JP2004137653A - Method for producing bleached pulp for papermaking - Google Patents

Method for producing bleached pulp for papermaking Download PDF

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JP2004137653A
JP2004137653A JP2003198996A JP2003198996A JP2004137653A JP 2004137653 A JP2004137653 A JP 2004137653A JP 2003198996 A JP2003198996 A JP 2003198996A JP 2003198996 A JP2003198996 A JP 2003198996A JP 2004137653 A JP2004137653 A JP 2004137653A
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pulp
bleaching
ozone
stage
concentration
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JP2003198996A
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JP4356380B2 (en
Inventor
Hideo Igarashi
五十嵐 英夫
Yukinori Kizara
木皿 幸紀
Hideichiro Mochizuki
望月 秀一郎
Isamu Yaegashi
八重樫 勇
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New Oji Paper Co Ltd
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Oji Paper Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for treating pulp in a high concentration ozone bleaching using a high pulp concentration, improving efficiency of ozone bleaching, and maintaining a sufficiently high pulp strength. <P>SOLUTION: This method for producing bleached pulp is provided by alkaline oxygen-bleaching an unbleached pulp obtained by steam cooking of wood chips, treating the pulp after the oxygen bleaching with an acid at ≤pH 2.5, then adjusting to 1-5% concentration, and having a sequence of dehydrating the pulp concentration up to 32-38mass%, ozone-bleaching and then performing an alkaline extraction of the pulp which is fiber-opened by a pre-breaker. Further bleaching the pulp in ECF and TCF-bleaching processes is provided by ozone-bleaching the pulp adjusted to have the manganese content of ≤10mg/kg of absolutely dried pulp, in the dehydrated pulp. <P>COPYRIGHT: (C)2004,JPO

Description

【0001】
【発明の属する技術分野】
本発明は製紙用漂白パルプの製造方法に関し、更に詳細には、パルプ濃度が高い高濃度オゾン漂白での漂白効率を向上させ、かつパルプ強度を低下させる事のない漂白パルプの製造方法に関するものである。
【0002】
【従来の技術】
従来、製紙用パルプを漂白する方法としては、C(分子状塩素)−E(アルカリ抽出)−H(次亜塩素酸ナトリウム)−D(二酸化塩素)等の多段漂白法があり、主として塩素系薬品が使用されてきたが、塩素とパルプ中の有機物との反応により生成される環境に有害なダイオキシン等の有機塩素化合物が問題となり、酸素を用いた漂白段を初段に用い、塩素系漂白薬品を減少させる方法が採用されてきた。更に近年では分子状塩素を用いないECF(Elemental Chlorine Free)漂白や、塩素系薬品を全く使用しないTCF(Totally Chlorine Free)漂白が実用化されてきており、酸素、オゾン、過酸化水素等の酸素系薬品は有効な漂白薬品となっている。
【0003】
塩素系薬品に比べてオゾンによるパルプの漂白は、オゾンのリグニンとの高い反応性に加えて、塩素系漂白と異なり、漂白過程で有機塩素化合物を生成しないといった利点がある。
【0004】
このため、オゾン漂白は早くから注目されていたが、オゾンは製造コストが高く、その強い酸化力のためパルプ繊維を痛めやすい等の欠点があり、これらがオゾン漂白実用化阻害の大きな要因となっていた。しかしながら、近年、オゾン発生装置の性能向上によりオゾン製造コストが大幅に低下し、また漂白方法も改善されたことにより、パルプ濃度7〜15質量%でオゾン漂白を行なう中濃度オゾン漂白法、あるいはパルプ濃度38〜42%でオゾン漂白を行なう高濃度オゾン漂白法が導入されつつある。
【0005】
オゾン漂白の処理条件として、酸性条件下で行なうこと、またオゾンガスを分解する遷移金属イオンをなるべく除去することが重要であり、一般的に知られている。例えば、「紙と周辺技術」(4)P2−9、(1987)(非特許文献1参照)には、「パルプのオゾン漂白について」と題する高木氏の論文に、pHに関して、「オゾンは酸性では比較的安定であるが、pH4以上ではpHの上昇とともに分解されやすくなり、〜中略〜pH2から3でオゾン漂白を行うとパルプ粘度低下の抑制にも効果がある。」と述べられており、オゾン処理は酸性下で行うことが推奨されている。また、これに関連して、オゾン処理の前処理として酸性下にした後に洗浄段を加え、オゾンガスを分解する金属イオンを除く技術も提唱されている。
【0006】
また、オゾンを含む漂白シーケンスとして、特開平6−346391号公報(特許文献1参照)には、オゾン処理時のpHを1〜3の酸性として行うことを含む技術が開示されている。また、特開平5−148785号公報(特許文献2参照)には、化学的に蒸解したリグノセルロース含有パルプをpH3.1から9.0までの範囲内で錯化剤を使用して処理することによって該パルプの微量金属含有状態に変化を与え、その後上記パルプをオゾン処理する方法が開示されている。しかしながら、上記の文献ならびに公報に開示されているオゾン処理条件は、オゾンの分解またはオゾン段でのパルプ粘度低下を抑制することを目的としたものであり、実際のオゾン漂白における金属量について具体的に規定したものではない。
【0007】
さらに、特開昭57−154489号公報(特許文献3)には、約20%から約45%までのパルプ濃度で酸性pHでパルプのオゾン処理を行なう方法が開示されている。しかしながら、パルプ濃度を20%から45%まで変化させると、パルプに随伴する液量が大きく異なるため、オゾン段に持ち込むMn量のコントロールが難しい。
【0008】
