Practical aspects of atmospheric corrosion Trends, experiences from Europe, experiences from Asia/Africa Policy aspects, costs.

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Presentation transcript:

Practical aspects of atmospheric corrosion Trends, experiences from Europe, experiences from Asia/Africa Policy aspects, costs

History of evidence of effects of air pollutants on materials In London an edict was issued in 1306 banning the use of 'sea-coal' as this is particularly high in chlorine Since the industrial revolution soiling and degradation of buildings in urban areas has been noticeable and often attributed to the effects of air pollution Systematic laboratory exposures in by Vernon in the 1930’s revealed the importance of SO 2 Field exposures in Germany by Schikorr in the 1940’s revealed the practical importance of SO 2 Field exposures in Nigeria by Ambler and Bain in the 1960’s revealed the practical importance of chlorides Field exposures within the Convention on Long-Range Transboundary Air Pollution (CLRTAP) lead to dose- response functions in the 1990’s

Zinc, Stockholm (Vanadis)

Steel, Kopisty (Czeck Republic)

Corrosion trend

Gas concentration trend

ICP Materials - Test sites 39 (29) test sites in 12 (15) European countries and in the United States and Canada

List of test sites

Bronze corrosion, SO 2 and NO 2 concentrations Site number

Important pollution parameters

Model for multi-pollutant impact and assessment of threshold levels for cultural heritage

Interaction of atmospheric pollutants, meteorological conditions and deposition mechanisms in the process of atmospheric corrosion Filled fields ( ): MULTI-ASSESS Unfilled fields: ICP Materials

HNO 3 HNO 3 concentration

Important parameters in the multi- pollutant situation

Comparison of corrosivity of HNO 3 and SO 2 +O 3 in laboratory exposure

Mapping TRhRainSO 2 pH Corrosion = f(T, Rh, Rain, SO 2, pH) Base maps Corrosion map

Map of corrosion rate of bronze in Germany Source: Federal Environmental Agency, Berlin, Germany

Acceptable and tolerable levels, target levels and limit values The acceptable level is the maximum level at which an acceptable response occurs. The acceptable response should be based on technical and economic considerations. The tolerable level is the maximum level at which a tolerable response occurs. The tolerable response should be based on experiences from restoration / maintenance work for cultural heritage objects. A target level is a specified level in a given context which should not be exceeded. A limit value is a target level that is legally binding.

Tolerable corrosion and pollution

Tolerable pollution levels in the multi- pollutant situation Definition of a tolerable corrosion rate, K t, depending on use and material, implicitly defines a tolerable multi-pollution situation, which can be reached by reducing one or several of the multi- pollutants: K t = f dry (T, RH, [SO 2 ] t, [HNO 3 ] t,...) + f wet (Rain[H + ] t )

Recent information on effects-based approaches for the Protocol reviews Source: MULT-ASSESS Publishable final report,

Air Quality Directive 99/30/EC Limit values of pollutants, µg m -3

Assessing corrosion costs

Corrosion costs Specification of a level of corrosion attack where replacement or maintenance is necessary makes it possible to calculate the lifetime, t: K = f dry (T, RH, [SO 2 ], t) + f wet (Rain[H + ], t) Stock at risk + lifetime  Corrosion costs

Sandstone Critical thickness fortechnical objectsornaments and inscriptions R crit = 5 mm = 5000  mR crit = 1 mm = 1000  m

Estimation of stock at risk Inspection (Individual building) Building Registers (District/City) Identikits (National) Allocation to census data (Regional)

Stock at risk of galvanised steel in Germany in m 2 /km 2

Yearly corrosion cost of galvanised steel in Germany due to pollution (DM/km 2 )

Reduction of costs due to decreased corrosion damage after execution of the 2 nd sulphur protocol (US$·10 6 )

Quantification of costs and benefits for cultural heritage Rock Carving in Tanum, Sweden Difficult to express in monetary terms the loss of objects of cultural heritage Indirect method for calculation of costs - willingness to pay (contingent valuation method) Direct benefits (reduced maintenance etc) Indirect benefits (incomes from tourism, increased employment etc)

Evidences of high corrosion rates

Results from Europe not transferable