the present invention is to overcome the deficiencies of the prior art, and provide a microorganism that promotes the removal of trace cadmium pollution in water by Solanum nigrum and a method for removing cadmium pollution. The method is simple to operate, economical and efficient, and environmentally friendly.

一种促进龙葵去除水中微量镉污染的微生物,为金黄杆菌Chryseobacterium sp.LKS03,保藏号为CCTCC NO:M 2010236。A microorganism that promotes the removal of trace cadmium pollution in water from Solanum nigrum is Chryseobacterium sp.LKS03, and its preservation number is CCTCC NO: M 2010236.

应用所述的微生物促进龙葵去除水中微量镉污染的方法,将龙葵种子表面灭菌后在金黄杆菌Chryseobacterium sp.LKS03菌液中浸泡1-3小时,取出播种,两周后转入水培;再过30天后的龙葵植株用于净化水。Apply the method for promoting the removal of trace cadmium pollution in water by microorganisms, sterilize the surface of Solanum nigrum seeds, soak them in the Chryseobacterium sp. ; After another 30 days the nightshade plants were used for water purification.

所述的龙葵种子经75%酒精溶液浸泡15秒进行表面灭菌,清水冲洗3次,晾干后用于内生菌菌液浸泡。The solanum nigrum seeds are soaked in 75% alcohol solution for 15 seconds to sterilize the surface, rinsed with clear water for 3 times, dried and used for soaking in endophytic bacteria solution.

所述的菌液配置过程如下:挑取金黄杆菌Chryseobacterium sp.LKS03菌种接种至100ml液体LB培养基中扩大培养12小时,4000转/分钟离心5分钟,倒去上清,用100ml 1/4浓度的改良霍格兰溶液重悬细菌菌体,即得到内生菌接种菌液。The preparation process of the bacterial solution is as follows: Pick the Chryseobacterium sp.LKS03 bacterial strain and inoculate it into 100ml liquid LB medium for expansion and cultivation for 12 hours, centrifuge at 4000 rpm for 5 minutes, pour off the supernatant, and use 100ml 1/4 Concentration of modified Hoagland's solution to resuspend bacterial cells to obtain endophyte inoculum.

所述的播种是将蛭石铺于托盘中,厚度4-6厘米,用1/4浓度的改良霍格兰溶液浇透,龙葵种子播种于其中。The sowing is to spread the vermiculite in the tray with a thickness of 4-6 cm, pour the modified Hoagland solution with 1/4 concentration, and sow nightshade seeds therein.

所述的水培是采用1/4浓度的改良霍格兰溶液作为水培营养液,4-6天换一次营养液,并不断补充。Said hydroponics adopts 1/4 concentration of modified Hoagland's solution as the hydroponic nutrient solution, and the nutrient solution is changed every 4-6 days and constantly replenished.

所述的1/4浓度的改良霍格兰溶液配方为:KNO3 125mg/L;KH2PO4 35mg/L;NH4H2PO420mg/L;MgSO4·7H2O 125mg/L;Ca(NO3)2·4H2O 235mg/L;FeSO4·7H2O 10mg/L。The formulation of the improved Hoagland's solution with 1/4 concentration is: KNO 3 125mg/L; KH 2 PO 4 35mg/L; NH 4 H 2 PO 4 20mg/L; MgSO 4 ·7H 2 O 125mg/L; Ca(NO 3 ) 2 .4H 2 O 235 mg/L; FeSO 4 .7H 2 O 10 mg/L.

所述的龙葵植株用于净化水的时间为30-40天。The time for the said nightshade plant to purify water is 30-40 days.

所述的龙葵植株根部与水体接触来净化水。The roots of the Solanum nigrum plant are in contact with the water body to purify the water.

