WO2007025417A1 - Procede de blanchiment de la pate - Google Patents

Procede de blanchiment de la pate Download PDF

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Publication number
WO2007025417A1
WO2007025417A1 PCT/CN2005/002173 CN2005002173W WO2007025417A1 WO 2007025417 A1 WO2007025417 A1 WO 2007025417A1 CN 2005002173 W CN2005002173 W CN 2005002173W WO 2007025417 A1 WO2007025417 A1 WO 2007025417A1
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Prior art keywords
pulp
bleaching
weight
tower
concentration
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PCT/CN2005/002173
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English (en)
French (fr)
Inventor
Youming Li
Zhonghao Chen
Mingyou Liu
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South China Uni. Of Tech.
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Publication of WO2007025417A1 publication Critical patent/WO2007025417A1/zh

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    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/12Bleaching ; Apparatus therefor with halogens or halogen-containing compounds
    • D21C9/14Bleaching ; Apparatus therefor with halogens or halogen-containing compounds with ClO2 or chlorites
    • D21C9/144Bleaching ; Apparatus therefor with halogens or halogen-containing compounds with ClO2 or chlorites with ClO2/Cl2 and other bleaching agents in a multistage process
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/1026Other features in bleaching processes
    • D21C9/1036Use of compounds accelerating or improving the efficiency of the processes
    • DTEXTILES; PAPER
    • D21PAPER-MAKING; PRODUCTION OF CELLULOSE
    • D21CPRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
    • D21C9/00After-treatment of cellulose pulp, e.g. of wood pulp, or cotton linters ; Treatment of dilute or dewatered pulp or process improvement taking place after obtaining the raw cellulosic material and not provided for elsewhere
    • D21C9/10Bleaching ; Apparatus therefor
    • D21C9/16Bleaching ; Apparatus therefor with per compounds
    • D21C9/163Bleaching ; Apparatus therefor with per compounds with peroxides

