JP3768986B2 - Process for producing bleached kraft pulp with improved thermal fading - Google Patents
Process for producing bleached kraft pulp with improved thermal fading Download PDFInfo
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- 238000005562 fading Methods 0.000 title claims description 39
- 238000000034 method Methods 0.000 title claims description 34
- 239000002655 kraft paper Substances 0.000 title claims description 27
- 238000004061 bleaching Methods 0.000 claims description 57
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 claims description 19
- 239000000460 chlorine Substances 0.000 claims description 19
- 229910052801 chlorine Inorganic materials 0.000 claims description 18
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 16
- 239000001301 oxygen Substances 0.000 claims description 16
- 229910052760 oxygen Inorganic materials 0.000 claims description 16
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 14
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 13
- 229910052802 copper Inorganic materials 0.000 claims description 13
- 239000010949 copper Substances 0.000 claims description 13
- 238000005406 washing Methods 0.000 claims description 11
- 239000012978 lignocellulosic material Substances 0.000 claims description 8
- PWHULOQIROXLJO-UHFFFAOYSA-N Manganese Chemical compound [Mn] PWHULOQIROXLJO-UHFFFAOYSA-N 0.000 claims description 7
- 238000010306 acid treatment Methods 0.000 claims description 7
- 238000010411 cooking Methods 0.000 claims description 7
- 229910052742 iron Inorganic materials 0.000 claims description 7
- 229910052748 manganese Inorganic materials 0.000 claims description 7
- 239000011572 manganese Substances 0.000 claims description 7
- 238000004519 manufacturing process Methods 0.000 claims description 7
- 239000011121 hardwood Substances 0.000 claims description 5
- 239000002023 wood Substances 0.000 claims description 4
- QWPPOHNGKGFGJK-UHFFFAOYSA-N hypochlorous acid Chemical compound ClO QWPPOHNGKGFGJK-UHFFFAOYSA-N 0.000 claims 1
- 239000011122 softwood Substances 0.000 claims 1
- OSVXSBDYLRYLIG-UHFFFAOYSA-N dioxidochlorine(.) Chemical compound O=Cl=O OSVXSBDYLRYLIG-UHFFFAOYSA-N 0.000 description 66
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 36
- 239000004155 Chlorine dioxide Substances 0.000 description 33
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 33
- 235000019398 chlorine dioxide Nutrition 0.000 description 33
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 21
- 229910001428 transition metal ion Inorganic materials 0.000 description 17
- 239000008399 tap water Substances 0.000 description 16
- 235000020679 tap water Nutrition 0.000 description 16
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 14
- 239000000126 substance Substances 0.000 description 12
- 230000035484 reaction time Effects 0.000 description 11
- 235000011121 sodium hydroxide Nutrition 0.000 description 11
- 239000000123 paper Substances 0.000 description 9
- 239000002253 acid Substances 0.000 description 8
- 238000006243 chemical reaction Methods 0.000 description 6
- 230000000052 comparative effect Effects 0.000 description 6
- WQYVRQLZKVEZGA-UHFFFAOYSA-N hypochlorite Chemical compound Cl[O-] WQYVRQLZKVEZGA-UHFFFAOYSA-N 0.000 description 6
- 229920005610 lignin Polymers 0.000 description 6
- 238000012360 testing method Methods 0.000 description 6
- 230000002378 acidificating effect Effects 0.000 description 5
- 238000000605 extraction Methods 0.000 description 5
- 239000000706 filtrate Substances 0.000 description 5
- IAJILQKETJEXLJ-UHFFFAOYSA-N Galacturonsaeure Natural products O=CC(O)C(O)C(O)C(O)C(O)=O IAJILQKETJEXLJ-UHFFFAOYSA-N 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- 229920002488 Hemicellulose Polymers 0.000 description 3
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 3
- QXDMQSPYEZFLGF-UHFFFAOYSA-L calcium oxalate Chemical compound [Ca+2].[O-]C(=O)C([O-])=O QXDMQSPYEZFLGF-UHFFFAOYSA-L 0.000 description 3
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- QGGOCWIJGWDKHC-FSIIMWSLSA-N (2s,3s,4r,5r)-2,4,5-trihydroxy-3-methoxy-6-oxohexanoic acid Chemical compound OC(=O)[C@@H](O)[C@@H](OC)[C@H](O)[C@@H](O)C=O QGGOCWIJGWDKHC-FSIIMWSLSA-N 0.000 description 2
- HEDRZPFGACZZDS-UHFFFAOYSA-N Chloroform Chemical compound ClC(Cl)Cl HEDRZPFGACZZDS-UHFFFAOYSA-N 0.000 description 2
- AEMOLEFTQBMNLQ-AQKNRBDQSA-N D-glucopyranuronic acid Chemical compound OC1O[C@H](C(O)=O)[C@@H](O)[C@H](O)[C@H]1O AEMOLEFTQBMNLQ-AQKNRBDQSA-N 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- QGGOCWIJGWDKHC-UHFFFAOYSA-N O4-Methyl-D-glucuronsaeure Natural products OC(=O)C(O)C(OC)C(O)C(O)C=O QGGOCWIJGWDKHC-UHFFFAOYSA-N 0.000 description 2
- KFSLWBXXFJQRDL-UHFFFAOYSA-N Peracetic acid Chemical compound CC(=O)OO KFSLWBXXFJQRDL-UHFFFAOYSA-N 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000000835 fiber Substances 0.000 description 2
- 229940097043 glucuronic acid Drugs 0.000 description 2
- 239000012286 potassium permanganate Substances 0.000 description 2
- 238000004076 pulp bleaching Methods 0.000 description 2
- 239000013055 pulp slurry Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 241000609240 Ambelania acida Species 0.000 description 1
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 1
- 235000017491 Bambusa tulda Nutrition 0.000 description 1
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 241000218631 Coniferophyta Species 0.000 description 1
- AEMOLEFTQBMNLQ-YMDCURPLSA-N D-galactopyranuronic acid Chemical compound OC1O[C@H](C(O)=O)[C@H](O)[C@H](O)[C@H]1O AEMOLEFTQBMNLQ-YMDCURPLSA-N 0.000 description 1
- 244000166124 Eucalyptus globulus Species 0.000 description 1
- 229920002324 Galactoglucomannan Polymers 0.000 description 1
- 240000000797 Hibiscus cannabinus Species 0.000 description 1
- 241000282414 Homo sapiens Species 0.000 description 1
- WAEMQWOKJMHJLA-UHFFFAOYSA-N Manganese(2+) Chemical compound [Mn+2] WAEMQWOKJMHJLA-UHFFFAOYSA-N 0.000 description 1
- 244000082204 Phyllostachys viridis Species 0.000 description 1
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 229920001131 Pulp (paper) Polymers 0.000 description 1
- 241001007763 Sitala Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 230000032683 aging Effects 0.000 description 1
- 239000010905 bagasse Substances 0.000 description 1
- 239000011425 bamboo Substances 0.000 description 1
- 239000007844 bleaching agent Substances 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 150000001732 carboxylic acid derivatives Chemical class 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 239000002738 chelating agent Substances 0.000 description 1
- JFBJUMZWZDHTIF-UHFFFAOYSA-N chlorine chlorite Inorganic materials ClOCl=O JFBJUMZWZDHTIF-UHFFFAOYSA-N 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 238000009897 hydrogen peroxide bleaching Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 235000006408 oxalic acid Nutrition 0.000 description 1
- 238000005502 peroxidation Methods 0.000 description 1
- -1 polyethylene Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001021 polysulfide Polymers 0.000 description 1
- 239000005077 polysulfide Substances 0.000 description 1
- 150000008117 polysulfides Polymers 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 229910052979 sodium sulfide Inorganic materials 0.000 description 1
- GRVFOGOEDUUMBP-UHFFFAOYSA-N sodium sulfide (anhydrous) Chemical compound [Na+].[Na+].[S-2] GRVFOGOEDUUMBP-UHFFFAOYSA-N 0.000 description 1
- 238000007655 standard test method Methods 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 229910052723 transition metal Inorganic materials 0.000 description 1
- 150000003624 transition metals Chemical class 0.000 description 1
- WFKWXMTUELFFGS-UHFFFAOYSA-N tungsten Chemical compound [W] WFKWXMTUELFFGS-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000010937 tungsten Substances 0.000 description 1
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 1
- 229920001221 xylan Polymers 0.000 description 1
- 150000004823 xylans Chemical class 0.000 description 1
Landscapes
- Paper (AREA)
Description
本願発明は、リグノセルロース物質をバッチまたは連続蒸解釜にてクラフト法で蒸解して得られたパルプをアルカリ酸素脱リグニンと洗浄精選を行い、さらに一般的に公知とされている酸処理を処理することによりパルプ中の遷移金属イオンを除去したあとにオゾンまたは二酸化塩素の初段とする多段無塩素漂白シーケンスで漂白処理してなる熱退色性が改良された無塩素漂白クラフトパルプの製造方法に関するものである。 In the present invention, pulp obtained by digesting lignocellulosic material in a batch or continuous digester by kraft method is subjected to alkaline oxygen delignification and washing and selection, and further generally known acid treatment is processed. This invention relates to a method for producing chlorine-free bleached kraft pulp with improved thermal fading, which is obtained by bleaching in a multi-stage chlorine-free bleaching sequence with ozone or chlorine dioxide as the first stage after removing transition metal ions from the pulp. is there.
