Impact of air pollution on outdoor cultural heritage objects and decoding the role of particulate matter: a critical review.

Atmospheric gases and particulate matter (PM) in contact with the material's surface lead to chemical and physical changes, which in most cases cause degradation of the cultural heritage material. Atmospheric damage and soiling are recognized as two pivotal forms of deterioration of cultural heritage materials caused by air pollution. However, the atmospheric damage effect of PM is rather complicated; its variable composition accelerates the deterioration process. Considering this, one of the important contributions of this work is to review the existing knowledge on PM influence on atmospheric damage, further recognize, and critically evaluate the main gaps in current understanding. The second phenomenon related to cultural heritage material and PM pollution is soiling. Even if soiling was recognized long ago, its definition and knowledge have not changed much for several decades. In the past, it was believed that black carbon (BC) was the primary soiling agent and that the change of the lightness could effectively measure the soiling. With the change of pollution situation, the lightness measurements do not represent the degree of soiling correctly. The additional contribution of this work is thus, the critical evaluation of soiling measurements, and accordingly, due to the change of pollution situation, redefinition of soiling is proposed. Even though numerous studies have treated soiling and atmospheric damage separately, there is an overlap between these two processes. No systematic studies exist on the synergy between soiling and atmospheric damage caused by atmospheric PM.

Determination of sulfur oxides formed during the S(IV) oxidation in the presence of iron.

The reaction products (i.e., sulfate (SO4(2-)) and dithionate (S2O6(2-))) of S(IV) oxidation in the presence of iron(III) under different experimental conditions were investigated. Ion-interaction chromatography was used for the separation of sulfate and dithionate using tetrabutylammonium hydroxide (TBAOH) as an ion-pair reagent. The chromatographic method was optimized by varying the composition of the mobile phase (i.e., concentration of TBAOH, acetonitrile and Na2CO3) and by varying the flow rate of the mobile phase. The method was successfully applied to the determination of dithionate formed during the S(IV) oxidation in the presence of Fe(III). In air-saturated solutions sulfate was observed as the only product, while in N2-saturated solutions dithionate was also determined, but it is the minor reaction product and represents about 4% of the total amount of oxidized HSO3- under the studied conditions.

Mechanistic Information on the Redox Cycling of Nickel(II/III) Complexes in the Presence of Sulfur Oxides and Oxygen. Correlation with DNA Damage Experiments.

The reactions of the water-soluble complexes [NiCR](2+) (where CR = 2,12-dimethyl-3,7,11,17-tetraazabicyclo[11.3.1]heptadeca-1(17),2,11,13,15-pentaene) and [NiKGH-CONH(2)](+) (where KGH-CONH(2) = lysylglycylhistidinecarboxamide) with sulfite/O(2) and peroxymonosulfate have been investigated using spectrophotometric and rapid-scan techniques. In most cases, the spectral changes suggest the formation of an intermediate Ni(III) species, followed by decomposition reactions which involve a back-reaction to Ni(II). Only in the case of the [NiCR](2+)-S(IV)-O(2) system is the formed Ni(III) species stable in solution. When sulfite and oxygen are used to oxidize Ni(II) to Ni(III), the reaction is oxygen dependent and an induction period could be observed, whereas the use of the strong oxidizing agent peroxymonosulfate resulted in no induction period and no oxygen dependence. In addition, the oxidation of Ni(II) to Ni(III) was faster if peroxymonosulfate was used instead of sulfite/O(2). The [NiKGH-CONH(2)](+) complex reacts much faster with sulfite/O(2) and peroxymonosulfate than the [NiCR](2+) does. Rate constants for the oxidation process and possible reaction mechanisms, based on available literature data, that can account for the observed kinetic observations in a qualitative way are presented, and the results are correlated with previously obtained data on DNA modification using these systems.