Definitions

  • This invention relates to a pulp bleaching process for the paddle paper industry, and more particularly to a wood and grass paper paddle cleaning bleaching process. '
  • the existing pulp bleaching methods mainly include the following processes: Chlorination (C) One alkali treatment (E) - Hypochlorite (H) bleaching (referred to as CEH bleaching, the same below), CEH bleaching mainly has the following problems:
  • Chlorine is used as a bleaching agent for chlorination. Chlorine gas itself is toxic and has a high operational risk.
  • AOX carcinogenic organic chloride
  • CEH has a low bleaching concentration and a large amount of bleached water.
  • the wastewater cannot be recycled and has a large discharge.
  • the pulp After bleaching, the pulp has low whiteness (75% ISO or less), and the yellowing is serious. It is impossible to make high-grade paper products. To improve the apparent whiteness of the pulp, it is necessary to add a fluorescent whitening agent with carcinogenic effect, and a fluorescent whitening agent. It is a chemical that is prohibited from use in food packaging paper.
  • the single-stage oxygen delignification rate is low, and the delignification rate is 40-50%.
  • the two-stage oxygen delignification uses two medium-concentration pumps, which are washed between stages and have complicated processes.
  • Bleaching equipment requires strong corrosion resistance, and bleaching equipment cannot be localized.
  • the object of the present invention is to provide a pulp cleaning and bleaching method for the defects of the existing pulp bleaching technology, instead of using chlorine gas which pollutes the environment, but using non-polluting oxygen and hydrogen peroxide to clean the bleaching agent, through a single section Double-tower oxygen bleaching and activation pretreatment process achieves high-efficiency bleaching, with high bleaching efficiency and whiteness of more than 85%; its construction investment is low, only about 1/5 of chlorine dioxide bleaching; less pollution, its AOX is reduced by 70% Above, the wastewater discharge is reduced by 70%, and the COD & emissions are reduced by more than 60%.
  • the production line can be constructed for the pulp bleaching production line or based on the existing pulp bleaching production line, especially suitable for wood with a daily output of 50 to 300 tons. , grass raw material pulp clean bleaching.
  • the pulp cleaning bleaching process of the present invention is: Oxygen delignification (0) - hypochlorite bleaching (H) - activation pretreatment (M, - M activator pretreatment) - hydrogen peroxide bleaching (P) ( Referred to as OHMP, the same below), specifically including the following steps:
  • 0.5-1.0% by weight of oxygen, 0.5-1.0% by weight of NaOH and steam are added to the pulp, and the pulp is placed in the second upflow tower to maintain the temperature in the tower at 100-110 °C.
  • the top pressure is 0.35-0.45 MPa, and the residence time of the pulp in the tower is about 30-50 minutes.
  • the pulp delignification rate reaches about 60%.
  • the activator is an organic compound containing an acid anhydride group, such as sulfite anhydride, cis olefinic anhydride, mannose anhydride, succinic anhydride, cesium phthalate or maleic anhydride, etc., due to the influence of related reactive groups
  • the lignin, the main component of pulp whiteness has an activation effect, thereby increasing the bleaching effect of subsequent hydrogen peroxide.
  • the present invention Compared with the existing pulp bleaching method, the present invention has the following advantages -
  • Oxygen delignification is a single-stage two-column process. There is no need for a medium-booster pump between the two oxygen delignification towers. No need for a booster pump, no need for washing. A medium-concentration pump is used to achieve pulp throughout the oxygen delignification system. Medium transport; • Oxygen delignification tower bottom does not require a distributor, and the top of the tower does not require a discharger. '
  • the pretreatment of the pulp by the activator activates the main component of the pulp which affects the whiteness of the pulp, and improves the bleaching effect of the subsequent hydrogen peroxide.
  • the whiteness increase is increased to 15-20% or more.
  • the traditional concept of hydrogen peroxide bleaching whiteness increase is only below 10%.
