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CN107445390A - A kind of " three-stage process " biodegradation method for being used to administer heavy metal - Google Patents

A kind of " three-stage process " biodegradation method for being used to administer heavy metal Download PDF

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CN107445390A
CN107445390A CN201610374924.7A CN201610374924A CN107445390A CN 107445390 A CN107445390 A CN 107445390A CN 201610374924 A CN201610374924 A CN 201610374924A CN 107445390 A CN107445390 A CN 107445390A
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heavy metal
wastewater
straw
heavy metals
tank
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曾伟民
石丽娟
喻子凌
陈桢
陈雷
李振桦
余润兰
李交昆
申丽
刘元东
吴学玲
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Central South University
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Sorption (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

本发明公开一种用于治理重金属的“三段法”生物降解方法,处理步骤如下:1)将排出的重金属废水从秸秆槽底部进入所述秸秆槽中,适当控制进水流速,确保3小时的有效吸附时间;2)从所述秸秆槽自流出来的清液进入人工湿地系统,利用其独特的基质—植物—微生物生态系统,通过吸附、沉淀和富集等作用降低废水中的重金属;3)经过所述人工湿地系统处理的废水进入好氧池,通过池内活性污泥中微生物的表面络合、生物吸附及絮凝作用进一步降低废水中的重金属含量。本发明采用“废弃秸秆—水生植物—微生物”三段法生物降解方法治理重金属废水,有效利用农业废弃物、成本低廉、重金属处理彻底、环境友好无二次污染,工艺简单,运营管理方便。

The invention discloses a "three-stage method" biodegradation method for treating heavy metals. The treatment steps are as follows: 1) Enter the discharged heavy metal wastewater from the bottom of the straw tank into the straw tank, and properly control the flow rate of the water inflow to ensure 3 hours 2) The clear liquid flowing out from the straw trough enters the constructed wetland system, and uses its unique substrate-plant-microbial ecosystem to reduce heavy metals in wastewater through adsorption, precipitation and enrichment; 3 ) The wastewater treated by the constructed wetland system enters the aerobic pool, and the heavy metal content in the wastewater is further reduced through surface complexation, biosorption and flocculation of microorganisms in the activated sludge in the pool. The invention adopts the three-stage biodegradation method of "abandoned straw-aquatic plants-microbes" to treat heavy metal wastewater, effectively utilizes agricultural waste, has low cost, thoroughly treats heavy metals, is environmentally friendly and has no secondary pollution, and has simple process and convenient operation and management.

Description

一种用于治理重金属的“三段法”生物降解方法A "three-stage method" biodegradation method for treating heavy metals

技术领域technical field

本发明涉及重金属污水治理领域,具体为一种用于治理重金属的“三段法”生物降解方法。The invention relates to the field of heavy metal sewage treatment, in particular to a "three-stage method" biodegradation method for treating heavy metals.

背景技术Background technique

目前,重金属废水来源广、水量大,重金属废水主要来源于电镀、采矿、化工、电解、农药、医药、烟草、油漆、颜料等工业,此类废水具有毒效长期持续,生物不可降解等特点,通过食物链作用进入人体,并在人体内累积,从而导致各种疾病和机能紊乱,最终对人体健康造成严重危害。随着我国工业的迅猛发展,重金属废水大量排放,重金属污染日益严重,如何对其有效治理、回收利用成为人们共同关注的问题。At present, heavy metal wastewater has a wide range of sources and a large amount of water. Heavy metal wastewater mainly comes from industries such as electroplating, mining, chemical industry, electrolysis, pesticides, medicine, tobacco, paint, and pigments. This type of wastewater has the characteristics of long-term toxic effects and non-biological degradation. It enters the human body through the food chain and accumulates in the human body, causing various diseases and dysfunction, and finally causing serious harm to human health. With the rapid development of my country's industry, a large amount of heavy metal wastewater is discharged, and heavy metal pollution is becoming more and more serious. How to effectively treat and recycle it has become a common concern of people.

