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    The treatment and reusing technology of printing and

    dyeing wastewater

    YI XuenongSchool of Environment and Architecture

    University of Shanghai for Science and Technology

    Shanghai, China

    Zhang YansenSchool of Environment and Architecture

    University of Shanghai for Science and Technology

    Shanghai, China

    AbstractA kind of technology and process of treating printing

    and dyeing wastewater with high efficiency and low energy

    consumption was presented. Based on the analysis of the current

    methods this article summed up the more practical way,

    combining theory with practice, to provide some references for

    the similar projects.

    Keywords-printing and dyeing wastewater; treatment

    technology; polyvinyl alcohol

    PVA

    ; wastewater reusing

    The printing and dyeing wastewater is a major part of

    textile printing industrial wastewater .In recent years, as the

    rapid development of dyestuff industry and finishing

    technology, new additives, dyes, finishing agents are widely

    used in the printing and dyeing industry .In the wastewater

    more and more poisonous organic compound are found, andeven some organic matter are carcinogenic, mutagenic, cause

    distortion, which has done mankind a great disservice. China

    is one of the countries that struggle with serious problems

    about water shortage and water pollution .As the water crisisincreasingly, more attention must be paid to reduce pollutant

    emissions from the every printing and dyeing processes, useof clean production technologies, recycle of wastewater,

    which are of great political and economic significance for

    alleviating the water crisis and maintaining sustainable

    development.

    1 The characteristics and hazards of printing and dyeing

    wastewater

    According to their sources, printing and dyeing wastewaterpollutants can be divided into two categories: one is from

    entrainment material of the fiber material; the other is used in

    the processing of slurry, oil, dyes, chemical additives, etc. The

    characteristics of printing and dyeing wastewater are complex

    composition, high organic matter content , color depth, highchemical oxygen demand ,relatively low biochemical oxygen

    demand ,poor biodegradability and large emissions , etc.

    1.1Hazards to human health

    1.1.1 Cause acute and chronic poisoning

    Printing and dyeing wastewater sometimes contains heavy

    metal salts which are difficult to degrade using normal

    biochemical methods, thus they can long-stand in the natural

    environment and endanger human health through the foodchain and so on

    [1]. So that the human body poisoning, such as

    methyl mercury poisoning (Mina Mata disease), cadmium

    poisoning (Itai-itai disease), arsenic poisoning, chromium

    poisoning, cyanide poisoning, pesticide poisoning. Of lead,

    barium, fluoride can also cause harm to human health. Theseacute and chronic poisoning is the main aspects of causing

    serious harm to human health.

    1.1.2 Carcinogenesis

    Printing and dyeing wastewater contains benzene, amine,

    pyrene, polycyclic aromatic hydrocarbons, halogenated

    hydrocarbons and other organic pollutants[2]. All thesematerials can be accumulated in suspended solids, sediments

    and aquatic organisms. Long-term consumption of water or

    food containing these substances may induce cancer. Printing

    and dyeing industry use a large amount of Chromium

    relatively: dyeing industry often uses it as an oxidant andpotassium dichromate mordant; the preparation of printing

    rollers consumes a large amount of Chromium .Chromium has

    also been confirmed to cause cancer, we should pay particular

    attention to its emissions and utilization.

    1.2 The harm to the environment

    It is estimated that more than 50 million tons of textile dyesare used all over the world. A large number of wastewater

    brought by the process of printing and dyeing is discharged

    into the rivers, lakes, seas and surface water. The dye in the

    wastewater can absorb light, reducing the transparency of

    water and affecting the growth of aquatic life and microbial,

    which is not conducive to self-purification of water.Meantime it is easy to create visual pollution and also severe

    pollution of water can affect human health. The pollutions and

    emissions must be strictly controlled for those things like

    resin finishing agent, organic metal flame retardants and

    978-1-4244-4713-8/10/$25.00 2010 IEEE

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    waterproofing agents containing cadmium which can easily

    produce formaldehyde, resulting in badly contaminated but

    difficult to treat by the traditional methods.