一方、近年、環境問題意識の高まりにともない、漂白排水の全てを回収するクローズド化技術や一部を回収するセミクローズド化技術が注目されている。塩素や二酸化塩素などの塩素系薬品を用いた漂白では漂白工程で発生する塩素イオンが回収工程の配管等の腐食の原因となるため、クローズド化は難しいが、オゾン漂白は塩素イオンを発生しないため、クローズド化およびセミクローズド化しやすいという特徴を有している。しかしながら、オゾン漂白においても、クローズド化あるいはセミクローズド化した場合には、ノンプロセスエレメントと呼ばれる金属イオンの蓄積が問題となる。例えば、マンガン、カルシウムなどの金属イオンはオゾン漂白性への影響だけでなく、クローズド化に対しても配管等の詰まりや腐食といった悪影響を与えることが知られている。また、オゾン漂白段およびアルカリ抽出段の排水を前段のアルカリ酸素漂白段の希釈水や洗浄水に使用する場合、排水中の金属イオンが酸素漂白での効率低下と収率、粘度、強度低下をもたらしてしまう。
【0009】
アルカリ酸素漂白段では、アルカリ雰囲気下でリグニンがイオン化して多量のフェノール性水酸基を生成し、酸素分子と反応してカルボン酸などに分解され、リグニン分子は低分子化してアルカリに溶解する。この反応の過程で一部過酸化水素が発生し、マンガン、鉄、銅などの遷移金属の触媒作用によりヒドロキシラジカルが生成される。このヒドロキシラジカルは水系では最も強い一電子酸化剤であり、セルロースと反応し、パルプ収率低下や粘度、強度低下の原因となる。
【0010】
【特許文献1】特開平6−346391号公報
【特許文献2】特開平5−148785号公報
【特許文献3】特開昭57−154489号公報
【非特許文献1】「紙と周辺技術」(4)、p2−9、(1987)
【0011】
【発明が解決しようとする課題】
本発明の目的は、パルプ濃度が高い高濃度オゾン漂白に関し、オゾン漂白の効率を向上させ、かつパルプ強度を十分高く保つ処理方法を提供することにある。
【0012】
【問題を解決するための手段】
本発明者らは、パルプ濃度が高い高濃度オゾン漂白において、オゾン漂白の効率向上方法を種々検討した結果、pH2.5以下の酸による処理とツインロールプレスによるパルプの脱水とからなるオゾン漂白前処理により、パルプ濃度を32〜38質量%とし、その時のパルプ中のMn含有量を10mg/パルプ絶乾kg以下に調整し、オゾン漂白を行なうことにより、オゾン漂白の効率を大幅に向上させることを見出し、本発明をなすに到った。
【0013】
本願発明は以下の発明を包含する。
(1)木材チップを蒸解して得られた未晒パルプをアルカリ酸素漂白し、得られた酸素漂白後のパルプをpH2.5以下で酸処理後、濃度1〜5%に調整したのち、パルプ濃度を32〜38質量%まで脱水し、プレブレーカーにて解繊したパルプをオゾン漂白、次いでアルカリ抽出するシーケンスを有し、更にECF、TCF漂白工程で漂白する製紙用パルプの製造方法において、脱水後パルプのマンガン含有量が10mg/パルプ絶乾kg以下に調整されたパルプをオゾン漂白する製紙用漂白パルプの製造方法。
【0014】
(2)前記プレブレーカーは、プレス上部に鋸状の歯を持つ(1)記載の製紙用漂白パルプの製造方法。
【0015】
(3)前記脱水はツインロールプレス型の脱水機を用い、該ツインロールプレス型脱水機は8〜12mmのロールクリアランスを有する(1)記載の製紙用漂白パルプの製造方法。
【0016】
(4)オゾン漂白後のアルカリ抽出段をオゾン処理後の洗浄無しに希釈タンク内で行ない、かつ処理条件がパルプ濃度2〜6質量%、処理温度30〜50℃、処理時間5〜60分である(1)記載の製紙用漂白パルプの製造方法。
【0017】
(5)オゾン漂白におけるオゾン添加率が対パルプ当り0.4〜0.7質量%である(1)記載の製紙用漂白パルプの製造方法。
【0018】
(6)酸素漂白後のKα価と風乾パルプ1トンに対する添加オゾン1kg当りに生じるアルカリ抽出段後のKα価の差分が1.2〜1.7の範囲である(1)記載の製紙用漂白パルプの製造方法。
【0019】
(7)オゾン漂白後のECF漂白工程を、アルカリ抽出段(E)、過酸化水素漂白段(P)、二酸化塩素漂白段(D)で行う(1)記載の製紙用漂白パルプの製造方法。
【0020】
(8)アルカリ抽出段の洗浄ろ液をアルカリ酸素漂白段の希釈水および/または洗浄水に使用する送る(1)記載の製紙用パルプの製造方法。
【0021】
【発明の実施の形態】
本発明で使用される原料パルプとしては、木材チップを修正連続蒸解法(Modified Continuous Cooking) 、拡大修正連続蒸解法(Extended Modified Continuous Cooking)、全缶等温蒸解法(Isothermal Cooking)、Lo−Solids蒸解法、スーパーバッチ蒸解法、Compact蒸解法、KOBUDOMARI蒸解法等のクラフト蒸解(ポリサルファイド法を含む)、またはサルファイト蒸解等の蒸解法により得られた化学パルプを使用することができる。更に、本発明に使用される木材チップは、特に限定されるものではなく、アスペン、ブナ、アカシア、ユーカリ、マングローブ等の広葉樹材が好ましく、マツ、トウヒ、ダグラスファー等の針葉樹材、さらにバガス、ケナフ、エスパルト草、イネ、アシ等の草本植物由来のリグノセロース材料にも条件を満たせば適用できることはいうまでもない。
【0022】
本発明では、原料パルプとしてカッパー価が15〜25の未晒広葉樹パルプ(以下LUKPとする)が主に使用される。むろん請求の範囲を満たすものであれば、未晒針葉樹パルプ(NUKP)も使用できる。LUKPのカッパー価が15未満の場合では、パルプの漂白性は向上するものの、パルプ歩留まりが低下するとともに、パルプ強度の低下が起こるため実操業では採用が難しい。また蒸解後のカッパー価が25を越える場合では、漂白薬品が多く必要となるばかりでなく、蒸解後のカス率が高くなり、最終製品でのチリが多くなることから、これも実操業では採用が難しい。
【0023】
本発明において、公知の蒸解法によって得られたLUKPは、カッパー価が6〜14となるように酸素漂白工程が行われる。この酸素漂白工程は、好ましくは8〜12のカッパー価のパルプを与える工程である。この処理工程でのパルプのカッパー価が14を越えると、その後の漂白工程でいたずらに薬品を消費するため好ましくなく、反対に6未満の場合は、漂白前の段階でパルプの強度ならびに収率が著しく低下するので好ましくない。
【0024】
酸素漂白を経たパルプは、まずpH2.5以下で酸処理される。本発明に使用される酸はpH2.5以下に調整できるものであれば無機酸、有機酸のいずれでも良いが、硫酸、硝酸、塩酸、亜硫酸、亜硝酸等の無機酸、中でも硫酸が入手し易い上に取扱が容易であるため好適に用いられる。酸処理の時間は5分以上であれば特に限定されるものではなく、パルプ濃度も1〜15質量%の範囲であれば特に問題ないが、酸の拡散とパルプの攪拌性から1〜5質量%の低濃度で処理するのが好ましい。また、酸の添加場所としては特に限定されないが、次工程のツインロールプレス型脱水機のろ液を酸素漂白後の希釈水として用い、このろ液の循環ラインに酸を添加することも可能である。
【0025】
酸処理を経たパルプは、パルプ濃度1〜5質量%に調整された後にツインロールプレス型脱水機に送られパルプ濃度32〜38質量%まで脱水される。脱水前のパルプ濃度を1〜5質量%とすることでパルプ中の金属が溶液側に溶出し易くなり、続く脱水でMn等の金属を効果的に除去できる。脱水後のパルプ濃度が32質量%より低い場合は、水分がオゾンの反応を阻害するため好ましくなく、またパルプ濃度が38質量%を超えるとパルプ塊が硬く締まり、オゾンとパルプが均一に反応し難くなるため好ましくない。またパルプの脱水はロールクリアランスが8〜12mmのツインロールプレス型脱水機が用いられる。ロールクリアランスが8mmより小さい場合はパルプ塊が絞まりすぎるため好ましくなく、また12mmより大きい場合はパルプの脱水が不十分となり実際的ではない。
【0026】