重金属治理常用方法有三种:1)化学法,通过投加药剂,将重金属离子转化成沉淀,从而除去。该方法对高浓度重金属废水处理效率高,容易产生有害的副产物,且产生废渣量较大造成二次污染;2)物理化学法,不改变废水中重金属的化学形态,对其进行吸附、浓缩、分离、甚至回收利用,但处理成本较高,难以广泛应用;3)生物法,通过生物体及其衍生物对水中重金属离子的吸附吸附、絮凝和富集等作用将其除去。生物法对重金属离子有较强的吸附转化能力,对有机物耐受性好,当有机物污染≤5000mg/L时不影响对重金属离子的吸附;具有经济、高效、环保等特点,但仅适应于中低浓度重金属废水处理。现有的单一重金属废水处理方法存在着种种不足,需要一种或几种方法联合使用更有效地解决重金属污染的问题。There are three commonly used methods for heavy metal treatment: 1) chemical method, by adding chemicals to convert heavy metal ions into precipitates, thereby removing them. This method has high treatment efficiency for high-concentration heavy metal wastewater, and it is easy to produce harmful by-products, and a large amount of waste residue is generated to cause secondary pollution; 2) Physical and chemical methods, which do not change the chemical form of heavy metals in wastewater, and can be adsorbed and concentrated , separation, and even recycling, but the treatment cost is high and it is difficult to be widely used; 3) biological method, through the adsorption, flocculation and enrichment of heavy metal ions in water by organisms and their derivatives to remove them. The biological method has a strong ability to adsorb and transform heavy metal ions, and has good tolerance to organic matter. When the organic matter pollution is ≤5000mg/L, it will not affect the adsorption of heavy metal ions; it has the characteristics of economy, high efficiency, and environmental protection, but it is only suitable for medium Low concentration heavy metal wastewater treatment. The existing single heavy metal wastewater treatment method has various deficiencies, and one or several methods need to be used in combination to solve the problem of heavy metal pollution more effectively.

我国是农业大国,每年产生的农业废弃物高达上亿吨。这些废弃物大多被直接丢弃,更有一些被焚烧,对环境、生产和生活造成极大地影响。而国外已有大量关于农业废弃物对废水处理的研究,农业废弃物的空隙度较高,比表面积较大,可以与金属离子发生物理吸附,农业废弃物主要成分纤维素、半纤维素、木质素和果胶表面含有大量的活基团,如羧基、羟基等,这些活性基团可以跟重金属离子通过离子交换、鳌合等方式结合,达到去除重金属离子的目的。为使此类天然有机吸附剂有较理想的吸附能力,需通过化学改性引入更多的羟基、羧基、巯基、磷酸根、胺基等活性基团,如柠檬酸修饰、碱化处理、巯基改性等。经过化学改性后的农业废弃物作为高效的天然有机吸附剂,不仅将农业废弃物资源化利用起来,减少了环境污染,同时由于具有原料来源丰富、品种多、成本低廉、吸附容量大、吸附设备简单、产品易降解等特点,比具有良好吸附性能但价格昂贵的活性炭有更广阔的市场前景。my country is a big agricultural country, and the agricultural waste produced every year is as high as hundreds of millions of tons. Most of these wastes are directly discarded, and some are incinerated, which has a great impact on the environment, production and life. However, there have been a large number of researches on the treatment of wastewater by agricultural waste in foreign countries. Agricultural waste has a high porosity and a large specific surface area, which can physically adsorb metal ions. The main components of agricultural waste are cellulose, hemicellulose, and wood. The surface of pectin and pectin contains a large number of active groups, such as carboxyl, hydroxyl, etc. These active groups can be combined with heavy metal ions through ion exchange, chelation, etc., to achieve the purpose of removing heavy metal ions. In order to make this kind of natural organic adsorbent have a better adsorption capacity, it is necessary to introduce more active groups such as hydroxyl, carboxyl, sulfhydryl, phosphate, amine through chemical modification, such as citric acid modification, alkalization treatment, sulfhydryl, etc. modified etc. As a highly efficient natural organic adsorbent, the chemically modified agricultural waste not only recycles agricultural waste and reduces environmental pollution, but also has abundant raw material sources, many varieties, low cost, large adsorption capacity, and high adsorption capacity. The equipment is simple and the product is easy to degrade, which has a broader market prospect than activated carbon with good adsorption performance but expensive price.

