Recent reports have highlighted the potential damage caused to a range
of media, including materials, by ozone (O-3) The limited data availa
ble indicate significant damage to rubber products and surface coating
s but either insignificant or unquantifiable damage to textiles and ot
her polymeric materials at the range of atmospheric concentrations enc
ountered in the U.K. Materials in the indoor environment have been exc
luded from economic analyses. Legislation was put in place in 1993 in
the U.K. in order to reduce NOx (NOx = NO + NO2) and VOC (volatile org
anic compounds) emissions from motor vehicles which is likely to resul
t in reduced peak O-3 episodes but increased average levels of O-3 in
urban areas which may result in increased damage to materials. A detai
led assessment of the costs of O-3 damage to materials is not currentl
y possible because of insufficient information on relevant dose-respon
se functions and the stock at risk. Alternative methods were thus adop
ted to determine the potential scale of the problem. Scaling of U.S. e
stimates made in the late 1960s provides a range for the U.K. of pound
170 million-pound 345 million yr(-1) in current terms. This includes
damage to surface coatings and elastomers, and the cost of antiozonant
protection applied to rubber goods. Independent estimates were made o
f the costs of protecting rubber goods in the U.K. These were based on
the size of the antiozonant market, and provide cost ranges of pound
25 million-pound 63 million yr(-1) to manufacturers and pound 25 milli
on-pound 189 million yr(-1) to consumers. The only rubber goods for wh
ich a damage estimate (not including protection costs) could be made w
ere tyres, using data from the U.S.A. and information on annual tyre s
ales in the U.K. A range of pound 0-pound 4 million yr(-1) was estimat
ed. The cost of damage to other rubber goods could not be quantified b
ecause of a lack of data on both the stock at risk and exposure-respon
se functions. The effect of O-3 On the costs of repainting were estima
ted under scenarios of increased urban concentrations of O-3 using dam
age functions derived from the literature. The cost was estimated to b
e in the range of pound 0-pound 60 million yr(-1) for a change from 15
to 20 ppb O-3, and pound 0 to pound 182 million yr(-1) for a change f
rom 15 to 30 ppb O-3. The wide ranges derived for effects on surface c
oatings are a reflection of the uncertainty associated with the dose-r
esponse functions used.