ツインロールプレス型脱水機により脱水されたパルプは、プレス上部に設置された鋸状の歯を持つプレブレーカーにより解繊された後、搬送スクリューによりオゾンリアクターへ送られオゾン漂白される。オゾン漂白においてはオゾン添加率は、対パルプ0.4〜0.7質量%で行われ、オゾンガス濃度は特に限定されないが、現在の一般的なオゾン発生機の能力であるオゾン濃度8〜13質量%のオゾンガスが使用できる。オゾン添加率が0.4質量%より低い場合は、後段の漂白段での負荷が高くなり薬品添加率の上昇とパルプ強度の低下を招くので好ましくない。またオゾン添加率が0.7質量%を超える場合では、パルプ強度が低下するので好ましくない。オゾンはマンガン、鉄、銅、ニッケル、コバルト等の重金属と接触して分解することが知られている。これらの金属のうち、Mnは未晒パルプ中に20〜100mg/パルプ絶乾kg程度含まれるため、オゾン漂白性に大きな影響を与える。オゾン漂白時にパルプに含まれるMn量が10mg/パルプ絶乾kgを超えるとオゾンの分解が顕著となるため、Mn量を10mg/パルプ絶乾kg以下とすることでオゾン漂白性を大きく向上することが出来る。
【0027】
オゾン漂白されたパルプは、希釈スクリューにてアルカリを添加したアルカリ抽出段の洗浄ろ液で希釈され、オゾンリアクター下部の希釈タンクに送られる。本発明における実質的なアルカリ抽出はこの希釈タンク内で行なわれ、パルプ濃度は2〜6質量%、処理温度30〜50℃、処理時間5〜60分の条件で処理される。このような処理工程を経たパルプは、カッパー価が十分に低下する。一般的なオゾン漂白を導入している工場では、風乾パルプ1トンに対して、添加オゾン1kg当りに生じる酸素漂白後のカッパー価とアルカリ抽出段後のカッパー価の差分は1.0程度であるが、本発明では効率的にオゾン漂白がおこなわれるためにこの差分が1.2〜1.7と非常に高い。ここでは水分を10%含むパルプのことを風乾パルプとする。
【0028】
本発明において、好適には、アルカリ抽出段後の洗浄ろ液を黒液回収工程に送ることで、オゾン漂白およびアルカリ抽出で発生する有機物を熱エネルギーとして回収および、排出CODの削減が出来、環境負荷を大きく軽減できる。一方で、洗浄ろ液を前段アルカリ酸素漂白段の希釈水や洗浄水に使用する場合、持ち込まれるマンガンなどの金属イオンの影響で酸素漂白の効率や粘度、強度の低下が起こるため、金属イオンを除去しなければならない。
【0029】
オゾン漂白後の漂白シーケンスは、ECF漂白またはTCF漂白であれば特に限定されないが、例えば、A−Z−E−D、A−Z−Eo−D、A−Z−E−D−P、A−Z−Eo−D−P、A−Z−E−D−D、A−Z−Eo−D−D、A−Z−E−P−D等のシーケンスが挙げられる。ここで(A)は酸処理段、(Z)はオゾン処理段、(E)はアルカリ抽出段、(Eo)は酸素で強化されたアルカリ抽出段である。そのほか(D)は二酸化塩素段を示しており、(P)は過酸化水素段を示す。また、各段間の(−)は洗浄工程を表す。さらに、上記のシーケンスに薬品の減添及びパルプ品質の改良を目的として漂白工程の一部に酵素処理(Ez)段を設けても良く、D段の二酸化塩素段を分割添加(dnD、DND、dED等)しても良い。
【0030】
本発明で用いたパルプのカッパー価測定方法、Mn含有量測定方法、パルプ白色度測定方法は次の通りである。
【0031】
カッパー価測定方法
パルプのカッパー価は、JIS P 8211に準じて測定した。
【0032】
Mn含有量測定方法
パルプ中のMn含有量の測定は、絶乾約5gのパルプサンプルを小数点以下3桁まで精秤し、パルプサンプルを灰化した後に塩酸水溶液にて灰分を溶解し、原子吸光法により測定した。溶液中のMn含有量は、ろ過後、適宜希釈して原子吸光法により測定した。
【0033】
パルプ白色度測定方法
パルプの白色度は、JIS P 8212に準じて測定した。
【0034】
パルプ粘度測定方法
パルプの粘度は、JIS P 8215に準じて測定した。
【0035】
【実施例】
次に、本発明の実施例について説明するが、本発明はこれによりなんら限定されるものではない。尚、実施例および比較例中の薬品添加率は特に断らない限り対パルプ質量%を表す。
【0036】
実施例1
国内広葉樹30%/ユーカリ材70%の混合材をクラフト蒸解した未晒パルプを、洗浄、酸素漂白を行ないカッパー価9.7のパルプを得た。このパルプをパルプ濃度4質量%になるようにツインロールプレス脱水機のろ液で希釈し、硫酸を添加してpH2.2に調整した後、35℃で10分間酸処理を行なった。次に、このパルプをツインロールプレス型脱水機(ロールクリアランス10mm)にてパルプ濃度37.2質量%まで脱水し、プレス上部に鋸状の歯をもつプレブレーカーにて解繊した後にオゾンリアクター内でオゾン漂白を行なった。この時のパルプ中のMn含有量は5.8mg/パルプkgであり、オゾン添加率は0.5%であった。次に、オゾン漂白後パルプをアルカリ抽出後の洗浄ろ液で希釈し、希釈タンク内でアルカリ抽出を行なった。
【0037】
アルカリ抽出段の条件は、アルカリ添加率0.9%、パルプ濃度4質量%、滞留時間15分で行なった。アルカリ抽出段後の白色度は67.2%、カッパー価は3.2であり、風乾パルプ1トンに対する添加オゾン1kg当たりの酸素漂白後のカッパー価とアルカリ抽出段後のカッパー価の差分は1.44であった。次に、過酸化水素漂白と二酸化塩素漂白を順次行ない、最終白色度が86.2%で粘度が14.3mPa・sの漂白パルプを得た。過酸化水素漂白段の条件は、アルカリ添加率0.4%、過酸化水素添加率0.30%、パルプ濃度12質量%、処理温度65℃、滞留時間70分であった。また二酸化塩素漂白段の条件は、二酸化塩素添加率0.25%、パルプ濃度12質量%、処理温度70℃、滞留時間150分であった。結果を表1に示した。表中のオゾン1kg当たりのカッパー価低下度とは、酸素漂白後のカッパー価と風乾パルプ1トンに対する添加オゾン1kg当たりのアルカリ抽出段後のカッパー価の差分を示す。
【0038】
実施例2
実施例1と同一の酸素漂白後のパルプを用い、酸処理時のpHを2.4とし、脱水後パルプ濃度を33.5質量%とした以外は実施例1と同一の条件で処理を行なった。この時のオゾン漂白時のMn含有量は8.6mg/パルプkgであり、アルカリ抽出段後の白色度は66.9%、カッパー価は4.0であった。風乾パルプ1トンに対する添加オゾン1kg当たりの酸素漂白後のカッパー価とアルカリ抽出段後のカッパー価の差分は1.27であった。また、過酸化水素漂白と二酸化塩素漂白を順次行なった後の漂白パルプは白色度85.9%、粘度13.9mPa・sであった。結果を表1に示した。
【0039】
実施例3
実施例1で得られたアルカリ抽出段ろ液を希釈水として用いて、100℃、酸素圧0.5MPa、アルカリ添加率2.0%、反応時間60分の条件で、実施例1で使用したカッパー価18の未晒パルプのアルカリ酸素漂白をおこなった。酸素漂白に使用した希釈水のMn濃度および、酸素漂白後のカッパー価、粘度を表2に示した。
【0040】
実施例4
実施例2で得られたアルカリ抽出ろ液を希釈水として使用する以外は実施例3と同様にして酸素漂白をおこなった。酸素漂白に使用した希釈水のMn濃度および、酸素漂白後のカッパー価、粘度を表2に示した。
【0041】
比較例1
実施例1と同一の酸素漂白後パルプを用い、酸処理時のpHを3.2とし、脱水後のパルプ濃度を36.8質量%とした以外は実施例1と同一の処理を行なった。この時のオゾン漂白時のMn含有量は15.6mg/パルプkgであり、アルカリ抽出段後の白色度は64.1%、カッパー価は5.1であった。風乾パルプ1トンに対する添加オゾン1kg当たりの酸素漂白後のカッパー価とアルカリ抽出段後のカッパー価の差分は1.02であった。また、過酸化水素漂白と二酸化塩素漂白を順次行なった後の漂白パルプは白色度83.1%、粘度11.8mPa・sであった。結果を表1に示した。
【0042】
比較例2
実施例1と同一の酸素漂白後のパルプを用い、ツインロールプレス型脱水機によるパルプ脱水時のパルプ濃度を40.5%とした以外は実施例1と同一の処理を行なった。この時のオゾン漂白時のMn含有量は5.8mg/パルプkgであり、アルカリ抽出段後の白色度は65.4%、カッパー価は4.8であった。風乾パルプ1トンに対する添加オゾン1kg当たりの酸素漂白後のカッパー価とアルカリ抽出段後のカッパー価の差分は1.08であった。また、過酸化水素漂白と二酸化塩素漂白を順次行なった後の漂白パルプは白色度83.8%、粘度12.0mPa・sであった。結果を表1に示した。