現在、製紙用原料であるパルプは、主にクラフト蒸解法で生産しており、クラフトパルプはバッチまたは連続蒸解釜にて製造され、そのあと、漂白工程からの環境負荷のCOD(化学的酸素要求量)、BOD(生学的酸素要求量)を減少するためにアルカリ酸素脱リグニンを行い、未晒パルプのカッパー価をさらに下げて次いで漂白工程へ移行する。パルプの漂白方法としては主に3があり、従来の塩素漂白法、無塩素漂白法(Elementary Chlorine Free=ECF)及び完全無塩素漂白法(Totally Chlorine Free=TCF)である。塩素漂白法では、元素状塩素、次亜塩素酸塩、二酸化塩素、酸素、過酸化水素、苛性ソーダ等の薬品の組み合わせによりパルプを漂白処理するが、この塩素漂白法からなる有機塩素化合物負荷が環境に悪影響する恐れがあり、近年の環境保護の高まりにより塩素の使用が避けられ、さらに、次亜塩素酸塩の使用により発生されるクロロホルムが人体に悪影響を及ぼす懸念もあり、次亜塩素酸塩の使用を止める方向になっているため、塩素と次亜塩素酸塩を含まないECF及びTCF漂白が主力方法になり、その場合、一般的な使用薬品は、ECF漂白法で二酸化塩素、過酸化水素、オゾン、酸素、苛性ソーダ等、TCF漂白法でキレート剤、過酸化水素、オゾン、酸素、苛性ソーダ及び過酢酸であるが、ECFパルプはTCFパルプに比べ白色度が高く、コストも安価であるため、ECF漂白法が現在の主流となっている。 Currently, pulp, which is a raw material for papermaking, is mainly produced by the kraft cooking method. Kraft pulp is manufactured in a batch or continuous digester, and then environmental impact COD (chemical oxygen demand from the bleaching process). Amount) and BOD (biological oxygen demand) are reduced by alkaline oxygen delignification, the kappa number of unbleached pulp is further lowered, and the process proceeds to the bleaching step. There are mainly 3 bleaching methods for pulp, which are the conventional chlorine bleaching method, chlorine-free bleaching method (Elementary Chlorine Free = ECF) and complete chlorine-free bleaching method (Totally Chlorine Free = TCF). In the chlorine bleaching method, pulp is bleached with a combination of chemicals such as elemental chlorine, hypochlorite, chlorine dioxide, oxygen, hydrogen peroxide, and caustic soda. The use of chlorine has been avoided due to the recent increase in environmental protection, and there is also a concern that chloroform generated by the use of hypochlorite may adversely affect the human body. ECF and TCF bleaching, which does not contain chlorine and hypochlorite, has become the main method. In that case, common chemicals used are chlorine dioxide and peroxidation by the ECF bleaching method. Hydrogen, ozone, oxygen, caustic soda, etc. are chelating agents, hydrogen peroxide, ozone, oxygen, caustic soda and peracetic acid in the TCF bleaching method, but ECF pulp is whiter than TCF pulp. Degree is high, because the cost is also inexpensive, ECF bleaching method has now become mainstream.
多段無塩素漂白法では、初段が一般的に二酸化塩素段(D0段と略)またはオゾン段(Z段と略)であり、紙パルプ産業の操業経験によると、これらの初段後の洗浄機の蓚酸カルシウムというスケールが多発しており、大変な問題となっている。パルプ中のヘキセンウロン酸(HexAと略)は二酸化塩素またはオゾンと反応し蓚酸を生成し、次いで蓚酸は液中のカルシウムと反応し、蓚酸カルシウムを作成する。蓚酸カルシウム問題を防止するために漂白工程に入るまえに酸処理条件下で酸性水溶液中でパルプを処理すること(A段と略)が現状の好ましい手段である。公知文献に記載されているA段条件はいくつかがあり、例えば、先ず、フィンランドのUPM―キメニ社ヴィサフォレスト工場では1996年7月からpH3.5、温度90℃、滞留時間最大7.5時間のA段(Sitala, M., Winberg, K., Alenius, M., Henricson, K., Lonnberg, B., 1998 International Pulp Bleaching Conference, Book 1, 279頁)、次に、ブラジルのクラビン社リオセル工場では1999年9月よりpH3.5、温度90℃、滞留時間100〜150分のA段(Ratnieks, E., Ventura, J. W., Mensch, M. R., Zanchin, R. A., Pulp Paper Can., 102(12):93(2001))、さらに、アールストローム社(現在、アンドリッツ社に社名変更)は、自社のAHLTM段(A段と同様)の条件(pH:3〜4、温度:90〜110℃、滞留時間:1〜3時間)を発表した(Henricson, K., Paperi ja Puu, 79(8):546(1997))。 The multistage chlorine-free bleaching process, the first stage is generally chlorine dioxide stage (D 0 stage substantially) or ozone stage (Z stage substantially), according to operational experience paper pulp industry, washing machines after these first stage The scale of calcium oxalate is frequently occurring, which is a serious problem. Hexenuronic acid (abbreviated as HexA) in the pulp reacts with chlorine dioxide or ozone to produce oxalic acid, which then reacts with calcium in the liquor to produce calcium oxalate. In order to prevent the calcium oxalate problem, the presently preferred method is to treat the pulp in an acidic aqueous solution under acid treatment conditions before entering the bleaching step (abbreviated as stage A). There are several stage A conditions described in the public literature. For example, at the UPM-Kimeni Visa Forest factory in Finland, pH 3.5, temperature 90 ° C, residence time up to 7.5 hours from July 1996. Stage A (Sitala, M., Winberg, K., Alenius, M., Henricson, K., Lonnberg, B., 1998 International Pulp Bleaching Conference, Book 1, page 279), followed by Rio Bcel, Brazil From September 1999, the A stage (Ratnieks, E., Ventura, JW, Mensch, MR, Zanchin, RA, Pulp Paper Can., 102) (pH 3.5, temperature 90 ° C, residence time 100-150 minutes) ): 93 (2001)), and further, Ahlstrom (currently changed its name to Andritz) is the condition (pH: 3-4, temperature: 90-110) of its own AHL TM stage (similar to the A stage). (Henricson, K., Paperi ja Puu, 79 (8): 546 (199) 7)).
