CN109052620A - A kind of method of cadmium ion in removal heavy metal wastewater thereby - Google Patents
A kind of method of cadmium ion in removal heavy metal wastewater thereby Download PDFInfo
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- CN109052620A CN109052620A CN201810764489.8A CN201810764489A CN109052620A CN 109052620 A CN109052620 A CN 109052620A CN 201810764489 A CN201810764489 A CN 201810764489A CN 109052620 A CN109052620 A CN 109052620A
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/005—Combined electrochemical biological processes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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Abstract
The invention discloses a kind of methods of cadmium ion in removal heavy metal wastewater thereby, heavy metal wastewater thereby containing cadmium is handled using the electrical energy drive microorganism electrolysis cell that microbiological fuel cell degradation of organic substances generates, overall process does not consume external electric energy, secondary pollution is not generated, is a kind of environmental-friendly new method of heavy metal containing wastewater treatment containing cadmium.This method comprising the following three steps: 1, the determination of MFC operating parameter;2, building of the MFC-MEC from driving coupled system;3, the processing of the heavy metal wastewater thereby containing cadmium: by step 1 and 2, heavy metal wastewater thereby containing cadmium is handled using MEC cathode reaction, catholyte is heavy metal wastewater thereby containing cadmium, and pH value is 1~5, and anode uses carbon paper, and cathode material uses stainless steel, titanium plate and carbon paper.After reaction to MEC, cathode is taken out, MEC cathode reduction products is collected, is detected through XRD, MEC cathode product is cadmium carbonate, and cadmium ion removal rate is 89.5%.
Description
Technical field
The present invention relates to bioelectrochemistry and heavy metal containing wastewater treatment field, cadmium in specially a kind of removal heavy metal wastewater thereby
The method of ion.
Background technique
With the rapid development of our country's economy, process of industrialization is constantly accelerated, and people's lives level is greatly improved,
But consequently also bring water environment pollution problem.In the industrial processes such as plating, metallurgy, chemical industry, it can generate a large amount of useless
Water, these waste water composition complicated components, in addition to containing organic contamination beyond the region of objective existence difficult to degrade, also containing an a large amount of poisonous and hazardous huge sum of moneys
Belong to substance, if this kind of waste water is dealt with improperly, it will cause great harm to ecology, environment, human health.
Cadmium toxicity in waste water is big, is easily absorbed by the body, and accumulates in human body, can damage renal tubule, will lead to when serious
Renal failure.Itai-itai event in Japan occurred to 1977 for nineteen fifty-five, was typical chronic cadium poisoning event, more than 20
It is dead to cause more than 200 people by Nian Jian.Thus, cadmium once enters environment, will result in biggish harm.Also occurred in China
Serious cadmium pollution event, therefore the processing of the heavy metal wastewater thereby containing cadmium is very urgent, must be handled before discharge of wastewater, with
Reach discharge standard, avoids pollution the generation of event.The common technology of heavy metal containing wastewater treatment containing cadmium includes changing both at home and abroad at present
Learn the precipitation method, ferrite process, ion-exchange, electric flocculation method, membrane separation process, absorption method, bioanalysis etc., some technology and methods
It has successfully been applied in the processing of the heavy metal wastewater thereby containing cadmium.
Patent (CN104211221A) is directed to low concentration heavy metal wastewater thereby containing cadmium, by sequentially adding aluminium polychloride, phosphorus
It is stirred after sour sodium, anion, finally precipitating filtering, this method has many advantages, such as at low cost, without secondary pollution.
Patent (CN103466776A) is directed to the heavy metal wastewater thereby containing cadmium of high concentration, and sodium hydroxide and three polysulfide cyanogen are added
Sour sodium, this method have good removal effect to the cadmium of various forms in water body.
Patent (CN102464396A) is fixed on carrier by the emulsion for being prepared into foaming agent, organic solvent, auxiliary agent
On, for handling heavy metal wastewater thereby containing cadmium, this process flow is simply, at normal temperature carry out, noiseless, and agents useful for same is nontoxic, nothing
Harmful, non-volatile, lotion can be recycled, and treatment effect is obvious.