【0043】
参考例
比較例1で得られたアルカリ抽出ろ液を希釈水として使用し、100℃、酸素圧0.5MPa、アルカリ添加率2.0%、反応時間60分の条件でカッパー価18の未晒パルプのアルカリ酸素漂白を行った。酸素漂白に使用した希釈水のMn濃度および、酸素漂白後のカッパー価、粘度を表2に示した。
【0044】
【表1】

Figure 2004137653
【0045】
【表2】
Figure 2004137653
【0046】
結果表1から明らかなように、pH2.5以下で酸処理を行なう高濃度オゾン漂白において、脱水後のパルプ濃度が32〜38質量%の範囲でかつオゾン漂白時のMn含有量が10mg/パルプkg以下の場合ではアルカリ抽出段後のカッパー価が十分低下し、また漂白パルプも高白色度でかつ高粘度が得られており、オゾン漂白の効率を向上させることが可能となった。さらに、オゾン漂白段に続くアルカリ抽出段の洗浄ろ液をアルカリ酸素漂白段の希釈水として使用する場合の酸素漂白の効率が上がり、粘度も向上した。
【0047】
【発明の効果】
以上の様に、本発明は高白色度でカッパー価の低いパルプが得られ、効率の良い製紙用オゾン漂白パルプの製造が可能となった。[0001]
TECHNICAL FIELD OF THE INVENTION
The present invention relates to a method for producing bleached pulp for papermaking, and more particularly, to a method for producing bleached pulp that improves bleaching efficiency in high-concentration ozone bleaching with high pulp concentration and does not reduce pulp strength. is there.
[0002]
[Prior art]
Conventionally, as a method for bleaching paper pulp, there is a multi-stage bleaching method such as C (molecular chlorine) -E (alkali extraction) -H (sodium hypochlorite) -D (chlorine dioxide). Chemicals have been used, but organic chlorine compounds such as dioxins that are harmful to the environment generated by the reaction of chlorine with organic matter in the pulp poses a problem, and the bleaching stage using oxygen is used in the first stage. Have been adopted. Further, in recent years, ECF (Elemental Chlorine Free) bleaching without using molecular chlorine and TCF (Totally Chlorine Free) bleaching without using any chlorine-based chemicals have been put into practical use. The system chemicals are effective bleaching chemicals.
[0003]
Compared to chlorine-based chemicals, bleaching of pulp with ozone has the advantage that, unlike chlorine-based bleaching, it does not generate organic chlorine compounds in the bleaching process, in addition to the high reactivity of ozone with lignin.
[0004]
For this reason, ozone bleaching has been attracting attention from an early stage.However, ozone has drawbacks such as high production cost, and its oxidizing power tends to damage pulp fibers, and these are major factors that hinder the practical use of ozone bleaching. Was. However, in recent years, the ozone production cost has been drastically reduced due to the improvement of the performance of the ozone generator, and the bleaching method has been improved, so that the ozone bleaching method of performing ozone bleaching at a pulp concentration of 7 to 15% by mass, or pulp A high-concentration ozone bleaching method for performing ozone bleaching at a concentration of 38 to 42% is being introduced.
[0005]
It is important and generally known that ozone bleaching is performed under acidic conditions and that transition metal ions that decompose ozone gas are removed as much as possible. For example, in "Paper and Peripheral Technologies" (4) P2-9, (1987) (see Non-Patent Document 1), in Takagi's paper entitled "On Ozone Bleaching of Pulp", regarding the pH, "Ozone is acidic. Is relatively stable, but when the pH is 4 or higher, it is easily decomposed as the pH increases, and ozone bleaching at a pH of about 2 to 3 is also effective in suppressing the decrease in pulp viscosity. " It is recommended that ozone treatment be performed under acidic conditions. In connection with this, a technique for removing metal ions that decompose ozone gas by adding a washing stage after acidification as a pretreatment of ozone treatment has also been proposed.