发明内容Contents of the invention

本发明所解决的技术问题在于提供一种用于治理重金属的“三段法”生物降解方法,以解决上述背景技术中的缺点。The technical problem solved by the present invention is to provide a "three-stage method" biodegradation method for treating heavy metals, so as to solve the above-mentioned shortcomings in the background technology.

本发明所解决的技术问题采用以下技术方案来实现:一种用于治理重金属的“三段法”生物降解方法,处理步骤如下:The technical problem solved by the present invention is achieved by the following technical solutions: a "three-stage method" biodegradation method for treating heavy metals, the processing steps are as follows:

1)在重金属含量为50-500mg/L的重金属废水池的出口处设有一秸秆槽,所述重金属废水池排出的重金属废水将从所述秸秆槽的底部进进入所述秸秆槽中,所述重金属废水的流速控制在保证3小时的有效吸附时间;2)从所述秸秆槽自流出来的清液进入人工湿地系统,所述人工湿地系统中的基质—植物—微生物生态系统会通过吸附、沉淀和富集作用降低废水中的重金属;3)在所述人工湿地系统经过处理的废水进一步进入好氧池内,所述好氧池内的活性污泥中培养着微生物,所述好氧池污泥接种量为池容的20%,池内连续曝气,控制溶解氧2-4mg/L,pH调整到6.5-8.5,并根据重金属废水中有机物的含量将水力停留时间设定为10-24小时。通过池内活性污泥中微生物的表面络合、生物吸附及絮凝作用进一步降低废水中的重金属含量,使其稳定达到《污水综合排放标准》的一级标准。1) A straw tank is provided at the outlet of the heavy metal waste water tank with a heavy metal content of 50-500mg/L, and the heavy metal waste water discharged from the heavy metal waste water tank will enter the straw tank from the bottom of the straw tank, and the The flow rate of the heavy metal wastewater is controlled to ensure an effective adsorption time of 3 hours; 2) The clear liquid flowing out from the straw tank enters the constructed wetland system, and the substrate-plant-microbial ecosystem in the constructed wetland system will be absorbed through adsorption, precipitation 3) the treated wastewater in the constructed wetland system further enters the aerobic pool, and microorganisms are cultivated in the activated sludge in the aerobic pool, and the sludge in the aerobic pool is inoculated The volume is 20% of the tank volume, the tank is continuously aerated, the dissolved oxygen is controlled to 2-4mg/L, the pH is adjusted to 6.5-8.5, and the hydraulic retention time is set to 10-24 hours according to the content of organic matter in the heavy metal wastewater. Through the surface complexation, biosorption and flocculation of microorganisms in the activated sludge in the pool, the heavy metal content in the wastewater is further reduced, so that it can stably meet the first-level standard of the "Comprehensive Wastewater Discharge Standard".

