Ash/Tephra Fall (Physical and Chemical)
Primary reference(s)
BGS, no date. . Accessed 22 April 2021.
Additional scientific description
The term ‘volcanic ash’ is often used loosely to include larger fragments, more correctly termed ‘lapilli’ (2 to 64 mm in diameter). The largest tephra clasts (> 64 mm) are called blocks and bombs. Fragments of all sizes generated during fragmentation of magma and lava are also known as ‘pyroclasts’, whether they travel through the atmosphere or are directly entrained in lateral moving flows.
Along with emissions of gas, tephra is the most frequent and widespread volcanic hazard. It is ejected into the atmosphere and transported laterally by wind and/or lateral gravitational spreading of umbrella clouds before falling out under gravity. Fine tephra (mainly volcanic ash) also rises convectively above pyroclastic density currents and lava fountains (Bonadonna et al., 2015, 2021; Jenkins, 2015). Tephra can affect very large areas; volcanic ash can remain airborne for days and can be transported for thousands of kilometres and may disrupt air traffic. Blocks and bombs mostly follow a ballistic trajectory, and so are not strongly affected by wind; nonetheless, the smallest blocks can also be entrained within convective plumes impacting a larger area than ballistic clasts. Tephra can cause fatalities directly, owing to ballistic impact, and indirectly due to collapse of buildings (mostly roofs) and trees due to tephra load. In addition, public health threats, clean-up and disruption to critical infrastructure services, aviation and primary production can lead to substantial societal impacts and costs, even at thicknesses on the ground of a few millimetres. Hot tephra (e.g., large lapilli and blocks and bombs) can also trigger fires if falling on ignitable material (e.g., dry vegetation, wooden structures). Intense tephra fall reduces visibility and may cause complete darkness during daylight hours, creating significant hazards for driving, for example (USGS, no date).
Lightning may be generated by friction between the fine airborne particles, which can be localised above the volcano or accompany large ash plumes as they move downwind. The impacts can be experienced across wide areas and can be long-lived, since eruptions can last from hours to years (IVHHN, 2021).
Tephra-fall deposits may also be the source of secondary hazards (e.g., lahars) and can be remobilised into the atmosphere by wind, traffic and human activities, prolonging the impacts. Tephra varies in appearance depending upon the composition of the magma and the style of the eruption (Bonadonna et al., 2015).
Various analytical and numerical models have been developed that forecast tephra dispersal and deposition from the finest fractions to ballistic blocks (e.g., Folch, 2012; Bonadonna et al., 2015; Biass et al., 2016; Osman et al., 2019). The International Civil Aviation Organization (ICAO) leads operational forecasting of ash cloud transport for the benefit of the aviation sector (ICAO, 2012; Lechner et al., 2017).
To assess severity at a site, tephra falls are most commonly described (e.g., eyewitness accounts) or measured according to their thickness. Increasingly though, loading (mass per unit area; kg/m2) is more informative for assessing impact to structures and agriculture, and enables consideration of water saturation (Jenkins et al., 2015). For respiratory health exposure and hazard assessment, monitoring of airborne concentrations of fine particulates is preferable, alongside physicochemical and toxicological characterisation of the ash particles (e.g., Horwell et al., 2013).
There were 52 recorded fatal incidents as a result of tephra (not including ballistics) between 1500 AD and 2017 resulting in 4315 fatalities and these occurred between 0.5 and 170 km from the source volcano at a median distance of 10 km (Brown et al., 2017). Over the same period, there were 57 fatal incidents due to ballistics, with 367 recorded fatalities 0 to 7 km from the volcanic source (Brown et al., 2017).
Approximate tephra thicknesses (hazard intensities) that relate to key damage and functionality states for a range of building types, critical infrastructure and agricultural categories are given by Jenkins et al. (2015).
Metrics and numeric limits
Not applicable.
Key relevant UN convention / multilateral treaty
Sendai Framework for Disaster Risk Reduction 2015–2030 (Ä¢¹½´«Ã½, 2015).
Examples of drivers, outcomes and risk management
Tephra particles can have acid coatings which may react with rain to damage vegetation and cause corrosion. The acid coating is rapidly removed by rain, which may then pollute local water supplies. Tephra can increase river turbidity leading to environmental problems.
Finer particles of ash may irritate the lungs and eyes (humans and animals) and exacerbate the symptoms of existing respiratory conditions (e.g., asthma and bronchitis) (Horwell and Baxter, 2006; IVHHN, 2020a).
In most eruptions, volcanic ash causes relatively few health problems, but generates much anxiety. However, there is insufficient evidence to be certain whether ash can trigger chronic diseases such as lung cancer and silicosis (if crystalline silica is a major component) (Horwell et al., 2012; IVHHN, 2020a), and all fine particulate matter (e.g., PM2.5) is considered to negatively impact mortality and morbidity, particularly for respiratory and cardiovascular diseases (WHO, 2013).