無塩素漂白法では二酸化塩素、過酸化水素、オゾン等を使用するため、完成漂白パルプは塩素漂白ものに比べ物流・保管時等の退色性が激しく、その退色性は一般に光よりも熱によるものと考えられ、特開2002−266271、2003−96680により、二酸化塩素をベースしたECF漂白パルプの熱退色性(80℃)を改善するためには、JIS P8206による過マンガン酸カリウム価が1.5以下、PC価が10.0以下、そしてヘキセンウロン酸(HexAと略)が10mmol/kgBDパルプ以下になることが必要となる。 The chlorine-free bleaching method uses chlorine dioxide, hydrogen peroxide, ozone, etc., so the finished bleached pulp is more fading than in the case of chlorine-bleached during distribution and storage, and the fading is generally due to heat rather than light. In order to improve the thermal fading (80 ° C.) of chlorine dioxide-based ECF bleached pulp according to JP 2002-266271, 2003-96680, the potassium permanganate value according to JIS P8206 is 1.5. Hereinafter, it is necessary that the PC value is 10.0 or less and the hexeneuronic acid (abbreviated as HexA) is 10 mmol / kg BD pulp or less.
また、特開2003−105684では、アルカリ酸素脱リグニン後のクラフトパルプの無塩素漂白において、D0段の代替として酸性側(pH:1.5〜4.5)で実施するP段を使用し、且つ酸性P段後のパルプのHexAが15mmol/kgBDパルプ以下の条件を満すと、漂白クラフトパルプの熱退色性が改善されることを示した。
さらに、特願2003−334843では、最終白色度82〜90%ハンターの無塩素漂白クラフトパルプにおいて、熱風乾燥機の温度105℃と滞留時間12時間の条件下で熱退色を行った前後の国際CIEのL*a*b*色度システムのb*値の差異(Δb*)が2.20以下となり、従来塩素漂白パルプと同等以下で熱退色性が改良され、これらの無塩素漂白パルプに当たってカッパー価が2.20以下、カルボキシル基が22.0meq/100gBDパルプ以下になることを知見した。
Moreover, in JP-A-2003-105684, in the chlorine-free bleaching of kraft pulp after alkaline oxygen delignification, the P stage that is carried out on the acidic side (pH: 1.5 to 4.5) is used as an alternative to the D0 stage, And when HexA of the pulp after the acid P stage satisfies the condition of 15 mmol / kg BD pulp or less, the thermal fading property of the bleached kraft pulp was improved.
Furthermore, in Japanese Patent Application No. 2003-334843, an international CIE before and after thermal bleaching was performed on a chlorine-free bleached kraft pulp having a final whiteness of 82 to 90% under conditions of a hot air dryer temperature of 105 ° C. and a residence time of 12 hours. The difference in b * value (Δb * ) of the L * a * b * chromaticity system is 2.20 or less, and the thermal fading is improved to be equal to or less than that of conventional chlorine bleached pulp. It was found that the value was 2.20 or less and the carboxyl group was 22.0 meq / 100 g BD pulp or less.
以上の公知特開公報において、無塩素漂白クラフトパルプの熱退色への影響因子として残存リグニン(過マンガン酸カリウム価またはカッパー価で表れる)、HexA、カルボキシル酸等が記載され、その内、残存リグニン及びHexAが最も注目因子である。しかし、熱退色への影響因子は、現在でも複雑な課題で完全に解明できていなく、リグノセルロース物質のヘミセルロース、セルロースと抽出物も原因であろうと推定されているが、一方、パルプ繊維の微少成分である遷移金属イオンはあまりふれられていない。遷移金属イオンは微少の濃度下でも漂白過程の酸化還元反応を開始または維持し、晒パルプの熱退色の原因となる発色物質を生成する能力をもっている。 In the above-mentioned publicly known Japanese Patent Laid-Open Publications, residual lignin (expressed in terms of potassium permanganate value or kappa number), HexA, carboxylic acid, etc. are described as factors affecting the thermal fading of chlorine-free bleached kraft pulp, of which residual lignin And HexA are the most notable factors. However, the factors that affect thermal fading have not been fully elucidated due to complicated problems, and it is estimated that the lignocellulosic materials hemicellulose, cellulose and extract are also the cause. The component transition metal ions are not often touched. Transition metal ions have the ability to initiate or maintain a redox reaction in the bleaching process, even at very low concentrations, and to generate color-developing substances that cause thermal bleaching of the bleached pulp.
パルプ中の遷移金属イオンは、一般に漂白剤であるオゾン、酸素、過酸化水素を分解し、発生した水酸化ラジカルがパルプ品質を劣化させると言われている。多段漂白シーケンス中、すなわち、シーケンスの中間段または最終段の位置、のアルカリ過酸化水素段があった場合、パルプの遷移金属イオンの作用において二か鉄(Fe2+)とマンガン(Mn2+)は過酸化水素を分解するが、三か鉄(Fe3+)及び銅は過酸化水素分解速度よりも残存リグニン分解速度の方が高いという調査結果があった(Smith, P. K., McDonough, T. J., Svensk Papperstidn., 88(12): R106 (1985))。一方、遷移金属イオンは触媒作用によってオゾンの分解速度を増加し、漂白効率を低下させる。金属イオンはアルカリ性では繊維に吸着しているが酸性になると液中に溶出するのでオゾン段は「メタルトラップ」になり遷移金属イオンが蓄積されやすい(宮西孝則、「パルプの洗浄・精選・漂白」、紙パルプ技術協会2000年、頁248)。 It is said that transition metal ions in pulp generally decompose bleaching agents such as ozone, oxygen, and hydrogen peroxide, and generated hydroxyl radicals degrade pulp quality. If there was an alkaline hydrogen peroxide stage in the multi-stage bleaching sequence, i.e., at the middle or final stage of the sequence, diiron (Fe2 + ) and manganese (Mn2 + ) in the action of the transition metal ions of the pulp ) Decomposes hydrogen peroxide, but tri-iron (Fe 3+ ) and copper were found to have a higher rate of residual lignin decomposition than that of hydrogen peroxide (Smith, PK, McDonough, TJ , Svensk Papperstidn., 88 (12): R106 (1985)). On the other hand, transition metal ions increase the decomposition rate of ozone by catalysis and decrease the bleaching efficiency. Metal ions are adsorbed on the fiber when alkaline, but when they become acidic they elute into the liquid, so the ozone stage becomes a “metal trap” and transition metal ions are likely to accumulate (Takanori Miyanishi, “Pulp washing / selection / bleaching”). Pulp and Paper Technology Association 2000, p. 248).
パルプ繊維中の遷移金属イオンの位置は、ヘミセルロース及びリグニンの2ヶ所となっており、遷移金属イオンがヘミセルロースのウロン酸と結合し、また、リグニンとの複合体を生成する。ウロン酸は、HexA、4−O−メチルグルクロン酸、ガラクトウロン酸、グルクロン酸等が含まれており、HexA、4−O−メチルグルクロン酸はキシランの側鎖に、ガラクトウロン酸、グルクロン酸がガラクトグルコマンナンの側鎖に結びつき、遷移金属イオンはこれらのウロン酸のカルボキシル基に結合する(Vuorinen, T., Teleman, A.,Fagerstrom, P., Buchert, J., Tenkanen, M., 1996 International Pulp Bleaching Conference, Book 1, p. 43; Forsskahl, I., In “Forest Products Chemistry”, Eds., Stenius, P., Fapet Oy, Helsinki, Finland, 2000, p.303)。さらに、最近、遷移金属イオンである銅はリグニンと複合体化することが知見され、天然リグノセルロース物質にもこのような複合体が存在するのではないかと推定されている(Yoon, B-H., Wang, L-J., Kim, G-S., J. Pulp Paper Sci., 25 : 289(1999);Ghosh, A., Ni, Y., J. Pulp Paper Sci., 24(1): 26(1998))。 The positions of transition metal ions in the pulp fiber are two places, hemicellulose and lignin, and the transition metal ions bind to uronic acid of hemicellulose and also form a complex with lignin. Uronic acid includes HexA, 4-O-methylglucuronic acid, galacturonic acid, glucuronic acid and the like. HexA, 4-O-methylglucuronic acid has galactouronic acid and glucuronic acid in the side chain of xylan. Tungsten to the side chain of galactoglucomannan, transition metal ions bind to the carboxyl groups of these uronic acids (Vuorinen, T., Teleman, A., Fagerstrom, P., Buchert, J., Tenkanen, M., 1996 International Pulp Bleaching Conference, Book 1, p. 43; Forsskahl, I., In “Forest Products Chemistry”, Eds., Stenius, P., Fapet Oy, Helsinki, Finland, 2000, p. 303). Furthermore, recently, copper, which is a transition metal ion, has been found to be complexed with lignin, and it is presumed that such a complex also exists in natural lignocellulosic materials (Yoon, BH., Wang, LJ., Kim, GS., J. Pulp Paper Sci., 25: 289 (1999); Ghosh, A., Ni, Y., J. Pulp Paper Sci., 24 (1): 26 (1998) ).