本发明中,进一步的,所述秸秆槽中投放的可以是玉米秸秆、小麦秸秆、花生壳、甜菜渣或稻壳中的一种农业废弃物,将这些农业废弃物进行初级的切割处理,这些被处理过的农业废弃物为使此类天然有机吸附剂有较理想的吸附能力,同时将这些农业废弃物进行二次处理,通过檬酸修饰、碱化处理、巯基改性的化学改性方式在这些农业废弃物中引入更多的羟基、羧基、巯基、磷酸根、胺基活性基团。In the present invention, further, the straw trough can be put in a kind of agricultural waste from corn stalks, wheat straws, peanut shells, sugar beet pulp or rice husks, and these agricultural wastes are subjected to primary cutting treatment, these In order to make this kind of natural organic adsorbents have better adsorption capacity, the treated agricultural wastes are subjected to secondary treatment through chemical modification methods such as citric acid modification, alkalization treatment and sulfhydryl modification. Introduce more active groups of hydroxyl, carboxyl, mercapto, phosphate, and amine into these agricultural wastes.

本发明中,进一步的,所述人工湿地系统中的湿地基质由砾石、土壤按1:1组成,在所述湿地基质上种植的水生植物由对重金属吸收能力较强的芦苇、香蒲、美人蕉、风车草组成,通过人工湿地的物理沉淀、过滤、化学沉淀、吸附、微生物交互作用以及植物的吸收作用,实现重金属的有效去除。In the present invention, further, the wetland substrate in the constructed wetland system is composed of gravel and soil at a ratio of 1:1, and the aquatic plants planted on the wetland substrate are composed of reeds, cattails, cannas, Composed of windmill grass, through the physical precipitation, filtration, chemical precipitation, adsorption, microbial interaction and absorption of plants in the constructed wetland, the effective removal of heavy metals is realized.

本发明中,进一步的,重金属废水经过“废弃秸秆—水生植物”吸附、沉淀、富集作用后,重金属含量远低于《污水综合排放标准》的一级标准。In the present invention, further, after the heavy metal wastewater is absorbed, precipitated and enriched by "abandoned straw-aquatic plants", the heavy metal content is far lower than the first-level standard of the "Comprehensive Wastewater Discharge Standard".

本发明的有益效果:Beneficial effects of the present invention:

1、本发明采用“废弃秸秆—水生植物—微生物”三段法生物降解技术治理中低浓度重金属废水,通过改性秸秆的高效吸附、水生植物的吸收富集及好氧池中微生物的络合、代谢及生物絮凝等的协同作用,可以将废水中的重金属降低到极低的水平,且整套工艺环境友好无二次污染,工艺简单,运营管理方便。1. The present invention adopts the "waste straw-aquatic plant-microbe" three-stage biodegradation technology to treat medium and low concentration heavy metal wastewater, through the efficient adsorption of modified straw, the absorption and enrichment of aquatic plants and the complexation of microorganisms in the aerobic pool The synergistic effect of , metabolism and biological flocculation can reduce the heavy metals in the wastewater to an extremely low level, and the whole process is environmentally friendly without secondary pollution, the process is simple, and the operation and management are convenient.

2、改性后的农作物秸秆作为环境友好型的新型生物吸附材料,具有丰富的孔隙结构、巨大的比表面积、良好的吸附性能,兼具原料来源广泛、成本低廉、易生物降解等优势,同时将农业废弃物资源化利用起来,减少了环境污染。2. As a new environment-friendly bio-adsorption material, the modified crop straw has a rich pore structure, a huge specific surface area, and good adsorption performance. It also has the advantages of a wide range of raw material sources, low cost, and easy biodegradation. The utilization of agricultural waste resources reduces environmental pollution.

附图说明Description of drawings

图1为本发明一种用于治理重金属的“三段法”生物降解方法示意图。Fig. 1 is a schematic diagram of a "three-stage method" biodegradation method for controlling heavy metals according to the present invention.

具体实施方式detailed description

为了使本发明实现的技术手段、创作特征、达成目的与功效易于明白了解,下面结合具体图示,进一步阐述本发明。In order to make the technical means, creative features, goals and effects achieved by the present invention easy to understand, the present invention will be further described below in conjunction with specific illustrations.

