JP4603298B2 - Pulp bleaching method - Google Patents

Pulp bleaching method Download PDF

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JP4603298B2
JP4603298B2 JP2004169367A JP2004169367A JP4603298B2 JP 4603298 B2 JP4603298 B2 JP 4603298B2 JP 2004169367 A JP2004169367 A JP 2004169367A JP 2004169367 A JP2004169367 A JP 2004169367A JP 4603298 B2 JP4603298 B2 JP 4603298B2
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pulp
bleaching
light irradiation
acid
light
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JP2005350778A (en
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正一 宮脇
一博 黒須
隆 越智
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Nippon Paper Industries Co Ltd
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Priority to EP05748560A priority patent/EP1790771A4/en
Priority to CN2005800255211A priority patent/CN1993518B/en
Priority to US11/628,961 priority patent/US20070246176A1/en
Priority to CA2569848A priority patent/CA2569848C/en
Priority to PCT/JP2005/010521 priority patent/WO2005121442A1/en
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本発明は、酸処理後洗浄したパルプをアルカリ性条件下で、紫外光及び/又は可視光を照射することを特徴とするパルプの漂白方法に関するものである。   The present invention relates to a pulp bleaching method characterized by irradiating ultraviolet light and / or visible light under alkaline conditions to a pulp washed after acid treatment.

紙パルプ工場の漂白工程から排出される物質が環境に与える影響に関心が集まる中、従来の塩素及び/又は塩素系薬品を主に用いた漂白方法から、塩素を使わないECF漂白や更に進んで塩素系薬品を全く使用しないTCF漂白が全世界的に主流となりつつある。このような背景から、ECF漂白やTCF漂白で使用される薬品としては、二酸化塩素や過酸化水素、酸素、オゾンなどの薬品類に限定されてきている。しかしながら、これらの薬品のみでは、組合せも自ずと限定されることもあり、漂白によって得られるパルプ品質、特に白色度には限界があり、あるいはそれを得るためには高価な薬品を大量に使用しなければならない等の問題がでてきている。これらの問題を解決するために、これまでにない漂白性能に優れた非塩素系薬品、あるいは新たな漂白方法の開発が求められている。   While interest has been focused on the environmental impact of substances discharged from the bleaching process of pulp and paper mills, the conventional bleaching method mainly using chlorine and / or chlorine-based chemicals, ECF bleaching without chlorine and further progress TCF bleaching, which does not use any chlorinated chemicals, is becoming the mainstream worldwide. Against this background, chemicals used in ECF bleaching and TCF bleaching have been limited to chemicals such as chlorine dioxide, hydrogen peroxide, oxygen and ozone. However, with these chemicals alone, combinations may naturally be limited, and there is a limit to the pulp quality obtained by bleaching, especially whiteness, or a large amount of expensive chemicals must be used to obtain it. Problems such as having to come out have come out. In order to solve these problems, there has been a demand for the development of a non-chlorine chemical having an unprecedented bleaching performance or a new bleaching method.

従来からパルプに由来する各種の金属が酸素系漂白薬品の分解を促進し、酸素系漂白薬品を無駄に消費することが知られている。そこで、この金属を除去し、酸素系漂白薬品の漂白効率を高める技術として、比較的低温の酸処理および/またはキレート剤処理などが提示されている。この酸処理の技術として、リグノセルロース材料から製造されたパルプを酸素漂白によって脱リグニンする方法において、まず、パルプに亜硝酸塩および酸を添加してパルプを前処理し、続いて酸素漂白を行う漂白方法、あるいは、蒸解処理された化学パルプに対して、酸処理を行った後、アルカリ性媒体中で過酸化物と加圧酸素による脱リグニンを行う漂白方法が開示されている(例えば、特許文献1、あるいは、特許文献2)。また、このほか、蒸解処理された化学パルプに対して、高温高圧酸素漂白処理を行い、次いで酸処理またはキレート剤処理を行った後、アルカリ性媒体中で過酸化物、または過酸化水素と酸素により脱リグニン・漂白を行う漂白方法が開示されている(例えば、特許文献3)。   Conventionally, it is known that various metals derived from pulp accelerate the decomposition of oxygen bleaching chemicals and waste oxygen bleaching chemicals. Therefore, as a technique for removing this metal and increasing the bleaching efficiency of oxygen-based bleaching chemicals, a relatively low-temperature acid treatment and / or chelating agent treatment has been proposed. In this acid treatment technique, pulp produced from lignocellulosic material is delignified by oxygen bleaching. First, nitrite and acid are added to the pulp to pretreat the pulp, followed by oxygen bleaching. Or a bleaching method in which delignification with peroxide and pressurized oxygen is performed in an alkaline medium after acid treatment is performed on the chemical pulp that has been digested or treated (for example, Patent Document 1). Or, Patent Document 2). In addition, after the digested chemical pulp is subjected to high-temperature and high-pressure oxygen bleaching treatment, followed by acid treatment or chelating agent treatment, it is treated with peroxide or hydrogen peroxide and oxygen in an alkaline medium. A bleaching method for performing delignification and bleaching is disclosed (for example, Patent Document 3).

また、ECFまたはTCF漂白パルプの退色に係わる物質に関する最近の新たな知見として、従来のリグニンやその変性物以外にヘキセンウロン酸が関与していることが知られ出している。このヘキセンウロン酸は、蒸解工程においてヘミセルロース中のメチルグルクロン酸から脱メチルすることで生成する.このヘキセンウロン酸はパルプの退色性に関与していると言われている.このヘキセンウロン酸を除去する方法の一つとして、比較的高温の酸処理技術が提示されている.これは、漂白前のパルプを高温且つ酸性下で処理することにより、このヘキセンウロン酸およびリグニン変性物を酸加水分解し除去するものである.例えば、硫酸塩法またはアルカリ法によって製造したセルロースパルプの懸濁液を加熱し、約85〜150℃で約2〜5のpHで処理し、セルロースパルプ中のヘキセンウロン酸の少なくとも約50%を除去し、パルプのカッパー価を2〜9単位減少させる技術が開示されている(特許文献4参照。)。   Moreover, it is known that hexeneuronic acid is involved in addition to conventional lignin and its modified products as a recent new finding regarding substances related to fading of ECF or TCF bleached pulp. This hexeneuronic acid is produced by demethylation from methylglucuronic acid in hemicellulose in the cooking process. This hexeneuronic acid is said to be involved in the fading of pulp. As one of the methods for removing this hexeneuronic acid, a relatively high temperature acid treatment technique has been proposed. In this method, the hexeneuronic acid and the lignin-modified product are removed by acid hydrolysis by treating the unbleached pulp under high temperature and acidity. For example, a suspension of cellulose pulp produced by the sulfate or alkaline method is heated and treated at about 85-150 ° C. at a pH of about 2-5 to remove at least about 50% of hexeneuronic acid in the cellulose pulp. However, a technique for reducing the pulp kappa number by 2 to 9 units is disclosed (see Patent Document 4).

また、光照射を利用する漂白技術として、未晒しKPの過酸化水素漂白において紫外光を照射する技術(例えば、非特許文献1、あるいは特許文献5参照)、あるいは未晒しKPの酸素漂白において紫外光を照射する技術(例えば、非特許文献2、参照参照)が開示されている。   In addition, as a bleaching technique using light irradiation, a technique of irradiating ultraviolet light in hydrogen peroxide bleaching of unexposed KP (see, for example, Non-Patent Document 1 or Patent Document 5), or an ultraviolet light in oxygen bleaching of unexposed KP. A technique for irradiating light (for example, see Non-Patent Document 2) is disclosed.

