CN1989292A - Method for black liquor treatment - Google Patents
Method for black liquor treatment Download PDFInfo
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- CN1989292A CN1989292A CNA2005800251920A CN200580025192A CN1989292A CN 1989292 A CN1989292 A CN 1989292A CN A2005800251920 A CNA2005800251920 A CN A2005800251920A CN 200580025192 A CN200580025192 A CN 200580025192A CN 1989292 A CN1989292 A CN 1989292A
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- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/0007—Recovery of by-products, i.e. compounds other than those necessary for pulping, for multiple uses or not otherwise provided for
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- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C11/00—Regeneration of pulp liquors or effluent waste waters
- D21C11/04—Regeneration of pulp liquors or effluent waste waters of alkali lye
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Abstract
本发明涉及黑液的处理方法。本发明可从造纸及纸浆制造业排出的碱性黑液有效地分别提取木质素和碱,且使处理后的水成为净化水。在黑液中加酸将pH值调整至2.5~3.5,添加凝聚剂,使黑液中所含的木质素沉积,并分离木质素和清水。理想的是将臭氧气体作为微气泡使其与清水接触反应。
This invention relates to a method for treating black liquor. The invention can effectively extract lignin and alkali separately from alkaline black liquor discharged from paper and pulp manufacturing industries, and produces purified water after treatment. Acid is added to the black liquor to adjust the pH to 2.5–3.5, and a coagulant is added to cause the lignin contained in the black liquor to precipitate, thus separating the lignin from the purified water. Ideally, ozone gas is used as microbubbles to react with the purified water.
Description
技术领域technical field
现在,对于由造纸及纸浆制造业所排出的黑液处理,由于黑液的性状含有很多有害物质,因而作为其对策是进行巨大的设备投资,进行碱的回收和黑液的浓缩化,并进行包含利用能量的焚烧处理,但这些处理的成本很高且将大气污染物质、恶臭物质排放到大气中,本发明涉及提供一种该黑液的处理方法。At present, for the treatment of black liquor discharged from the paper and pulp manufacturing industry, since the properties of the black liquor contain many harmful substances, the countermeasures are to make a huge investment in equipment, recover the alkali, concentrate the black liquor, and carry out Incineration treatment using energy is included, but the cost of these treatments is very high and air pollutants and malodorous substances are discharged into the atmosphere. The present invention relates to providing a treatment method for the black liquor.
背景技术Background technique
黑液从木质的蒸煮(木质素的除去)工序排出。黑液的实质是蒸煮液,由于蒸煮液为将木质素溶解在水中而使用烧碱,进而为了促进脱木质素而使用硫化钠,所以黑液中除木质素外,还含有硫化钠经水解生成的硫化氢、甲硫醇、二甲基硫、二甲基二硫,另含有碳水化合物、有机酸、树脂类的有害的碱性液态物质。Black liquor is discharged from the wood cooking (removal of lignin) process. The essence of the black liquor is the cooking liquor. Because the cooking liquor uses caustic soda to dissolve lignin in water, and then uses sodium sulfide to promote delignification, so the black liquor contains not only lignin, but also sodium sulfide produced by hydrolysis. Hydrogen sulfide, methyl mercaptan, dimethyl sulfide, dimethyl disulfide, and harmful alkaline liquid substances containing carbohydrates, organic acids, and resins.
现有的黑液的处理方法是,为将其浓缩而提高固体成分浓度,使用规模大的多效能真空蒸发罐法来浓缩,进一步通过空气的氧化来提高浓缩度,然后在将硫化钠和硫酸盐废液加入到该黑液中后,使其燃烧,从得到的灰中回收无机化合物的碳酸钠、硫化钠,焚烧的能量用于锅炉的供水加热,但其大部分排放到大气中。The processing method of existing black liquor is, in order to concentrate it and improve the solid content concentration, use the large-scale multi-effect vacuum evaporator method to concentrate, further improve the degree of concentration through the oxidation of air, and then add sodium sulfide and sulfuric acid Salt waste liquid is added to this black liquor and burned to recover inorganic compounds such as sodium carbonate and sodium sulfide from the obtained ash. The energy of incineration is used for boiler water supply heating, but most of it is discharged into the atmosphere.