  • the whiteness of traditional CEH bleaching bleaching does not exceed 75% ISO.
  • the whiteness of the pulp after bleaching can be increased to 85% or more. Since the whiteness of the pulp is improved, the paper product does not need to be added with a toxic fluorescent whitening agent. Food packaging paper, etc.;
  • the yellowing rate of pulping is only 20% of that of conventional CEH bleaching.
  • Figure 1 is a process flow diagram of the present invention.
  • About 3% consistency pulp is pumped to vacuum washers # 1 to a concentration of 13-15% by addition of about 2% NaOH, 0.1% MgS0 4 , low pressure steam into the pulp to approximately 70 ° C, over 1 #
  • the medium-thick slurry pump is sent to the 1# medium-concentration mixer.
  • the medium-pressure steam is added before the 1# medium-concentration mixer to keep the pulp at 100-110 °C, and about 2% oxygen is introduced before the 2 # medium-concentration mixer.
  • the pulp enters the 1 #liter flow oxygen delignification tower through a 2 # medium consistency mixer.
  • the temperature in the column is maintained at 100-110 ° C, the pressure at the top of the column is about 0.6 MPa, and the residence time of the pulp in the column is 40-60 minutes.
  • the medium-concentration paddle pump is fed into the 4 # medium-concentration mixer, and low-pressure steam is added before the 4 # medium-concentration mixer to keep the pulp at 90-95 °C, and 2.0-2.5% peroxidation is introduced before the 5 # medium-concentration mixer.
  • Hydrogen the pulp enters the upflow hydrogen peroxide bleaching tube through the 5 # medium concentration mixer, and then enters the downflow hydrogen peroxide bleaching tower.
  • the kappa number of the pulp before bleaching is about 15-20.
  • the pulp enters the 1# medium thick slurry pump riser, and the low pressure steam is added at the lower end of the riser to increase the pulp temperature to about 70 ,.
  • the pulp is sent to the 1 # medium consistency mixer through the 1 # medium thick slurry pump, and the 1 # medium concentration mixer is used. before joining medium pressure steam to increase the temperature of the pulp 110 V, and then was fed to the mixer 2 # 1 # concentrated oxygen delignification tower bottom, before the addition of 2% oxygen concentration in a mixer # 2 (on dry basis paddle ).
  • the residence time of the pulp in the # 1 oxygen delignification tower is 40-60 minutes, and the temperature inside the tower is maintained at 11 (TC, the pressure at the top of the tower is about 0.6 Mpa.
  • the pulp from the top of the 1 # oxygen delignification tower is sent to the 3# medium-concentration mixer by the pressure head of the medium-concentration pump, and 0.5% oxygen, NaOH and medium-pressure steam are added before the 3 # medium-concentration mixer is required.
  • the rate of delignification of pulp after oxygen delignification reached about 60%.
  • the washed concentrated pulp is adjusted to a concentration of about 10%, 2.5% calcium hypochlorite is added, mixed by a 1 # low-concentration mixer, and then introduced from the upper part of the hypochlorite bleaching tower, and low-pressure steam is added to the 1 ⁇ thick mixer. , to ensure that the temperature of the pulp in the hypochlorite bleaching tower is about 40 ,, and the residence time is controlled at 90 minutes.
  • the water is adjusted at the bottom of the hypochlorite bleaching tower to adjust the pulp concentration to about 3 %, and then pumped to a 4 # vacuum washer for washing and concentration.
  • the washed concentrated pulp is adjusted to a concentration of about 5%, 0.5% of M activation pretreatment agent is added, mixed by the 2 # low concentration mixer, and then introduced from the upper part of the M pretreatment tower, and low pressure steam is added to the 2 # low concentration mixer. , to ensure that the temperature of the pulp in the M pretreatment tower is about 50 ° C, and the residence time is controlled to about 40 minutes.
  • the water was adjusted at the bottom of the M pretreatment tower to adjust the pulp concentration to about 3%, and then pumped to a 5 # vacuum washer for washing and concentration.
  • the water is adjusted to a concentration of about 3%, and then pumped to a 6 # vacuum washer for washing and concentration.
  • auxiliaries are used in an amount of 92-95% relative to the absolute dry pulp.