实施例:如图1所示,实施方式:一种用于治理重金属的“三段法”生物降解方法,其步骤如下:Embodiment: As shown in Figure 1, implementation method: a kind of " three-stage method " biodegradation method for controlling heavy metal, its steps are as follows:

一、将重金属废水从秸秆槽底部进水,控制流速保证3小时的有效吸附时间。为提高秸秆的吸附性能,需对其进行化学修饰,增多其活性基团;1. The heavy metal wastewater is fed from the bottom of the straw tank, and the flow rate is controlled to ensure an effective adsorption time of 3 hours. In order to improve the adsorption performance of straw, it needs to be chemically modified to increase its active groups;

二、从秸秆槽自流出来的清液进入人工湿地系统,利用其独特的基质—植物—微生物生态系统,通过吸附、沉淀和富集等作用降低废水中的重金属;2. The clear liquid flowing out of the straw trough enters the constructed wetland system, and uses its unique substrate-plant-microbial ecosystem to reduce heavy metals in wastewater through adsorption, precipitation and enrichment;

三、接着进入好氧池,通过活性污泥中微生物的表面络合、生物吸附及絮凝作用进一步降低重金属含量,达到排放标准。3. Then enter the aerobic pool, and further reduce the heavy metal content through the surface complexation, biosorption and flocculation of microorganisms in the activated sludge to meet the discharge standard.

所述步骤一中被处理的重金属废水中重金属含量为50-500mg/L之间。The heavy metal content in the heavy metal wastewater treated in the step 1 is between 50-500mg/L.

所述步骤一中秸秆槽中投放的可以是玉米秸秆、小麦秸秆、花生壳、甜菜渣或稻壳等中的一种农业废弃物,将其切割成5cm左右的小段。农业废弃物主要成分纤维素、半纤维素、木质素和果胶表面含有大量的活基团,如羧基、羟基等,这些活性基团可以跟重金属离子通过离子交换、鳌合等方式结合,达到去除重金属离子的目的。为使此类天然有机吸附剂有较理想的吸附能力,需通过化学改性引入更多的羟基、羧基、巯基、磷酸根、胺基等活性基团,如柠檬酸修饰、碱化处理、巯基改性等。In the first step, the straw trough can be put into a kind of agricultural waste such as corn stalks, wheat straws, peanut shells, beet pulp or rice husks, which are cut into small pieces of about 5 cm. The main components of agricultural waste, cellulose, hemicellulose, lignin and pectin, contain a large number of active groups on the surface, such as carboxyl, hydroxyl, etc. These active groups can combine with heavy metal ions through ion exchange, chelation, etc. to achieve The purpose of removing heavy metal ions. In order to make this kind of natural organic adsorbent have a better adsorption capacity, it is necessary to introduce more active groups such as hydroxyl, carboxyl, sulfhydryl, phosphate, amine through chemical modification, such as citric acid modification, alkalization treatment, sulfhydryl, etc. modified etc.

所述步骤二中人工湿地基质由砾石、土壤按1:1组成,水生植物由对重金属吸收能力较强的芦苇、香蒲、美人蕉、风车草等组成。通过人工湿地的物理沉淀、过滤、化学沉淀、吸附、微生物交互作用以及植物的吸收作用,实现重金属的有效去除。根据重金属废水的浓度,可调整人工湿地的停留时间在20-48h。In the second step, the constructed wetland matrix is composed of gravel and soil at a ratio of 1:1, and the aquatic plants are composed of reeds, cattails, cannas, windmills, etc., which have a strong ability to absorb heavy metals. The effective removal of heavy metals is achieved through physical precipitation, filtration, chemical precipitation, adsorption, microbial interaction, and plant absorption in constructed wetlands. According to the concentration of heavy metal wastewater, the residence time of the constructed wetland can be adjusted to 20-48h.

