Roof Runoff
Roof Runoff, which is generally created by precipitation flow from roof surfaces, represents one of the sub-flows of urban runoff, which on the other hand is the urban subset of surface runoff.
Roof runoff can be a significant source of water pollution, particularly in Europe because of the widespread use of metal roofing materials such as copper and zinc. In urbanized areas most of the roof runoff enters the sewer system and is either directly transported to the recieving waters or, in case of combined sewer systems, sent to waste water treatment facilities. While in the first scenario roof runoff is not treated at all, the combined sewer system on the other hand bears the risk of sewer overflow due to limited sewer capacity during heavy precipitation events.
Content Table
Main Constituents
It took about twenty years after the first studies on road runoff quality to spark scientific interest for roof runoff, because pollution loads had been underestimated for a long time. In a study investigating pollution sources into the mixed sewer system of Paris in 2001 it was found that roof runoff was the major source for the metals copper, zinc, cadmium and lead.1 The number of metal roofs in Paris is especially high due to its many historic buildings.
In contrast to other urban runoff sources where the main source of contamination originates from deposition on the washed-off surfaces in the case of roof runoff the roofing material itself is mostly responsible for the presence of contaminants in runoff. Therefore the spectrum of contaminants is also much smaller and generally limited to heavy metals as the main components.The presence of other major contaminants is generally due to locally or temporally specific atmospheric impairment and will be reflected by similar amounts in runoff from adjacent areas due to dry or wet deposition on these.
Even though other conventional roofing materials like tile, polyester, shingle can also contribute measurable concentrations of copper and zinc their release of heavy metals is marginal compared to zinc and copper roofs.
Runoff Properties
Runoff from metal roofs is special as for aged roofs the presence of the according metal ions is independent of the total precipitation volume or duration. After reaching its maximum thickness the metal oxide layer represents an almost unlimited reservoir of metal ions. Thus, there are two rates that define the amount of metal washed off: the corrosion rate and the runoff rate
Corrosion and corrosion rate
Corrosion is simply the conversion of pure metal into its oxides. For copper the first step is commonly the formation of yellow-reddish Cuprite (Cu2O). With the presence of CO2, SO2, or chlorides (coastal areas) and moisture these are transformed into the basic, blue salts CuCO3∙Cu(OH)2. CuSO4∙Cu(OH)2, or CuCl2∙3Cu(OH)2. This blue salts in combination with the yellow color of the Cuprite make the roof appear it is distinctive green color.
For Zinc this conversion into its oxo-salts is not as apparent.The oxidation starts Immediately on contact with carbon dioxide of the air to the softer, colorless carbonates Zn5(OH)3(CO3)2 and Zn4CO3(OH)3∙H2O or in the presence of SO2 the sulfates Zn4SO4(OH)6∙xH2O2.
Runoff rate
Runoff rates depend on the applied metallic material, the climatic and pollution situation and on roof properties such as age, height, inclination and direction. They can be calculated when all runoff events are collected as follows:3

with Rp is the runoff of zinc per m2 roof area a in g/m2; ρp is the mass concentration of zinc ions mg/L; νp is the sample volume in L. Rm is the runoff rate if m is equal to the number of rain events of one year.
Published runoff rates for zinc roofs4567vary between 2.3 to 7.5 g/m2a and between 1.0 and 3.9 g/m2a for copper roofs8910in Europe.
Related Articles
- ^ M. C. Gromaire, S. Garnaud, M. Saad, G. Chebbo: Contribution of different sources to the pollution of wet weather flows in combined sewers. Water Research 35, 521-533 (2001).
- ^ S. Jouen, B. Hannoyer, A. Barbier, J. Kasperek, M. Jean: A comparison of runoff rates between Cu, Ni, Sn and Zn in the first steps of exposition in a French industrial atmosphere. Materials Chemistry and Physics 85, 73-80 (2004)
- ^ M. Faller, D. Reiss, Runoff behaviour of metallic materials used for roofs and facades – a 5-year field exposure study in Switzerland, Materials and Corrosion 56 (2005) 244–249.
- ^ I.O. Wallinder, P. Verbiest, W. He, C. Leygraf, The influence of patina age and pollutant levels on the runoff rate of zinc from roofing materials, Corrosion Science 40 (1998) 1977–1982.
- ^ R.H.J. Korenromp, J.C.T. Hollander, Diffusive emissions of zinc due to atmospheric corrosion of zinc and zinc coated (galvanised)materials, TNO Institute of Environmental Sciences, Energy Research and Process Innovation, Apeldoorn, 1999.
- ^ A.U. Leuenberger-Minger, M. Faller, P. Richner, Runoff of copper and zinc caused by atmospheric corrosion, Materials and Corrosion 53 (2002) 157–164.
- ^ A. Schriewer, H. Horn, B. Helmreich, Time focused measurements of roof runoff quality, Corrosion Science, Volume 50, Issue 2, February 2008, Pages 384-391
- ^ W. He, I. Odnevall Wallinder, C. Leygraf, A comparison between corrosion rates and runoff rates from new and aged copper and zinc as roofing material, Water, Air, and Soil Pollution Focus 1 (2001) 67–82.
- ^ I. Odnevall Wallinder, P. Verbiest, C. Leygraf, Effects of exposure direction and inclination on the runoff rates of zinc and copper roofs, Corrosion Science 42(2000) 1471–1487.
- ^ K. Athanasiadis, H. Horn, B. Helmreich, A field study on the first flush effect of copper roof runoff, Corrosion Science, Volume 52, Issue 1, January 2010, Pages 21-29
