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Paper Conservation: Decisions & Compromises

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Evaluation of stochiometric effects (“side effects”<br />

is not an appropriate title)<br />

The molar Ca/P ratios of the samples Phy-1 to<br />

Phy-4 are similar (0.605 ± 0.05), meaning that in<br />

the pH range 4.8 to 6, the CP is deposited in the<br />

samples with an average stochiometry of 3.6 calcium<br />

atoms per phytate molecule. This suggests<br />

that the precipitate is a mixture of Ca:Phytate<br />

3:1, Ca:Phytate 3.5:1 and Ca:Phytate 4:1, consistently<br />

with existing data: The Ca:Phytate n:1 is<br />

known to be soluble for low values of n (n=1<br />

and n=2), and insoluble for higher n values (2 <<br />

n) (Graf 1983). The specification of phytate solutions<br />

can be calculated versus pH considering<br />

the 12 pKa values of this acid (Heighton et al<br />

2008): In the pH range from 5 to 6, three species<br />

of phytate, respectively bounded to four, five, and<br />

six protons are co-existing in solution, meaning<br />

that resp. eight, seven, and six free sites remain<br />

available for calcium bounding. If we consider<br />

that each calcium can occupy maximum two<br />

available phytate sites, and that calcium does not<br />

remove bound protons, the resulting Ca:Phytate<br />

precipitate stochiometry should be between 3:1<br />

and 4:1, consistently with the measured value of<br />

3.6:1.<br />

In our experimental procedures, the phytate<br />

concentration in the solution is 1.75 mM, and<br />

the concentration of iron in solution remains<br />

below 0.044 mM, a value estimated under the<br />

assumption that all iron present in the paper is<br />

dissolved. Phytate is also present in large excess<br />

compared to iron. In these conditions, its high<br />

affinity toward iron is expected to lead to the<br />

formation of soluble iron phytate 1:1 complexes,<br />

thus facilitating iron removal from the paper in<br />

comparison to pure water. This is not the case.<br />

Pure water appears the most efficient for iron removal<br />

(50 % of iron is lost). On the contrary, iron<br />

is more likely to remain in the paper when CP is<br />

present in solution (only 30 % of iron is lost). Far<br />

from enhancing iron removal from the samples,<br />

the CP solution helps to retain iron in the paper.<br />

present in low concentration and can be incorporated<br />

in the calcium:phytate precipitate without<br />

noticeably changing its stochiometry.<br />

It was recently demonstrated on quite similar<br />

laboratory samples (Rouchon et al 2011b) that<br />

the cellulose depolymerisation was mainly due<br />

to oxidative mechanisms provoked by surrounding<br />

oxygen. Consequently, the poor efficiency<br />

of CP treatment, when performed alone (Phy-1<br />

to Phy-4) refers to the fact that phytate does<br />

not inhibit iron at this pH level. The ability of<br />

phytate to chelate iron is correlated to its capacity<br />

to block all iron coordination sites. This<br />

property was evidenced in mild alkaline, but not<br />

in acidic conditions. In these conditions protons<br />

are obviously competing with calcium and iron<br />

for phytate bounding. We think that the iron<br />

which remains in the paper after CP treatment is<br />

only poorly bound to CP and thus not inhibited.<br />

When the CP treatment is followed by deacidification,<br />

the pH of the paper rises to approx. 8 and<br />

approx. two of the protonated sites of phytate<br />

become available (Heighton et al 2008), thus favouring<br />

the inhibition of iron through chelation.<br />

Conclusion<br />

This study confirms that the calcium phytate<br />

treatment should necessarily be followed by a<br />

calcium hydrogencarbonate deacidification in order<br />

to achieve long term stability. It additionally<br />

shows that the precipitation of calcium phytate<br />

in the treating solution does not significantly<br />

impact the efficiency of the treatment. We think<br />

that iron is not inhibited in the pH range 5 to 6,<br />

because it has to compete with protons and calcium<br />

ions to bind phytate. After deacidification,<br />

the removal of protons releases approx. two new<br />

chelating sites on each phytate molecule, which<br />

is probably enough to efficiently inhibit iron.<br />

In CP solutions, calcium is used at a concentration<br />

of 4.4 mM, i.e. in large excess over iron (<<br />

0.044 mM). It is already known that the addition<br />

of calcium in iron phytate solutions provokes<br />

co-precipitation phenomena (Subba Rao and Narasinga<br />

Rao 1983). Similarly, the fact that CP solution<br />

helps to retain iron in the paper appears to<br />

us related to co-precipitation phenomena. Iron is<br />

ICOM-CC Graphic Documents Working Group Interim Meeting | Vienna 17 – 19 April 2013<br />

48

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