    2 The treatment technology of printing and dyeing

    wastewater

    2.1 The traditional treatment process and its improvement

    2.1.1 Adsorption process

    The most widely used physical approaches the adsorption

    process. Activated carbon, clay, porous material such as

    powder or granules are mixed with water ,or let water through

    filter bed composed with granular material, so that waste

    water pollutants are adsorbed on the surface of porous

    material or filtered to remove . The method for the removal of

    dissolved organic matter in waste water is very effective, but

    can not remove the water and the hydrophobic colloidal dyes.

    2.1.2 Coagulation treatment

    They are of two main Methods, flotation and r coagulating

    sedimentation. in which the mostly used Coagulant is

    aluminum or iron salt-based. The main advantages of

    coagulation process is simple, easy operation and

    management, equipment investment, covering an small area ,

    with high hydrophobic dye decolonization efficiency ;

    drawback is that operating costs are relatively high ,sludge

    with high water, poor performance and child care, the

    treatment effect on the hydrophilic dye worse.

    2.1.3 Biological treatment method

    Biological treatment methods include aerobic and anaerobic

    method. Currently the main method used is aerobic dyeingwastewater treatment. Aerobic is divided into aerobic and

    biofilm process. A large number of organic materials are

    decomposed by activated sludge, also part of the color. You

    can also fine-tune the PH value, operating efficiency and low

    cost, water quality is better suited to deal with a high organic

    content printing and dyeing wastewater; biofilm

    Decolonization of dyeing wastewater higher than the activated

    sludge process. Contact oxidation method is a kind of biofilm

    characteristics of activated sludge method, the equivalent of

    adding aeration tank filling, so filling the surface covered with

    a variety of biofilm in the biofilm, the wastewater at the sametime there is a certain amount of suspension the activated

    sludge and biofilm detachment, so that waste water to be

    purified.

    2.2 New treatment technology

    2.2.1 Photochemical oxidation

    The advantages of photochemical oxidation are with themild reaction conditions (ambient temperature and pressure),

    oxidation ability and speed Photochemical oxidation can be

    divided into light decomposition, photosensitizing oxidation,

    light-induced oxidation and photo catalytic oxidation. Amongthem, the present study is more photo catalytic oxidation. The

    research on dyes of photo catalytic degradation is focused on

    photo catalyst. Some iron ligand compounds have

    photochemical activity. They can be used to degrate organic

    compounds. TiO2 is a ideal photo catalyst because of is

    stabilization insoluble innocuity etc. The traditional

    powder TiO2 is hard to use in practice, because it does notsuit to flow system and hard to separate.

    2.2.2 Membrane technology

    The technology disposals the wastewater by separating

    concentratingrecycling. The membrane technology includes

    micro filtration membrane ultra filtration membrane

    nanometer membrane and RO membrane. Membrane

    technology does not need to plus chemical reagents, in the

    process, it does not produce secondary pollution; the process

    is simple to operate, it can be carried out under atmosphericpressure with low energy consumption; some salts and dyes

    can be recycled from the wastewater and be reused; The

    treated wastewater can be directly reused, reducing waste

    emissions. But the membrane technology also exists some

    problems, such as membrane fouling, membrane flux,

    membrane cleaning and the resistance to acid and alkali of the

    membrane, etc.

    3 The treatment methods of PVA in printing and dyeing

    wastewater

    The process of printing and dyeing wastewater includes:

    desizing, scouring, bleaching, mercerization, dyeing, printingand finishing, etc. The most pollutants in printing and dyeing

    wastewater are from the slurries of the process of sizing,mainly PVA slurry. PVA is a kind of organic macromolecular

    compounds that is difficult to biochemical degradation, and it

    is also an important micro-organisms immobilized material.

    Recently, because of its increasing usage, the environmental

    problems that PVA causes become increasingly serious. Many

    experts and scholars at home and abroad are studying thetreatment methods of PVA wastewater and have made a series

    of results[3]

    .

    3.1 Membrane technology

    As is introduced above, membrane separation method is a

    method that uses micro porous membrane to filter and

    separates the certain substances in the wastewater by the

    Selective permeability of the membrane. Feng Bing-ling used

    chitosan ultra filtration membrane to treat printing and dyeing

    wastewater, the removal rate of COD could reach about 80%,

    the decolonization rate exceeded 95%[4]

    .