而且,将碳酸钠溶解到水中,将氢氧化钙转化为烧碱,将烧碱再次用于蒸煮液并实现其循环利用。Also, sodium carbonate is dissolved in water, calcium hydroxide is converted into caustic soda, and caustic soda is reused and recycled for cooking liquor.
但是,现有技术中的措施的设备费巨大,且恶臭物质漏出到处理设施外,使用过多的水,木质素的大半被焚烧并作为排放气体排放到大气中,这些所需的处理成本都极大。However, the equipment cost of the measures in the prior art is huge, and the malodorous substance leaks out of the treatment facility, uses too much water, and most of the lignin is incinerated and discharged into the atmosphere as exhaust gas, all of which require treatment costs. great.
在日本的造纸及纸浆等工厂附近能够感觉到独特的臭味,这是由二甲基硫之类的硫化合物引起的,由于使用大量的水并在使用后进行排放,且排放气体的排放量也极高,所以期望有对环境更有利的方法来进行黑液处理。A unique odor can be felt near paper and pulp factories in Japan, which is caused by sulfur compounds such as dimethyl sulfide, due to the use of a large amount of water and discharge after use, and the amount of exhaust gas emissions It is also extremely high, so it is desirable to have a more environmentally friendly method for black liquor treatment.
发明内容Contents of the invention
本发明就是解决上述问题的方法,是下述构成的黑液处理方法。The present invention is a method for solving the above-mentioned problems, and is a black liquor processing method having the following configuration.
(1)一种黑液的处理方法,其特征是,在将从造纸及纸浆制造业排出的碱性黑液用水稀释后,在该液中加酸而将pH值调整至2.5~3.5,再添加少量的凝聚剂,使黑液中所含的木质素成为固形物而沉积,或者沉积及浮起,并分离为固形物的木质素和清水。(1) A treatment method for black liquor, characterized in that, after diluting the alkaline black liquor discharged from the paper and pulp manufacturing industry with water, adding acid to the liquor to adjust the pH value to 2.5 to 3.5, and then Add a small amount of coagulant to make the lignin contained in the black liquor become solid and deposit, or deposit and float, and separate into solid lignin and clear water.
该情况下,所加酸的种类是盐酸、硫酸、硝酸、蚁酸、氢氟酸等,利用该处理可使黑液中所含的大半木质素沉积,并很容易地分离木质素。In this case, the kind of acid to be added is hydrochloric acid, sulfuric acid, nitric acid, formic acid, hydrofluoric acid, etc., and most of the lignin contained in the black liquor can be deposited by this treatment, and the lignin can be easily separated.
(2)一种黑液的处理方法,其特征是,使臭氧气体与上述(1)记载的清水接触反应,用臭氧的氧化能力将从清水中所含的未沉积的木质素、木质中所含的有机酸及树脂类、半纤维素中所含的可溶性碳水化合物或其它硫化合物中选择的任一种或两种以上成分氧化分解。(2) A processing method for black liquor, characterized in that ozone gas is contacted with the clear water recorded in the above (1) to react, and the undeposited lignin and wood contained in the clear water are removed by the oxidation ability of ozone. Any one or two or more components selected from organic acids and resins contained in hemicellulose, soluble carbohydrates contained in hemicellulose or other sulfur compounds are oxidatively decomposed.
(3)一种黑液的处理方法,其特征是,在对清水进行沙滤后,再进行上述(2)中记载的臭氧气体的接触反应。(3) a processing method of black liquor, characterized in that, after carrying out sand filtration to clear water, carry out the contact reaction of ozone gas recorded in above-mentioned (2) again.