所述的龙葵用于处理镉离子浓度为不高于200μg/L的饮用水;所述的龙葵植株经过一轮2-12小时净水处理后,继续水培培养24小时,龙葵将大部分吸收的金属镉从根部运输到叶片和茎秆保存,恢复净水能力,可进行下一轮净水处理。每株龙葵对应净化1-1.2升镉污染的水。The Solanum nigrum is used to treat drinking water with a concentration of cadmium ions not higher than 200 μg/L; the Solanum nigrum plant will continue to be hydroponic for 24 hours after a round of water purification treatment for 2-12 hours, and the Solanum nigrum will be Most of the absorbed metal cadmium is transported from the roots to the leaves and stems for storage, and the water purification ability is restored, which can be used for the next round of water purification treatment. Each Solanum nigrum corresponds to purifying 1-1.2 liters of cadmium-polluted water.

经处理后水样均达到国家制定的生活饮用水水质标准(GB5749-85),一般均低于3μg/L。The treated water samples all meet the national drinking water quality standard (GB5749-85), generally lower than 3μg/L.

龙葵完成循环净水后的处理:龙葵植株内部所吸收的镉可通过机械压榨的方式提取出来,提取率接近80%;压榨后的植物残渣经烘干、粉碎,可以用于工业废水的重金属吸附去除。Treatment after the Solanum nigrum completes the circulating water purification: The cadmium absorbed by the Solanum nigrum plant can be extracted by mechanical pressing, and the extraction rate is close to 80%; the plant residue after pressing can be used for industrial wastewater treatment after drying and crushing. Heavy metal adsorption and removal.

本发明针对饮用水中微量镉污染的去除效果好、操作简便、适用范围广,在饮用水净化方面具有很大的应用潜力。The invention has good removal effect on trace cadmium pollution in drinking water, simple operation and wide application range, and has great application potential in drinking water purification.

菌种分离自湖南省衡阳水口山矿区尾砂矿附近采集的龙葵植株,为龙葵内生菌。将采集的整株龙葵植株用清水冲洗干净,分别取部分根、茎、叶于2%(v/v)的次氯酸溶液中浸泡3分钟用于表面消毒,然后在无菌水中漂洗5次去除植物表面残留的次氯酸。表面灭菌后的植物用无菌研钵研磨至糊状,用1%(m/v)氯化钠稀释10-10000倍分别涂布在固体LB培养基平面上,培养48小时。根据菌落形态的差异挑取内生菌单菌落进行扩大培养。在经过重金属耐受性、促植物生长因子等检测后,选取了编号为LKS03的内生菌进行植物接种。LKS03具有较高的生产ACC(1-氨基环丙烷-1-羧酸)脱氨酶和IAA(吲哚乙酸)的能力,在Cd 2mM、Zn5mM、Pb 5mM的培养条件下其生长不受明显影响,菌种活力正常。The strain was isolated from Solanum nigrum plants collected near the tailings mine of Shuikoushan mining area in Hengyang, Hunan Province, and it is an endophytic bacterium of Solanum nigrum. Rinse the collected whole Solanum nigrum plant with clear water, get some roots, stems, and leaves respectively and soak them in 2% (v/v) hypochlorous acid solution for 3 minutes for surface disinfection, then rinse them in sterile water for 5 minutes. Remove residual hypochlorous acid on the plant surface for the first time. The surface-sterilized plants were ground to a paste with a sterile mortar, diluted 10-10000 times with 1% (m/v) sodium chloride, and spread on solid LB medium planes respectively, and cultivated for 48 hours. According to the difference in colony morphology, a single colony of endophytic bacteria was picked for expansion culture. After testing for heavy metal tolerance and plant growth-promoting factors, the endophytic bacteria numbered LKS03 were selected for plant inoculation. LKS03 has a high ability to produce ACC (1-aminocyclopropane-1-carboxylic acid) deaminase and IAA (indole acetic acid), and its growth is not significantly affected by the culture conditions of Cd 2mM, Zn5mM, and Pb 5mM , the strain viability is normal.