本願発明は、無塩素漂白クラフトパルプにおける上記のような課題を改善しようとしてなされたもので、次のような手段からなっている。 The present invention has been made in order to improve the above-described problems in chlorine-free bleached kraft pulp, and comprises the following means.
本願発明は、無塩素漂白クラフトパルプの熱退色性を改良するにあたり、クラフト蒸解法でリグノセルロース物質をバッチまたは連続蒸解釜にて蒸解して得られたパルプ成分をアルカリ酸素脱リグニンと、洗浄精選を順次にし、さらに酸性水溶液中で処理する点までは従来の未晒クラフトパルプの製造法と同様である。無塩素漂白工程では、オゾン漂白の場合、酸処理のあと洗浄段なしで高濃度オゾン漂白段に移行し、オゾン処理後にもパルプを洗浄せず、低pHと短滞留時間の弱アルカリ抽出段に移行し(特願2003−308517)、あるいは二酸化塩素漂白の場合、酸処理のあとにパルプを洗浄し、初段の二酸化塩素処理を行い、次いで従来の高pHアルカリ抽出段に移行する。いずれの場合にも、後段の二酸化塩素、過酸化水素の処理により最終白色度82〜90%ハンターの完成漂白パルプを製造するとともに、熱風乾燥機の温度105℃と滞留時間12時間の条件下で熱退色を行った前後の国際CIEのL*a*b*色度システムのb*値の差異(Δb*)が2.20以下となり、従来の塩素漂白パルプ(Δb*=2.20)と同等以下で熱退色性が改良される。また、これらの無塩素漂白クラフトパルプにおいては、分子吸光光度法にて測定される鉄含有量が25ppm以下、銅含有量が1ppm以下、マンガン含有量が3ppm以下であることが推奨される。なお、これらの遷移金属イオンの含有量は対絶乾パルプの重量ppmである。 In the present invention, in improving the thermal fading of chlorine-free bleached kraft pulp, pulp components obtained by digesting lignocellulosic material in a batch or continuous digester by kraft digestion are washed with alkaline oxygen delignin and washed and selected. The process is the same as in the conventional method for producing unbleached kraft pulp until the point is further processed in an acidic aqueous solution. In the chlorine-free bleaching process, in the case of ozone bleaching, the acid treatment is followed by a high-concentration ozone bleaching stage without a washing stage, and the pulp is not washed after the ozone treatment, and the low-pH and short residence time weak alkaline extraction stage is used. In the case of chlorine dioxide bleaching, the pulp is washed after the acid treatment, the first stage chlorine dioxide treatment is performed, and then the conventional high pH alkali extraction stage is carried out. In either case, a finished bleached pulp having a final whiteness of 82 to 90% is produced by treatment with chlorine dioxide and hydrogen peroxide in the latter stage, and under the conditions of a hot air dryer temperature of 105 ° C. and a residence time of 12 hours. Difference in b * value (Δb * ) of L * a * b * chromaticity system of international CIE before and after thermal fading is 2.20 or less, and conventional chlorine bleached pulp (Δb * = 2.20) Thermal fading is improved below or equal. In these chlorine-free bleached kraft pulps, it is recommended that the iron content measured by molecular absorption spectrophotometry is 25 ppm or less, the copper content is 1 ppm or less, and the manganese content is 3 ppm or less. The content of these transition metal ions is ppm by weight of the dry pulp.
以下、本願発明をさらに詳しく説明する。 Hereinafter, the present invention will be described in more detail.
上記記載の特願2003−308517における酸処理(A段)条件下で、即ち、pH2.8〜3.2、温度85〜90℃、反応時間150〜180分、パルプ濃度8〜13%(好ましくは10〜12%)を用いて未晒パルプを酸処理すると、パルプ中の遷移金属イオン含有量が減少する。一方、オゾン漂白のための酸性pHを調整する(a段と略)目的で、パルプを温度30〜60℃(好ましくは50℃以下)、滞留時間は0〜30分(好ましくは5〜10分)、pH2〜3(硫酸にて)、パルプ濃度8〜13%(好ましくは10〜12%)、の条件下で処理を行うとパルプの遷移金属イオン含有量もともに低下する。本願発明の実施例では、A段においてpH3.1、温度90℃、反応時間150分、パルプ濃度10%の条件下で、a段はpH2.7、温度50℃、反応時間10分、パルプ濃度10%の条件下で未晒広葉樹パルプ(LUKPと略)を処理し、遷移金属イオン測定結果を表1に示した。A段はa段に比べ残存遷移金属イオンの銅、マンガンの除去率が明らかに上回っている。 Under the acid treatment (A stage) conditions in Japanese Patent Application No. 2003-308517 described above, that is, pH 2.8 to 3.2, temperature 85 to 90 ° C., reaction time 150 to 180 minutes, pulp concentration 8 to 13% (preferably 10-12%), the acid content of unbleached pulp reduces the transition metal ion content in the pulp. On the other hand, for the purpose of adjusting the acidic pH for ozone bleaching (abbreviated as a-stage), the pulp temperature is 30-60 ° C (preferably 50 ° C or less), and the residence time is 0-30 minutes (preferably 5-10 minutes). ), PH 2 to 3 (in sulfuric acid), and pulp concentration of 8 to 13% (preferably 10 to 12%), the transition metal ion content of the pulp also decreases. In the embodiment of the present invention, in stage A, pH 3.1, temperature 90 ° C., reaction time 150 minutes, pulp concentration 10%, stage a pH 2.7, temperature 50 ° C., reaction time 10 minutes, pulp concentration Unbleached hardwood pulp (abbreviated as LUKP) was treated under the condition of 10%, and the transition metal ion measurement results are shown in Table 1. The removal rate of the remaining transition metal ions copper and manganese is clearly higher in the A stage than in the a stage.
従って、多段無塩素漂白シーケンスの初段のオゾン段あるいは二酸化塩素段にもかかわらず、A段をさきに行うと完成漂白パルプの遷移金属イオン含有量は更に減少し、熱退色性が向上すると推奨される。 Therefore, in spite of the first ozone stage or chlorine dioxide stage of the multi-stage chlorine-free bleaching sequence, it is recommended that the transition metal ion content of the finished bleached pulp is further reduced and the thermal fading is improved when the stage A is performed first. The
熱退色試験方法において、最近のASTM(American Society for Testing and Materials)の推奨方法によると、温度100℃、滞留時間5日間、または温度90℃、滞留時間14日間、及びグラス管で熱退色を行うと自然退色と同等の結果が得られるが(ASTM’s Paper Aging Research Program、2002、ASTM International、PA)、この方法が存在するまでは熱退色の標準試験方法がないため、本願発明では、熱風乾燥機の温度105℃、滞留時間12時間の条件下で熱退色試験を実施した。 According to the latest ASTM (American Society for Testing and Materials) recommended method for thermal fading, thermal fading is performed at a temperature of 100 ° C. and a residence time of 5 days, or at a temperature of 90 ° C. and a residence time of 14 days, and a glass tube. The results are equivalent to natural fading (ASTM's Paper Aging Research Program, 2002, ASTM International, PA), but there is no standard test method for thermal fading until this method exists. The thermal fading test was carried out at a temperature of 105 ° C. and a residence time of 12 hours.
