The Analysis of Alkaline Reserve in Paper after Deacidification by VLADIMIR BUKOVSKY INTRODUCTION The aim of deacidification is the elimination of acids occurring in paper and catalyzing hydrolytic reactions leading to the cleavage of the cellulose fiber, the basic structural substance of paper. Acid in groundwood paper is created by the hydrolysis of aluminum sulphate, one of the substances used in the production of this kind of paper. Another source of acidity is formed by organic acids and acid function groups being able to exchange H+ (or H3O+) ions. These acids and groups are formed in handmade rag paper as well as in groundwood paper by natural ageing and are the components of the cellulose (oxicellulose) molecules, lignin, sizing agents1, or they occur in paper as free lowmolecular, non-volatile2, 3 and low-molecular, slowly volatile degradation products4,5. Another aim of deacidification is the creation in the paper of sufficient alkaline reserve (AR)6,7 to be able to prevent the paper, during several centuries of storage, from becoming acidic, either by natural oxidative degradation, further hydrolysis of aluminum sulphate, which is not removed from paper during deacidification, or by the influence of environmental pollutants. Every deacidification method, either mass or single sheet, results in the creation of such a reserve (usually formed by magnesium carbonate or calcium carbonate). As well as prolonging the lifetime of paper, resistance to outer detrimental factors such as, for example, the dangerous influence of light and acidic air pollution, is closely related to the extent of AR8. The problem we tried to solve in this research was the difficulty of determining in advance, the extent of alkaline reserve left in a paper after a deacidification treatment. This uncertainty is due to the enormous differences to be found in the material generally called „paper", i.e. differences in composition, quality, use, state of ageing, etc. The active element and the concentration of the deacidification substances used to eliminate the acidity of paper, however, are known and can be modified if necessary. MATERIAL AND METHODS Paper samples We used the same paper samples as in our previous work6,8; their composition is not repeated here. These are the samples used for this research: • Nl: Newsprint made in Steti, 1996, Czech Republic; • N2: Newsprint made in Vétrní, 1996, Czech Republic; • C: Newsprint from Croatia, 1942; • H: Newsprint from Hungary, 1881; • Wl: Chromatographic paper Whatman 1 (pure cellulose); Preparation of samples Paper samples measuring 6 x l cm were conditioned for 2 days at 20±l°C and 45% RH and then weighed. They were deacidified for 5 minutes using methano-lic solutions of methylmethoxymagnesium carbonate (MMMC) in different concentrations. The solutions were prepared by diluting the 10% stock solution into weight concentrations of 1%, 2%, 4% and 6% active substance. The 1% solution contained 0.41 mol/1 Mg or MMMC. After deacidification the papers were reconditioned for 2 days at 45% RH, 20±l°C and then weighed again. The alkaline reserve ARg , i.e. gravimetric, which should refer to magnesium carbonate, was calculated as a weight increase. Parallel to this treatment, samples of the same paper were modified only by soaking in pure methanol for 5 minutes. Preparation of water extracts to determine pH and potentiometric titration Water extracts were prepared by weighing the 1x6 cm paper strips cut into small pieces and extracted in 20 ml distilled water (pH 7.0) for 10 minutes at 100°C. After cooling the pH of the extract was measured and a potentiometric titration with 0.02 mol/1 HCl was done during which time the pH was continually measured using a pH-meter M-120 (Mikrotechna, Czech Republic). There were three parallel titrations. Determination of alkaline reserve by potentiometric titration Titrating this preparation and evaluating ∆pH at each 0.05ml addition of the titration solution, 6-7 peaks were found indicating 6-7 equivalent points (EP), Table 1 : pH at the equivalent points found during titration of the acid-base systems provided by deacidifying the samples with 4% and 6% MMMC solution. which most probably refer to the same number of acid-base systems. This number of EP was found in all analyzed samples, i.e. in samples that were deacidified and contained a measurable alkaline reserve. Since there was one significant point in the titration record, the