[0006]
Further, as a bleaching sequence including ozone, Japanese Patent Application Laid-Open No. 6-346391 (see Patent Literature 1) discloses a technique including performing an ozone treatment at an acidic pH of 1 to 3. Japanese Patent Application Laid-Open No. 5-148785 (Patent Document 2) discloses that a chemically digested lignocellulose-containing pulp is treated with a complexing agent within a pH range of 3.1 to 9.0. Discloses a method of changing the state of the pulp containing trace metals, and then subjecting the pulp to ozone treatment. However, the ozone treatment conditions disclosed in the above documents and publications are intended to suppress the decomposition of ozone or the decrease in pulp viscosity in the ozone stage. Not specified.
[0007]
Further, Japanese Patent Application Laid-Open No. 57-154489 (Patent Document 3) discloses a method of performing ozone treatment of pulp at an acidic pH with a pulp concentration of about 20% to about 45%. However, when the pulp concentration is changed from 20% to 45%, the amount of liquid accompanying the pulp varies greatly, and it is difficult to control the amount of Mn brought into the ozone stage.
[0008]
On the other hand, in recent years, with increasing awareness of environmental issues, a closed technology for collecting all of the bleaching wastewater and a semi-closed technology for collecting a part of the bleaching wastewater have been receiving attention. Bleaching using chlorine-based chemicals such as chlorine and chlorine dioxide is difficult to close because chlorine ions generated in the bleaching process cause corrosion of piping in the recovery process, but ozone bleaching does not generate chlorine ions. It is characterized by being easily closed and semi-closed. However, also in ozone bleaching, when closed or semi-closed, accumulation of metal ions called non-process elements becomes a problem. For example, it is known that metal ions such as manganese and calcium not only have an effect on ozone bleaching property but also have an adverse effect on closedness such as clogging and corrosion of pipes. In addition, when the wastewater from the ozone bleaching stage and the alkali extraction stage is used as dilution water or washing water in the preceding alkaline oxygen bleaching stage, metal ions in the wastewater reduce the efficiency and the yield, viscosity, and strength in oxygen bleaching. Will bring.
[0009]
In the alkaline oxygen bleaching stage, lignin is ionized in an alkaline atmosphere to generate a large amount of phenolic hydroxyl groups, reacts with oxygen molecules and is decomposed into carboxylic acids and the like, and the lignin molecules are reduced in molecular weight and dissolved in alkali. Hydrogen peroxide is partially generated in the course of this reaction, and a hydroxyl radical is generated by the catalytic action of a transition metal such as manganese, iron, or copper. The hydroxyl radical is the strongest one-electron oxidizing agent in an aqueous system, and reacts with cellulose to cause a decrease in pulp yield and a decrease in viscosity and strength.
[0010]
[Patent Document 1] JP-A-6-346391 [Patent Document 2] JP-A-5-148785 [Patent Document 3] JP-A-57-154489 [Non-Patent Document 1] "Paper and peripheral technology" ( 4), p2-9, (1987)
[0011]
[Problems to be solved by the invention]
An object of the present invention relates to high-concentration ozone bleaching having a high pulp concentration, and it is an object of the present invention to provide a processing method for improving ozone bleaching efficiency and maintaining pulp strength sufficiently high.
[0012]
[Means to solve the problem]
The present inventors have studied various methods for improving the efficiency of ozone bleaching in high-concentration ozone bleaching with a high pulp concentration. As a result, before ozone bleaching comprising treatment with an acid having a pH of 2.5 or less and dehydration of the pulp by a twin roll press. By processing, the pulp concentration is adjusted to 32 to 38% by mass, the Mn content in the pulp at that time is adjusted to 10 mg / pulverized pulp or less, and ozone bleaching is performed, thereby greatly improving the efficiency of ozone bleaching. And found the present invention.
[0013]
The present invention includes the following inventions.
(1) Unbleached pulp obtained by digesting wood chips is subjected to alkaline oxygen bleaching, and the resulting pulp after oxygen bleaching is acid-treated at a pH of 2.5 or less, adjusted to a concentration of 1 to 5%, and then pulp. The method has a sequence in which the pulp which has been dewatered to a concentration of 32 to 38% by mass, defibrated by a pre-breaker is ozone bleached, and then alkali-extracted. A method for producing bleached pulp for papermaking, wherein ozone bleaching is performed on pulp in which the manganese content of the post-pulp is adjusted to 10 mg / kg or less.
[0014]
(2) The method for producing bleached pulp for papermaking according to (1), wherein the pre-breaker has serrated teeth on the upper part of the press.
[0015]
(3) The method for producing bleached pulp for papermaking according to (1), wherein the dewatering is performed using a twin-roll press-type dehydrator, and the twin-roll press-type dehydrator has a roll clearance of 8 to 12 mm.
[0016]
(4) The alkali extraction stage after ozone bleaching is performed in the dilution tank without washing after ozone treatment, and the treatment conditions are pulp concentration of 2 to 6% by mass, treatment temperature of 30 to 50 ° C, and treatment time of 5 to 60 minutes. A method for producing bleached pulp for papermaking according to (1).
[0017]
(5) The method for producing bleached pulp for papermaking according to (1), wherein the ozone addition rate in the ozone bleaching is 0.4 to 0.7% by mass per pulp.
[0018]
(6) The bleaching for papermaking according to (1), wherein the difference between the Kα value after oxygen bleaching and the Kα value after 1 kg of ozone added to 1 ton of air-dried pulp after the alkali extraction stage is in the range of 1.2 to 1.7. Pulp manufacturing method.
[0019]
(7) The method for producing bleached pulp for papermaking according to (1), wherein the ECF bleaching step after ozone bleaching is performed in an alkali extraction stage (E), a hydrogen peroxide bleaching stage (P), and a chlorine dioxide bleaching stage (D).
[0020]
(8) The method for producing pulp for papermaking according to (1), wherein the washing filtrate in the alkali extraction stage is used as dilution water and / or washing water in the alkali oxygen bleaching stage.
[0021]
BEST MODE FOR CARRYING OUT THE INVENTION
As raw pulp used in the present invention, wood chips may be modified continuous cooking (Modified Continuous Cooking), extended modified continuous cooking (Extended Modified Continuous Cooking), all-can isotherm cooking, and isothermal cooking-oil cooking. Chemical pulp obtained by a kraft cooking (including a polysulfide method) such as a cooking method, a super batch cooking method, a Compact cooking method, a KOBUDO MARI cooking method, or a sulphite cooking method can be used. Further, the wood chips used in the present invention are not particularly limited, and are preferably hardwood materials such as aspen, beech, acacia, eucalyptus, mangrove, pine, spruce, softwood materials such as Douglas fir, and further bagasse, It goes without saying that the present invention can be applied to lignocellose materials derived from herbaceous plants such as kenaf, esparto grass, rice and reed as long as the conditions are satisfied.