紙及びパルプの退色前後の白色度差異(ΔR457)またはPC(Post color)価は退色性の一般的な公知指数であるが、紙において強度と白色度は重要な品質目であるとともに、色度も大事な品質因子で、さらに、晒パルプ及び紙は熱退色を行うと外見では黄色味が強く、漂白シーケンスの初段の薬品(例えば:二酸化塩素、オゾン、塩素等)と終段の薬品(例えば:二酸化塩素、過酸化水素等)の使用により、最終白色度が同等でありながら、完成漂白パルプのb*が異なる場合が存在するため、本願発明では、晒パルプの熱退色性の指数として熱退色前後のb*差異(Δb*)を使用し、b*は国際CIEのL*a*b*色度システムのものである。本願発明において、CIEのL*a*b*色度システムのb*値とハンターの色度b値との相関は以下の通りとなる。なお、CIEのL*a*b*色度及びハンターのLab色度は、Macbeth Color-eye 計にて測定した。
CIEシステムの色度b*値 = ハンターの色度b値×0.9429 + 0.0541
相関係数 R2 = 0.9997
この相関によるとハンター色度システムにて測定したb値は、CIEのL*a*b*色度システムから得られたb*値より少し高い結果であり、ハンター色度システムのb値を使用した場合では熱退色前後のΔbが2.30以下になると従来塩素漂白パルプと同等以下で熱退色性が改良されることが知見される。
Whiteness difference (ΔR 457 ) or PC (Post color) value before and after fading of paper and pulp is a commonly known index of fading, but strength and whiteness are important quality factors in paper and color. It is also an important quality factor. Furthermore, bleached pulp and paper have a yellowish appearance when subjected to thermal fading, and chemicals at the first stage of the bleaching sequence (eg: chlorine dioxide, ozone, chlorine, etc.) (For example: chlorine dioxide, hydrogen peroxide, etc.), the final whiteness is the same, but the b * of the finished bleached pulp may be different. The b * difference (Δb * ) before and after thermal fading is used, where b * is from the International CIE L * a * b * chromaticity system. In the present invention, correlation between the chromaticity b value of b * values and Hunter CIE L * a * b * chromaticity system is as follows. The CIE L * a * b * chromaticity and the Hunter Lab chromaticity were measured with a Macbeth Color-eye meter.
CIE system chromaticity b * value = Hunter chromaticity b value × 0.9429 + 0.0541
Correlation coefficient R 2 = 0.9997
According to this correlation, the b value measured by the Hunter chromaticity system is slightly higher than the b * value obtained from the CIE L * a * b * chromaticity system, and the b value of the Hunter chromaticity system is used. In this case, it is found that when Δb before and after thermal fading becomes 2.30 or less, the thermal fading is improved by the same or lower than that of conventional chlorine bleached pulp.
本願発明においてリグノセルロース物質の種類、クラフトパルプの蒸解方法と条件、未晒パルプのカッパー価、無塩素漂白のシーケンス等に拘らず、完成漂白パルプの白色度82〜90%ハンターの範囲では、熱風乾燥機の105℃と12時間で熱退色を行った後のΔb* が2.20以下で従来の塩素漂白パルプと同等以下になり、熱退色性が改善され、かつ、これらの完成漂白パルプにあっては、残存鉄含有量が25ppm以下、残存銅含有量が1ppm以下、そして残存マンガン含有量が3ppm以下のことが推奨される。 Regardless of the type of lignocellulosic material, kraft pulp cooking method and conditions, unbleached pulp kappa, chlorine-free bleaching sequence, etc. The Δb * after thermal bleaching at 105 ° C. for 12 hours in the dryer is 2.20 or less, which is equal to or less than that of conventional chlorine bleached pulp, and the thermal bleaching property is improved. In that case, it is recommended that the residual iron content is 25 ppm or less, the residual copper content is 1 ppm or less, and the residual manganese content is 3 ppm or less.
本願発明では、電気炉において550℃でパルプを灰化し、5mg灰分を5ml濃塩酸(35〜36%)で溶解し、蒸留水で100mlに希釈し、この溶液をもって、原子吸光光度計であるSolaar M Series AA Spectrometer にて鉄、銅とマンガンを測定した。 In the present invention, pulp is ashed at 550 ° C. in an electric furnace, 5 mg ash is dissolved with 5 ml concentrated hydrochloric acid (35 to 36%), diluted to 100 ml with distilled water, and this solution is used as a solar absorption spectrometer, Solara. Iron, copper and manganese were measured with an M Series AA Spectrometer.
本願発明の無塩素漂白方法として、初段はオゾン(Z段)、最終段は二酸化塩素または過酸化水素を使用した場合、白色度82〜90%ハンターの完成漂白パルプは、従来の塩素漂白パルプ(Δb* 値=2.20)にくらべΔb* 値が同等以下であり、熱退色性が改善されたことが知見される。 As the chlorine-free bleaching method of the present invention, when ozone (Z stage) is used in the first stage and chlorine dioxide or hydrogen peroxide is used in the last stage, a finished bleached pulp having a whiteness of 82 to 90% is a conventional chlorine bleached pulp ( Compared to Δb * value = 2.20), the Δb * value is equal to or less than that, and it is found that the thermal fading is improved.
本願発明で使用するリグノセルロース物質としては、木材物質(広葉樹,針葉樹等)のほか、非木材物質(たとえば、ケナフト、バガス、竹、藁等)も使用することができる。そして、蒸解法は従来のコンベンショナルまたは改良クラフト蒸解法があるが、蒸解液は白液(主成分:苛性ソーダと硫化ソーダ)またはオレンジ液(ポリサルファイド液)単独、または蒸解初段でオレンジ液、蒸解後段で白液の使用でも良い。 As the lignocellulosic material used in the present invention, in addition to wood materials (hardwood, conifers, etc.), non-wood materials (for example, kenaf, bagasse, bamboo, firewood, etc.) can also be used. There are conventional conventional or improved kraft cooking methods, but the cooking solution is white liquor (main components: caustic soda and sodium sulfide) or orange liquor (polysulfide liquor) alone, or orange liquor at the first stage of cooking, and after the cooking stage. White liquor may be used.
本願発明の明細書で記載されるアルカリ性の酸素脱リグニンと洗浄・精選の工程においては、設備及び操業方法は従来公知のものを使用することができる。アルカリ性の酸素脱リグニンは従来公知の一段方式または二段方式(たとえば、Dualox、OxyTracの二段方式等)でも良い。 In the process of alkaline oxygen delignification and cleaning / selection described in the specification of the present invention, conventionally known equipment and operation methods can be used. Alkaline oxygen delignification may be a conventionally known one-stage system or two-stage system (for example, Dualox, OxyTrac two-stage system, etc.).
本願発明に記載した熱退色性が改良された無塩素漂白クラフトパルプにおいては次のような効果がある。 The chlorine-free bleached kraft pulp with improved thermal fading described in the present invention has the following effects.
(1) 本願発明の製造方法で製造される熱退色性が改良された無塩素漂白クラフトパルプにおいて、完成白色度82〜90%ハンターの範囲では熱風乾燥機の温度105℃と滞留時間12時間の条件下で熱退色を行った前後の色度b*値の差異(Δb*)が2.20以下となり、従来の塩素漂白パルプと同等以下であり、物流・倉庫保存等によるパルプの黄色化が起きず、パルプの再漂白は行わなくても良く、次の抄紙工程での紙品質を保護でき、コスト削減が図れる。 (1) In the chlorine-free bleached kraft pulp with improved thermal fading produced by the production method of the present invention, the temperature of the hot air dryer is 105 ° C. and the residence time is 12 hours in the range of finished whiteness of 82 to 90%. The difference in chromaticity b * values before and after thermal bleaching under the conditions (Δb * ) is 2.20 or less, which is equivalent to or less than that of conventional chlorine bleached pulp. It does not occur, and the pulp does not need to be rebleached, the paper quality in the next papermaking process can be protected, and the cost can be reduced.