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Wood Science & Technology (AREA)
  • Paper (AREA)

Description

纸浆清洁漂白方法 技术领域
本发明涉及制桨造纸工业的纸浆漂白方法, 具体地说涉及木材类和草类纸桨清洁漂白 方法。 '
技术背景
现有的纸浆漂白方法主要包括如下流程: 氯化 (C) 一碱处理 (E) —次氯酸盐 (H) 漂白 (简称 CEH漂白, 下同), CEH漂白主要存在如下问题:
( 1 ) 氯化采用氯气作漂白剂, 氯气本身具有毒性, 操作危险性大。
(2) 氯化和碱处理过程产生大量的致癌毒性有机氯化物 (AOX), AOX不仅存 在于漂白废水中, 而且存在于纸浆和纸品中,废水中的 AOX对微生物具有毒性作用,难以 生化降解, 导致排放废水无法达到国家标准(GB3544 - 2001 )。
(3 ) CEH漂白浓度低, 漂白清水用量大, 废水无法实现循环回用, 排放量大。
(4) 漂后纸浆白度低(75%ISO以下), 返黄严重, 无法抄造高档纸品, 要提高 纸浆表观白度, 必须加入有致癌作用的荧光增白剂, 而荧光增白剂是食品包装用纸所禁止 使用的化学药品。
现有的纸浆漂白方法还有一种流程: 氧(0) —一段二氧化氯 —碱处理(E) — 二段二氧化氯(D2) —过氧化氢(P) (简称 O D! ED^漂白, 下同), 0 01 £0^漂白主要 存在如下问题-
( 1 ) 单段氧脱木素率低, 脱木素率在 40— 50%。 双段氧脱木素使用两台中浓浆 泵, 段间洗涤, 流程复杂。
' (2) 过氧化氢漂白效果差, 白度增量在 6%以下。
(3 ) 漂白系统建设投资大, 吨浆投资高达 2000元以上, 年产 5万吨漂白系统投 资一亿元以上。
(4) 二氧化氯制备成本高。
(5) 漂白设备要求有很强的抗腐蚀性, 漂白设备无法实现国产化。
(6) 漂白废水和纸浆中仍存在一定的毒性有机氯化物 (AOX)。
现有的纸浆漂白方法没有氧气 (0) 与次氯酸盐(H) 的组合、 没有活化预处理(M)、 没有活化预处理与过氧化氢 (P) 的组合。
发明内容
本发明的目的在于针对现有纸浆漂白技术存在的缺陷, 提供一种纸浆清洁漂白方法, 不采用对环境产生污染的氯气, 而是使用无污染的氧气和过氧化氢清洁漂白剂、 通过单段 双塔氧漂和活化预处理过程实现高效漂白, 其漂白效率高, 白度达 85 %以上; 其建设投资 低, 只为二氧化氯漂白的 1/5左右; 污染少, 其 AOX下降 70%以上, 废水排放量减少 70 % , COD&排放量下降 60%以上; 生产线可以为纸浆漂白生产线的建设或在现有纸浆漂白 生产线基础上改造形成,特别适合于日产 50吨至 300吨规模的木材、草类原料纸浆清洁漂 白。
本发明的纸浆清洁漂白方法流程为: 氧脱木素(0) —次氯酸盐漂白 (H) —活化预处 理(M, —种 M活化剂预处理) 一过氧化氢漂白 (P) (简称 OHMP, 下同), 具体包括以 下步骤:
( 1 ) 单段双塔氧脱木素(0)
浓度为 13— 15%重量的纸浆中加入占纸浆 1.5— 2.5 %重量的 NaOH和 0.05— 0.10%重 量的 MgS04, 通入蒸汽升温至 100— 110°C, 通入占纸浆 1.5— 2.5 %重量氧气, 置于第一个 升流塔内, 塔顶压力为 0.55— 0.65Mpa, 塔内温度为 100— 110°C, 纸桨在塔内的停留时间 ¾ 40-60分钟;
为了达到进一步脱木素效果, 补加占纸浆 0.5-1.0%重量氧气、 0.5-1.0%重量 NaOH和 蒸气,置纸浆于第二个升流塔内,保持塔内温度在 100— 110°C,塔顶压力为 0.35-0.45MPa, 纸浆在塔内的停留时间约 30— 50分钟。 ,
经氧脱木素后, 纸浆脱木素率达到 60%左右。
两个氧脱木素塔之间无需中浓桨泵, 无需增压泵, 无需洗涤, 由中浓浆泵实现纸 在 氧脱木素系统中的输送, 氧脱木素塔塔底无需分配器, 塔顶无需排料器。
(2) 次氯酸盐漂白 (H)
洗涤步骤(1 )得到的浓缩纸浆至 8— 10%重量, 加入占纸浆 2.0— 3.0%重量次氯酸盐, 通入蒸气升温至 35— 45 °C, 进入降流塔, 塔内停留时间为 1一 2小时;
(3 ) 活化剂预处理 (M)