LKS03为革兰氏阳性菌,适宜生长温度为25-30℃,高于38℃则生长明显受到抑制。在固体LB培养基上涂布、30℃培养2天后,其菌落直径为1-1.5mm,呈黄色,表面光滑、凸起、湿润。根据LKS03的16SrDNA序列测序结果(GenBank ID:HQ331133),结合菌落形态和生理特性分析,表明其为金黄杆菌属的细菌,将其命名为金黄杆菌Chryseobacterium sp.LKS03。LKS03 is a Gram-positive bacterium, and the suitable growth temperature is 25-30°C, and the growth is obviously inhibited if it is higher than 38°C. After coating on solid LB medium and culturing at 30°C for 2 days, the colony diameter is 1-1.5 mm, yellow in color, smooth, raised and moist on the surface. According to the 16SrDNA sequence sequencing results of LKS03 (GenBank ID: HQ331133), combined with the analysis of colony morphology and physiological characteristics, it was shown that it was a bacterium of the genus Chryseobacterium, and it was named Chryseobacterium sp.LKS03.

附图说明 Description of drawings

图1为龙葵净化不同镉浓度的模拟污染饮用水时间曲线图;Fig. 1 is the simulated polluted drinking water time curve diagram that Solanum nigrum purifies different cadmium concentrations;

图2为培养周期第45天和80天的龙葵净水时间曲线图;Fig. 2 is the water purification time curve of Solanum nigrum on the 45th day and 80 days of the culture cycle;

图3为接种金黄杆菌Chryseobacterium sp.LKS03的龙葵与未接种的龙葵净水能力的比较;Fig. 3 is the comparison of Solanum nigrum inoculated with Chryseobacterium sp.LKS03 and non-inoculated Solanum nigrum water purification ability;

图4为本发明接种了金黄杆菌Chryseobacterium sp.LKS03的龙葵连续4次净水处理效果图;Fig. 4 is that the present invention has been inoculated the Solanum nigrum of Chryseobacterium sp.LKS03 continuous 4 times water purification treatment effect figure;

图5为几种金属离子对本发明接种了金黄杆菌Chryseobacterium sp.LKS03的龙葵净水能力的影响。Fig. 5 is the impact of several metal ions on the water purification ability of Solanum nigrum inoculated with Chryseobacterium sp.LKS03 of the present invention.

具体实施方式 Detailed ways

下面结合实施例旨在进一步说明本发明,而非限制本发明。The following examples are intended to further illustrate the present invention, rather than limit the present invention.

实施例1Example 1

龙葵种子的萌发、接种金黄杆菌Chryseobacterium sp.LKS03和植株的水培培养:Germination of nightshade seeds, inoculation with Chryseobacterium sp.LKS03 and hydroponic culture of plants:

1.龙葵种子经75%酒精溶液浸泡15秒进行表面灭菌,清水冲洗3次,晾干后用于金黄杆菌Chryseobacterium sp.LKS03接种。1. Solanum solanum seeds are soaked in 75% alcohol solution for 15 seconds to sterilize the surface, rinsed with water for 3 times, dried and used for Chryseobacterium sp.LKS03 inoculation.

2.将灭菌后的龙葵种子浸泡于金黄杆菌Chryseobacterium sp.LKS03接种菌液中2小时,取出即用于播种。2. Soak the sterilized Solanum nigrum seeds in Chryseobacterium sp.LKS03 inoculum solution for 2 hours, take them out and use them for sowing.

3.蛭石铺于托盘中,厚度约5厘米,用1/4浓度的改良霍格兰溶液浇透,龙葵种子播种于其中。2-3天左右即发芽,2周左右龙葵可长至10厘米高并转入水培。3. Spread the vermiculite in a tray with a thickness of about 5 cm, pour it thoroughly with 1/4 concentration of modified Hoagland's solution, and sow nightshade seeds in it. It will germinate in about 2-3 days, and the black nightshade can grow to a height of 10 cm in about 2 weeks and be transferred to hydroponics.