(4)一种黑液的处理方法,其特征是,向上述(1)~(3)中任一项记载的清水中供给臭氧气体作为微气泡(微小气泡),并进行接触反应。(4) A method for treating black liquor, comprising supplying ozone gas as microbubbles (microbubbles) to the clean water described in any one of (1) to (3) above, and performing a contact reaction.
(5)一种黑液的处理方法,其特征是,在使臭氧气体与上述(2)~(4)中任一项记载的清水接触反应的工序中,首先用高速搅拌机混合臭氧气体和一部分清水,成为臭氧气体的微气泡混合液,将该微气泡混合液输送到清水中。(5) A processing method for black liquor, characterized in that, in the step of contacting and reacting ozone gas with the clear water described in any one of the above (2) to (4), at first mixing ozone gas and a part of it with a high-speed mixer Clear water becomes a microbubble mixture of ozone gas, and the microbubble mixture is sent to the clean water.
在固液分离等的清水中,含有木质素、半纤维素中所含的可溶性碳水化合物、木质中的有机酸及其中和物、木质中所含的树脂类及其皂化物、妥尔油、二甲基硫、硫化氢、甲硫醇、二甲基二硫等,虽然这些有机物的分解需要强力的氧化物质,但本发明已将其解决。In clear water such as solid-liquid separation, lignin, soluble carbohydrates contained in hemicellulose, organic acids and neutralized substances contained in wood, resins contained in wood and saponified substances, tall oil, Dimethyl sulfide, hydrogen sulfide, methyl mercaptan, dimethyl disulfide, etc. Although the decomposition of these organic substances requires strong oxidizing substances, the present invention has solved them.
作为强力氧化物质的臭氧气体虽然现在用臭氧产生机制备,其所含的O2、N2、CO2等为90%左右,10%左右为O3。因此,为使该O3产生最大限度的氧化能力,需要有为使O3易于进行氧化分解的条件,这就是在用酸将黑液的pH值下降到3左右时,O3的氧化能力提高,而且由于O3的气泡越小则反应面积越大,所以氧化能力大幅度地提高。Ozone gas as a powerful oxidizing substance is currently prepared by an ozone generator, but it contains about 90% of O 2 , N 2 , CO 2 , etc., and about 10% is O 3 . Therefore, in order to make the O3 produce the maximum oxidation capacity, it is necessary to have the conditions to make O3 easy to oxidize and decompose, that is, when the pH value of the black liquor is reduced to about 3 with acid, the oxidation capacity of O3 is improved , And because the smaller the bubbles of O 3 are, the larger the reaction area is, so the oxidation ability is greatly improved.
为了使O3气泡粒子小至微米级,可以通过例如以高速搅拌清水和O3,使O3气泡的大小成为极小的泡。该小泡直到到达清水的水面时才破裂并消失,在该破裂及消失的瞬间,虽可以说泡的内部温度达到数千度的高温,且达到数千个大气压的高压,但理想的是进行处理,通过这样添加酸来调整pH值后使O3气体成为小的微米级的泡。此时,如果同时照射超声波,则可促进破裂及消失作用,所以更理想。In order to make the O 3 bubble particles as small as the micron order, the size of the O 3 bubbles can be made extremely small by, for example, stirring clean water and O 3 at high speed. The small bubbles do not break and disappear until they reach the surface of the clear water. At the instant of breaking and disappearing, although it can be said that the internal temperature of the bubbles reaches a high temperature of several thousand degrees and a high pressure of thousands of atmospheres, it is ideal to carry out Processing, by adding acid in this way to adjust the pH value makes O 3 gas into small micron-sized bubbles. At this time, it is more preferable to irradiate ultrasonic waves at the same time because the cracking and disappearing effects can be accelerated.