所述步骤三中重金属废水经过“废弃秸秆—水生植物”吸附、沉淀、富集作用后,重金属浓度显著下降,再在好氧池微生物的作用下可将重金属降到极低的水平。好氧池污泥接种量为池容的20%,池内连续曝气,控制溶解氧2-4mg/L,pH调整到6.5-8.5,并根据重金属废水中有机物的含量将水力停留时间设定为10-24小时。In the third step, after the heavy metal wastewater is absorbed, precipitated and enriched by "abandoned straw-aquatic plants", the concentration of heavy metals is significantly reduced, and then the heavy metals can be reduced to an extremely low level under the action of microorganisms in the aerobic pool. The amount of sludge inoculum in the aerobic tank is 20% of the tank volume, the tank is continuously aerated, the dissolved oxygen is controlled at 2-4mg/L, the pH is adjusted to 6.5-8.5, and the hydraulic retention time is set to 10-24 hours.

以上显示和描述了本发明的基本原理和主要特征及本发明的优点,本行业的技术人员应该了解,本发明不受上述实施例的限制,上述实施例和说明书中描述的只是说明本发明的原理,在不脱离本发明精神和范围的前提下,本发明还会有各种变化和改进,这些变化和改进都落入要求保护的本发明范围内,本发明要求保护范围由所附的权利要求书及其等效物界定。Above shows and described basic principle of the present invention and main feature and the advantage of the present invention, those skilled in the art should understand that, the present invention is not limited by above-mentioned embodiment, what described in above-mentioned embodiment and specification sheet just illustrates the present invention Principle, under the premise of not departing from the spirit and scope of the present invention, the present invention also has various changes and improvements, and these changes and improvements all fall within the claimed scope of the present invention, and the claimed protection scope of the present invention is defined by the appended claims Requirements and their equivalents are defined.

Claims (3)