4.1/4浓度的改良霍格兰溶液同样作为水培营养液,5天换一次营养液,并不时补充。再过30天后的龙葵植株用于净化水。The improved Hoagland solution with a concentration of 4.1/4 is also used as a hydroponic nutrient solution, and the nutrient solution is changed every 5 days and replenished from time to time. After another 30 days the nightshade plants were used for water purification.

实施例2Example 2

Chryseobacterium sp.LKS03具有较高的生产ACC(1-氨基环丙烷-1-羧酸)脱氨酶和IAA(吲哚乙酸)的能力,可以促进植物根部的生长。在生长周期的第45天和第80天,接种了金黄杆菌Chryseobacterium sp.LKS03植株与没有接种的植株各采集5株样本,测定根长和根重,结果如表2所示:Chryseobacterium sp.LKS03 has a high ability to produce ACC (1-aminocyclopropane-1-carboxylic acid) deaminase and IAA (indole acetic acid), which can promote the growth of plant roots. On the 45th day and the 80th day of the growth cycle, inoculated Chryseobacterium sp.LKS03 plants and plants without inoculation respectively collected 5 samples, measured root length and root weight, and the results are shown in Table 2:

表2Table 2

Figure BDA0000028940320000041
Figure BDA0000028940320000041

接种了金黄杆菌Chryseobacterium sp.LKS03的龙葵植株在生长周期的第45天,根长和根重与未接菌的龙葵相比,分别增加了21.8%和25.8%;在第80天,根长和根重则分别增加了25.7%和38.8%。实验结果表明,接种Chryseobacteriumsp.LKS03对龙葵的根部生长有显著的促进作用。On the 45th day of the growth cycle, the root length and root weight of Solanum nigrum plants inoculated with Chryseobacterium sp.LKS03 increased by 21.8% and 25.8%, respectively; The length and root weight increased by 25.7% and 38.8%, respectively. The experimental results showed that the inoculation of Chryseobacteriumsp.LKS03 had a significant effect on the root growth of Solanum nigrum.

实施例3Example 3

采用自来水添加重金属离子来模拟污染饮用水,模拟污染饮用水中镉浓度为50μg/L,比较接菌的龙葵和未接菌龙葵净化模拟污染饮用水的能力。1升模拟污染饮用水注入水槽中,龙葵固定于水槽上方,根部与水体接触,跟踪检测16个小时内水体中镉浓度的变化,镉浓度由原子分光光度计进行测定,净水效果如图3所示:由实验结果可看出,接种Chryseobacteriumsp.LKS03的龙葵3小时内将饮用水中镉含量降低至国标以下(<10μg/L),未接种内生菌的龙葵则需要4.5个小时,处理效率提高了近33%。由此可见接种内生菌后,龙葵根部吸收镉离子的速度更快,净水效率更高。Tap water was added with heavy metal ions to simulate polluted drinking water. The concentration of cadmium in the simulated polluted drinking water was 50 μg/L. The ability of inoculated nightshade and non-inoculated nightshade to purify the simulated contaminated drinking water was compared. 1 liter of simulated polluted drinking water was poured into the water tank. Solanum nigrum was fixed above the water tank, and the roots were in contact with the water body. The change of cadmium concentration in the water body was tracked and detected within 16 hours. The cadmium concentration was measured by an atomic spectrophotometer. The water purification effect is shown in the figure Shown in 3: It can be seen from the experimental results that Solanum nigrum inoculated with Chryseobacteriumsp. hours, the processing efficiency increased by nearly 33%. It can be seen that after inoculation of endophytic bacteria, the root of Solanum nigrum absorbs cadmium ions faster and the water purification efficiency is higher.