(6)一种黑液的处理方法,其特征是,上述(5)记载的高速搅拌机的构造是用不锈钢制造,且将清水到入到以3000~20000转的高速转动的叶片型搅拌机中,并通入臭氧。清水和臭氧在搅拌机中混合,此时,臭氧成为微气泡,将该微小气泡和上水的混合液从下放出到储存在反应槽中的清水中并长时间滞留在清水中。(6) a treatment method for black liquor, characterized in that the structure of the high-speed stirrer described in (5) above is made of stainless steel, and clear water is entered into the blade-type stirrer rotating at a high speed of 3000~20000 revolutions, And into the ozone. Clean water and ozone are mixed in the mixer. At this time, the ozone becomes micro-bubbles, and the mixture of the micro-bubbles and upper water is discharged from the bottom into the clean water stored in the reaction tank and stays in the clean water for a long time.
(7)一种黑液的处理方法,其特征是,将由上述(1)得到的清水或用由上述(2)~(6)中任一项得到的臭氧进行氧化处理的清水液作为黑液的稀释水或纸浆制造用的用水加以利用。(7) A treatment method for black liquor, characterized in that the clear water obtained by the above (1) or the clear water that is oxidized by the ozone obtained in any one of the above (2) to (6) is used as the black liquor Dilution water or water used in pulp manufacturing is used.
(8)一种黑液的处理方法,其特征是,在将进行了上述(2)~(6)中任一项记载的臭氧气体的接触反应的清水进行中和处理后,进行接触活性炭的吸附处理。(8) A treatment method for black liquor, characterized in that, after the clear water having undergone the contact reaction of ozone gas described in any one of the above-mentioned (2) to (6) is neutralized, the process of contacting activated carbon is carried out. Adsorption treatment.
在清水中含有的有机物完全分解成为CO2和H2O,且最终可由活性炭吸附除去杂质而得到净化水,所得到的这种净化水(清水)既可作为稀释用,也可作为纸浆制造用的用水利用。The organic matter contained in the clear water is completely decomposed into CO 2 and H 2 O, and finally the purified water can be obtained by removing impurities by adsorption of activated carbon. The obtained purified water (clear water) can be used for dilution or for pulp manufacturing of water use.
这样,根据本发明,黑液中的木质素的除去(分离)可通过调整溶解的木质素的pH值使其变成悬浊物而很容易地实现。Thus, according to the present invention, the removal (separation) of lignin in black liquor can be easily realized by adjusting the pH of dissolved lignin so that it becomes a suspension.
而且,这可在常温常压下进行,随着O3的使用电费也因酸与微气泡的效果而可更进一步大幅下降。Moreover, this can be carried out at normal temperature and pressure, and the electricity cost of using O 3 can be further greatly reduced due to the effect of acid and microbubbles.
通常,臭氧(O3)的氧化分解能力虽基于臭氧所具有的氧原子的氧化能力,但通过酸的添加使黑液中的pH值下降到3左右,使酸所具有的氢原子和臭氧原子结合,生成具有超过氧原子的强氧化能力的活性氧。由于这种活性氧的氧化能力具有远大于氧原子的氧化能力的分解能力,所以在处理对象物的清水中添加酸,使其pH值为3左右,并通过加臭氧而大幅提高分解能力。Usually, although the oxidative decomposition ability of ozone (O 3 ) is based on the oxidation ability of the oxygen atom possessed by ozone, the pH value in the black liquor is lowered to about 3 by the addition of acid, so that the hydrogen atom possessed by the acid and the ozone atom Combined, active oxygen having a strong oxidizing power exceeding that of oxygen atoms is generated. Since the oxidizing ability of this active oxygen has a decomposition ability far greater than that of oxygen atoms, acid is added to the clean water of the object to be treated to make the pH value about 3, and the decomposition ability is greatly improved by adding ozone.
附图说明Description of drawings
图1是本发明实施例的系统构成图。FIG. 1 is a system configuration diagram of an embodiment of the present invention.
图2是本发明实施例的流程图。Fig. 2 is a flowchart of an embodiment of the present invention.