あるいは、還元剤を用いるパルプの漂白方法において紫外光及び/又は可視光を照射する技術(特許文献6参照)、あるいは、酸化剤として、ROOR’で示される有機過酸化物の存在下、紫外及び/又は可視光を照射する技術(特許文献7参照)、が開示されている。
特許第2895977号公報 特開平6−101186号公報 特開平6−158573号公報 特表平10−508346号公報 特開2002−88673号公報 特開2002−88671号公報 特開2002−88672号公報 B.Marccia,et al.J34〜J39、JOURNAL OF PULP AND PAPER SCIENCE: VOL.17,NO.2,March 1991 J.AbBot,et al.p198〜202、Appita Vol,46,No.3,May 1993
Alternatively, a technique of irradiating ultraviolet light and / or visible light in a pulp bleaching method using a reducing agent (see Patent Document 6), or in the presence of an organic peroxide represented by ROOR ′ as an oxidizing agent, ultraviolet and A technique for irradiating visible light (see Patent Document 7) is disclosed.
Japanese Patent No. 2895977 JP-A-6-101186 JP-A-6-158573 Japanese National Patent Publication No. 10-508346 JP 2002-88673 A Japanese Patent Laid-Open No. 2002-88671 JP 2002-88672 A B. Marccia, et al. J34-J39, JOURNAL OF PULP AND PAPER SCIENCE: VOL.17, NO.2, March 1991 J. AbBot, et al. p198 ~ 202, Appita Vol, 46, No.3, May 1993

本発明の目的は、前述の様な、パルプの酸処理あるいは光照射技術を更に発展させ、塩素系薬品を軽減し、かつ従来の漂白方法と比較してより効率的な漂白方法を開発することにある。   The object of the present invention is to further develop the acid treatment or light irradiation technology of pulp as described above, to reduce chlorine chemicals, and to develop a more efficient bleaching method compared to conventional bleaching methods. It is in.

発明者らは、鋭意検討の結果、酸処理後洗浄したパルプをpH10〜13の範囲のアルカリ性条件下、波長100〜400nmの紫外光及び/又は可視光を照射することにより、非常に効率の良い非塩素系の漂白方法を見出し、本発明に至ったものである。   As a result of intensive studies, the inventors of the present invention are very efficient by irradiating ultraviolet light and / or visible light having a wavelength of 100 to 400 nm under alkaline conditions in the range of pH 10 to 13 after the acid-treated pulp is washed. The present inventors have found a non-chlorine bleaching method and have arrived at the present invention.

発明の実施の形態BEST MODE FOR CARRYING OUT THE INVENTION

本発明の漂白方法の対象となるパルプは、酸処理後洗浄したクラフトパルプ(KP)であり、特に未晒しKP、酸素脱リグニンKP、オゾン漂白KPが好適である。また、パルプ原料としては、特に限定するものではなく、広葉樹木材あるいは針葉樹木材の他、ケナフ、麻、イネ、バカス、竹等の植物でも良い。   The pulp to be subjected to the bleaching method of the present invention is kraft pulp (KP) washed after acid treatment, and unbleached KP, oxygen delignification KP, and ozone bleaching KP are particularly suitable. The pulp raw material is not particularly limited, and plants such as kenaf, hemp, rice, bacus, and bamboo may be used in addition to hardwood wood or softwood wood.

本発明の酸処理に使用する酸の種類は、無機酸でも有機酸でも良い。無機酸としては、硫酸、塩酸、硝酸、亜硫酸、亜硝酸、リン酸、二酸化塩素発生装置の残留酸などの鉱酸を使用できる。好適には、硫酸である。有機酸としては、酢酸、乳酸、蓚酸、クエン酸、蟻酸などを使用できる。酸処理時のpHは、1.0〜6.0の範囲であり、好ましくは1.0〜5.0、更に好ましくは2.0〜5.0、最適には2.5〜3.5である。pHが1.0未満の場合はヘキセンウロン酸等と有害金属の除去は充分であるが、酸が過剰であるため粘度低下が大きくなる。一方、pHが6.0を超えると酸濃度が低く、ヘキセンウロン酸等と有害金属の除去が不十分となる。ヘキセンウロン酸の多い広葉樹パルプの場合、酸処理時のpHを2.5〜3.5とすると、酸処理の温度を下げることが可能であり、酸処理コストを低減できるという効果が生じてくる。 酸処理は大気圧下、加圧下のいずれでも実施可能であり、処理温度としては80℃〜180℃、好ましくは80℃〜130℃である。温度が30℃以上かつ80℃未満では金属除去の面では効果はあるが、ヘキセンウロン酸等の除去効果がない。なお、100℃未満であれば耐圧性の反応容器を必要としないので設備コスト的に有利である。   The acid used for the acid treatment of the present invention may be an inorganic acid or an organic acid. As the inorganic acid, mineral acids such as sulfuric acid, hydrochloric acid, nitric acid, sulfurous acid, nitrous acid, phosphoric acid, and residual acid of chlorine dioxide generator can be used. Sulfuric acid is preferred. As the organic acid, acetic acid, lactic acid, succinic acid, citric acid, formic acid and the like can be used. The pH during the acid treatment is in the range of 1.0 to 6.0, preferably 1.0 to 5.0, more preferably 2.0 to 5.0, optimally 2.5 to 3.5. It is. When the pH is less than 1.0, the removal of hexeneuronic acid and the like and harmful metals is sufficient, but since the acid is excessive, the viscosity decreases greatly. On the other hand, when the pH exceeds 6.0, the acid concentration is low, and the removal of hexeneuronic acid and the like and harmful metals becomes insufficient. In the case of hardwood pulp having a large amount of hexeneuronic acid, if the pH during acid treatment is 2.5 to 3.5, the temperature of the acid treatment can be lowered, and the effect of reducing the acid treatment cost is produced. The acid treatment can be carried out under atmospheric pressure or under pressure, and the treatment temperature is 80 ° C. to 180 ° C., preferably 80 ° C. to 130 ° C. If the temperature is 30 ° C. or higher and lower than 80 ° C., the metal removal is effective, but there is no removal effect of hexeneuronic acid or the like. In addition, if it is less than 100 degreeC, since a pressure-resistant reaction container is not required, it is advantageous at an equipment cost.

酸処理時のパルプ濃度は、0.1〜50重量%の範囲であり、好ましくは1.0〜30重量%、更に好ましくは2.0〜20重量%である。
ヘキセンウロン酸等と有害金属の除去効果は、酸処理時のpH、反応温度、および反応時間で決定される。これより、反応時間は他の2条件に合わせて適宜設定されるが、反応温度90℃での反応時間1.5〜6時間、反応温度95℃での反応時間50分間〜5時間、反応温度100℃での反応時間30分間〜4.5時間、反応温度120〜130℃での反応時間5〜50分間が典型とされている。
The pulp concentration during acid treatment is in the range of 0.1 to 50% by weight, preferably 1.0 to 30% by weight, and more preferably 2.0 to 20% by weight.
The effect of removing hexeneuronic acid and the like and harmful metals is determined by the pH during the acid treatment, the reaction temperature, and the reaction time. From this, the reaction time is appropriately set according to the other two conditions, but the reaction time at a reaction temperature of 90 ° C. is 1.5 to 6 hours, the reaction time at a reaction temperature of 95 ° C. is 50 minutes to 5 hours, the reaction temperature Typical reaction times are 30 minutes to 4.5 hours at 100 ° C., and reaction times 5 to 50 minutes at a reaction temperature of 120 to 130 ° C.