(2) また、完成無塩素漂白クラフトパルプの残存鉄含有量を25ppm以下、残存銅含有量が1ppm以下、残存マンガン含有量が3ppm以下とすることで熱退色性が改良され、長期の物流・倉庫保存等が可能になり、ランニング費用が低減でき、さらに、天然原材料であるリグノセルロース物質(例えば、広葉樹、針葉樹と非木材のチップ)の使用量を削減でき、地球環境を保護する効果がある。 (2) In addition, the finished chlorine-free bleached kraft pulp has a residual iron content of 25 ppm or less, a residual copper content of 1 ppm or less, and a residual manganese content of 3 ppm or less. It can be stored in a warehouse, running costs can be reduced, and the amount of natural raw material lignocellulosic substances (for example, hardwood, coniferous and non-wood chips) can be reduced, which has the effect of protecting the global environment. .
本件出願人の先願にかかる特願2003−334843で記載した最終白色度82〜90%ハンターの無塩素漂白クラフトパルプにおいて、熱風乾燥機の温度105℃と滞留時間12時間の条件下で熱退色を行った前後の国際CIEのL*a*b*色度システムのb*値の差異(Δb*)が2.20以下になり、従来の塩素漂白パルプと同等以下で、熱退色性が改善され、これらの無塩素漂白パルプにあっては、カッパー価が2.20以下、カルボキシル基が22.0meq/100gBDパルプ以下とすることを推奨したが、本願発明では、これらのパルプの残存遷移金属イオンの熱退色性への影響が知見されたので、以下にいくつかの実施例及び比較例を示す。なお、これらの実施例と比較例の中のE段にはEo段、Ep段及びEop段(酸素単独、過酸化水素単独または酸素と過酸化水素の共同使用を含む中性またアルカリ性抽出段)が含まれている。 In the chlorine-free bleached kraft pulp with a final whiteness of 82-90% described in Japanese Patent Application No. 2003-334443 according to the prior application of the present applicant, heat fading under conditions of a hot air dryer temperature of 105 ° C. and a residence time of 12 hours The difference in the b * value (Δb * ) of the international CIE L * a * b * chromaticity system before and after the test was 2.20 or less, the same or less than the conventional chlorine bleached pulp, and improved thermal fading In these chlorine-free bleached pulps, it was recommended that the copper number be 2.20 or less and the carboxyl group be 22.0 meq / 100 g BD pulp or less. In the present invention, the residual transition metal of these pulps Since the influence on the thermal fading property of ions was found, some examples and comparative examples are shown below. The E stage in these examples and comparative examples includes the Eo stage, the Ep stage and the Eop stage (oxygen alone, hydrogen peroxide alone or a neutral or alkaline extraction stage including the joint use of oxygen and hydrogen peroxide). It is included.
下記の各漂白シーケンスにおける薬品添加率は、対絶乾パルプ当たりの重量%であり、各段間の横棒(−)は洗浄段を示す。高濃度Z段以外、他の漂白段は、ポリエチレン袋にて行った。 The chemical addition rate in each of the following bleaching sequences is% by weight per dry pulp, and a horizontal bar (-) between each stage indicates a washing stage. Other than the high concentration Z stage, the other bleaching stages were carried out in polyethylene bags.
(実施例1〜3、及び参考例1)
(AZE)−D1−D2、(AZE)−D−P、(AZE)−P−D、A−D0−E−D1−D2のシーケンスについての漂白温度、パルプ濃度、反応時間、薬品添加率等の詳細は、次の通りである。
(Examples 1 to 3 and Reference Example 1)
Bleaching temperature, pulp concentration, reaction time for the sequence of (AZE) -D 1 -D 2 , (AZE) -DP, (AZE) -PD, AD 0 -ED 1 -D 2 Details of the chemical addition rate are as follows.
(実施例1)
(AZE)−D1−D2シーケンスによる漂白
(1) 使用パルプ:アルカリ性酸素脱リグニンと洗浄を行った実生産ラインのカッパー価11.7の混合ユーカリ広葉樹クラフトパルプ(LUKPと略)をサンプリングし、使用しながら5℃の場所で保管した。
Example 1
(AZE) -D 1 -D 2 bleaching (1) Pulp used: Sampling of mixed eucalyptus hardwood kraft pulp (abbreviated as LUKP) with an alkaline oxygen delignification and washing of the actual production line with a copper number of 11.7 Stored at 5 ° C. while using.
(2) A段(酸処理段):パルプ濃度10.5%のLUKPを作成し、次いで4N硫酸溶液にてパルプスラリーのpHを約3.1にし、最終パルプ濃度10.0%を調整した。(硫酸添加率:1.10%、pH:3.10)このパルプは、90℃の恒温槽において時間150分で処理した後、洗浄せずに遠心分離機にてパルプ濃度38.7%までに脱水した。(カッパー価:8.0)
(3) Z段(高濃度オゾン処理段):A段後の濃度38.7%のパルプは、60gBD/バッチで2リットル容量の茄形フラスコに入れ、ラボ用エバポレーターに取付けた後、濃度約10%のオゾンガスをフラスコに注入し、オゾンとパルプを反応させた(オゾン添加率:0.46%)。なお、高濃度オゾン処理は、50℃の恒温槽にて行った。オゾン漂白したパルプは洗浄せずに集めて混ぜた。
(2) Stage A (acid treatment stage): LUKP having a pulp concentration of 10.5% was prepared, and then the pH of the pulp slurry was adjusted to about 3.1 with a 4N sulfuric acid solution to adjust the final pulp concentration to 10.0%. . (Sulfuric acid addition rate: 1.10%, pH: 3.10) This pulp was treated in a constant temperature bath at 90 ° C. for 150 minutes, and then washed to a pulp concentration of 38.7% in a centrifuge without washing. Dehydrated. (Copper number: 8.0)
(3) Stage Z (high-concentration ozone treatment stage): The pulp with a concentration of 38.7% after stage A was placed in a 2 liter vertical flask at 60 g BD / batch and attached to a laboratory evaporator. 10% ozone gas was injected into the flask to react ozone and pulp (ozone addition rate: 0.46%). The high-concentration ozone treatment was performed in a constant temperature bath at 50 ° C. Ozone bleached pulp was collected and mixed without washing.
(4) E段(弱アルカリ性抽出段):Z段後の濃度38.7%のパルプに苛性ソーダを0.9%添加し、パルプ濃度14%、70℃で30分保持した。抽出したパルプは、水道水(2リットル/200g絶乾パルプ)で洗浄し、パルプ濃度18%に脱水濃縮した。 (4) Stage E (weakly alkaline extraction stage): 0.9% of caustic soda was added to the 38.7% concentrated pulp after the Z stage, and the pulp was held at 70% for 30 minutes at a pulp concentration of 14%. The extracted pulp was washed with tap water (2 liters / 200 g absolute dry pulp) and dehydrated and concentrated to a pulp concentration of 18%.
(5) D1段(二酸化塩素漂白段):E段後のパルプに二酸化塩素を0.2%添加し、パルプ濃度14%、75℃で117分間二酸化塩素処理を行った。反応後のパルプろ液pHは5.5であった。得られたパルプは、水道水(2リットル/200g絶乾パルプ)で洗浄し、パルプ濃度18%に脱水した。 (5) D 1st stage (chlorine dioxide bleaching stage): 0.2% of chlorine dioxide was added to the pulp after stage E, and chlorine dioxide treatment was performed at a pulp concentration of 14% and 75 ° C. for 117 minutes. The pulp filtrate pH after the reaction was 5.5. The obtained pulp was washed with tap water (2 liters / 200 g absolute dry pulp) and dehydrated to a pulp concentration of 18%.