calculation of alkaline reserve was made for the EP area 1-3 (AR1-3) and for the total EP area (AR1-7). The titration curves are given in Fig. 1, pH of the peaks in Table 1. Despite their similarity there was a significant difference in the pH of some EP of paper H. RESULTS AND DISCUSSION When evaluating the alkaline reserve in papers deacidified according to the classic non-aqueous method using MMMC, we tried, using two types of modern and two selected historic newsprints, to suggest procedures that would result in the required alkaline reserve. Additionally, chromatographic pure cellulose paper was submitted to the same analysis. Alkaline reserve: pure cellulose paper W1 Pure cellulose paper is neutral and its end-of-titration is reached at pH 5.2. After deacidification in solutions of various MMMC concentrations the amount of created alkaline reserve was proportional to the concentration of the solutions; the dependence was linear (Table 2, Fig. 2). Even a high increase in pH of the paper extract was related to deacidification. If just 1% MMMC solution was used, the pH reached pH 8.6, and with increasing MMMC concentrations it gradually rose to pH 9.8. The end-of-titration pH value in the range of AR1-3 was the same for various ARs in the paper and the extracts made from them; it ranged from pH 5.7 up to pH 6.0, the average being approximately pH 6.0. Fig. 2: Left column: growth of alkaline reserve after deacidification; : ARg stated by weight; O: AR1-3 stated by titration; •: AR1-7 stated by titration. - Right column: curves marked by • refer to the pH of water extracts before titration. Lowest point • on the ordinate refers to the end-of-titration of papers, which were not deacidified (0% MMMC). Empty columns represent the pH of end-oftitration in the range AR1-3 black columns represent the pH of end-of-titration in the range AR1-7, when titration was completed. Table 2: Alkaline reserve (ARg; weight %) created by deacidifying the papers with MMMC solutions of several concentrations. The end-of-titration pH values in the range of AR1-7 varied from pH 4.0 to pH 4.6. Comparing the ARg amount stated by weighing (weight %) and by titration in the range of AR1-3 (pH EP approximately pH 6.0) it seemed that this titration, despite lower values, approached ARg, i.e. those found by weighing. We can assume that the acid-base systems bound to cellulose account for the difference between the amount of AR1-3 found by titration, the amount of ARg found by weighing (which are very similar) and the amount of AR1-7. This probably even includes the value of pH 5.2 found at the end-oftitration of the pure cellulose paper Wl. Alkaline reserve in newsprints: Paper number N1 The original paper was acid sized with an extract of pH 4.0; its titration in the range of AR1-7 ended at ca. pH 2.2. pH 7.0 of the extract was not achieved by deacidification with MMMC concentrations lower than 1.5%, and pH 9.5 of the extract was not reached until higher concentrations of MMMC (>4%) were used. The end-of-titration of paper in the range of AR1-3, i.e. those papers the pH extract of which had not reached pH 7.0, was completed at between pH 3.4 to pH 4.5. The end-of-titration pH of about pH 6.0 was reached in those papers, the pH extracts of which were higher than pH 7.0, irrespective of the amount of AR. Measured values in the extracts up to the pH 7.0 represent the neutralization of individual acid functional groups in the original paper components. This applies even to very similar ARg. The titration in the range of AR1-7 of papers that were not deacidified because a MMMC solution of lower EP concentration had been used, was very close to pH 2.5-3.1, and the end-of-titration at approximately, pH 4.0-4.2 was reached in papers, the pH extract of which was pH 7.0 or higher, comparable to Wl. We assumed that, in relation to acidic papers, ARg and titration in the range of AR1-3 gave relatively accurate information on the size of AR. AR found by AR1-7 titration was somewhat inaccurate. The difference between ARg, AR1-3 and AR1-7 probably referred to the titration of the acid-based systems of the cellulose and of lignin, or of some other non-cellulosic paper components. Paper N2 The original paper was slightly acidic (pH 5.8) and its end-of-titration (EP) was at pH 4.O. pH 7.0 of the extract was achieved with 1% MMMC solution. The titration curve was similar to that of Nl. When titrating the paper in its water