    3.2 Ozone oxidation technology

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    This method is using ozone to degrade the PVA, the

    process is: A long-chain between the molecules cut and the

    molecules break into small molecules, so the rate of theBOD5/COD increase, which is favorable to the follow up

    biochemical treatment. In the actual operation, it does not just

    use the ozone, but also together use other enhanced

    technologies, such as ultrasound wave, UV and so on. The

    results of an experiment show that, after 12 min treatment, the

    degradation rate of PVA with O3/ultrasound, O3/UV synergyis more improved than directly under the O3 oxidation,

    showing a good synergistic effect[5]

    .

    3.3 Chemical condensation technology

    PVA is a non-ionic organic polymers, the adsorption of

    some electric charge produced by the traditional coagulants is

    very weak, merely has no effect to the degradation of PVA. In

    the case of containing more salts, salting-out effect makes

    PVA separate out. At the same time, borax and PVA

    molecules start up double-diol-type combination[6]

    . The

    experiments show that under the combined effect of the borax

    cross linking and Salting-out reaction, the PVA in the

    wastewater can be separated out as the gel forms, so as to

    achieve the purpose of recycling.

    3.4 Biodegradation technology

    Although the biodegradability of waste water that contains

    PVA is poor, PVA can be degraded under the effect of some

    enzymes. As early as 1936, people found PVA can bedegraded into carbon dioxide and water under the effect of the

    fungus Fusarium. Using highly efficient degradation bacteria

    to deal with PVA-containing wastewater is through screening

    and domestication PVA-degrading bacteria, to achieve thePVA completely biodegradable. As is reported, PVA-

    degrading bacteria include pseudomonas, brevibacterium,

    etc[7]

    . The PVA-degrading enzymes isolated from these

    degrading bacteria include sec-alcohol oxidasepolyvinyl

    alcohol dehydrogenaseB-diketone hydrolase, etc.

    4 Printing and dyeing wastewater reuse technology

    In order to meet the future demand for printing and dyeing

    industry, we must strength the protection, management and

    use of existing water resources[8]

    . Improve the reuse ratio of

    water and development of new water sources can greatlyalleviate the contradiction of the water supply and demand toreduce effluent emissions and the existing water pollution.

    The printing and dyeing wastewater reuse technologies

    include :AdsorptionCoagulationChemical Oxidation

    Electrochemical Biological treatment Photochemical

    oxidation Membrane technology Ultrasound

    technologyHigh-energy physics method and so on.

    The development direction of the reuse of printing and

    dyeing wastewater has two paths: Emphasis on the promotion

    of the comprehensive management of the waster water andcontinuous optimization of the wastewater reuse program

    [9].

    In the design of water-recycling facility we should

    calibrate the maximum dosage. Water desalination is an

    important factor for maintaining balance of circulation system,

    ensuring product quality and stable operation of the sewage

    system. If not, the largest recycling dosage should be in

    control within 30%.

    5 Pilot scale study

    The process printing and dyeing wastewater treatment is

    further introduced in company in Liaoning Province, which

    has the similar technics .

    5.1 Process of treatment

    The investigation shows that concentrations of pollutants in

    the production process are very high, especially ,PVA ,whichis as high as 14000mg/L. We apply the chemical treatment-

    anaerobic treatment -aerobic treatment process in order to

    effectively reduce concentrations of pollutants, which can

    obtain good effects. First, it is the pretreatment of biochemical

    treatment and that is coagulation with the use of PAM. PVA

    residual concentration with different dosage of PAM is in

    Table1.( the assumption price of PAM in the market is 20000

    Yuan/ton)Table1 Record of experimental data

    concentration

    of PAM5 3 1 0.5

    0.1

    0.05

    residualconcentration

    of PVA

    mg/L

    4900 6100 7250 8700 9500 10000

    cost of PAM

    Yuan

    1000 600 200 100 20 10

    From the table above we know concentration of PAM and

    residual concentration of PVA are inverse ratio while cost of

    PAM and concentration of PAM are direct proportion.

