Page 79 - Copper and Bronze in Art: Corrosion, Colorants, Getty Museum Conservation, By David Scott
P. 79

on  exposure  of copper  samples to various liquid,  solid, and gaseous contaminants. The  thick­
          ness of the corrosion products  that  develop  on the copper  after  one month of exposure  is
          determined using electrolytic cathodic reduction, establishing four levels of corrosivity. Other
          organizations  may divide the levels differendy, but the principal information  is basically the
                                            G
          same. The lowest level of severity, labeled I ,  may typically have an H 2 S  concentration of less
          than 3 ppb; S0 2 ,  less than  10 ppb;  Cl 2 ,  less than ι ppb;  N O x , less than 50 ppb; and  0 3 , less than
          2 ppb. Some of these levels may be considered high for the museum environment. The I  rat­
                                                                                G
          ing of 3 ppb is too high for objects, and palliative measures are often taken at exposure  levels of
                                                                 i
          loo  ppt. Likewise, nitrogen oxides are often regarded with suspicion f levels as high as 50 ppb
          are found inside the museum. The lowest possible  values  are desirable  for any of these pollu­
          tants.  Levels of  N 0 2  at the St. Vitus  Cathedral in Prague, for example,  reached  15 ppb, but
          ammonia levels were substantial at 20 ppb. These ammonia levels could begin to have an effect
          on  exposed  copper  and brass, so it is impossible to consider  anything in isolation.  Johannson,
          Rendahl, and Kucera (i998) and Johannson  (i998) report on an interesting research project that
          applied atmospheric  corrosivity measurements to forty-two indoor sites, including nine  muse­
          ums and churches;  these reports should be consulted for further  information.
                                I  DEPOSITION  OF  PARTICULATE  MATTER  Particulate pollution,
          arising from  tobacco  smoke, asbestos, suspended particulate matter, and particles large enough
          to  be precipitated, is especially important as a corrosion initiator on polished metal surfaces. In
          metropolitan areas today, most of the sulfur acquired by surfaces is not supplied in gaseous form
          from  reactions with  sulfur dioxide but rather  as dry deposition. Lobnig and  colleagues  (1993)
          draw attention to the bimodal distribution of airborne particulates; predominating the distri­
          bution are fine particles smaller than 2.5 μιη in diameter and coarse particles larger than 2.5  μιη.
          For  environments  with  extremely efficient  air-filtration  systems, the coarse particles  are less
          important,  since  they can be removed with  about  95% efficiency, while  the fine particles are
          removed only at levels between  10%  and  70%.  The most abundant  ions present in these fine par­
          ticles are sulfate and ammonium ions. Lobnig and colleagues  (1993) exposed polished copper to
          simulated particulate matter consisting of submicron particles of ammonium sulfate. After  five
                                                                   (
          days of exposure  at 75%  relative humidity, which is the critical level for NH 4 ) 2 S0 4 , corrosion
          of the copper had occurred with formation of cuprite and antlerite. There is little doubt that sur­
          faces left uncleaned  for a long period of time, perhaps several years,  create unsightly corrosion
         problems that are not well documented in the literature.
             Current  interest in the subject  is driven by the perceived  threat of corrosion to  copper
          alloys in electronic  materials  caused by submicron-size  atmospheric  particulates.  Comizzoli
          and coworkers (1993), for example, provide data for the average airborne concentration of ionic
          species and total mass of particles in the air of Newark, New  Jersey, together with the average
          accumulation rates for ions on both vertical and horizontal surfaces.  For sulfates,  the indoor
          deposition velocity varied from  0.002 to 0.010 cm/s.  Because the rate of deposition of ammo-



                        C H A P T E R  O N E
                        62
   74   75   76   77   78   79   80   81   82   83   84