Page 59 - Copper and Bronze in Art: Corrosion, Colorants, Getty Museum Conservation, By David Scott
P. 59

I  BUFFERING  GAPACITY  OF SOILS  Soils  vary  greatly in  their
           buffering  capacity, and there is a range of factors responsible  for this, from  carbonate buffers at
           pH  >  6.2 to ferrihydrite buffers  at pH <  3.2.  The  most poorly buffered  soils are those origi­
            nating from  the weathering of siliceous bedrock,  such  as quartzites,  feldspathic  gneisses, and
            granites; these soils have a low  capacity to replenish base cations lost in  acid neutralization reac­
            tions. They also have a low  ability to retain sulfate, which explains why Scandinavia was the  first
           European  area to suffer widespread  acidification of lakes—its  geology is dominated by gneiss,
            schist, and quartzite.
               Central European  soils have been more resistant to acidification, but with sulfur-deposition
                                                                               I
            rates up to ten times greater than in the past, their buffering capacity is in jeopardy. f the agri­
            cultural use of the land ceases, the addition of lime may also cease, reducing the pH level from
            6 to 5 in clay soils, or to about 4-4.5 in sandy soils. At the  same time, draining wetlands  may
            cause dramatic  acidification of soils because of the quantities of sulfur compounds  that would
           be released and the resulting oxidation of sulfides.
               Some soil  components  are still  not well  understood.  One  of these is soil  humus,  which
           influences buffering capacity, metal-binding capacity, and water retention, as well as the  absorp­
           tion of hydrophobic organic compounds. The study by Geilmann (i956) is a classic account of
            the influence of humic acid on bronze  corrosion  (see  CHAPTER  11).  The  complex structure of
           humus  has  only recendy  been elucidated. According to Wershaw  (1992), it consists of ordered
            aggregates of amphiphiles, which are molecules with  separate polar  and nonpolar parts com­
           posed mainly of relatively unaltered plant polymer segments attached  to carboxylic acid groups.
           These react with  soil mineral grains  to form membranelike  coatings with highly charged  exte­
           rior surfaces that act  as separate ion-exchange  phases.
                                  I  PROBLEMS  FOR CONSERVATION  RESEARCH  The difficulties of
           either  inferences  based on  soil  conditions or on  deductions  derived from  the  examination of
            objects is well illustrated by the work of Chase and Quanyu  (1997), who studied a suite of exca­
           vated bronze  fragments  from  the  site of Tienma-Qu in China  (Western Zhou dynasty, 1000-
            650  B.C.E.). Some of these bronzes were totally corroded while others were quite well  preserved.
           The  authors  were  unable  to assign  these differences  to particular  tombs or environments by
           examination of the soil samples. This is not an isolated case. Highly detailed statistical studies
           along the lines of the Swedish study would be necessary to accurately characterize  and  correlate
           soil corrosivity with artifact condition.
               The work by Wagner  and  coworkers  (1997), funded  by the  European  Environment  Pro­
           gramme of the Directorate General  XII for Science,  Research and Development under  the gen­
           eral aegis of research for the "Protection and Conservation  of the European  Cultural Heritage,"
           is currently at an early stage of development. It  will be interesting to see what develops from this
           collaborative project and whether  the research  will  augment  the findings of the  Swedish  study
           coordinated by Mattsson.



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