Patent (CN104478128A) based on existing chemical precipitation and coagulation and filtration technique, without or be difficult into
Under conditions of the transformation of row Large scale processes, change dispensing and mode of operation and pH value control mode, solves Trace Cadmium in waste water and reach
Mark the problem of discharge.With using varieties of reagent few, reagent dosage is few, and raw materials used economical and easily available, does not add into system
Any harmful element, at low cost, high treating effect.
Patent (CN101367575) cooperates with quickly processing absorption cadmium using frustule wall and bacterium cell wall, realizes in waste water
The removal of cadmium, this method can be widely applied to the cleaning treatment of heavy metal wastewater thereby containing cadmium and resource utilization of industrialized production.It is raw
Object electro-chemical systems include microbiological fuel cell (Microbial Fuel Cell, MFC) and microorganism electrolysis cell
(Microbial Electrolytic Cell, MEC).The MFC of early stage is concentrated mainly on anode chamber in terms of wastewater treatment, leads to
Anode microbial action degradation of organic waste water is crossed, is produced electricl energy while realizing wastewater treatment.With the development of bioelectrochemistry,
It was found that many heavy metal ion can also be used as cathode electronics receptor, the application range further expansion of MFC.With this technology
Development, the electricity generation ability of MFC improves, and the configuration of device is also more diversified, has also appeared at the same time more
The experimental exploring that kind MFC and other technologies are coupled, such as photosynthetic type MFC (Photo-MFC), phytomicroorganism fuel cell
(PMFC), anaerobic fluidized bed microbiological fuel cell (AFB-MFC) etc..MFC-MEC is exactly that it constantly explores lower one kind constructed
New coupled mode, i.e., produced electricl energy by MFC, and driving MEC operation not only utilizes the electric energy of MFC, but also be able to achieve different redox
The removal and recycling of current potential heavy metal ion.Although there are many treating method of the heavy metal wastewater thereby containing cadmium, simple improvement can disappear
Very high cost is consumed, is resulted in waste of resources.
Summary of the invention
To solve the above-mentioned problems, the present invention is a kind of emerging clean energy resource and waste water using MFC-MEC coupled system
Processing technique.It is calculated according to Nernst equation, Cu2+Electrode potential be positive, reaction spontaneous can carry out, meet MFC reducing condition,
And produce electricl energy, with Cu2+When for cathode electronics receptor, MFC's is stabilized the output voltage as 200~750mV, and Cd2+Reduction electricity
Position is -0.403V, and the electric energy that MFC is generated is the operation that can drive MEC.Using this feature, MFC is connected with MEC, is realized
Cadmium ion in heavy metal wastewater thereby, is restored removal by running from driving for coupled system in the form of cadmium carbonate.By utilizing MFC
Electricity production driving MEC operation, while realizing the removal of removal of Cadmium from wastewater, to achieve the purpose that administer water pollution, whole process
Without additional electric energy, cleanliness without any pollution.
A method of removal heavy metal wastewater thereby cadmium ion, include the following three steps:
1) MFC and MEC parameter is determined;
2) MFC-MEC series coupled;
3) MFC-MEC handles heavy metal wastewater thereby containing cadmium from driving coupled system;
Wherein the anode of MFC is connected with the cathode of MEC by conducting wire, and the cathode of MFC and the anode of MEC pass through series resistance
Coupling is connected;Series circuit is constituted, is run using the electrical energy drive MEC that MFC is generated.
The anode inoculum of the MFC and MEC is activated sludge, and the anode activity that anolyte is volume ratio 1:2-1:4 is dirty
The mixed liquor of mud and anode substrate sodium acetate;
The catholyte of the MFC is copper-containing solution, and the catholyte of the MEC is cadmium-containing solution.
Wherein, the determining MFC and MEC parameter comprises the steps of,
The dischargeable capacity of the anode chamber MFC and cathode chamber is 300~500mL, and the catholyte copper ion initial concentration is 500
~2000mg/L, pH value are 3~5, and saturated sodium chloride solution is used to adjust conductivity for 5~8.5mS/cm, between anode and cathode
Away from for 6~8cm;
The dischargeable capacity of the anode chamber MEC and cathode chamber is 100~500mL, and the cadmium wastewater cadmium ion initial concentration is
900~1000mg/L, pH value are 1~5;
The anode material of MFC and MEC is carbon paper, and cathode is using one of stainless steel, titanium plate or carbon paper, anode and cathode
Spacing is 6~8cm, is separated by between two Room by anion-exchange membrane;
MFC-MEC series coupled is, when to MFC output voltage stabilization being 200~700mV, preferably 500~700mv, passes through
MEC is connected by series resistance coupled modes with MFC, and the resistance is 800-1000 Ω;
It is by the MFC-MEC system of series coupled that MFC-MEC, which handles heavy metal wastewater thereby containing cadmium from driving coupled system,
It runs at normal temperatures and pressures, to after reaction, take out MEC cathode, collects cathode reduction products.