1.一种用于治理重金属的“三段法”生物降解方法,其特征在于,处理步骤如下:1. A "three-stage method" biodegradation method for controlling heavy metals is characterized in that the processing steps are as follows: 1)在重金属含量为50-500mg/L的重金属废水池的出口处设有一秸秆槽,所述重金属废水池排出的重金属废水将从所述秸秆槽的底部进进入所述秸秆槽中,所述重金属废水的流速控制在保证3小时的有效吸附时间;1) A straw tank is provided at the outlet of the heavy metal waste water tank with a heavy metal content of 50-500mg/L, and the heavy metal waste water discharged from the heavy metal waste water tank will enter the straw tank from the bottom of the straw tank, and the The flow rate of heavy metal wastewater is controlled to ensure an effective adsorption time of 3 hours; 2)从所述秸秆槽自流出来的清液进入人工湿地系统,所述人工湿地系统中的基质—植物—微生物生态系统会通过吸附、沉淀和富集作用降低废水中的重金属;2) The clear liquid flowing out from the straw trough enters the constructed wetland system, and the substrate-plant-microbial ecosystem in the constructed wetland system will reduce the heavy metals in the wastewater through adsorption, precipitation and enrichment; 3)在所述人工湿地系统经过处理的废水进一步进入好氧池内,所述好氧池内的活性污泥中培养着微生物,所述好氧池污泥接种量为池容的20%,池内连续曝气,控制溶解氧2-4mg/L,pH调整到6.5-8.5,并根据重金属废水中有机物的含量将水力停留时间设定为10-24小时。通过池内活性污泥中微生物的表面络合、生物吸附及絮凝作用进一步降低废水中的重金属含量,使其稳定达到《污水综合排放标准》的一级标准。3) The treated waste water in the artificial wetland system further enters the aerobic pool, and microorganisms are cultivated in the activated sludge in the aerobic pool. Aeration, control the dissolved oxygen 2-4mg/L, adjust the pH to 6.5-8.5, and set the hydraulic retention time to 10-24 hours according to the content of organic matter in the heavy metal wastewater. Through the surface complexation, biosorption and flocculation of microorganisms in the activated sludge in the pool, the heavy metal content in the wastewater is further reduced, so that it can stably meet the first-level standard of the "Comprehensive Wastewater Discharge Standard". 2.根据权利要求1所述一种用于治理重金属的“三段法”生物降解方法,其特征在于:所述秸秆槽中投放的可以是玉米秸秆、小麦秸秆、花生壳、甜菜渣或稻壳中的一种农业废弃物,将这些农业废弃物进行初级的切割处理,这些被处理过的农业废弃物为使此类天然有机吸附剂有较理想的吸附能力,同时将这些农业废弃物进行二次处理,通过檬酸修饰、碱化处理、巯基改性的化学改性方式在这些农业废弃物中引入更多的羟基、羧基、巯基、磷酸根、胺基活性基团。2. A "three-stage method" biodegradation method for controlling heavy metals according to claim 1, characterized in that: corn stalks, wheat straws, peanut shells, sugar beet pulp or rice stalks can be placed in the straw tank. A kind of agricultural waste in the shell, these agricultural wastes are subjected to primary cutting treatment, these processed agricultural wastes are used to make this kind of natural organic adsorbent have a better adsorption capacity, and these agricultural wastes are processed at the same time The secondary treatment involves introducing more hydroxyl, carboxyl, sulfhydryl, phosphate, and amine active groups into these agricultural wastes through chemical modification methods such as citric acid modification, alkalization treatment, and sulfhydryl modification. 3.根据权利要求1所述一种用于治理重金属的“三段法”生物降解方法,其特征在于:所述人工湿地系统中的湿地基质由砾石、土壤按1:1组成,在所述湿地基质上种植的水生植物由对重金属吸收能力较强的芦苇、香蒲、美人蕉、风车草组成,通过人工湿地的物理沉淀、过滤、化学沉淀、吸附、微生物交互作用以及植物的吸收作用,实现重金属的有效去除。3. A kind of " three-stage method " biodegradation method that is used to control heavy metal according to claim 1, it is characterized in that: the wetland substrate in the said artificial wetland system is made up of gravel, soil by 1:1, in said The aquatic plants planted on the wetland substrate are composed of reeds, cattails, cannas, and windmill grasses that have strong absorption capacity for heavy metals. Through the physical precipitation, filtration, chemical precipitation, adsorption, microbial interaction and plant absorption of the constructed wetland, heavy metals can be realized. effective removal.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108109713A (en) * 2017-12-13 2018-06-01 四川知创空间孵化器管理有限公司 A kind of processing method of radioactivity medical waste water
CN118993361A (en) * 2024-08-02 2024-11-22 靖江市华晟重金属防控有限公司 Heavy metal wastewater treatment device with self-cleaning function

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102285740A (en) * 2010-06-21 2011-12-21 天津科技大学 Non-waste treatment method for garbage leachate
US8252182B1 (en) * 2008-09-11 2012-08-28 University Of Central Florida Research Foundation, Inc. Subsurface upflow wetland system for nutrient and pathogen removal in wastewater treatment systems
CN105036487A (en) * 2015-08-18 2015-11-11 湖南艾布鲁环保科技有限公司 Device and method for further treating and recycling heavy metal waste water

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8252182B1 (en) * 2008-09-11 2012-08-28 University Of Central Florida Research Foundation, Inc. Subsurface upflow wetland system for nutrient and pathogen removal in wastewater treatment systems
CN102285740A (en) * 2010-06-21 2011-12-21 天津科技大学 Non-waste treatment method for garbage leachate
CN105036487A (en) * 2015-08-18 2015-11-11 湖南艾布鲁环保科技有限公司 Device and method for further treating and recycling heavy metal waste water

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108109713A (en) * 2017-12-13 2018-06-01 四川知创空间孵化器管理有限公司 A kind of processing method of radioactivity medical waste water
CN118993361A (en) * 2024-08-02 2024-11-22 靖江市华晟重金属防控有限公司 Heavy metal wastewater treatment device with self-cleaning function

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