[0022]
In the present invention, unbleached hardwood pulp having a kappa number of 15 to 25 (hereinafter referred to as LUKP) is mainly used as a raw material pulp. Of course, unbleached softwood pulp (NUKP) can be used as long as it satisfies the claims. When the kappa number of LUKP is less than 15, the bleachability of the pulp is improved, but the pulp yield is lowered and the pulp strength is lowered. If the copper value after the digestion exceeds 25, not only is it necessary to use a large amount of bleaching chemicals, but also the post-digestion rate increases and the final product becomes more dusty, so this is also used in actual operations. Is difficult.
[0023]
In the present invention, LUKP obtained by a known cooking method is subjected to an oxygen bleaching step so that the kappa number becomes 6 to 14. This oxygen bleaching step is preferably a step of providing pulp having a kappa number of 8 to 12. If the kappa number of the pulp in this treatment step exceeds 14, it is not preferable because chemicals are unnecessarily consumed in the subsequent bleaching step. Conversely, if the kappa number is less than 6, the strength and yield of the pulp at the stage before bleaching are reduced. This is not preferable because it significantly decreases.
[0024]
Pulp that has undergone oxygen bleaching is first acid-treated at a pH of 2.5 or less. The acid used in the present invention may be any of inorganic acids and organic acids as long as it can be adjusted to pH 2.5 or less.Sulfuric acid, nitric acid, hydrochloric acid, sulfurous acid, inorganic acids such as nitrous acid, among which sulfuric acid is obtained It is preferably used because it is easy to handle and easy to handle. The time of the acid treatment is not particularly limited as long as it is 5 minutes or more, and there is no particular problem as long as the pulp concentration is in the range of 1 to 15% by mass. % Is preferred. Further, the place where the acid is added is not particularly limited, but it is also possible to use the filtrate of the twin roll press type dehydrator in the next step as dilution water after oxygen bleaching, and to add the acid to the circulation line of this filtrate. is there.
[0025]
The pulp that has been subjected to the acid treatment is adjusted to a pulp concentration of 1 to 5% by mass and then sent to a twin roll press type dehydrator to be dehydrated to a pulp concentration of 32 to 38% by mass. By setting the pulp concentration before dehydration to 1 to 5% by mass, metals in the pulp are easily eluted to the solution side, and metals such as Mn can be effectively removed by subsequent dehydration. When the pulp concentration after dehydration is lower than 32% by mass, the moisture inhibits the reaction of ozone, which is not preferable. When the pulp concentration exceeds 38% by mass, the pulp mass is firmly tightened, and the ozone and the pulp react uniformly. It is not preferable because it becomes difficult. For dewatering the pulp, a twin roll press type dehydrator having a roll clearance of 8 to 12 mm is used. If the roll clearance is smaller than 8 mm, the pulp mass is too narrow, which is not preferable. If it is larger than 12 mm, the pulp is insufficiently dewatered and is not practical.
[0026]
The pulp dewatered by the twin roll press dewatering machine is defibrated by a pre-breaker having serrated teeth provided on the upper part of the press, and then sent to an ozone reactor by a conveying screw to be ozone bleached. In the ozone bleaching, the ozone addition rate is 0.4 to 0.7% by mass with respect to the pulp, and the ozone gas concentration is not particularly limited. However, the ozone concentration of 8 to 13 mass which is the capacity of the current general ozone generator is used. % Ozone gas can be used. If the ozone addition ratio is lower than 0.4% by mass, the load in the subsequent bleaching stage becomes high, which causes an increase in the chemical addition ratio and a decrease in pulp strength, which is not preferable. On the other hand, if the ozone addition rate exceeds 0.7% by mass, the pulp strength is undesirably reduced. Ozone is known to decompose upon contact with heavy metals such as manganese, iron, copper, nickel and cobalt. Of these metals, Mn has a significant effect on ozone bleaching because unbleached pulp contains about 20 to 100 mg / kg of absolutely dried pulp. When the amount of Mn contained in the pulp exceeds 10 mg / kg of pulp absolutely dry during ozone bleaching, the decomposition of ozone becomes remarkable. Can be done.
[0027]
The ozone bleached pulp is diluted with a washing filtrate of an alkali extraction stage to which an alkali is added by a dilution screw, and sent to a dilution tank below the ozone reactor. The substantial alkali extraction in the present invention is performed in this dilution tank, and the pulp concentration is 2 to 6% by mass, the treatment temperature is 30 to 50 ° C, and the treatment time is 5 to 60 minutes. Pulp that has undergone such a treatment step has a sufficiently reduced kappa number. In a factory where general ozone bleaching is introduced, the difference between the kappa number after oxygen bleaching and the kappa number after alkali extraction, which is generated per kg of added ozone, per ton of air-dried pulp is about 1.0. However, in the present invention, since ozone bleaching is carried out efficiently, this difference is very high at 1.2 to 1.7. Here, pulp containing 10% of water is referred to as air-dried pulp.
[0028]
In the present invention, preferably, the washing filtrate after the alkali extraction stage is sent to a black liquor recovery step, whereby organic matter generated in ozone bleaching and alkali extraction is recovered as heat energy, and the emission COD can be reduced. The load can be greatly reduced. On the other hand, when the washing filtrate is used for dilution water or washing water in the pre-alkali oxygen bleaching stage, the efficiency, viscosity and strength of oxygen bleaching decrease due to the effects of metal ions such as manganese brought in. Must be removed.
[0029]
The bleaching sequence after ozone bleaching is not particularly limited as long as it is ECF bleaching or TCF bleaching. For example, AZED, AZ-Eo-D, AZ-EDP, A -Z-Eo-DP, AZ-E-DD, AZ-Eo-DD, AZ-E-P-D, and the like. Here, (A) is an acid treatment stage, (Z) is an ozone treatment stage, (E) is an alkali extraction stage, and (Eo) is an alkali extraction stage reinforced with oxygen. In addition, (D) shows a chlorine dioxide stage, and (P) shows a hydrogen peroxide stage. (-) Between each stage indicates a washing step. Further, an enzymatic treatment (Ez) stage may be provided in a part of the bleaching step for the purpose of adding chemicals and improving pulp quality in the above sequence, and a chlorine dioxide stage of D stage is divided and added (dnD, DND, dED etc.).
[0030]
The method for measuring the kappa number, the method for measuring the Mn content, and the method for measuring pulp whiteness of the pulp used in the present invention are as follows.
[0031]
Method for measuring kappa number Kappa number of pulp was measured according to JIS P 8211.
[0032]
Mn content measurement method Mn content in pulp is measured by precisely weighing a pulp sample of about 5 g in absolute dryness to three decimal places, ashing the pulp sample and then dissolving the ash in an aqueous hydrochloric acid solution. And measured by the atomic absorption method. The Mn content in the solution was measured by an atomic absorption method after being appropriately diluted after filtration.
[0033]
Pulp whiteness measurement method The whiteness of pulp was measured according to JIS P8212.
[0034]
Pulp viscosity measurement method The pulp viscosity was measured according to JIS P8215.
[0035]
【Example】
Next, examples of the present invention will be described, but the present invention is not limited thereto. The chemical addition rates in Examples and Comparative Examples represent pulp mass% unless otherwise specified.