洗涤浓缩的纸浆至 5— 6%重量浓度, 加入占纸浆 0.3— 0.7%重量的活化剂并通入蒸气 升温至 50— 55°C, 进入降流预处理塔, 塔内停留时间为 30— 40min, 塔底稀释纸浆至 2.5 一 3.5%重量;
所述活化剂是含有酸酐基团的有机化合物, 例如亚硫酸酯酐、顺顶烯而酸酐、甘露酐、 丁二酐、 邻苯二甲酸酑或马来酸酐等, 由于相关活性基团对影响纸浆白度的主要成分木素 具有活化作用, 从而提高了后续过氧化氢的漂白效果。
(4) 过氧化氢漂白 (P)
纸桨经洗漆浓缩至 13— 15 %重量的浓度, 加入占纸浆 1.5— 2.5 %重量 NaOH、 2.0— 3.0 %重量 Na2Si03、 0.05— 0.10 %重量 MgS04, 通入蒸气, 纸浆在 90— 95 °C下通入占纸浆 2.0-2.5%重量的过氧化氢,进入升流式过氧化氢漂白管, 再进入降流式过氧化氢漂白塔,纸 浆在塔内停留 90— 120min, 塔底稀释纸桨至 2.5— 3.5%重量浓度。
以上各种助剂的用量均相对与绝干浆。
与现有纸浆漂白方法比较, 本发明具有如下优点-
(1) 无元素氯清洁漂白 (ECF)方法, 环境效果好
• 取消使用毒性原材料氯气, 采用清洁漂白原材料氧气和过氧化氢作漂白剂; • 与传统 CEH漂白比较, 毒性 AOX下降 70%以上, AOX产生量大大低于国家 排放标准; CODCr排放量下降 60%以上;
• 氧脱木素段(O)废水进入纸浆黑液提取工段, 没有废水排放, 预处理段(M) 和过氧化氢段 (P) 废水实现逆流循环回用, 减少废水总排放量的 70%左右。
(2) 氧脱木素效果好, 流程简单
• 氧脱木素率达到 60%左右;
• 氧脱木素属单段双塔流程, 两个氧脱木素塔之间无需中浓桨泵, 无需增压泵, 无需洗涤, 由一台中浓浆泵实现纸浆在整个氧脱木素系统中的输送; • 氧脱木素塔塔底无需分配器, 塔顶无需排料器。 '
(3) 活化预处理提高过氧化氢漂白效果
通过釆用活化剂对纸浆进行预处理, 活化了纸浆中影响纸浆白度的主要成分木素, 提 高后续过氧化氢的漂白效果, 白度增量提髙到 15— 20%以上, 打破一般过氧化氢漂白白度 增量只在 10%以下的传统观念。
(4)建设投资少
由于不釆用高建设投资的二氧化氯漂白方法, 建设投资只占二氧化氯漂白的 1/5左右。
(5)提高成桨质量和档次, 可生产高档纸品
• 传统 CEH漂白漂后白度不超过 75%ISO, 采用本发明, 漂后纸浆白度可提高到 85 %ISO以上, 由于纸浆白度提高, 纸品无需添加有毒的荧光增白剂, 可作为食品包 装用纸等;
• 纸浆强度比传统 CEH漂白提高 20%左右;
• 采用本发明, 成浆返黄率只为传统 CEH漂白的 20%。
(6)漂白技术的适应性广
• 适应木材化学浆、 草类化学浆的漂白;
• 适应 50吨 /日以上各种规模的化学浆漂白生产;
• 适应制浆清洁漂白生产线的建设和传统 CEH漂白生产线的改造。 ' 附图说明
图 1是本发明的工艺流程图。
具体实施方式
实施例 1
结合图 1, 本发明方法更详细的流程包括如下步骤:
(1)单段双塔氧脱木素
约 3%浓度的纸浆泵送至 1#真空洗浆机浓缩至 13— 15 %的浓度,加入约 2%NaOH、 0.1 %MgS04, 通入低压蒸气使纸浆达到约 70°C, 经 1#中浓浆泵送入 1#中浓混合器, 在 1#中 浓混合器前加入中压蒸气使纸浆保持在 100— 110°C,在 2#中浓混合器前通入 2%左右氧气, 纸浆经 2#中浓混合器进入 1 #升流式氧脱木素塔。 保持塔内温度为 100— 110°C, 塔顶压力 约为 0.6Mpa, 纸浆在塔内的停留时间为 40— 60分钟。
纸浆从 1#升流式氧脱木素塔塔顶出来经 3#中浓混合器进入 2#升流式氧脱木素塔,在 3 #中浓混合器前按需要补加 0.5-1.0%氧气、 0.5-1.0%NaOH和中压蒸气, 保持 2#升流式氧脱 木素塔内温度在 100— 110°C, 塔顶压力约为 0.4MPa, 纸浆在塔内的停留时间约 40分钟, 然后由 2#升流式氧脱木素塔顶喷放至喷放锅, 喷放锅底加入稀释水将纸浆稀释至约 3 %的 浓度, 然后泵送至 2#真空洗浆机和 3#真空洗浆机进行串联洗涤浓縮。
(2) 氯酸盐漂白 (H)
经 3#真空洗浆机洗涤浓缩至 8_ 10%的纸桨加入约 2.5%左右的次氯酸盐, 通过 1#低 浓混合机, 并通入低压蒸气至 40°C左右, 混合均匀的纸浆进入降流漂白塔, 塔内停留时间 约为 1.5小时, 塔底稀释纸浆至 3 %左右的浓度, 泵送至 4#真空洗浆机洗涤浓缩。
(3) 活化剂预处理(M)