また、酸性条件下で行われるオゾン漂白も、本願の対象とする酸処理の一形態であり、通常の酸性オゾン漂白の条件が適用できる。ちなみに、一般的な酸性オゾン漂白の条件は、オゾン濃度1〜20重量%のオゾンガスを用いて、pH1.0〜8.0、パルプ濃度0.1〜50重量%、温度は25〜95℃、が好適とされている。また、ここでの圧力についても負圧の状態から加圧された状態まで特に限定されない。   In addition, ozone bleaching performed under acidic conditions is a form of acid treatment targeted by the present application, and normal acidic ozone bleaching conditions can be applied. By the way, the conditions of general acidic ozone bleaching are: pH 1.0-8.0, pulp concentration 0.1-50% by weight, temperature 25-95 ° C., using ozone gas with ozone concentration 1-20% by weight, Is preferred. Further, the pressure here is not particularly limited from a negative pressure state to a pressurized state.

なお、酸処理に際しては、EDTA、DPTA等のキレート剤を併用することにより、光照射処理における更に大きな漂白反応促進効果が得られる。
酸処理の結果、その後の紫外光及び/又は可視光の光照射処理において漂白効果が促進される理由は明白ではないが、パルプ中の残留リグニンと金属イオン、特に鉄イオンとが金属錯体を形成し、これが光照射処理によって着色化する。従って、酸処理によって金属イオンを除去することによって光照射処理による漂白効果が向上すると推察される。
In addition, in the acid treatment, by using a chelating agent such as EDTA or DPTA in combination, a greater bleaching reaction promoting effect in the light irradiation treatment can be obtained.
The reason why the bleaching effect is promoted in the subsequent UV and / or visible light irradiation treatment as a result of acid treatment is not clear, but residual lignin in the pulp and metal ions, especially iron ions, form metal complexes. However, this is colored by the light irradiation treatment. Therefore, it is presumed that the bleaching effect by the light irradiation treatment is improved by removing the metal ions by the acid treatment.

本発明において、オゾンを含む酸処理の後に、処理パルプの脱水及び/又は洗浄を行うが、これらはパルプ製造において公知の脱水機及び/又は洗浄機を用いることができる。また、洗浄には新水のほか、酸処理以降の漂白工程で発生する漂白排水や抄紙工程から発生する抄紙排水等を使用することができる。   In the present invention, after the acid treatment including ozone, the treated pulp is dehydrated and / or washed, and these may be a known dehydrator and / or washer used in pulp production. In addition to fresh water, bleaching wastewater generated in the bleaching process after the acid treatment, papermaking wastewater generated from the papermaking process, and the like can be used for washing.

本発明においては、前記酸処理したパルプに対して、アルカリ性条件下で、波長100〜400nmの紫外光及び/又は可視光を照射するが、アルカリ性条件としては、pHは10〜13である。広葉樹パルプを処理とする場合には、pH10〜12が、また針葉樹パルプを処理とする場合には、pH11〜13が特に好ましい。なお、このpH調整のために使用するアルカリとしては、通常のアルカリ性薬剤が使用可能であるが、取扱い易さ等の点からNaOH、KOH、珪酸Na、炭酸Naが、特に好ましい。   In the present invention, the acid-treated pulp is irradiated with ultraviolet light and / or visible light having a wavelength of 100 to 400 nm under alkaline conditions, and the pH is 10 to 13 as alkaline conditions. When treating hardwood pulp, pH 10-12 is particularly preferred, and when treating softwood pulp, pH 11-13 is particularly preferred. In addition, as an alkali used for this pH adjustment, a normal alkaline chemical | medical agent can be used, However NaOH, KOH, silicate Na, and Na carbonate are especially preferable from points, such as easiness of handling.

本発明の光照射処理時の、パルプ濃度は0.1〜12重量%が好ましい。0.1重量%未満では漂白反応効率は高くなるものの、エネルギー効率が低下するため好ましくない。12重量%を超える場合には、照射装置内でのパルプスラリ−の流動性が悪くなるため、漂白反応効率が低下するため好ましくない。   The pulp concentration during the light irradiation treatment of the present invention is preferably 0.1 to 12% by weight. If it is less than 0.1% by weight, the efficiency of the bleaching reaction is increased, but the energy efficiency is lowered, which is not preferable. When the content exceeds 12% by weight, the fluidity of the pulp slurry in the irradiation device is deteriorated, so that the bleaching reaction efficiency is lowered, which is not preferable.

また、この照射処理時の、パルプスラリーの温度は20〜95℃が好ましく、20℃未満では漂白反応効率が低く、また一方、95℃を超える場合には、パルプ品質悪化の可能性がでてくることや、あるいは反応装置内圧力が大気圧を超える可能性がでてくるため、耐圧性を考慮した装置設計が必要となるなど点で、いずれも好ましくない。   Moreover, the temperature of the pulp slurry at the time of this irradiation treatment is preferably 20 to 95 ° C, and if it is less than 20 ° C, the bleaching reaction efficiency is low. On the other hand, if it exceeds 95 ° C, the pulp quality may be deteriorated. Neither is it preferable to design an apparatus that takes pressure resistance into consideration, or the reactor internal pressure may exceed atmospheric pressure.

本発明の照射装置において、照射する光の波長としては、100〜400nmの波長が好ましいが、200〜360nmの波長が特に好ましい。100nm未満の波長では、セルロースの光分解が促進されるためパルプ強度が著しく低下し、また400nmを超える波長では、光着色物質の光励起が不十分であるため光漂白性が大幅に低下するので、いずれも好ましくない。   In the irradiation apparatus of the present invention, the wavelength of light to be irradiated is preferably a wavelength of 100 to 400 nm, but a wavelength of 200 to 360 nm is particularly preferable. When the wavelength is less than 100 nm, the pulp strength is remarkably reduced because the photodegradation of cellulose is promoted, and when the wavelength exceeds 400 nm, the photobleaching property is greatly reduced because the photoexcitation of the photo-colored substance is insufficient. Neither is preferred.

照射する光源としては、100〜400nmの波長領域の光を持つものが使用でき、具体的には、キセノンショートアークランプ、超高圧水銀ランプ、高圧水銀ランプ、低圧水銀ランプ、重水素ランプ、メタルハライドランプ等〔木下忍「UV照射装置」、接着(2002年、46巻7号)p20〜27、あるいは杉森彰「光化学 第8章光化学の実験方法I」、(裳華房、1998年発行)p126〜136、参照〕が一例として挙げられ、これらの1種あるいは2種以上を任意に組合せて使用することができる。   As a light source for irradiation, a light source having a wavelength in the range of 100 to 400 nm can be used. Specifically, a xenon short arc lamp, an ultrahigh pressure mercury lamp, a high pressure mercury lamp, a low pressure mercury lamp, a deuterium lamp, a metal halide lamp. Etc. [Kinoshita Shinobu "UV Irradiation Device", Adhesion (2002, Vol. 46, No. 7) p20-27, or Sugimori Akira "Photochemistry Chapter 8, Experimental Method I of Photochemistry", (Suikabo, 1998) p126- 136, see] is an example, and one or more of these can be used in any combination.