[0036]
Example 1
Unbleached pulp obtained by kraft digestion of a mixture of 30% domestic hardwood / 70% eucalyptus wood was washed and oxygen bleached to obtain pulp having a kappa number of 9.7. The pulp was diluted with the filtrate of a twin roll press dehydrator so that the pulp concentration was 4% by mass, adjusted to pH 2.2 by adding sulfuric acid, and then subjected to an acid treatment at 35 ° C. for 10 minutes. Next, the pulp was dewatered to a pulp concentration of 37.2% by mass with a twin-roll press type dewatering machine (roll clearance 10 mm), defibrated with a pre-breaker having saw-shaped teeth on the upper part of the press, and then in an ozone reactor. Ozone bleaching. At this time, the Mn content in the pulp was 5.8 mg / kg of pulp, and the ozone addition rate was 0.5%. Next, the pulp after ozone bleaching was diluted with the washing filtrate after alkali extraction, and alkali extraction was performed in a dilution tank.
[0037]
The conditions for the alkali extraction stage were as follows: an alkali addition rate of 0.9%, a pulp concentration of 4% by mass, and a residence time of 15 minutes. The whiteness after the alkali extraction stage was 67.2% and the kappa number was 3.2. The difference between the kappa number after oxygen bleaching per kg of added ozone and the kappa number after the alkali extraction stage was 1 ton of air-dried pulp. .44. Next, hydrogen peroxide bleaching and chlorine dioxide bleaching were sequentially performed to obtain bleached pulp having a final whiteness of 86.2% and a viscosity of 14.3 mPa · s. The conditions of the hydrogen peroxide bleaching stage were as follows: alkali addition rate 0.4%, hydrogen peroxide addition rate 0.30%, pulp concentration 12 mass%, treatment temperature 65 ° C, residence time 70 minutes. The chlorine dioxide bleaching stage conditions were as follows: chlorine dioxide addition rate 0.25%, pulp concentration 12 mass%, treatment temperature 70 ° C, residence time 150 minutes. The results are shown in Table 1. The degree of reduction in the kappa number per kg of ozone in the table indicates the difference between the kappa number after oxygen bleaching and the kappa number after the alkali extraction stage per kg of added ozone per 1 ton of air-dried pulp.
[0038]
Example 2
The same pulp after oxygen bleaching as in Example 1 was used, the treatment was performed under the same conditions as in Example 1, except that the pH during acid treatment was set to 2.4 and the pulp concentration after dehydration was set to 33.5% by mass. Was. The Mn content during ozone bleaching at this time was 8.6 mg / kg pulp, the whiteness after the alkali extraction stage was 66.9%, and the kappa number was 4.0. The difference between the kappa number after oxygen bleaching and the kappa number after the alkali extraction stage per kg of added ozone per 1 ton of air-dried pulp was 1.27. The bleached pulp after the hydrogen peroxide bleaching and the chlorine dioxide bleaching had a whiteness of 85.9% and a viscosity of 13.9 mPa · s. The results are shown in Table 1.
[0039]
Example 3
Using the filtrate of the alkali extraction stage obtained in Example 1 as dilution water, it was used in Example 1 under the conditions of 100 ° C., oxygen pressure 0.5 MPa, alkali addition rate 2.0%, and reaction time 60 minutes. Unbleached pulp having a kappa number of 18 was subjected to alkaline oxygen bleaching. Table 2 shows the Mn concentration of the dilution water used for oxygen bleaching, and the Kappa number and viscosity after oxygen bleaching.
[0040]
Example 4
Oxygen bleaching was carried out in the same manner as in Example 3 except that the alkaline extraction filtrate obtained in Example 2 was used as dilution water. Table 2 shows the Mn concentration of the dilution water used for oxygen bleaching, and the Kappa number and viscosity after oxygen bleaching.
[0041]
Comparative Example 1
The same treatment as in Example 1 was performed, except that the same pulp after oxygen bleaching as in Example 1 was used, the pH during acid treatment was 3.2, and the pulp concentration after dehydration was 36.8% by mass. The Mn content during ozone bleaching at this time was 15.6 mg / kg pulp, the whiteness after the alkali extraction stage was 64.1%, and the kappa number was 5.1. The difference between the kappa number after oxygen bleaching and the kappa number after alkali extraction per kg of added ozone per 1 ton of air-dried pulp was 1.02. The bleached pulp after the hydrogen peroxide bleaching and the chlorine dioxide bleaching had a whiteness of 83.1% and a viscosity of 11.8 mPa · s. The results are shown in Table 1.
[0042]
Comparative Example 2
The same treatment as in Example 1 was performed, except that the same pulp after oxygen bleaching as in Example 1 was used, and the pulp concentration at the time of pulp dewatering by a twin roll press dehydrator was 40.5%. The Mn content during ozone bleaching at this time was 5.8 mg / kg pulp, the whiteness after the alkali extraction stage was 65.4%, and the kappa number was 4.8. The difference between the Kappa number after oxygen bleaching and the Kappa number after the alkali extraction stage per kg of added ozone per 1 ton of air-dried pulp was 1.08. The bleached pulp after the hydrogen peroxide bleaching and the chlorine dioxide bleaching had a whiteness of 83.8% and a viscosity of 12.0 mPa · s. The results are shown in Table 1.
[0043]
Reference Example The alkali extract filtrate obtained in Comparative Example 1 was used as diluting water, and was not exposed to a kappa number of 18 at 100 ° C., an oxygen pressure of 0.5 MPa, an alkali addition rate of 2.0%, and a reaction time of 60 minutes. The pulp was subjected to alkaline oxygen bleaching. Table 2 shows the Mn concentration of the dilution water used for oxygen bleaching, and the Kappa number and viscosity after oxygen bleaching.
[0044]
[Table 1]
Figure 2004137653
[0045]
[Table 2]
Figure 2004137653
[0046]
Results As is clear from Table 1, in high-concentration ozone bleaching in which acid treatment is performed at pH 2.5 or lower, the pulp concentration after dehydration is in the range of 32 to 38% by mass, and the Mn content during ozone bleaching is 10 mg / pulp. In the case of less than kg, the kappa number after the alkali extraction stage was sufficiently reduced, and the bleached pulp was also obtained with high whiteness and high viscosity, making it possible to improve the efficiency of ozone bleaching. Further, the efficiency of oxygen bleaching when the washing filtrate of the alkali extraction stage following the ozone bleaching stage was used as dilution water for the alkali oxygen bleaching stage was increased, and the viscosity was also improved.
[0047]
【The invention's effect】
As described above, according to the present invention, pulp having high whiteness and low kappa number was obtained, and efficient production of ozone bleached pulp for papermaking became possible.