Livestock should ideally be under cover during tephra falls and veterinary services may be needed for respiratory, ingestion, eye and dental problems (USGS, 2020).
Medical services can expect an increase in the number of patients with respiratory and eye symptoms during and after a tephra-fall event, which can be measured by existing syndromic surveillance or by application of the International Volcanic Health Hazard Network standardised epidemiological protocols (IVHHN, 2020b; Mueller et al., 2020).
The fertility of the soils around many volcanoes is due to the weathering of old ash deposits, and the addition of thin tephra falls to soil can be beneficial in the long term. In many cases though, volcanic ash needs to be removed from urban and agricultural areas to prevent remobilisation and repeated impacts, as well as to prevent it from washing into drainage networks. Therefore, sites need to be identified to dispose of the ash, preferably before an eruption. Cleaning tephra from roofs, roads, agricultural land, and critical infrastructure may require significant volumes of water, trucks, diggers, etc., and can have significant associated costs (Hayes et al., 2015).
References
Biass, S., J.-L. Falcone, C. Bonadonna, F. Di Traglia, M. Pistolesi, M. Riso and P. Lestuzzi, 2016. Great Balls of Fire: A probabilistic approach to quantify the hazard related to ballistics – A case study at La Foss volcano, Vulcano Island, Italy. Journal of Volcanology and Geothermal Research, 325:1-14.
Bonadonna, C., A. Costa, A. Folch and T. Koyaguchi, 2015. Tephra dispersal and sedimentation. In: Sigurdsson, H., B. Houghton, S. McNutt (eds.), The Encyclopedia of Volcanoes, 2nd edition. Academic Press, pp. 587-597.
Bonadonna, C., S. Biass, S. Menoni and C.E. Gregg, 2021. Assessment of risk associated with tephra-related hazards. In: Papale, P. (ed), Forecasting and Planning for Volcanic Hazards, Risks, and Disasters, Chapter 8.
Brown, S., S. Jenkins, R.S.J. Sparks, H. Odbet and M.R. Auker, 2017. Volcanic fatalities database: analysis of volcanic threat with distance and victim classification. Journal of Applied Volcanology, 6:15.
Folch, A., 2012. A review of tephra transport and dispersal models: evolution, current status, and future perspectives. Journal of Volcanology and Geothermal Research, 235-236:96-115.
Hayes, J.L., T.M. Wilson and C. Magill, 2015. Tephra fall clean-up in urban environments. Journal of Volcanology and Geothermal Research, 304:359-377.
Horwell, C.J. and P.J. Baxter, 2006. The respiratory health hazards of volcanic ash: a review for volcanic risk mitigation. Bulletin of Volcanology, 69:1-24.
Horwell, C.J., B.J. Williamson, K. Donaldson, J.S. Le Blond, D.E. Damby and L. Bowen, 2012. The structure of volcanic cristobalite in relation to its toxicity; relevance for the variable crystalline silica hazard. Particle and Fibre Toxicology, 9:44.
Horwell, C.J., P.J. Baxter, S.E. Hillman and 15 others, 2013. Physicochemical and toxicological profiling of ash from the 2010 and 2011 eruptions of Eyjafjallajökull and GrÃmsvötn volcanoes, Iceland using a rapid respiratory hazard assessment protocol. Environmental Research, 127:63-73.
ICAO, 2012. . Accessed 15 October 2020.
IVHHN, 2020a. .
IVHHN, 2020b. . Accessed 15 October 2020.
IVHHN, 2021. . Accessed 22 April 2021.
Jenkins, S.F., T.M. Wilson, C. Magill et al., 2015. Volcanic ash fall hazard and risk. In: Loughlin, S.C., S. Sparks, S.K. Brown et al. (eds.), Global Volcanic Hazards and Risk. Cambridge University Press, pp. 173-222.
Lechner, P., A. Tupper, M. Guffanti, S. Loughlin and T. Casadvell, 2017. .
Mueller, W., H. Cowie, C.J. Horwell, P.J. Baxter et al., 2020. . Accessed 15 October 2020.
Osman, S., E. Rossi, C. Bonadonna, C. Frischknecht, D. Andronico, R. Cioni and S. Scollo, 2019. Exposure-based risk assessment and emergency management associated with the fallout of large clasts at Mount Etna. Natural Hazards and Earth System Sciences, 19:589-610.
Ä¢¹½´«Ã½, 2015. Sendai Framework for Disaster Risk Reduction 2015-2030. United Nations Office for Disaster Risk Reduction (Ä¢¹½´«Ã½). Accessed 12 October 2020.
USGS, no date. . Accessed 22 April 2021.
USGS, 2020. . Accessed 15 October 2020.
WHO, 2013. . Accessed 29 November 2019.