また、照射反応装置においてパルプが受ける照射の程度は、照射反応装置内でのパルプの滞留時間を調節することや、照射光源のエネルギー量を調節すること等により、任意に設定できる。照射反応装置内でのパルプの滞留時間調節の具体的な一例を挙げれば、照射装置内のパルプ濃度を水希釈によって調節することや、あるいは空気や窒素等の不活性気体をパルプスラリー中に吹き込むことによってパルプ濃度を調節することなどである。これらの条件は、目標とする光照射反応後のパルプ品質(白色度等)にあわせて、適宜設定できる。   Further, the degree of irradiation received by the pulp in the irradiation reactor can be arbitrarily set by adjusting the residence time of the pulp in the irradiation reactor, adjusting the energy amount of the irradiation light source, or the like. Specific examples of adjusting the residence time of pulp in the irradiation reactor include adjusting the pulp concentration in the irradiation device by diluting with water, or blowing an inert gas such as air or nitrogen into the pulp slurry. For example, adjusting the pulp concentration. These conditions can be appropriately set in accordance with the pulp quality (whiteness etc.) after the target light irradiation reaction.

また、135〜242nmの波長領域の光を照射する場合、光源周辺の気層部には通常空気が存在するためオゾンが生成する。本発明においては、この光源周辺部に連続的に空気を供給する一方で、生成するオゾンを連続的に抜き出し、光照射原料に注入することにより、系外からオゾンを供給すること無しに、反応の助剤としてオゾンを利用することができる。また更に、光源周辺の気層部に酸素を供給することにより更に大量のオゾンを得ることができる。もちろん、発生したオゾンは、光照射反応時の助剤としてだけでなく、通常のオゾン漂白にも使用できる。このように、本発明では、光照射反応装置で副次的に発生するオゾンを利用できることも大きな利点である。   In addition, when irradiating light in the wavelength region of 135 to 242 nm, ozone is generated because air usually exists in the air layer around the light source. In the present invention, while continuously supplying air to the periphery of the light source, the generated ozone is continuously extracted and injected into the light irradiation raw material, so that the reaction can be performed without supplying ozone from outside the system. Ozone can be used as an auxiliary agent. Furthermore, a larger amount of ozone can be obtained by supplying oxygen to the gas layer around the light source. Of course, the generated ozone can be used not only as an auxiliary agent in the light irradiation reaction but also in normal ozone bleaching. As described above, in the present invention, it is also a great advantage that ozone generated secondary by the light irradiation reaction apparatus can be used.

この考え方を更に積極的に応用して、光照射反応装置に用いる光源を、波長100〜400nmに特性波長領域を持ち、かつ特性波長の異なる光源のうちから複数を選定して用いることができる。具体的には、オゾン発生効率の高い135〜242nmの狭い波長特性を持つ光源と、光照射反応に適した100〜400nmの波長領域をまんべんなく持つ光源との組合せ等であり、これにより更に高い漂白効率を得ることができる。   By applying this concept more actively, a plurality of light sources used in the light irradiation reaction apparatus can be selected from light sources having a characteristic wavelength region in the wavelength range of 100 to 400 nm and having different characteristic wavelengths. Specifically, it is a combination of a light source having a narrow wavelength characteristic of 135 to 242 nm, which has high ozone generation efficiency, and a light source having a wavelength region of 100 to 400 nm suitable for light irradiation reaction. Efficiency can be obtained.

また、本発明の光照射処理においては、助剤として、還元剤(NaBH4、ヒドラジン、水素)、酸化剤(酸素、オゾン)、過酸化物(過酸化水素、過酢酸、過炭酸Na、過ホウ酸Na)、水素供与性有機化合物(アルコール、鎖状アミンとして、エチルアミン、ジエチルアミン、また環状アミンとして、テトラメチルピペリジン)、アセチル基を有する有機化合物(α−アセチル−γ−ブチロラクトン、アセトール、アセトン)を併用して、照射反応効率を高めることができる。 In the light irradiation treatment of the present invention, as an auxiliary agent, a reducing agent (NaBH 4 , hydrazine, hydrogen), an oxidizing agent (oxygen, ozone), a peroxide (hydrogen peroxide, peracetic acid, sodium percarbonate, hydrogen peroxide) Boric acid Na), hydrogen donating organic compound (alcohol, chain amine, ethylamine, diethylamine, cyclic amine, tetramethylpiperidine), organic compound having acetyl group (α-acetyl-γ-butyrolactone, acetol, acetone) ) Can be used in combination to increase the irradiation reaction efficiency.

本発明における光照射反応装置を用いるシステムの一例を、図1に示す。
酸処理されたパルプは、光照射原料調整タンク(10)に受け入れられ、ここで撹拌されながら、光照射反応に適した温度・pH・パルプ濃度に調整される。調整された光照射原料1は、光照射反応装置供給ポンプ(11)により、光照射反応装置(12)に送られる。必要により、その前に、薬液として光照射反応における還元剤等の助剤が添加される。なお、この助剤の添加場所としては、図1の薬液添加場所の他、光照射原料調整タンク(10)、あるいは両方であっても良く、助剤の性質あるいは光照射反応条件にあわせて任意に設定できるが、迅速に反応する助剤あるいはそれ自体分解性の高い助剤については、できるだけ光照射反応装置(12)に入る直前、すなわち図1の薬液添加場所に添加することが好ましい。
An example of a system using the light irradiation reaction apparatus in the present invention is shown in FIG.
The acid-treated pulp is received in the light irradiation raw material adjustment tank (10), and is adjusted to a temperature, pH, and pulp concentration suitable for the light irradiation reaction while being stirred here. The adjusted light irradiation raw material 1 is sent to the light irradiation reaction device (12) by the light irradiation reaction device supply pump (11). If necessary, an auxiliary agent such as a reducing agent in the light irradiation reaction is added as a chemical solution before that. In addition to the chemical solution addition site shown in FIG. 1, this auxiliary agent may be added to the light irradiation raw material adjusting tank (10), or both, and may be arbitrarily selected according to the nature of the auxiliary agent or the light irradiation reaction conditions. However, it is preferable to add an auxiliary agent that reacts quickly or an auxiliary agent that is highly decomposable by itself as soon as it enters the light irradiation reactor (12), that is, at the chemical solution addition site in FIG.

また、必要に応じて、光照射反応装置(12)に入る前に、気体を供給することができる。これにより、光照射反応装置(12)内でのパルプ濃度(この場合、気体の密度が小さいので、容量%として考慮)の調整が可能となるため、光照射反応装置(12)内でのパルプの滞留時間あるいは照射反応時間を任意に調整できる。なお、この場合に用いる気体の種類としては、空気あるいは窒素等の不活性気体が好適であり、これらを微細気泡としてパルプスラリー中に分散して用いる。また、光反応の助剤のうち、水素、酸素、オゾン等の気体を用いる場合にも、同様に図Eの場所に供給することができる。   Further, if necessary, a gas can be supplied before entering the light irradiation reactor (12). This makes it possible to adjust the pulp concentration in the light irradiation reactor (12) (in this case, since the density of the gas is small, so it is considered as volume%), so the pulp in the light irradiation reactor (12) The residence time or irradiation reaction time can be arbitrarily adjusted. In addition, as a kind of gas used in this case, inert gas, such as air or nitrogen, is suitable, and these are disperse | distributed and used in a pulp slurry as a fine bubble. Moreover, also when using gas, such as hydrogen, oxygen, ozone, among the assistants of photoreaction, it can supply to the place of FIG. E similarly.