Claims (8)

木材チップを蒸解して得られた未晒パルプをアルカリ酸素漂白し、得られた酸素漂白後のパルプをpH2.5以下で酸処理後、濃度1〜5%に調整したのち、パルプ濃度を32〜38質量%まで脱水し、プレブレーカーにて解繊したパルプをオゾン漂白、次いでアルカリ抽出するシーケンスを有し、更にECF、TCF漂白工程で漂白する製紙用パルプの製造方法において、脱水後パルプのマンガン含有量が10mg/パルプ絶乾kg以下に調整されたパルプをオゾン漂白することを特徴とする製紙用漂白パルプの製造方法。The unbleached pulp obtained by digesting the wood chips is subjected to alkaline oxygen bleaching, and the obtained pulp after oxygen bleaching is acid-treated at a pH of 2.5 or less, and then adjusted to a concentration of 1 to 5%. A pulp that has been dehydrated to about 38% by mass, defibrated by a pre-breaker, has a sequence of ozone bleaching and then alkali extraction, and further, in a method of producing pulp for papermaking that is bleached in an ECF and TCF bleaching step, A method for producing bleached pulp for papermaking, wherein pulp whose manganese content is adjusted to 10 mg / kg or less of pulp absolute dryness is ozone bleached. 前記プレブレーカーは、プレス上部に鋸状の歯を持つことを特徴とする請求項1記載の製紙用漂白パルプの製造方法。The method for producing bleached pulp for papermaking according to claim 1, wherein the prebreaker has serrated teeth on an upper part of the press. 前記脱水はツインロールプレス型の脱水機を用い、該ツインロールプレス型脱水機は8〜12mmのロールクリアランスを有することを特徴とする請求項1記載の製紙用漂白パルプの製造方法。The method for producing bleached pulp for papermaking according to claim 1, wherein the dewatering is performed using a twin-roll press type dehydrator, and the twin-roll press type dehydrator has a roll clearance of 8 to 12 mm. オゾン漂白後のアルカリ抽出段をオゾン処理後の洗浄無しに希釈タンク内で行ない、かつ処理条件がパルプ濃度2〜6質量%、処理温度30〜50℃、処理時間5〜60分であることを特徴とする請求項1記載の製紙用漂白パルプの製造方法。The alkali extraction stage after ozone bleaching is performed in a dilution tank without washing after ozone treatment, and the treatment conditions are that the pulp concentration is 2 to 6% by mass, the treatment temperature is 30 to 50 ° C, and the treatment time is 5 to 60 minutes. The method for producing bleached pulp for papermaking according to claim 1, characterized in that: オゾン漂白におけるオゾン添加率が対パルプ当り0.4〜0.7質量%であることを特徴とする請求項1記載の製紙用漂白パルプの製造方法。The method for producing bleached pulp for papermaking according to claim 1, wherein the ozone addition rate in ozone bleaching is 0.4 to 0.7% by mass per pulp. 酸素漂白後のKα価と風乾パルプ1トンに対する添加オゾン1kg当りに生じるアルカリ抽出段後のKα価の差分が1.2〜1.7の範囲であることを特徴とする請求項1記載の製紙用漂白パルプの製造方法。2. The papermaking process according to claim 1, wherein the difference between the K.alpha. Value after oxygen bleaching and the K.alpha. Value after 1 kg of ozone added to 1 ton of air-dried pulp after the alkali extraction stage is in the range of 1.2 to 1.7. For producing bleached pulp. オゾン漂白後のECF漂白工程を、アルカリ抽出段(E)、過酸化水素漂白段(P)、二酸化塩素漂白段(D)で行うことを特徴とする請求項1に記載の製紙用漂白パルプの製造方法。The bleaching pulp for papermaking according to claim 1, wherein the ECF bleaching step after the ozone bleaching is performed in an alkali extraction stage (E), a hydrogen peroxide bleaching stage (P), and a chlorine dioxide bleaching stage (D). Production method. アルカリ抽出段の洗浄ろ液をアルカリ酸素漂白段の希釈水および/または洗浄水に使用することを特徴とする請求項1に記載の製紙用パルプの製造方法。The method for producing pulp for papermaking according to claim 1, wherein the washing filtrate of the alkali extraction stage is used as dilution water and / or washing water of the alkali oxygen bleaching stage.
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JP2004360124A (en) * 2003-06-06 2004-12-24 Nippon Paper Industries Co Ltd Method for bleaching lignocellulose substance
JP2008519176A (en) * 2004-11-05 2008-06-05 アクゾ ノーベル エヌ.ブイ. Cellulose fiber processing method
US8007636B2 (en) 2004-11-05 2011-08-30 Akzo Nobel N.V. Method of treating cellulose fibres with chlorine dioxide and an alkyl cellulose derivative
KR20150139503A (en) * 2013-02-08 2015-12-11 게페 첼루로제 게엠베하 Softwood kraft fiber having an improved a-cellulose content and its use in the production of chemical cellulose products
JP2018159079A (en) * 2008-12-19 2018-10-11 キシレコ インコーポレイテッド Processing method of biomass
CN111979822A (en) * 2020-08-07 2020-11-24 齐鲁工业大学 Sequential bleaching process suitable for element-free chlorine (ECF) short-procedure bleaching
JP2022549123A (en) * 2020-08-07 2022-11-24 斉魯工業大学 Short-Procedure ECF Bleaching Process X/DZP (X/ZDP) for Kraft Wood Pulp

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004360124A (en) * 2003-06-06 2004-12-24 Nippon Paper Industries Co Ltd Method for bleaching lignocellulose substance
JP2008519176A (en) * 2004-11-05 2008-06-05 アクゾ ノーベル エヌ.ブイ. Cellulose fiber processing method
JP4684296B2 (en) * 2004-11-05 2011-05-18 アクゾ ノーベル ナムローゼ フェンノートシャップ Cellulose fiber processing method
US8007636B2 (en) 2004-11-05 2011-08-30 Akzo Nobel N.V. Method of treating cellulose fibres with chlorine dioxide and an alkyl cellulose derivative
JP2018159079A (en) * 2008-12-19 2018-10-11 キシレコ インコーポレイテッド Processing method of biomass
KR20150139503A (en) * 2013-02-08 2015-12-11 게페 첼루로제 게엠베하 Softwood kraft fiber having an improved a-cellulose content and its use in the production of chemical cellulose products
KR102180512B1 (en) 2013-02-08 2020-11-19 게페 첼루로제 게엠베하 Softwood kraft fiber having an improved a-cellulose content and its use in the production of chemical cellulose products
CN111979822A (en) * 2020-08-07 2020-11-24 齐鲁工业大学 Sequential bleaching process suitable for element-free chlorine (ECF) short-procedure bleaching
JP2022549123A (en) * 2020-08-07 2022-11-24 斉魯工業大学 Short-Procedure ECF Bleaching Process X/DZP (X/ZDP) for Kraft Wood Pulp
JP7311932B2 (en) 2020-08-07 2023-07-20 斉魯工業大学 Short-Procedure ECF Bleaching Process X/DZP (X/ZDP) for Kraft Wood Pulp

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