经 4#真空洗浆机洗涤浓缩的纸浆调整浓度至 5 %左右通过 2#低浓混合机,加入约 0.5% 的 M活化剂, 并通入低压蒸气至 50°C左右, 混合均匀的纸浆进入降流预处理塔,塔内停留 时间为 40min左右, 塔底稀释纸浆至 3 %左右的浓度, 泵送至 5 #真空洗桨机洗涤浓缩。
(4)过氧化氢漂白 (P)
纸浆经 5#真空洗浆机洗涤浓缩至 13 %左右的浓度, 加入约 2%NaOH、 2%Na2Si03、 0.1 %MgSO4, 通入低压蒸气使纸浆达到 50°C左右, 经 2#中浓桨泵送入 4#中浓混合器, 在 4#中浓混合器前加入低压蒸气使纸浆保持在 90— 95°C,在 5#中浓混合器前通入 2.0-2.5%过 氧化氢,纸浆经 5#中浓混合器进入升流式过氧化氢漂白管,再进入降流式过氧化氢漂白塔, 纸浆在塔内停留 90min左右, 塔底稀释纸浆至 3 %左右的浓度, 泵送至 6#真空洗浆机洗涤 浓缩。 以上各种助剂的用量均相对与绝干浆- 得到纸浆白度 80-85%ISO, 产率 92-95%。 实施例 2
日产 150吨芦苇化学浆清洁漂白方法:
(1 )纸浆浓缩和氧脱木素药品的加入
漂前纸浆卡伯值约为 15-20左右。
保持存池纸浆温度在 40°C、 浓度在 3 %左右, 用浆泵将纸浆泵入 1#真空洗浆机浓缩, 浓缩后纸浆浓度约为 13— 15 %。
在洗浆机出口螺旋加入约 2%NaOH、 0.1 %MgSO4 (对绝干浆计)进行混合, 通过重力 送入氧脱木素系统。
(2) 纸浆氧脱木素及洗涤浓缩
纸浆进入 1#中浓浆泵立管, 在立管下端加入低压蒸气, 提高纸浆温度到 70Ό左右, 纸 浆经 1#中浓浆泵送入 1#中浓混合器,在 1#中浓混合器前加入中压蒸气提高纸桨温度至 110 V , 再经 2#中浓混合器送入 1#氧脱木素塔底部, 在 2#中浓混合器前加入 2%氧气(对绝干 桨计)。 纸浆在 1 #氧脱木素塔的停留时间为 40— 60分钟, 保持塔内温度 11(TC, 塔顶压力 0.6Mpa左右。
利用中浓浆泵的压头将 1#氧脱木素塔顶部出来的纸浆送入 3#中浓混合器, 按需要 3# 中浓混合器前补加 0.5 %氧气、 NaOH以及中压蒸气, 保证纸桨温度在 105— 110°C, 3#中浓 混合器出浆从 2#氧脱木素塔底部进入, 纸浆在 2#氧脱木素塔的停留时间为 40分钟左右, 保持塔内温度 105— 110°C, 塔顶压力 0.4Mpa左右。
利用 2#氧脱木素塔塔顶压力将纸浆喷入喷放锅, 喷放锅底注水调整经氧脱木素的纸浆 浓度在 3 %左右, 泵入 2#真空洗浆机和 3#真空洗浆机进行串联洗涤浓缩。
经氧脱木素后纸浆脱木素率达到 60%左右。
(3 ) 纸浆次氯酸盐漂白及洗涤浓縮
经洗涤浓缩的纸浆调整浓度为 10%左右, 加入 2.5%的次氯酸钙, 由 1 #低浓混合机混 合后从次氯酸盐漂白塔上部进入, 在 1Ί氏浓混合机中加入低压蒸气, 保证纸浆在次氯酸盐 漂白塔的温度在 40Ό左右, 停留时间控制在 90分钟。
在次氯酸盐漂白塔底部注水调整纸浆浓度在 3 %左右, 然后泵送至 4#真空洗浆机洗涤 浓缩。
(4) 纸浆 M活化剂预处理及洗涤浓缩
经洗涤浓缩的纸浆调整浓度为 5%左右, 加入 0.5 %的 M活化预处理剂, 由 2#低浓混 合机混合后从 M预处理塔上部进入, 在 2#低浓混合机中加入低压蒸气, 保证纸浆在 M预 处理塔的温度在 50°C左右, 停留时间控制在 40分钟左右。 在 M预处理塔底部注水调整纸浆浓度在 3 %左右,然后泵送至 5#真空洗浆机洗涤浓缩。
(5)纸浆过氧化氢漂白及洗涤
经洗涤浓缩至 13 %左右的纸浆, 加入 1.5%NaOH、 0.1 %MgS04和 2%Na2Si03, 在 5# 真空洗浆机出口螺旋中混合进入 2#中浓浆泵立管, 在立管下端加入低压蒸气, 提高纸浆温 度至 50°C左右, 纸浆经 2#中浓浆泵送入 4#中浓混合器, 在 4#中浓混合器前加入低压蒸气 提高纸浆温度至 90°C, 在 5#中浓混合器前加入 2.0-2.5%过氧化氢 (对绝干浆计), 通过 5# 中浓混合器送入过氧化氢升流管, 然后进入过氧化氢降流漂白塔。 纸浆在降流漂白塔的停 留时间 90— 120分钟, 保持塔内温度 90°C。
在过氧化氢降流漂白塔底部注水调整浓度在 3 %左右, 然后泵送至 6#真空洗浆机洗涤 浓缩。
漂后纸浆白度达到 80— 85 %ISO。
以上各种助剂的用量均相对与绝干浆, 产率 92— 95%。