次に、光照射反応装置(12)を出た光照射反応後のパルプは、目標とするパルプ品質が得られたものについては、光照射反応を終了し次工程へ送る(C1: 光照射反応後のパルプ1)。また、一方目標とするパルプ品質が得られなかったものについては、光照射反応を繰返すため再循環する(C2:光照射反応後のパルプ2)。この、C1とC2の比率に関しては、目標とするパルプ品質に対応させて、任意に設定することができる。   Next, as for the pulp after the light irradiation reaction that has exited the light irradiation reaction device (12), the light irradiation reaction is terminated and sent to the next process for those for which the target pulp quality is obtained (C1: light irradiation reaction). Later pulp 1). On the other hand, the pulp whose target pulp quality is not obtained is recycled to repeat the light irradiation reaction (C2: pulp 2 after the light irradiation reaction). The ratio between C1 and C2 can be arbitrarily set according to the target pulp quality.

なお、照射反応装置については、基本的には照射光源部とパルプスラリー容器部から構成され、照射光源部がパルプスラリー容器部の内部に存在する内部照射型と、照射光源部がパルプスラリー容器部の外部に存在する外部照射型とがあるが〔杉森彰「光化学 第8章光化学の実験方法I」、(裳華房、1998年発行)p126〜136、参照〕、本発明においては、特に限定されない。また、照射光源部からの光がパルプスラリーに照射されるが、通常、光源部周辺には空気等の気体が存在するため隔壁が必要である。その際、光エネルギーが減衰することなく隔壁を透過するために、隔壁材質の選定が重要である。   The irradiation reaction apparatus basically includes an irradiation light source part and a pulp slurry container part, and the irradiation light source part exists inside the pulp slurry container part, and the irradiation light source part is a pulp slurry container part. [See Akira Sugimori “Photochemistry Chapter 8, Experimental Method I for Photochemistry” (Isaka Hanafusa, 1998) p126-136], but in the present invention, it is particularly limited. Not. Moreover, although the light from an irradiation light source part is irradiated to a pulp slurry, since gas, such as air, exists normally around a light source part, a partition is required. At that time, it is important to select a material for the partition wall so that the light energy is transmitted through the partition wall without being attenuated.

本発明において、例えば、300nmより長波長の光を用いる場合は、硬質ガラス製のものを用いることができるが、254nmより短波長の光を用いる場合は、石英ガラス製のものを用いる。なお、このパルプスラリー容器の光透過反応に関与しない部分の材質については、用いる光の波長に対して劣化の少ない材質の中から適切なものを選定することができる。   In the present invention, for example, when light having a wavelength longer than 300 nm is used, one made of hard glass can be used. When using light having a wavelength shorter than 254 nm, one made of quartz glass is used. In addition, about the material of the part which does not participate in the light transmission reaction of this pulp slurry container, a suitable thing can be selected from the materials with little deterioration with respect to the wavelength of the light to be used.

光照射反応装置の一例を図2に示す。酸処理されたパルプを光照射反応に適した温度・pH・パルプ濃度に調整し、更に必要により還元剤等の助剤を添加した後、スラリー(a1)として、この反応層(20)に(25)より注入される。注入されたパルプスラリーは、装置(20)内で流動しながら、光照射光源(22)で発生し隔壁(21:石英ガラス管)を通過した光による照射反応を行った後、装置出口(26)から排出される。   An example of the light irradiation reaction apparatus is shown in FIG. The acid-treated pulp is adjusted to a temperature, pH, and pulp concentration suitable for the light irradiation reaction, and further, if necessary, an auxiliary such as a reducing agent is added to the reaction layer (20) as a slurry (a1). 25). The injected pulp slurry flows in the apparatus (20), undergoes an irradiation reaction with light generated by the light irradiation light source (22) and passed through the partition wall (21: quartz glass tube), and then the apparatus outlet (26 ).

また、必要に応じて、光照射反応装置(20)に付設される散気装置(24)を通じて、気体を供給することができる。これにより、光照射反応装置(20)内でのパルプ濃度(この場合、気体の密度が小さいので、容量%として考慮)の調整が可能となるため、光照射反応装置(20)内でのパルプの滞留時間あるいは照射反応時間を任意に調整できる。なお、この目的で用いる気体の種類としては、空気あるいは窒素等の不活性気体が好適であり、これらを微細気泡としてパルプスラリー中に分散して用いる。   Moreover, gas can be supplied as needed through the diffuser (24) attached to a light irradiation reaction apparatus (20). This makes it possible to adjust the pulp concentration in the light irradiation reactor (20) (in this case, since the density of the gas is small, so it is considered as volume%), so the pulp in the light irradiation reactor (20) The residence time or irradiation reaction time can be arbitrarily adjusted. In addition, as a kind of gas used for this purpose, inert gas, such as air or nitrogen, is suitable, and these are disperse | distributed and used in a pulp slurry as a fine bubble.

一方、光反応の助剤のうち、水素、酸素、オゾン等の気体を用いる場合にも、この散気装置(24)を通じて、気体を供給することができる。
また、図2に示す様に、光照射光源として135〜242nmの波長領域の光を用い、光源冷却用気体(b1)として、空気あるいは酸素を注入した場合、光照射部から排出される気体中にはオゾンが存在する。このオゾンを含む排出ガスは、散気装置(24)を通じて光照射反応装置(20)内のパルプスラリー中に注入することにより、系外からオゾンを供給すること無しに、反応の助剤としてオゾンを利用することができる。また、発生したオゾンは、光照射反応時の助剤以外の通常のオゾン漂白にも使用できる。また水素、酸素、オゾン等の光照射反応の助剤として効果のある気体を系外から注入し、併用することもできる。これら気体の利用に関しては、三方弁(23a、23b)を付設することにより任意に設定できる。
On the other hand, also when using gas, such as hydrogen, oxygen, ozone, among the assistants of photoreaction, gas can be supplied through this diffuser (24).
In addition, as shown in FIG. 2, when light having a wavelength region of 135 to 242 nm is used as a light irradiation light source and air or oxygen is injected as a light source cooling gas (b1), There is ozone. The exhaust gas containing ozone is injected into the pulp slurry in the light irradiation reactor (20) through the air diffuser (24), so that ozone can be used as a reaction aid without supplying ozone from outside the system. Can be used. The generated ozone can also be used for ordinary ozone bleaching other than the auxiliary agent during the light irradiation reaction. In addition, a gas having an effect as an auxiliary agent for the light irradiation reaction such as hydrogen, oxygen and ozone can be injected from outside the system and used in combination. Use of these gases can be arbitrarily set by attaching three-way valves (23a, 23b).

なお、光照射反応装置において、温度・pHの調節装置、ガス濃度検出装置等の付帯設備を必要に応じて任意に付設することができる。
また、本発明の光照射処理は1回以上複数回繰り返すことができるが、これは漂白効率や目標とするパルプ品質(白色度)、あるいは組合せる他の漂白方法との関係等の状況にあわせて適宜設定できる。光照射処理は1回以上複数回繰り返す例は、(1)図1における光照射装置を2個以上設けることができる。この場合には、シリーズであっても、パラレルであってもよい。(2)図1における光照射装置の中に照射光源を複数個(特性の同じものでも、異なるものでもよい)設けることができる。(3)図1に示されるシステム内を再循環することができる。
In addition, in the light irradiation reaction apparatus, ancillary equipment such as a temperature / pH adjusting device, a gas concentration detecting device and the like can be arbitrarily attached as necessary.
In addition, the light irradiation treatment of the present invention can be repeated one or more times, but this is in accordance with the situation such as bleaching efficiency, target pulp quality (whiteness), or the relationship with other bleaching methods to be combined. Can be set as appropriate. Examples in which the light irradiation treatment is repeated one or more times are as follows: (1) Two or more light irradiation devices in FIG. 1 can be provided. In this case, it may be a series or parallel. (2) A plurality of irradiation light sources (having the same characteristics or different characteristics) may be provided in the light irradiation apparatus in FIG. (3) The system shown in FIG. 1 can be recirculated.