extract in the range of AR1-3 , the EP was reached at pH 4.44.5. The end-of-titration at pH 5.6-6.2 was reached when the AR, created by deacidification using higher concentrations of the MMMC solutions were larger. This is comparable to the situation found for paper Nl. Since there was a very low content of acid groups in this paper (the extract was pH 5.8), the course of the curve of ARg, found by weighing and by titration in the range of AR1-3, was a little different from that of Nl. We assumed that AR1-3 relatively precisely reflected the amount of AR in the paper. The course of titration in the range of AR1-7 was very similar to that of Nl. Again the difference between the two titrations refers to different acid-base systems], i.e. of cellulose, lignin and other paper components. Table 3: Expected capacity of acid-base systems, expressed as percentage, derived from the titration curves and from the consumption of the titration agent. Paper C The paper was in the acid region (pH 5.3) and its acidity was completely titrated off at pH 3.2. pH 7.0 of the extract was reached by deacidifying the paper with 1% MMMC solution. On the titration curve we again found 6-7 EPs, but from Table 3 it can be seen that the majority of them, i.e. 70% were in the acid area (EP 4-7). In Wl this amount was 43%, and in Nl 51%-57%. Titrating the paper in the range of AR1-3 and when the pH of the extract was nearly pH 7.0, the endof-titration was reached at pH ca. 4.2. When the AR was higher than 2% and the pH of the extracts higher than pH 7.0, the end-of-titration was at pH 6.1-6.2. The end-of-titration in the range of AR1-7 was completed at pH 3.5-3.7. The determination of AR1-3 provided significantly lower values than that of ARg;; that of AR1-7, however, provided similar values. Alkaline reserve stated by weighing (ARg) referred to a high percentage of degradation products having EP 4-7 in the significantly acid area. This referred to very similar values in the titration curve of AR1-7. In this case the ARg found by weighing was considerably higher than the true alkaline reserve, and values found by weighing should be revised according to the values of AR1-3 found by titration. They are probably closer to the true AR. Paper H The paper was very acidic (pH 3.7) and the end-of-titration of its extract was completed at about pH 2.0. pH 7.0 in the paper extract was reached after deacidification with 4% MMMC solution, and a 6% solution modified the pH of the extract to numbers higher than pH 8.0. This situation was the result of the paper being highly sized, which meant that it was only able to absorb relatively lower amounts of the deacidification solutions9. The titration curve was similar to other curves, but the share of acid-based systems in the acid area was similar to that of the historic newsprint paper C. That is on the AR4-7 range paper H has a result of 66.3% and paper C a result of 70.9% (Table 3). The end-of-titration of extracts of pH higher than pH 6.0 in the range of AR1-3 was completed at pH 4.7-5.0, that of AR1-7 at ca. pH 3.0. The titration in the range of AR1-3 recorded a low content of AR created by the deacidification of this paper. It reached 1% when a 6% deacidification solution was used and 2% AR with the approximately 10% MMMC solution (range of AR1-3). Similarly as in paper C, the values of ARg were very close to the values of AR1-7. Compared to the titration in the range of AR1-3, ARg referred to a large number of acid-based systems., which could be titrated in acid area. CONCLUSIONS Pure cellulose paper Wl • It is relatively easy to determine precisely the preparation of AR in such a paper and assign it to a certain MMMC concentration. For potentiometric determination of AR it is necessary to titrate to pH 6.0 (range of AR1-3). In these conditions there is a good congruence between AR determination by weighing and by titration. • It is possible to prepare a large alkaline reserve. • The amount of titratable substances below pH 6 is small. Newsprints Nl and N2 • In modern newsprints it is possible to calculate relatively precisely the size of AR and prepare it by means of various MMMC concentrations if the pH in extracts is higher than pH 7.0. The analysis indicated a good congruence between ARg determined by weighing and AR1-3 determined by titration to pH 6.0. • At lower extract pH the end-of-titration in the range of AR1-3 is reached at lower pH and does not refer to