Chromophores in cellulosics, XVIII. Degradation of the cellulosic key chromophore 5,8-dihydroxy-[1,4]-naphthoquinone under conditions of chlorine dioxide pulp bleaching: a combined experimental and theoretical study

被引:6
作者
Hosoya, Takashi [1 ]
Zwirchmayr, Nele Sophie [2 ]
Klinger, Karl Michael [2 ]
Reiter, Heidemarie [3 ]
Spitzbart, Martin [3 ]
Dietz, Thomas [4 ]
Eibinger, Klaus [5 ]
Kreiner, Wolfgang [6 ]
Mahler, Arnulf Kai [6 ]
Winter, Heribert [6 ]
Roeder, Thomas [7 ]
Potthast, Antje [2 ]
Elder, Thomas [8 ]
Rosenau, Thomas [2 ,9 ]
机构
[1] Kyoto Prefectural Univ, Grad Sch Life & Environm Sci, Sakyo Ku, Shimogamohangi Cho 11-5, Kyoto, Kyoto, Japan
[2] Univ Nat Resources & Life Sci, Dept Chem, Div Chem Renewable Resources, Muthgasse 18, A-1190 Vienna, Austria
[3] Mondi Uncoated Fine & Kraft Paper GmbH, Marxergasse 4A, A-1030 Vienna, Austria
[4] Evonik Degussa, Rodenbacher Chaussee 4, D-63457 Hanau, Germany
[5] Zellstoff Pols AG, Dr Luigi Angeli Str 9, A-8761 Pols, Austria
[6] SAPPI Papier Holding GmbH, Brucker Str 21, A-8101 Gratkorn, Austria
[7] Lenzing AG, Werkstr 2, A-4860 Lenzing, Austria
[8] Forest Serv, USDA, Southern Res Stn, 521 Devall Dr, Auburn, AL 36849 USA
[9] Abo Akad Univ, Johan Gadolin Proc Chem Ctr, Porthansgatan 3, Turku 20500, Finland
关键词
Cellulose; Pulp bleaching; Chromophores; Brightness; Brightness reversion; Yellowing; 5,8-dihydroxy-[1,4]-naphthoquinone; Chlorine dioxide; Ab initio calculations; Density functional theory (DFT); BIOLOGICAL EVALUATION; 1,4-NAPHTHOQUINONE DERIVATIVES; RESIDUAL CHROMOPHORES; ANTIBACTERIAL AGENTS; ANTICANCER AGENTS; ANTIFUNGAL; ACID; IDENTIFICATION; 1,4-QUINONES; OXIDATIONS;
D O I
10.1007/s10570-018-1912-2
中图分类号
TB3 [工程材料学]; TS [轻工业、手工业、生活服务业];
学科分类号
0805 ; 080502 ; 0822 ;
摘要
5,8-Dihydroxy-[1,4]-naphthoquinone (DHNQ) is one of the key chromophores occurring in all types of aged cellulosics. This study investigates the degradation of DHNQ by chlorine dioxide at moderately acidic (pH 3) conditions, corresponding to the conditions of industrial bleaching ("D stage"). The degradation involves three major pathways. As initial reaction, a hydrogen transfer from DHNQ to chlorine dioxide via a PCET mechanism occurs to form a radical DHNQ. and chlorous acid. DHNQ. is then attacked by water to give a pentahydroxynaphthalene radical PHN. that is stabilized by strong delocalization of the non-paired electron into its aromatic ring. PHN. immediately disproportionates to give the observable intermediate 1,2,4,5,8-pentahydroxynapththalene (I), which was comprehensively confirmed by NMR and MS (path A). In the presence of excess ClO2, I is immediately further oxidized into acetic acid, glycolic acid, oxalic acid and CO2 as the final, stable, and non-colored products (path C). In the absence of excess ClO2, elimination of water from I regenerates DHNQ (path B), so that at roughly equimolar DHNQ/ClO2 ratios ClO2 is fully consumed while a major part of DHNQ is recovered. To avoid such DHNQ "recycling" under ClO2 consumption-and to completely degrade DHNQ to colorless degradation products instead-ClO2 must be applied in at least fivefold molar excess relative to DHNQ.
引用
收藏
页码:4941 / 4954
页数:14
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