    Considering the high gremoval efficiency of the pollutants in

    the follow-up biological treatment we choose 0.5as optical

    concentration. Route of process is seen in fig 1:

    Fig.1 Process of treating PVA-contained wastewater and reusing

    raw water

    regulation tank mechanic reactor

    anaerobic tankaerobic tanksecondarysedimentation tank

    effluent

    PAM

    returned sludge

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    5.2 Interpretation of process of treatment

    Sewage generated from the production process firstly flow

    into regulation tank, which is responsible for storage andregulation of wastewater to ensure the stable quality and

    quantity of wastewater. Then it reaches mechanical reactor

    after the addition of

    polyaluminium chloride(shortened from PAC).There is a

    series of physical and chemical reactions with the help of

    mechanical agitation, which also can reduce pollutionconcentration greatly, especially PVA, at the same time. The

    anaerobic tank is mainly for decomposing macromolecular

    organic into macromolecule organic through the metabolism

    of anaerobe, which is good for follow-up treatment. Aerobic

    pool is to further decompose macromolecules organics so as

    to make effluent up to standard. Finally it flows intosecondary sedimentation tank, separating sludge from effluent.

    A part of the sludge will flow back to anaerobic tank and

    aerobic pool, other is for beneficial utilization[10]

    .

    5.3 Treatment effect

    After the normal operation of the equipment, recycling rate

    of PVA and removal rate of COD can arrive at approximately

    80 percent, which decrease concentration of PVA immensely.

    It plays a key role in improving the overall treatment effect of

    printing and dyeing wastewater and making effluent meets the

    standard.

    6 Conclusion

    From the result of study and discussion above, the proposed

    method and technology is feasible for treating the printing

    and dyeing wastewater . First we apply phy-chemical methodto treat wastewater of PVA, which can effectively low cost

    and investment, decrease treatment load of subsequent

    processing structures, increase biodegradability of wastewater.

    It can also create conditions for subsequent aerobic and

    anaerobic wastewater treatment to obtain higher efficiency.

    We are able to enable effluent up to national standard making

    use of this technique although initial concentration is as high

    as 14000mg/L. Whats more, anaerobic process can produce

    biogas, which can be used as new energy and reduce the harm

    on environment. At last, the project is set up with recycling

    process. Recycling water can be used for landscape irrigation

    and production process, which can save precise water and

    reduce production cost. Anyhow this technique can gain goodeconomic benefit and social benefit, and have some

    promotional value and application prospects.

    References

    [1] Guo Li. Study on Recovery Method of Polyvinyl Alcohol in DesizingWastewater[D]. Donghua University, 2008.

    [2] Li Chengxuan, Fan Xuerong, Wang Qiang. Effects of poly(vinylalcohol) in desizing wastewater and its degradation performance[J].Dyeing auxiliaries, 2007, 24(6): 7210.

    [3] Zhu Puxin, Yao Yongyi. PVA biodegradability and applicationprospect [J]. Cotton Textile Technology, 2005, 33(2): 62264.

    [4] Zhang Huizhen, Liu Bailing, Luo Rong. Recent Advances in theBiodegradability of PVA and its Derivative Material [J]. Journal of theGraduate School of the Chinese Academy of Sciences, 2005, 22 (6):6572666.

    [5] Lee Jea, An KimMal2Nam. Isolation of new and potent poly(vinylalcohol) degrading strains and their degradation activity [J]. PolymerDegradation and Stability, 2003, 81(2): 3032308.

    [6] Lin Shaoning, Fang Borong. Study on degradation of PVA with bacteriaof F8633[J]. China textile university journal, 1990, 16(3): 18223.

    [7] Lin Jian. Applications of biochemical technology in PVA wastewatertreatment [J]. The Light & Textile Industries of Fujian, 2005, 10(36):241.

    [8] Porter John J. Recovery of polyvinyl alcohol and hotwater from thetextile wastewater using thermally stable membranes[J]. Journal ofMem2brane Science, 1998, 15(1): 45253.

    [9] Dong Shengxiong, Gong Qi,Zhao. Study on Separation of PolyvinylAlcohol(PVA) by Ultrafiltration from Desizing Wastewater [J]. Journalof Textile Research, 2004, 25(2): 73275.

    [10] Yan Deshun. Condensation for recovery of polyvinyl alcohol ofdesizing wastewater[J]. Chongqing Environmental Science, 1984, 5 (8):42246.