Claims

权 利 要 求 书
1、 一种纸浆清洁漂白方法, 其特征在于包括以下步骤-
( 1 ) 单段双塔氧脱木素
浓度为 13— 15 %重量的纸浆中加入占纸浆 1.5— 2.5 %重量的 NaOH和 0.05— 0.10%重 量的 MgS04, 通入蒸汽升温至 100— 110°C, 通入占纸浆 1.5— 2.5 %重量氧气, 置于第一个 升流塔内, 塔顶压力为 0.55— 0.65Mpa, 塔内温度为 100— 110°C, 纸浆在塔内的停留时间 为 40— 60分钟;
(2) 次氯酸盐漂白
洗涤步骤(1 )得到的浓缩纸浆至 8— 10%重量, 加入占纸浆 2.0— 3.0%重量次氯酸盐, 通入蒸气升温至 35— 45°C, 进入降流塔, 塔内停留时间为 1一 2小时, 塔底稀释纸浆至 2.5 —3.5 %重量;
(3 ) 活化剂预处理
洗涤浓缩的纸桨至 5— 6%重量浓度, 加入占纸浆 0.3— 0.7°/。重量的活化剂并通入蒸气 升温至 50— 55°C, 进入降流预处理塔, 塔内停留时间为 30— 40min, 塔底稀释纸浆至 2.5 一 3.5 %重量; 所述活化剂是含有酸酐基团的有机化合物;
(4) 过氧化氢漂白
纸浆经洗涤浓縮至 13— 15 %重量的浓度, 加入占纸桨 1.5— 2.5%重量 NaOH、 2.0— 3.0 %重量 Na2Si03、 0.05— 0.10%重量 MgS04, 通入蒸气, 纸浆在 90— 95°C下通入占纸浆 2.0-2.5%重量的过氧化氢, 进入升流式过氧化氢漂白管, 再进入降流式过氧化氢漂白塔,纸 浆在塔内停留 90— 120min, 塔底稀释纸浆至 2.5— 3.5 %重量浓度;
以上各种助剂的用量均相对与绝干浆。
2、 根据权利要求 1所述的方法, 其特征在于完成步骤 (1 )后, 补加占纸浆 0.5-1.0% 重量氧气、 0.5-1.0%重量 NaOH和蒸气, 置纸浆于第二个升流塔内, 保持塔内温度在 100 一 110°C, 塔顶压力为 0.35-0.45MPa, 纸浆在塔内的停留时间约 30—50分钟。
3、根据权利要求 1或 2所述的方法, 其特征在于所述活化剂是亚硫酸酯酐、顺顶烯而 酸酐、 甘露酐、 丁二酐、 邻苯二甲酸酐或马来酸酐。 .
PCT/CN2005/002173 2005-09-02 2005-12-13 Procede de blanchiment de la pate WO2007025417A1 (fr)

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CN104088187A (zh) * 2014-06-05 2014-10-08 华南理工大学 一种纸浆漂白方法
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WO1995021290A1 (en) * 1994-02-07 1995-08-10 Warwick International Group Limited Pulp bleaching
CN1438384A (zh) * 2003-03-06 2003-08-27 华南理工大学 中浓纸浆双升流塔氧气漂白方法

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FR2553444B1 (fr) * 1983-10-13 1986-07-18 Centre Tech Ind Papier Traitement a l'hypochlorite de pates papetieres chimiques
NZ237019A (en) * 1990-02-19 1992-11-25 Amcor Ltd Bleaching paper pulp by initially treating with oxygen and/or hydrogen peroxide and subsequently treating with a bleaching agent without intervening washing steps
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WO1995021290A1 (en) * 1994-02-07 1995-08-10 Warwick International Group Limited Pulp bleaching
CN1438384A (zh) * 2003-03-06 2003-08-27 华南理工大学 中浓纸浆双升流塔氧气漂白方法

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