(6) D2段(二酸化塩素漂白段):D2段のパルプ濃度、処理温度、反応時間、反応後のろ液pH、パルプの洗浄方法は全てD1段と同様であるが、二酸化塩素の添加率のみは低く0.1%とした。以上により、(AZE)−D1−D2シーケンスによる完成パルプを得た。 (6) D 2 stage (chlorine dioxide bleaching stage): D 2 stage pulp concentration, treatment temperature, reaction time, filtrate pH after reaction, and pulp washing method are all the same as D 1 stage, but chlorine dioxide Only the addition rate of 0.1% was low. As a result, a finished pulp by the (AZE) -D 1 -D 2 sequence was obtained.
(実施例2)
(AZE)−D−Pシーケンスによる漂白
(1) (AZE)段:上記に記載された(AZE)−D1−D2シーケンスの(AZE)段のパルプを使用した。
(Example 2)
(AZE) bleaching -D-P sequence (1) (AZE) stage: Using been (AZE) -D 1 -D 2 sequence (AZE) stage pulp described above.
(2) D段(二酸化塩素漂白段):上記の(AZE)−D1−D2シーケンスのD1段後のパルプを用いた。 (2) D stage (chlorine dioxide bleaching stage): Pulp after D 1 stage of the above (AZE) -D 1 -D 2 sequence was used.
(3) P段(過酸化水素漂白段):D段後のパルプに過酸化水素を0.15%添加し、パルプ濃度14%、70℃で120分間過酸化水素処理を行った後、水道水(2リットル/200g絶乾パルプ)でパルプを洗浄脱水し、完成漂白パルプを得た。なお、P段後のパルプろ液pHは9.5であった。 (3) P stage (hydrogen peroxide bleaching stage): 0.15% of hydrogen peroxide was added to the pulp after stage D, and after performing hydrogen peroxide treatment at a pulp concentration of 14% and 70 ° C. for 120 minutes, tap water The pulp was washed and dehydrated with water (2 liters / 200 g absolute dry pulp) to obtain a finished bleached pulp. The pulp filtrate pH after stage P was 9.5.
(実施例3)
(AZE)−P−Dシーケンスによる漂白
(1) (AZE)段:上記に記載された(AZE)−D1−D2シーケンスの(AZE)段のパルプを使用した。
Example 3
(AZE) bleaching with -P-D sequence (1) (AZE) stage: Using been (AZE) -D 1 -D 2 sequence (AZE) stage pulp described above.
(2) P段:上記の(AZE)−D−PシーケンスのP段の条件で実施し、過酸化水素添加率は、0.55%であった。 (2) P stage: It implemented on the conditions of P stage of said (AZE) -DP sequence, and the hydrogen peroxide addition rate was 0.55%.
(3) D段:この漂白段の条件は、上記の(AZE)−D1−D2シーケンスのD2段と同様であるが、二酸化塩素添加率は0.18%で、得られたパルプは水道水にて洗浄脱水を行い、完成漂白パルプとした。 (3) D stage: The conditions of this bleaching stage are the same as those of D 2 stage of the (Aze) -D 1 -D 2 sequence, but the chlorine dioxide addition rate is 0.18%, and the obtained pulp Was washed and dehydrated with tap water to obtain a finished bleached pulp.
(参考例1)
A−D0−E−D1−D2シーケンスによる漂白
(1) A段:上記に記載した(AZE)−D1−D2シーケンスのA段後のパルプを取り、水道水で洗浄し、パルプ濃度18%に脱水した。
(Reference Example 1)
Bleaching with A-D 0 -E-D 1 -D 2 Sequence (1) A stage: take the pulp after A stage of the described (AZE) -D 1 -D 2 sequence, were washed with tap water, Dehydrated to a pulp concentration of 18%.
(2) D0段:A段後のパルプに二酸化塩素を0.366%添加し、パルプ濃度4%、4N希硫酸にてpHを3.5に調整し、温度58℃、時間25分の処理を行った後、水道水(2リットル/200g絶乾パルプ)でパルプを洗浄脱水した。 (2) D 0 stage: 0.366% chlorine dioxide is added to the pulp after stage A, the pH is adjusted to 3.5 with 4% pulp concentration, 4N dilute sulfuric acid, temperature 58 ° C., time 25 minutes After the treatment, the pulp was washed and dehydrated with tap water (2 liters / 200 g absolutely dry pulp).
(3) E段(アルカリ抽出段):D0段後のパルプに苛性ソーダを0.72%添加し、パルプ濃度14%、70℃で66分保持した。抽出したパルプは水道水で洗浄し、パルプ濃度18%までに濃縮した。 (3) E stage (alkali extraction stage): 0.72% of caustic soda was added to the pulp after D 0 stage, and the pulp concentration was 14% and kept at 70 ° C. for 66 minutes. The extracted pulp was washed with tap water and concentrated to a pulp concentration of 18%.
(4) D1段及びD2段(二酸化塩素漂白段):E段後のパルプは、上記に記載した(AZE)−D1−D2シーケンスのD1段及びD2段の条件と同様に実施したが、それぞれの二酸化塩素添加率は0.06%(D1段)と0.15%(D2段)であった。得られたパルプは水道水にて洗浄脱水を行い、完成漂白パルプとした。 (4) D 1 stage and D 2 stage (chlorine dioxide bleaching stage): Pulp after E stage is the same as the conditions of D 1 stage and D 2 stage of (AZE) -D 1 -D 2 sequence described above was carried out, were each chlorine dioxide addition rate 0.06% (D 1 stage) and 0.15% (D 2 stages). The obtained pulp was washed and dehydrated with tap water to obtain a finished bleached pulp.
(実施例4〜6)
(aZE)−D1−D2、(aZE)−D−P、(aZE)−P−Dのシーケンスの漂白温度、パルプ濃度、反応時間は上記記載実施例1〜3と同様で、さらに、a処理段は上記段落[0013]に記載した。実施例1〜6の薬品添加率を表2に示す。
(Examples 4 to 6)
The bleaching temperature, pulp concentration, and reaction time of the sequences (aZE) -D 1 -D 2 , (aZE) -DP, and (aZE) -P-D are the same as those in Examples 1 to 3 above, and The processing stage a is described in paragraph [0013] above. Table 2 shows the chemical addition ratios of Examples 1 to 6.
(参考例2)
A−D0−E−D1−Pシーケンスによる漂白
(1) A段(酸処理段):パルプ濃度10.5%のLUKPを作成し、次いで4N硫酸溶液でパルプスラリーのpHを約3.1にし、最終パルプ濃度10.0%に調整した(硫酸添加率:1.10%、pH:3.2)。このパルプは、90℃の恒温槽にて反応時間150分で処理した後、水道水で洗浄し、パルプ濃度18%に脱水した。(カッパー価:8.1;もとのパルプのカッパー価:11.3)。
(Reference Example 2)
A-D 0 bleaching -E-D 1 -P Sequence (1) A stage (acid stage): Creates a pulp concentration of 10.5 percent LUKP, then the pH of the pulp slurry with 4N sulfuric acid solution of about 3. 1 and the final pulp concentration was adjusted to 10.0% (sulfuric acid addition rate: 1.10%, pH: 3.2). This pulp was treated in a constant temperature bath at 90 ° C. for a reaction time of 150 minutes, washed with tap water, and dehydrated to a pulp concentration of 18%. (Kappa number: 8.1; original pulp copper number: 11.3).
(2) D0段:A段後のパルプに二酸化塩素を0.335%添加し、パルプ濃度4.5%、4N希硫酸にてpHを3.5に調整し、温度58℃、時間25分の処理を行った後、水道水(2リットル/200g絶乾パルプ)でパルプを洗浄脱水した。 (2) D 0 stage: 0.335% of chlorine dioxide is added to the pulp after stage A, the pH is adjusted to 3.5 with a pulp concentration of 4.5% and 4N dilute sulfuric acid, and the temperature is 58 ° C. for 25 hours. After a minute treatment, the pulp was washed and dehydrated with tap water (2 liters / 200 g absolute dry pulp).