本発明の漂白方法は、塩素系、非塩素系を問わず他の全ての公知の漂白方法と任意に組合せることができる。具体的には、他の漂白方法に続いて本発明の漂白方法とする、あるいは、本発明の漂白方法に続いて他の漂白方法とすることができる。特に、本発明の漂白を行った後、過酸化水素処理をすることが、好ましい。また、これらのシーケンスを複数回繰り返すこともでき、その際、異なる漂白方法のと間に洗浄段を設けることもできる。また、光照射システムを組み込んだ漂白シーケンスを複数回繰り返すこともできる。なお、光照射処理を複数行う際には、光照射処理後に、洗浄を行うことが好ましい。   The bleaching method of the present invention can be arbitrarily combined with all other known bleaching methods regardless of chlorine or non-chlorine. Specifically, the bleaching method of the present invention can be followed by another bleaching method, or another bleaching method can be performed following the bleaching method of the present invention. In particular, it is preferable to perform a hydrogen peroxide treatment after the bleaching of the present invention. Further, these sequences can be repeated a plurality of times, and at this time, a washing stage can be provided between different bleaching methods. In addition, the bleaching sequence incorporating the light irradiation system can be repeated a plurality of times. In addition, when performing multiple light irradiation processes, it is preferable to wash | clean after a light irradiation process.

次に実施例に基づき、本発明をさらに詳細に説明するが、本発明はこれら
に限定されるものではない。
〈パルプ物性の測定〉
カッパー価の測定 カッパー価の測定:JIS P 8211に準じて行った。
EXAMPLES Next, although this invention is demonstrated further in detail based on an Example, this invention is not limited to these.
<Measurement of pulp properties>
Measurement of kappa number Measurement of kappa number: Measured according to JIS P 8211.

パルプの白色度測定:パルプを離解後、Tappi試験法T205os−71(JIS P 8209)に従って坪量60g/m2のシートを作製し、JIS
P 8148に準じてパルプの白色度を測定した。
〈実験装置〉
本願実施例で用いた実験装置を図3に示した。
Pulp whiteness measurement: After the pulp was disaggregated, a sheet having a basis weight of 60 g / m 2 was prepared according to Tappi test method T205os-71 (JIS P 8209).
The whiteness of the pulp was measured according to P8148.
<Experimental device>
The experimental apparatus used in the examples of the present application is shown in FIG.

光照射反応槽(1)として、3Lガラス製シリンダー(100mmφ×620mmH)を用いた。この光照射反応槽(1)には、図に示す攪はん機(4)、散気管(5)の他、温度調節装置並びにpH測定器を備えている。また、光照射光源(16W低圧水銀ランプ、日本フォトサイエンス社製AY−1)は、石英ガラス管(45mmφ×470mmH、厚さ2mm)内に設置し、光照射光源周辺には、空気を注入できる構造となっている。   A 3 L glass cylinder (100 mmφ × 620 mmH) was used as the light irradiation reaction tank (1). In addition to the agitator (4) and diffuser pipe (5) shown in the figure, the light irradiation reaction tank (1) is provided with a temperature control device and a pH measuring device. A light irradiation light source (16W low-pressure mercury lamp, AY-1 manufactured by Nippon Photo Science Co., Ltd.) is installed in a quartz glass tube (45 mmφ × 470 mmH, thickness 2 mm), and air can be injected around the light irradiation light source. It has a structure.

[実施例1]
日本製紙株式会社製の広葉樹酸素脱リグニン後のクラフトパルプ(カッパー価11.6、ISO白色度45.6%)を用いた。
[Example 1]
Kraft pulp (kappa number 11.6, ISO whiteness 45.6%) after hardwood oxygen delignification manufactured by Nippon Paper Industries Co., Ltd. was used.

以下の条件で酸処理を行い、カッパー価5.5、白色度47.5%のパルプを得た。
酸処理条件:パルプ濃度10重量%、pH3.0(硫酸使用)温度95℃、処理時間180分。処理終了後、パルプを水洗した。
Acid treatment was performed under the following conditions to obtain a pulp having a copper number of 5.5 and a whiteness of 47.5%.
Acid treatment conditions: Pulp concentration 10% by weight, pH 3.0 (using sulfuric acid) temperature 95 ° C., treatment time 180 minutes. After completion of the treatment, the pulp was washed with water.

このようにして得られた酸処理パルプの5g(絶乾)採り、パルプ濃度を0.25重量%とした後、NaOH及びH2SO4を用いて酸性〜アルカリ性領域にわたるpHのパルプスラリーを調整した。これらのスラリーを図3の実験装置に注入し、撹拌しながら、温度25℃、処理時間120分、254nmに主波長を持つ低圧紫外線ランプを使用の条件で光照射反応を行った。反応を終了したパルプは、洗浄した後、シートを作成し白色度を測定した。結果を図4及び表1に示した。図4中、光照射反応における処理pHが10〜13のパルプスラリー(3サンプル)を実施例1とし、10未満のパルプスラリーを参考例1(4サンプル)とした。 After taking 5 g (absolutely dry) of the acid-treated pulp thus obtained and adjusting the pulp concentration to 0.25% by weight, a pulp slurry having a pH ranging from acidic to alkaline is adjusted using NaOH and H 2 SO 4. did. These slurries were poured into the experimental apparatus shown in FIG. 3, and a light irradiation reaction was performed under the conditions of using a low-pressure ultraviolet lamp having a main wavelength of 254 nm at a temperature of 25 ° C. and a treatment time of 120 minutes while stirring. After the reaction, the pulp was washed and then a sheet was prepared to measure the whiteness. The results are shown in FIG. In FIG. 4, pulp slurry (3 samples) having a treatment pH in the light irradiation reaction of 10 to 13 was set as Example 1, and pulp slurry of less than 10 was set as Reference Example 1 (4 samples).

[実施例2]
実施例1と同じ広葉樹酸素脱リグニン後のクラフトパルプを用いて、以下の条件でオゾン処理を行い、カッパー価3.0、白色度56.6%のパルプを得た。
[Example 2]
Using the same hardwood oxygen delignified kraft pulp as in Example 1, ozone treatment was performed under the following conditions to obtain a pulp having a copper number of 3.0 and a whiteness of 56.6%.

オゾン処理条件:パルプ濃度10%、オゾン添加量7kg/ADTP、温度50℃、処理時間30秒、pH2.5(硫酸使用)。
このようにして得られたオゾン処理パルプの5g(絶乾)採り、実施例1と同様な条件で、酸性〜アルカリ性領域にわたるpHのパルプスラリー調整、及び光照射反応を行なった後、得られたパルプの白色度を測定した。結果を図4及び表1に示した。図4中、光照射反応における処理pHが10〜13のパルプスラリー(3サンプル)を実施例2とし、10未満のパルプスラリーを参考例2(4サンプル)とした。
Ozone treatment conditions: pulp concentration 10%, ozone addition amount 7 kg / ADTP, temperature 50 ° C., treatment time 30 seconds, pH 2.5 (using sulfuric acid).
It was obtained after taking 5 g (absolutely dry) of the ozone-treated pulp thus obtained, adjusting the pulp slurry at a pH ranging from acidic to alkaline under the same conditions as in Example 1, and performing light irradiation reaction. The whiteness of the pulp was measured. The results are shown in FIG. In FIG. 4, pulp slurry (3 samples) having a treatment pH in the light irradiation reaction of 10 to 13 was set as Example 2, and pulp slurry of less than 10 was set as Reference Example 2 (4 samples).