图3是本发明实施例的流程图。Fig. 3 is a flowchart of an embodiment of the present invention.
图中:In the picture:
1-黑液储存罐,2-pH调整槽,3-脱水机,4-臭氧反应槽,5-中和槽,6-活性碳塔,7-处理后水储存槽1-black liquor storage tank, 2-pH adjustment tank, 3-dehydrator, 4-ozone reaction tank, 5-neutralization tank, 6-activated carbon tower, 7-treated water storage tank
具体实施方式Detailed ways
下面,利用实施例说明本发明的实施方式。Next, embodiments of the present invention will be described using examples.
实施例1Example 1
图1表示实施例的系统构成图,图2表示其流程图。FIG. 1 shows a system configuration diagram of the embodiment, and FIG. 2 shows its flowchart.
首先,在图1中,从左方起标号1为黑液储存罐,黑液储存在其中。First, in Fig. 1, the
接着,标号2为pH调整槽,通过将黑液和稀释水装入其中,添加盐酸、硫酸等酸,并添加凝聚剂而慢慢搅拌,使木质素及其它物质沉积。此时,作为酸,理想的是添加微量的氢氟酸。Next,
随后,标号3为脱水机3,在其中通过例如压力过滤将木质素作为固形物取出。Subsequently,
标号4是臭氧反应槽,将用压力过滤除去了木质素的液体导入其中,将臭氧作为微气泡,使其进行接触反应。
在该阶段,由于作为强力氧化物质的臭氧气体最大限度地提高了氧化能力,且O3的气泡越小则反应面积越大,所以氧化能力大幅提高。At this stage, since ozone gas, which is a powerful oxidizing substance, maximizes the oxidizing ability, and the smaller the O bubbles , the larger the reaction area, so the oxidizing ability is greatly improved.
由于使O3气泡的粒子小至微米级,所以通过高速搅拌清水和O3,可使O3气泡的大小成为极小的泡,在该泡消失的瞬间,可以说泡的内部温度达到数千度的高温,且达到数千个大气压的高压,反应强烈地进行。Since the particles of the O 3 bubbles are down to the micron level, the size of the O 3 bubbles can be made into extremely small bubbles by stirring clean water and O 3 at a high speed. At the moment when the bubbles disappear, it can be said that the internal temperature of the bubbles reaches thousands. The high temperature of 100 degrees Celsius and the high pressure of thousands of atmospheres allow the reaction to proceed intensely.
标号5为中和槽,将碱液添加在其中进行中和,然后导入活性炭塔6,将杂质全部吸附除去,而成为已净化的处理后水。
处理后水储存在处理后水储存槽8中,然后(1)作为稀释用水导入pH调整槽2,或者(2)作为其它工业用水等使用。The treated water is stored in the treated water storage tank 8, and then (1) introduced into the
再有,在图2的流程图中,用附加文字进行更具体的说明。In addition, in the flow chart of FIG. 2, a more specific description is given with an additional character.
实施例2Example 2
根据图3所示的流程图进行黑液的处理。The processing of black liquor is carried out according to the flowchart shown in FIG. 3 .
首先,在10t黑液的原液(含有固体成分20%)中添加50t稀释用水而得到共计60t的被处理液,在其中加入盐酸900kg,再边搅拌边添加高分子凝聚剂1.8kg,而后放置,分离为液体部分和固体部分。First, add 50t of dilution water to the stock solution of 10t black liquor (containing 20% solid content) to obtain a total of 60t of treated liquid, add 900kg of hydrochloric acid therein, add 1.8kg of polymer coagulant while stirring, then place, Separation into a liquid part and a solid part.
将所得到的液体部分48t进行沙滤,将微气泡状臭氧气体导入到经沙滤得到的过滤水中进行氧化处理后,添加300kg烧碱液进行中和处理。接着,将该中和处理后的水通入活性碳塔,进行杂质的吸附处理,得到了净化水。The obtained liquid part 48t is subjected to sand filtration, microbubble ozone gas is introduced into the filtered water obtained through sand filtration for oxidation treatment, and then 300 kg of caustic soda is added for neutralization treatment. Next, the neutralized water was passed into an activated carbon tower to perform adsorption treatment of impurities to obtain purified water.