(3) E段:D0段後の濃度18%のパルプに苛性ソーダを0.741%添加し、パルプ濃度14%、70℃で65分保持した。抽出したパルプは、水道水(2リットル/200g絶乾パルプ)で洗浄し、パルプ濃度18%に脱水濃縮した。 (3) E stage: caustic soda was added 0.741% on D 0 stage after concentration of 18% of the pulp, pulp consistency 14%, was held 65 minutes at 70 ° C.. The extracted pulp was washed with tap water (2 liters / 200 g absolute dry pulp) and dehydrated and concentrated to a pulp concentration of 18%.
(4) D1段:E段後のパルプに二酸化塩素を0.07%添加し、パルプ濃度14%、75℃で65分間二酸化塩素処理を行った。反応後のパルプろ液pHは5.5であった。得られたパルプは、水道水(2リットル/200g絶乾パルプ)で洗浄し、パルプ濃度18%に脱水した。 (4) D stage 1 : 0.07% of chlorine dioxide was added to the pulp after stage E, and chlorine dioxide treatment was performed at a pulp concentration of 14% and 75 ° C. for 65 minutes. The pulp filtrate pH after the reaction was 5.5. The obtained pulp was washed with tap water (2 liters / 200 g absolute dry pulp) and dehydrated to a pulp concentration of 18%.
(5) P段:D1段後のパルプに過酸化水素を0.25%添加し、パルプ濃度14%、初期pH10.6になるように苛性ソーダで調整した後75℃の恒温槽にて60分間過酸化水素処理を行った。反応後のろ液pHは9.3であり、処理後のパルプは水道水で洗浄を行い、濃縮した。以上により、A−D0−E−D1−Pシーケンスによる完成パルプを得た。 (5) P stage: 0.25% of hydrogen peroxide is added to the pulp after the first stage D, adjusted with caustic soda so that the pulp concentration is 14% and the initial pH is 10.6, and then 60 ° C. in a thermostatic bath at 75 ° C. Hydrogen peroxide treatment was performed for a minute. The filtrate pH after the reaction was 9.3, and the treated pulp was washed with tap water and concentrated. Thus, to obtain a finished pulp by A-D 0 -E-D 1 -P sequence.
(比較例1)
C−E−H−Dシーケンスによる従来塩素漂白
C段、E段、D段の処理温度、反応時間及びパルプ濃度は、上記参考例2のA−D0−E−D1−PシーケンスのD0段(C段と相当)、E段、D1段(D段と相当)と同等であるが、薬品添加率は次の通りになる。C段での塩素:1.13%;E段での苛性ソーダ:0.865%;D段での二酸化塩素:0.35%。H段については、処理温度:75℃;反応時間:35分;パルプ濃度:14%;ハイポ添加率:0.25%の条件下でハイポ処理を行った。各処理段後のパルプは水道水で洗浄した。
(Comparative Example 1)
Conventional chlorine bleaching C stage by C-E-H-D sequence, E stage, D stage of the processing temperature, reaction time and pulp consistency, D of A-D 0 -E-D 1 -P sequence of the reference example 2 Although it is equivalent to 0 stage (equivalent to C stage), E stage, and D 1 stage (equivalent to D stage), the chemical addition rate is as follows. Chlorine in stage C: 1.13%; Caustic soda in stage E: 0.865%; Chlorine dioxide in stage D: 0.35%. For stage H, hypo treatment was performed under the conditions of treatment temperature: 75 ° C .; reaction time: 35 minutes; pulp concentration: 14%; hypo addition rate: 0.25%. The pulp after each treatment stage was washed with tap water.
(比較例2)
a−D0−E−D1−D2シーケンスによる漂白
a処理段は上記段落[0013]に記載した。D0段、E段、D1段、D2段のパルプ濃度、反応温度、反応時間は、上記記載参考例1のA−D0−E−D1−D2シーケンスの相当段の条件と同様で薬品添加率は次の通りになる。D0段での二酸化塩素:0.961%;E段での苛性ソーダ:1.52%:D1段での二酸化塩素:0.06%;D2段での二酸化塩素:0.15%。各処理段後のパルプは水道水で洗浄濃縮した。
(Comparative Example 2)
Bleaching with aD 0 -ED 1 -D 2 Sequence The a treatment stage is described in paragraph [0013] above. The pulp concentration, reaction temperature, and reaction time of the D 0 stage, E stage, D 1 stage, and D 2 stage are the same as the conditions of the corresponding stages of the A-D 0 -ED-D 1 -D 2 sequence of Reference Example 1 described above. Similarly, the chemical addition rate is as follows. Chlorine dioxide in D 0 stage: 0.961%; sodium hydroxide in E stage: 1.52%: chlorine dioxide by D 1 stage: 0.06%; chlorine dioxide in D 2 stage: 0.15%. The pulp after each treatment stage was washed and concentrated with tap water.
(比較例3)
A−D0−E−P−D1シーケンスによる漂白
A処理段は上記段落「0013」に記載した。他のD0段、E段、P段、D1段のパルプ濃度、反応温度、反応時間は、上記実施例8のA−D0−E−D1−Pシーケンスの相当段の条件と同様で薬品添加率は次の通りになる。D0段での二酸化塩素:0.335%;E段での苛性ソーダ:0.741%:P段での過酸化水素:0.45%;D1段での二酸化塩素:0.238%。なお、P段の初期pHと最終pHは、各々10.8と10.4であった。各処理段後のパルプは水道水で洗浄濃縮した。
(Comparative Example 3)
Bleaching A processing stage by A-D 0 -E-P- D 1 sequence described in the preceding paragraph "0013". The pulp concentration, reaction temperature, and reaction time of the other D 0 stages, E stages, P stages, and D 1 stages are the same as the conditions of the corresponding stages of the A-D 0 -ED 1 -P sequence in Example 8 above. The chemical addition rate is as follows. Chlorine dioxide in D 0 stage: 0.335%; sodium hydroxide in E stage: 0.741% hydrogen peroxide in P stages: 0.45%; chlorine dioxide by D 1 stage: 0.238%. The initial pH and final pH of the P stage were 10.8 and 10.4, respectively. The pulp after each treatment stage was washed and concentrated with tap water.
<パルプ品質の測定方法>
各完成パルプは、「JIS P8222」及び「JIS P8223」記載の方法にて手抄シートを作成した後、白色度測定と熱退色試験に供した。
<Method for measuring pulp quality>
Each finished pulp was subjected to whiteness measurement and a thermal fading test after a handsheet was prepared by the method described in “JIS P8222” and “JIS P8223”.
白色度 :「JIS P8123」記載の方法を基にハンター白色度計にてハンター白色度を求めた。 Whiteness: Hunter whiteness was determined with a Hunter whiteness meter based on the method described in “JIS P8123”.
熱退色試験 :白色度測定用手抄シートは、市販熱風乾燥機の中に縦方向で立って温度105℃と処理時間12時間の条件下で熱退色試験を行った。 Thermal fading test: The handsheet for whiteness measurement was subjected to a thermal fading test under the conditions of a temperature of 105 ° C. and a treatment time of 12 hours in a commercial hot air dryer in the vertical direction.
本願発明では最終白色度の82〜90%ハンターの無塩素漂白クラフトパルプにおいて実施例1〜6は比較例1の従来の塩素漂白パルプに比べ、熱風乾燥機の温度105℃と滞留時間12時間の条件下で熱退色を行った前後のΔb*が同等以下の結果であり、これらの無塩素漂白パルプの熱退色性が改良される結果が得られた。また、残存鉄含有量が25ppm以下、残存銅含有量が1ppm以下、そして残存マンガン含有量が3ppm以下であることが知見された。 In the present invention, in the chlorine-free bleached kraft pulp having a final whiteness of 82 to 90%, Examples 1 to 6 have a hot air dryer temperature of 105 ° C. and a residence time of 12 hours as compared with the conventional chlorine bleached pulp of Comparative Example 1. The Δb * values before and after thermal bleaching under the conditions were the same or lower, and the results of improving the thermal fading of these chlorine-free bleached pulps were obtained. It was also found that the residual iron content was 25 ppm or less, the residual copper content was 1 ppm or less, and the residual manganese content was 3 ppm or less.
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