实施例4Example 4

采用自来水添加重金属离子来模拟污染饮用水,模拟污染饮用水中镉浓度为100μg/L,1升模拟污染饮用水注入水槽中,接种了金黄杆菌Chryseobacterium sp.LKS03的龙葵固定于水槽上方,根部与水体接触,跟踪检测16个小时内水体中镉浓度的变化,镉浓度由原子分光光度计进行测定。净化处理完成后龙葵继续水培,24小时后继续进行饮用水净化处理。连续进行4个周期的饮用水净化处理,净水效果如图4所示:由图4可看出,龙葵的连续净水能力相当稳定。Tap water was added with heavy metal ions to simulate polluted drinking water. The cadmium concentration in the simulated polluted drinking water was 100 μg/L, and 1 liter of simulated polluted drinking water was poured into the tank. Solanum nigrum inoculated with Chryseobacterium sp.LKS03 was fixed above the tank, and the root Contact with water body, track and detect the change of cadmium concentration in water body within 16 hours, and the cadmium concentration is measured by atomic spectrophotometer. After the purification treatment is completed, the nightshade will continue to be hydroponics, and the drinking water purification treatment will continue after 24 hours. Four consecutive cycles of drinking water purification treatment are performed, and the water purification effect is shown in Figure 4: From Figure 4, it can be seen that the continuous water purification capacity of Solanum nigrum is quite stable.

实施例5Example 5

采用自来水添加重金属离子来模拟污染饮用水,镉浓度为100μg/L,同时分别加入几种2价金属阳离子,浓度为Zn 1000μg/L、Mn 500μg/L、Fe 1000μg/L、Ca 500mg/L、Mg 500mg/L,用以检测水中各种常见阳离子对接种了金黄杆菌Chryseobacterium sp.LKS03的龙葵净水能力的影响。跟踪检测12个小时内水体中镉浓度的变化,镉浓度由原子分光光度计进行测定。净水效果如图5所示:由图5可以看出,各种金属2价阳离子对龙葵净水影响很小,龙葵净水的适应范围很广。Use tap water to add heavy metal ions to simulate polluted drinking water. The concentration of cadmium is 100μg/L. At the same time, several divalent metal cations are added respectively. Mg 500mg/L, used to detect the effects of various common cations in water on the water purification ability of nightshade inoculated with Chryseobacterium sp.LKS03. Track and detect the change of cadmium concentration in the water body within 12 hours, and the cadmium concentration is measured by atomic spectrophotometer. The water purification effect is shown in Figure 5: It can be seen from Figure 5 that various metal divalent cations have little effect on the water purification of nightshade nightshade, and the scope of application of nightshade nightshade water purification is very wide.

Claims (9)