[比較例1]
実施例1と同じ広葉樹酸素脱リグニン後のクラフトパルプの5g(絶乾)採り、実施例1と同様な条件で、酸性〜アルカリ性領域にわたるpHのパルプスラリー調整、及び光照射反応を行なった後、得られたパルプの白色度を測定した。結果を図4及び表1に示した。
[Comparative Example 1]
After taking 5 g (absolutely dry) of kraft pulp after broad-leaved oxygen delignification as in Example 1, under the same conditions as in Example 1, adjusting the pH slurry slurry in the acidic to alkaline region, and performing a light irradiation reaction, The whiteness of the obtained pulp was measured. The results are shown in FIG.

Figure 0004603298
Figure 0004603298

[実施例3]
実施例1と同じ酸処理パルプの5g(絶乾)採り、パルプ濃度を0.25重量%とした後、(NaOH及びH2SO4を用いて)pH11.5のパルプスラリーを調整した。このスラリーを図3の実験装置に注入し、撹拌しながら、温度25℃、254nmに主波長を持つ低圧紫外線ランプを使用の条件で、処理時間を変えた光照射反応を行った。反応を終了したパルプは、洗浄した後、シートを作成し白色度を測定した。結果を図5及び表2に示した。
[Example 3]
After taking 5 g (absolutely dry) of the same acid-treated pulp as in Example 1 and setting the pulp concentration to 0.25% by weight, a pulp slurry having a pH of 11.5 was prepared (using NaOH and H 2 SO 4 ). This slurry was poured into the experimental apparatus shown in FIG. 3, and a light irradiation reaction was carried out under stirring at a temperature of 25 ° C. under a condition that a low-pressure ultraviolet lamp having a dominant wavelength at 254 nm was used. After the reaction, the pulp was washed and then a sheet was prepared to measure the whiteness. The results are shown in FIG.

[実施例4]
実施例2と同じオゾン処理パルプの5g(絶乾)採り、実施例3と同様な条件で、処理時間を変えた光照射反応を行ない白色度を測定した。結果を図5及び表2に示す。
[Example 4]
5 g (absolutely dry) of the same ozone-treated pulp as in Example 2 was taken, and under the same conditions as in Example 3, a light irradiation reaction was performed while changing the treatment time, and the whiteness was measured. The results are shown in FIG.

[比較例2]
比較例1と同じ広葉樹酸素脱リグニン後のクラフトパルプの5g(絶乾)採り、実施例3と同様な条件で、処理時間を変えた光照射反応を行ない白色度を測定した。結果を図5及び表2に示した。
[Comparative Example 2]
5 g (absolutely dry) of kraft pulp after the broad-leaved tree oxygen delignification as in Comparative Example 1 was taken, and under the same conditions as in Example 3, a light irradiation reaction was performed with varying treatment time, and the whiteness was measured. The results are shown in FIG.

Figure 0004603298
Figure 0004603298

[実施例5]
日本製紙株式会社製の針葉樹酸素脱リグニン後のクラフトパルプ(カッパー価9.1、ISO白色度33.3%)を用いた。
[Example 5]
Kraft pulp (copper number 9.1, ISO whiteness 33.3%) after coniferous oxygen delignification manufactured by Nippon Paper Industries Co., Ltd. was used.

以下の条件で酸処理を行い、カッパー価9.1、白色度34.3%のパルプを得た。
酸処理条件:パルプ濃度10重量%、pH3(硫酸添加)温度95℃、処理時間180分。処理終了後、パルプを水洗した。
Acid treatment was performed under the following conditions to obtain a pulp having a kappa number of 9.1 and a whiteness of 34.3%.
Acid treatment conditions: Pulp concentration 10% by weight, pH 3 (sulfuric acid addition) temperature 95 ° C., treatment time 180 minutes. After completion of the treatment, the pulp was washed with water.

このようにして得られた酸処理パルプの5g(絶乾)採り、パルプ濃度を0.25重量%とした後、NaOH及びH2SO4を用いて酸性〜アルカリ性領域にわたるpHのパルプスラリーを調整した。これらのスラリーを図3の実験装置に注入し、撹拌しながら、温度25℃、処理時間120分、254nmに主波長を持つ低圧紫外線ランプを使用の条件で光照射反応を行った。反応を終了したパルプは、洗浄した後、シートを作成し白色度を測定した。結果を図5及び表3に示した。 After taking 5 g (absolutely dry) of the acid-treated pulp thus obtained and adjusting the pulp concentration to 0.25% by weight, a pulp slurry having a pH ranging from acidic to alkaline is adjusted using NaOH and H 2 SO 4. did. These slurries were poured into the experimental apparatus shown in FIG. 3, and a light irradiation reaction was performed under the conditions of using a low-pressure ultraviolet lamp having a main wavelength of 254 nm at a temperature of 25 ° C. and a treatment time of 120 minutes while stirring. After the reaction, the pulp was washed and then a sheet was prepared to measure the whiteness. The results are shown in FIG.

[比較例3]
実施例5と同じ針葉樹酸素脱リグニン後のクラフトパルプの5g(絶乾)採り、実施例5と同様な条件で、酸性〜アルカリ性領域にわたるpHのパルプスラリー調整、及び光照射反応を行なった後、得られたパルプの白色度を測定した。結果を図6及び表3に示した。
[Comparative Example 3]
5 g (absolutely dry) of kraft pulp after coniferous oxygen delignification as in Example 5 was taken, and under the same conditions as in Example 5, after adjusting the pH slurry slurry in the acidic to alkaline region, and performing a light irradiation reaction, The whiteness of the obtained pulp was measured. The results are shown in FIG.

Figure 0004603298
Figure 0004603298

[実施例6]
日本製紙株式会社製の広葉樹酸素脱リグニン後のクラフトパルプ(カッパー価9.5、ISO白色度47.5%)を用いた。
[Example 6]
Kraft pulp (kappa number 9.5, ISO whiteness 47.5%) after hardwood oxygen delignification manufactured by Nippon Paper Industries Co., Ltd. was used.

以下の条件で酸処理を行い、カッパー価5.5、白色度48.6%のパルプを得た。
酸処理条件:パルプ濃度10重量%、pH3(硫酸添加)、温度85℃、処理時間180分。処理終了後、パルプを水洗した。
Acid treatment was performed under the following conditions to obtain a pulp having a copper number of 5.5 and a whiteness of 48.6%.
Acid treatment conditions: Pulp concentration 10% by weight, pH 3 (sulfuric acid added), temperature 85 ° C., treatment time 180 minutes. After completion of the treatment, the pulp was washed with water.

このようにして得られた酸処理パルプの5g(絶乾)採り、パルプ濃度を0.5重量%とした後、NaOHを用いてpH11.5のパルプスラリーを調整した。これらのスラリーを図3の実験装置に注入し、撹拌しながら、温度25℃、処理時間120分、254nmに主波長を持つ低圧紫外線ランプを使用の条件で光照射反応を行った。反応を終了したパルプは、洗浄した後、シートを作成し白色度を測定した。結果を表4に示した。   5 g (absolutely dry) of the acid-treated pulp thus obtained was taken and the pulp concentration was adjusted to 0.5% by weight, and then a pH 11.5 pulp slurry was prepared using NaOH. These slurries were poured into the experimental apparatus shown in FIG. 3, and a light irradiation reaction was performed under the conditions of using a low-pressure ultraviolet lamp having a main wavelength of 254 nm at a temperature of 25 ° C. and a treatment time of 120 minutes while stirring. After the reaction, the pulp was washed and then a sheet was prepared to measure the whiteness. The results are shown in Table 4.