The anode substrate sodium acetate solution concentration is 0.9~1g/L;
The anode activated sludge is the sludge containing electricity production bacterium, and the dehydration for being derived from sewage treatment plant's dehydration machine room is dirty
Culture domestication liquid is added in the dewatered sludge, cultivates the volume ratio of domestication liquid and dewatered sludge are as follows: 1:5~2:5 for mud;, training
Support domestication liquid constituent: 0.2~0.4g/L sucrose, 0.2~0.4g/L potassium dihydrogen phosphate, 0.15~0.35g/L phosphoric acid hydrogen two
Potassium, 0.1~0.2g/L triammonium citrate, 0.01~0.3g/L sodium chloride, 0.3~0.5g/L magnesium chloride, 0.1~0.2g/L chlorination
Calcium, 0.10~0.40g/LNH4Cl, 0.9~1g sodium acetate, after nitrogen deoxidation with inoculum in anaerobic, be protected from light, normal temperature state
Lower domestication is cultivated 5~7 days.
Technical scheme the utility model has the advantages that
1. the electrical energy drive MEC operation generated with MFC, the electric energy that MEC utilizes MFC to generate in situ realize removal of Cadmium from wastewater
Removal, realize coupled system from driving operation, whole process does not consume external electric energy, without secondary pollution.
2.MFC maximum power density is up to 22278.4mW/m2, COD removal rate 83.3%, MFC tough cathode ion remaval rate
93.7%, MEC cathode cadmium ion remaval rate 89.5%.
3.MEC cathode surface precipitate is detected as CdCO through XRD3, it was demonstrated that the cadmium ion in waste water passes through MEC cathodic reduction
With CdCO after reaction3Precipitated product is precipitated, to realize the removal of removal of Cadmium from wastewater.
Detailed description of the invention
Fig. 1 MFC-MEC coupled system schematic diagram;
Fig. 2 MFC power density curve;
Fig. 3 MEC cathode product XRD spectrum.
Specific embodiment
MFC and MEC is equipped with cathode chamber and anode chamber in embodiment, by HMED-05181 anion-exchange membrane phase between two Room
Every wherein MFC catholyte is copper ions solution, and the catholyte of MEC is the waste water containing cadmium ion, and catholyte uses dilute sulfuric acid
Adjust pH value;The anode activated sludge and anode substrate sodium acetate that the anolyte of MFC and MEC is volume ratio 1:2-1:4.
Wherein the anode of MFC is connected with the cathode of MEC by conducting wire, and the cathode of MFC and the anode of MEC are by connecting 1000
The coupling of Ω resistance is connected;Series circuit is constituted, is run using the electrical energy drive MEC that MFC is generated.The anode material of MFC and MEC is
Carbon paper, cathode material are one of stainless steel, titanium plate or carbon paper.Conductivity is adjusted using saturated sodium chloride solution.
The amberplex is HMED-05181 anion-exchange membrane, and film effective area is 12cm2, first impregnated using preceding
In deionized water for 24 hours more than, make the abundant aquation of film and expansion, take the film out in the NaCl solution for being immersed in 5%, save it is standby
With.
The anode substrate sodium acetate solution concentration is 1g/L;
The anode activated sludge is to be derived from Changzhou Qing Tan sewage treatment plant dehydration machine room containing the sludge of electricity production bacterium
Culture domestication liquid is added in dewatered sludge in the dewatered sludge, and the volume ratio for cultivating domestication liquid and dewatered sludge is 2:5;Training
Support domestication liquid constituent: 0.38g/L sucrose, 0.21g/L K2HPO4·3H2O、0.21g/L KH2PO4、0.12g/L C6H5O7
(NH4)3、0.07g/L NaCl、0.40g/L MgCl2·6H2O、0.12g/L CaCl2、0.40g/L NH4Cl, 1.00g/L acetic acid
Sodium.After nitrogen deoxidation with inoculum anaerobic, be protected from light, under normal temperature state domestication culture 7 days.