1. one kind promotes black nightshade to remove the mikrobe that Trace Cadmium is polluted in the water, it is characterized in that described mikrobe is golden yellow bacillus Chryseobacterium sp.LKS03, and preserving number is CCTCC NO:M 2010236.
2. application rights requires 1 described mikrobe to promote black nightshade to remove the method that Trace Cadmium is polluted in the water; It is characterized in that; With in golden yellow bacillus Chryseobacterium sp.LKS03 bacterium liquid, soaking 1-3 hour behind the black nightshade seed surface sterilization, take out sowing, change water planting over to after two weeks; Black nightshade plant after 30 days is used to purify waste water.
3. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water; It is characterized in that; Described black nightshade seed soaks through 75% spirituous solution and carried out surface sterilization in 15 seconds; Flushing with clean water 3 times is used for golden yellow bacillus Chryseobacterium sp.LKS03 bacterium liquid and soaks after drying.
4. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water; It is characterized in that; Described bacterium liquid layoutprocedure is following: enlarged culturing is 12 hours in the golden yellow bacillus Chryseobacterium of picking sp.LKS03 bacterial classification inoculation to the 100ml liquid LB substratum, 4000 rev/mins centrifugal 5 minutes, remove supernatant; With the resuspended bacterium thalline of the improvement Hoagland solution of 100ml 1/4 concentration, promptly obtain bacterium liquid; The improvement Hoagland solution prescription of described 1/4 concentration is: KNO 3125mg/L; KH 2PO 435mg/L; NH 4H 2PO 420mg/L; MgSO 47H 2O 125mg/L; Ca (NO 3) 24H 2O 235mg/L; FeSO 47H 2O 10mg/L.
5. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water; It is characterized in that described sowing is that vermiculite is laid in the pallet, thickness 4-6 centimetre; Improvement Hoagland solution with 1/4 concentration irrigates, and black nightshade seed is seeded in wherein; The improvement Hoagland solution prescription of described 1/4 concentration is: KNO 3125mg/L; KH 2PO 435mg/L; NH 4H 2PO 420mg/L; MgSO 47H 2O 125mg/L; Ca (NO 3) 24H 2O 235mg/L; FeSO 47H 2O 10mg/L.
6. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water, it is characterized in that, described water planting is to adopt the improvement Hoagland solution of 1/4 concentration as mill water culture nutrient solution, changes one time of nutrition liquid in 4-6 days, and constantly replenishes; The improvement Hoagland solution prescription of described 1/4 concentration is: KNO 3125mg/L; KH 2PO 435mg/L; NH 4H 2PO 420mg/L; MgSO 47H 2O 125mg/L; Ca (NO 3) 24H 2O 235mg/L; FeSO 47H 2O 10mg/L.
7. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water, it is characterized in that the time that described black nightshade plant is used to purify waste water is 30-40 days.
8. mikrobe according to claim 2 promotes black nightshade to remove the method that Trace Cadmium is polluted in the water, it is characterized in that described black nightshade plant root contacts with water body purifies waste water.
9. promote black nightshade to remove the method that Trace Cadmium is polluted in the water according to claim 2 or 7 or 8 described mikrobes, it is characterized in that described black nightshade is used to handle concentration of cadmium ions for not being higher than the tap water of 200 μ g/L; After described black nightshade plant is taken turns clean water treatment in 2-12 hour through one, continue water planting and cultivated 24 hours, carry out the next round clean water treatment, the corresponding 1-1.2 that purifies of every strain black nightshade rises the water of cadmium pollution.
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CN103241839B (en) * 2013-05-27 2014-12-03 沈阳大学 Treatment method of treating cadmium contaminated water
CN106554086B (en) * 2016-11-29 2018-09-14 郑州轻工业学院 A kind of cadmium pollution food chain restorative procedure based on Pu Ye-fungi synergy
CN107282010A (en) * 2017-07-03 2017-10-24 安徽天顺环保设备股份有限公司 A kind of heavy metal absorbent
CN108658245A (en) * 2018-04-30 2018-10-16 桂林理工大学 A kind of preparation method of processing lead zinc waste water microbial flocculant
CN109105237A (en) * 2018-06-26 2019-01-01 南京工程学院 Remove and measure the experimental method that wetland plant rhizosphere microorganism group influences phosphorus in plant absorption water
CN118253573A (en) * 2024-03-05 2024-06-28 南京农业大学 Application of chrysobacterium aurum CHR6 or siderophore thereof in enhancing super-accumulation plant to repair heavy metal contaminated soil
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Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1724184A (en) * 2004-07-23 2006-01-25 中国科学院沈阳应用生态研究所 A kind of method of utilizing the plant of Solanaceae cadmium pollution soil repair

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1724184A (en) * 2004-07-23 2006-01-25 中国科学院沈阳应用生态研究所 A kind of method of utilizing the plant of Solanaceae cadmium pollution soil repair

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
代淑娟等.枯草芽孢杆菌对电镀废水中镉的吸附.《有色金属》.2010,(第3期),全文. *
张春燕等.龙葵生长对镉污染的响应.《河西学院学报》.2007,第23卷(第5期),全文. *
曹吉吉.一株龙葵内生细菌SDE06去除Cd2+的实验.《微生物学通报》.2009,第36卷(第3期),全文. *
杨晶.柠檬酸杆菌吸附重金属镉的研究.《水处理技术》.2009,(第5期),全文. *

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