Page 63 - Copper and Bronze in Art: Corrosion, Colorants, Getty Museum Conservation, By David Scott
P. 63

Exposure time (days)


                                   Graph of exposure time in days against weight gain for copper
                          F I G U R E  1.7
                          samples exposed to S0 2 ,  N0 2 ,  0 3,  S0 2  with N0 2 ,  and  S0 2  with  0 3 .  There
                          is a strong synergistic effect  for mixtures of S0 2  with N0 2 ,  and  S0 2  with  0 3
                          (Strandberg and Johansson 1997a).



           higher than  69 ppb, or the humidity is lower than  75%,  the copper  remains  shiny. FIGURE  1.7
           shows  a graph  of exposure  time in days  against  weight gain for  copper  samples  exposed  to
           sulfur  dioxide, nitrogen dioxide, ozone,  sulfur dioxide with nitrogen, and sulfur dioxide with
           ozone.  Strandberg  and Johansson  (1997a) showed that there  is a strong synergistic effect  with
           mixtures of sulfur dioxide and nitrogen dioxide, and with  sulfur dioxide and ozone,  and  that
           this results in a substantial increase in the corrosion rate. The development of the black patina
           was influenced neither by these mixtures nor by the degree of cold-working of the  copper.
              The  results  are  explained by  the  development  of a passivating  chemisorbed  sulfite  film
           at high  SO 2  concentrations;  at low concentrations  and high  humidity,  the  adsorbed  sulfite is
           destroyed by the formation of soluble species and by oxidation to sulfate. The thin oxide layer
           is  attacked by the acidic surface;  copper is anodically dissolved; oxygen is cathodically reduced;
           and cuprite is precipitated forming a dull black layer 200-300 nm thick. It is not clear why this
           layer is black rather than red.
              Although  SO 2  levels in  the  West  are  generally  declining, levels  of nitrogen  oxides  are
           slowly increasing. Estimates indicate that at the end of the nineteenth century annual  emissions
           were  less than  1 X 1 0  1 2  g. A century later, in the  1980s, they had  increased  to approximately
           18 X 10  1 2  g. In urban  areas, ozone  levels doubled  over  the  same period, from  about  20 ppb
           during  the  I88OS to  about  40 ppb in the  1980s. An analysis  by  Graedel  (i987a)  suggests that





                         C H A P T E R  O N E
                         46
   58   59   60   61   62   63   64   65   66   67   68