Influence of the embodiment 1:MEC cathode material to MFC-MEC coupled system processing cadmium wastewater
Change the cathode material of MEC: first group of cathode material is stainless steel, and second group of cathode material is titanium plate, third group
Cathode material is carbon paper, constructs three groups of coupling devices.MFC, MEC dischargeable capacity are the anode and yin of 500mL, MFC and MEC
The volume ratio of interpolar distance 8cm, activated sludge and substrate is 1:4;MFC catholyte copper ion concentration is 1280mg/L, conductivity
For 5mS/cm, pH value 5;MEC catholyte concentration of cadmium ions is 985mg/L, pH value 4.9.It is 700mV to MFC output voltage
When, MEC is connected with MFC by series system, coupled system is run at normal temperatures and pressures, when cathode material is titanium plate, MEC
Cadmium ion removal rate is 51.5% in catholyte, compared with stainless steel, the coupled system that carbon paper is MEC cathode, Cd2+Removal rate point
10.2%, 8.1% is not improved, and it is as shown in Figure 2 that MFC electricity production effect connected in series is shown in Table 1, MFC power density curve.System
Cathode is taken out after end of run, collects MEC cathode reduction products, cathode product is analyzed using XRD diffractometer, is in 2 θ
There is diffraction maximum at 23.49 °, 30.27 °, 36.42 °, 43.81 °, 49.51 °, 49.90 °, 49.51 °, 58.27 °, as seen Fig. 3 institute
Show, it is consistent with the characteristic peak of cadmium carbonate by computer search.
Influence of the embodiment 2:MEC catholyte pH to MFC-MEC coupled system processing cadmium wastewater
In addition to following difference, other conditions are identical for embodiment 2 and embodiment 1.The volume of MFC, MEC activated sludge and substrate
Than being 1:2, cathode material is carbon paper, and MFC catholyte copper ion concentration is 512mg/L, pH value 3, conductivity 8.1mS/
Cm, MEC catholyte concentration of cadmium ions are 985mg/L.It adjusts MEC catholyte pH value and is respectively as follows: pH=1, pH=3 and pH=5.It is real
It tests when the results are shown in Table 2, pH=5, cadmium ion removal rate is 89.5%, and cathode product is detected as cadmium carbonate through XRD diffractometer.
Influence of 1 cathode material of table to coupled system
The influence that 2 pH value of table removes coupled system electrical property and cadmium ion
MEC catholyte pH | Open-circuit voltage (mV) | Internal resistance (Ω) | Cadmium ion removal rate (%) |
1 | 254 | 672 | 45.2 |
3 | 343 | 1263 | 82.4 |
5 | 304 | 1291 | 89.5 |
The present invention is by handling MFC and MEC series coupled cadmium wastewater, not consuming it can be seen from table one and table two
Cadmium ion removal rate can be up to 89.5% in the case where expense external electric energy, while the catholyte anolyte of MFC and MEC is sludge
Or sewage, with current consumption mass energy, the existing method for removing cadmium for generating new pollutant is completely different.The present invention is weight containing cadmium
The processing of metallic wastewater provides more feasible more environmentally-friendly new method.Obviously, above-described embodiment be only be clearly to say
Bright example, and do not limit the embodiments.For those of ordinary skill in the art, in above description
On the basis of can also make other variations or changes in different ways.There is no need and unable to give all embodiments
Exhaustion.And obvious changes or variations extended from this are still within the protection scope of the invention.
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Cited By (3)
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CN110330095A (en) * | 2019-04-22 | 2019-10-15 | 武汉理工大学 | Carry out the method except cadmium electricity production simultaneously using algae cathode microbial fuel cell |
CN115763832A (en) * | 2022-09-15 | 2023-03-07 | 云南师范大学 | Coupling device of MEC and MFC with shared electrode and application |
CN116655059A (en) * | 2023-05-06 | 2023-08-29 | 山东科技大学 | Wastewater treatment device and method for synchronously removing high-concentration heavy metals and sulfate radicals |
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Application publication date: 20181221 |