该净化水用作上述稀释水或纸浆制造用水。This purified water is used as the above-mentioned dilution water or pulp manufacturing water.
另一方面,由上述固液分离工序得到的12t固体部分经压力过滤过滤,分离为610kg脱离液11和390kg脱水块(含水率78%)。再有,在过滤时使用了1t滤布清洗水和3kg凝聚剂。On the other hand, 12 t of solids obtained from the above solid-liquid separation process were filtered by pressure filtration, and separated into 610 kg of dehydrated liquid 11 and 390 kg of dehydrated blocks (water content 78%). Furthermore, 1 ton of filter cloth cleaning water and 3 kg of coagulant were used for filtration.
上述脱离液和滤布清洗水添加到沙滤前的液体部分中。The above detachment liquid and filter cloth washing water are added to the liquid part before sand filtration.
此外,将生石灰39kg添加混合到上述脱水块中,得到了干松的粗粒状的处理物429kg。该处理物含有很多木质素,所以处理容易且成为不溶于水的组成物。In addition, 39 kg of quicklime was added and mixed to the above-mentioned dehydrated block to obtain 429 kg of a dry and loose coarse-grained processed product. Since this processed product contains a large amount of lignin, it is easy to handle and becomes a water-insoluble composition.
再有,表1中表示了黑液的原液和各工序的处理液的分析值。In addition, in Table 1, the analysis value of the raw liquid of black liquor and the processing liquid of each process is shown.
表1Table 1
接下页continued on next page
表1,接上页Table 1, continued from previous page
单位:BOD、COD为mg/L、SS为mg/kgUnit: BOD, COD is mg/L, SS is mg/kg
如从该表所示的数值所观察到的,最终得到的处理水(净化水)的水质,其BOD、COD、SS等全部是优良的值,可知是水质优良的净化水。As can be seen from the numerical values shown in the table, the water quality of the finally obtained treated water (purified water) has excellent values for BOD, COD, SS, etc., and it can be seen that it is purified water with excellent water quality.
本发明的黑液处理方法可作为造纸领域、纸浆制造领域的含木质素的黑液的有效处理方法使用。The black liquor treatment method of the present invention can be used as an effective treatment method for lignin-containing black liquor in the field of papermaking and pulp production.
根据本发明,可从黑液有效地分别提取木质素和碱,且处理后的水成为净化水,可用于黑液的稀释水、纸浆制造用的用水等各种用途。According to the present invention, lignin and alkali can be efficiently extracted separately from black liquor, and the treated water becomes purified water, which can be used for various purposes such as dilution water of black liquor and water for pulp production.