[比較例4]
実施例6と同じ酸処理パルプの15g(絶乾)採り、パルプ濃度を0.5重量%とした後、図3の実験装置に注入し、撹拌しながら、温度25℃、pH11.5で、120分間オゾン処理を行った(光照射光源は不使用)。この間のパルプに対する積算オゾン添加量は、0.7重量%であった。結果を表4に示した。
[Comparative Example 4]
After taking 15 g (absolutely dry) of the same acid-treated pulp as in Example 6 and setting the pulp concentration to 0.5% by weight, it was poured into the experimental apparatus of FIG. 3 and stirred at a temperature of 25 ° C. and a pH of 11.5. Ozone treatment was performed for 120 minutes (no light irradiation light source was used). During this time, the cumulative amount of ozone added to the pulp was 0.7% by weight. The results are shown in Table 4.

[実施例7]
実施例6と同じ酸処理パルプを15g(絶乾)採り、パルプ濃度を0.5重量%とした後、図3の実験装置に注入し、撹拌しながら、温度25℃、pH11.5で、120分間、254nmに主波長を持つ低圧紫外線ランプを使用してオゾン処理と光照射反応を同時に行った。この間のパルプに対する積算オゾン添加量は、0.7重量%であった。結果を表4に示した。
[Example 7]
15 g (absolutely dry) of the same acid-treated pulp as in Example 6 was taken, and the pulp concentration was adjusted to 0.5% by weight. Then, the pulp was poured into the experimental apparatus of FIG. 3 and stirred at a temperature of 25 ° C. and a pH of 11.5. Ozone treatment and light irradiation reaction were simultaneously performed using a low-pressure ultraviolet lamp having a dominant wavelength at 254 nm for 120 minutes. During this time, the cumulative amount of ozone added to the pulp was 0.7% by weight. The results are shown in Table 4.

[実施例8]
実施例1と同じ広葉樹酸素脱リグニン後のクラフトパルプ(カッパー価11.6、ISO白色度45.6%)を用いて、以下の条件でオゾン処理を行い、カッパー価3.0、白色度56.6%のパルプを得た。
[Example 8]
The same kraft pulp after broad-leaved oxygen delignification as in Example 1 (kappa number 11.6, ISO whiteness 45.6%) was subjected to ozone treatment under the following conditions, kappa number 3.0, whiteness 56 .6% pulp was obtained.

オゾン処理条件:パルプ濃度10%、オゾン添加量7kg/ADTP、温度55℃、処理時間30秒、pH2.5。
このようにして得られたオゾン処理パルプの15g(絶乾)採り、パルプ濃度を0.5重量%とした後、図3の実験装置に注入し、撹拌しながら、温度25℃、pH11.5で、120分間、254nmに主波長を持つ低圧紫外線ランプを使用して光照射反応を行った。結果を表4に示した。
Ozone treatment conditions: pulp concentration 10%, ozone addition amount 7 kg / ADTP, temperature 55 ° C., treatment time 30 seconds, pH 2.5.
15 g (absolutely dry) of the ozone-treated pulp thus obtained was taken, and the pulp concentration was adjusted to 0.5% by weight. Then, the pulp was poured into the experimental apparatus of FIG. 3 and stirred at a temperature of 25 ° C. and a pH of 11.5. Then, a light irradiation reaction was performed using a low-pressure ultraviolet lamp having a dominant wavelength at 254 nm for 120 minutes. The results are shown in Table 4.

Figure 0004603298
Figure 0004603298

本発明における照射反応装置を用いるシステムの一例を示す図である。It is a figure which shows an example of the system using the irradiation reaction apparatus in this invention. 本発明で用いる内部照射型の照射反応装置を示す図である。It is a figure which shows the internal irradiation type irradiation reaction apparatus used by this invention. 本発明実施例で用いた内部照射型の照射反応装置を示す図である。It is a figure which shows the internal irradiation type | mold irradiation reaction apparatus used by this invention Example. L材パルプを用いた光照射処理における処理pHと白色度の関係を示した図である。It is the figure which showed the relationship between process pH and whiteness in the light irradiation process using L material pulp. L材パルプを用いた光照射処理における光照射時間と白色度の関係を示した図である。It is the figure which showed the relationship between the light irradiation time in the light irradiation process using L material pulp, and whiteness. N材パルプを用いた光照射処理における処理pHと白色度の関係を示した図である。It is the figure which showed the relationship between process pH and whiteness in the light irradiation process using N material pulp.

符号の説明Explanation of symbols

10:光照射原料調整タンク
11:光照射反応装置供給ポンプ
12:光照射反応装置
20:光照射反応槽
21:石英ガラス管
22:光照射光源
23a,23b:三方弁
24:散気装置、散気管
25:パルプスラリー入口
26:パルプスラリー出口
27:攪拌機
10: Light irradiation raw material adjustment tank 11: Light irradiation reaction apparatus supply pump 12: Light irradiation reaction apparatus 20: Light irradiation reaction tank 21: Quartz glass tube 22: Light irradiation light source 23a, 23b: Three-way valve 24: Air diffuser, diffuser Trachea 25: Pulp slurry inlet 26: Pulp slurry outlet 27: Stirrer

Claims (6)

パルプの漂白方法であって、酸処理後洗浄したパルプを、pH10〜13の範囲であるアルカリ性条件下で、波長100〜400nmの紫外光及び/又は可視光を照射することを特徴とするパルプの漂白方法。 A pulp bleaching method, wherein a pulp washed after acid treatment is irradiated with ultraviolet light and / or visible light having a wavelength of 100 to 400 nm under alkaline conditions in the range of pH 10 to 13. Bleaching method. 前記酸処理が、pH1〜6、温度80℃以上の条件下で行われることを特徴とする請求項1記載のパルプの漂白方法。 The method of bleaching pulp according to claim 1, wherein the acid treatment is performed under conditions of pH 1 to 6 and temperature of 80 ° C or higher. 前記酸処理が、オゾンの存在下、pH1.0〜8.0、温度25〜95℃、の条件下で行われることを特徴とする請求項1記載のパルプの漂白方法。 The method for bleaching pulp according to claim 1, wherein the acid treatment is performed under conditions of pH 1.0 to 8.0 and temperature 25 to 95 ° C in the presence of ozone. 光照射処理が、還元剤、過酸化物、水素供与性有機化合物の群の中から選ばれた少なくとも1種類の化合物の存在下で行われることを特徴とする請求項1〜いずれか記載のパルプの漂白方法。 Light irradiation treatment, a reducing agent, a peroxide, according to claim 1 to 3, wherein any one, characterized in that is carried out in the presence of at least one compound selected from the group of hydrogen-donating organic compound Pulp bleaching method. 前記紫外光及び/又は可視光の照射光源が、波長特性の異なる複数光源からなることを特徴とする請求項1〜いずれか記載パルプの漂白方法。 Claim 1-4 bleaching method of any claimed pulps irradiation light source of the ultraviolet light and / or visible light, characterized in that it consists of different light sources having wavelength characteristics. 光照射処理を複数回繰り返すことを特徴とする請求項1〜いずれか記載のパルプの漂白方法。 Bleaching process according to claim 1-5 pulp according to any one of and repeating a plurality of times of light irradiation treatment.
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JP2593392B2 (en) * 1992-10-20 1997-03-26 本州製紙株式会社 Pulp bleaching method
JP2002088671A (en) * 2000-06-20 2002-03-27 National Institute Of Advanced Industrial & Technology Method for bleaching pulp
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