real AR. • The amount of titratable substances below pH 6.0 is relatively large. • The method of determining ARg, i.e. by weighing, provides relatively accurate results. Historic newsprints C and H • It is relatively difficult to reach a desired amount of AR in these papers using preparations of the deacidification solution. • There is a big difference between AR1-3 stated by titration and ARg stated by weighing. • Even using high MMMC concentrations, the AR reached in these papers is only 1-2%. • The amount of substances able to be titrated below pH 6.0 or pH 5.0 is large. • Determination of AR1-3 by titration represents only 29%-34% of the capacity of acid-based systems in the papers referring to the true AR; it is just about 50% of the ARg. SUMMARIES The analysis of alkaline reserve in paper after deacidification The creation of sufficiently large alkaline reserves is, besides elimination of acidity, another important aim of any deacidification of groundwood papers. It is problematic reaching a required alkaline reserve of 2% because the amount of alkaline reserve retained in the paper is determined by the type of paper and its initial acidity. It is also difficult because the amount and concentration of the chosen deacidification agent necessary for both aims must be adjusted to take both into account. With a mass method this adjusting is almost impossible. The research reported aimed at finding the relationship between the alkaline reserve measured as change of paper weight before and after deacidification on one side, and by titration on the other Analyse de la réserve alcaline du papier après la désacidification Parallèlement à l'élimination de l'acidité un autre but important recherché par la désacidification de papiers est de créer une réserve alcaline suffisante. Ce n'est pas facile d'obtenir la quantité souhaitée de 2% de réserve alcaline car il faut ajuster la quantité et la concentration de la solution de neutralisation à chaque type de papier et à son pH d'origine. Ceci est presque impossible lors d'une neutralisation de masse. L'objectif poursuivi par les recherches en question était d'établir une relation entre les quantités de réserve alcaline obtenues en mesurant le poids du papier avant et après la désacidification et les résultats obtenus par titration. Messen der alkalischen Reserve in Papier nach einer Neutralisierung Das Ziel der konservatorisch-restauratorischen Neutralisierung von sauer gefertigtem holzhaltigem Papier ist, neben dem Neutralisieren von dort vorhandener Säure, die Schaffung einer ausreichenden alkalischen Reserve. Es ist schwierig eine angestrebte Menge von ca. 2% zu erreichen, weil Menge und Konzentration der Neutralisierungslösung entsprechend dem Papiertyp und seinem Ausgangs-pH eingestellt werden müssen. Bei einer Massenneutralisierung ist dies geradezu unmöglich. Ziel der Untersuchungen, über die berichtet wird, war es, eine Relation zwischen den durch Wiegen und den durch Titration gemessenen Mengen an alkalischer Reserve zu finden. REFERENCES 1. Nikitin, N. L: Chemie dreva (Chemistry of wood). Praha: SNTL 1956: 82-87. 2. Bukovsky, V., & M. Trnková: The influence of secondary chromophores on photooxidation of paper. Part 2: The influence of light on groundwood paper. Restaurator 24 (2003): 118-132. 3. Dupont, A. L.: Degradation of cellulose at the wet/dry interface: I. The effect of some conservation treatments on brown lines. Restaurator 17 (1996): 1-21. 4. Carter, H., P. Begin & D. Grattan: Migration of volatile compounds through stacked sheets of paper during accelerated ageing. Part 1 : Acid migration at90°C. Restaurator 21 (2000): 77-84. 5. Bülow, A., P. Begin, H., Carter & T. Burns: Migration of volatile compounds through stacked sheets of paper during accelerated ageing. Restaurator 21 (2000): 187-203. 6. Bukovsky, V., & I. Kuka: The influence of Mg on the light induced oxidation of newsprint. Restaurator 22 (2001): 208-227. 7. Liers, J.: Determination of the content of alkalis and acids in paper. Restaurator 20 (1999): 126136. 8. Bukovsky, V.: The influence of light on ageing of newsprint paper. Restaurator 21 (2000): 5576. 9. Clark, R. J. B., P. J. Gibbs & R. A. Jarjis: An investigation into the deacidification by ethoxymagne-sium ethylcarbonate.J. Mater. Chem. 8 (1998): 2685-2690. Vladimir Bukovsky Slovak National Library Preservation Service Branch Nám.J.C. Hronského I, SK- 036 01 Martín Slovak Republic E-mail: bukovsky@snk.sk