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| JP260103/2004 | 2004-09-07 | ||
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| WO (1) | WO2006038072A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102192862A (en) * | 2011-03-07 | 2011-09-21 | 海南金海浆纸业有限公司 | Method for measuring solid content in heavy black liquid |
| CN103154097A (en) * | 2010-06-03 | 2013-06-12 | Fp创新研究中心 | Method for separating lignin from black liquor |
| CN104310683A (en) * | 2014-09-18 | 2015-01-28 | 林连山 | Development and control method of papermaking wastewater |
Families Citing this family (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101219837B (en) * | 2007-12-21 | 2010-12-15 | 辽宁三和环境工程有限公司 | Ozonation process and equipment for oil-containing alkali wastewater |
| CN102650109B (en) * | 2012-04-23 | 2014-07-23 | 刘彦坤 | Method for transforming pulping black liquor into powders containing fulvic acid and amino acid by complex microorganisms |
| FI127601B (en) * | 2014-04-03 | 2018-10-15 | Andritz Oy | Process for handling beverage solution from a process for the extraction of lignin |
| CN104032612A (en) * | 2014-06-17 | 2014-09-10 | 毛林涛 | Method for extracting lignin from alkaline straw pulp black liquor |
| KR101562193B1 (en) | 2014-10-08 | 2015-10-23 | 한경대학교 산학협력단 | Method for improving concentration of degradation products of black liquor |
| CN110420624B (en) * | 2019-08-22 | 2022-02-22 | 农业农村部环境保护科研监测所 | Porous biomass charcoal-based phosphate adsorbent and preparation method and application thereof |
| CN115467182B (en) * | 2022-08-23 | 2024-01-05 | 天津科技大学 | A kind of pulp production raw material pretreatment process |
Family Cites Families (16)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS50651A (en) * | 1973-05-07 | 1975-01-07 | ||
| JPS5149560A (en) * | 1974-10-25 | 1976-04-28 | Nippon Rensui Kk | Riguninganjuhaieki no shorihoho |
| JPS5242649A (en) * | 1975-09-30 | 1977-04-02 | Nittan Co Ltd | Method for processing pulp waste liquid |
| JPS5279560A (en) * | 1975-12-25 | 1977-07-04 | Nittan Co Ltd | Method of treating waste pulp liquid |
| JPS5358002A (en) * | 1976-11-05 | 1978-05-25 | Sanyo Kokusaku Pulp Co | Process for removing suspended material in sulphite pulp waste from broadleaf trees as raw material |
| JPS54131002A (en) * | 1978-03-30 | 1979-10-11 | Sumitomo Precision Prod Co | Oxdizing treatment apparatus in kraft pulp making plant |
| US4470876A (en) * | 1982-07-22 | 1984-09-11 | Beaupre Marc F | Kraft overload recovery process |
| JPH0784716B2 (en) * | 1985-10-29 | 1995-09-13 | 三菱重工業株式会社 | Method for recovering caustic soda from alkaline pulp waste liquor |
| US5635024A (en) * | 1993-08-20 | 1997-06-03 | Bountiful Applied Research Corporation | Process for separating lignins and dissolved organic compounds from kraft spent liquor |
| JP3451764B2 (en) * | 1994-12-22 | 2003-09-29 | 王子製紙株式会社 | Method of deodorizing wastewater containing odorous substances |
| JP2000015273A (en) * | 1998-07-03 | 2000-01-18 | Asahi Chem Ind Co Ltd | Treating method for paper pulp waste water |
| JP2001009465A (en) * | 1999-07-01 | 2001-01-16 | Nippon Solid Co Ltd | Treatment of papermaking wastewater |
| US6627784B2 (en) * | 2000-05-17 | 2003-09-30 | Hydro Dynamics, Inc. | Highly efficient method of mixing dissimilar fluids using mechanically induced cavitation |
| JP2003245662A (en) * | 2002-02-21 | 2003-09-02 | Fm Ecology Kenkyusho:Kk | Waste water treatment system |
| JP2003251384A (en) * | 2002-03-05 | 2003-09-09 | Fm Ecology Kenkyusho:Kk | Pretreatment method for biological wastewater treatment |
| JP2004050124A (en) * | 2002-07-23 | 2004-02-19 | Nippon Paper Industries Co Ltd | Processing method of waste water and equipment therefor |
-
2005
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN103154097A (en) * | 2010-06-03 | 2013-06-12 | Fp创新研究中心 | Method for separating lignin from black liquor |
| CN103154097B (en) * | 2010-06-03 | 2017-01-18 | Fp创新研究中心 | method for separating lignin from black liquor |
| CN102192862A (en) * | 2011-03-07 | 2011-09-21 | 海南金海浆纸业有限公司 | Method for measuring solid content in heavy black liquid |
| CN104310683A (en) * | 2014-09-18 | 2015-01-28 | 林连山 | Development and control method of papermaking wastewater |
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| JP2011078971A (en) | 2011-04-21 |
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