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Search: WFRF:(Johansson Ida) > VTI - The Swedish National Road and Transport Research Institute > Road dust load dyna...

Road dust load dynamics and influencing factors for six winter seasons in Stockholm, Sweden

Gustafsson, Mats, 1966- (author)
Statens väg- och transportforskningsinstitut,Miljö, MILJÖ,VTI, Sweden
Blomqvist, Göran, 1963- (author)
Statens väg- och transportforskningsinstitut,Miljö, MILJÖ,VTI, Sweden
Järlskog, Ida, 1991- (author)
Statens väg- och transportforskningsinstitut,Miljö, MILJÖ,VTI, Sweden
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Lundberg, Joacim (author)
Statens väg- och transportforskningsinstitut,Miljö, MILJÖ,VTI, Sweden
Janhäll, Sara, 1965- (author)
RISE,Energi och cirkulär ekonomi
Elmgren, Max (author)
SLB-analys, Sweden
Johansson, Christer (author)
SLB-analys, Sweden; Stockholm University, Sweden
Norman, Michael (author)
SLB-analys, Sweden
Silvergren, Sanna (author)
SLB-analys, Sweden
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 (creator_code:org_t)
Elsevier BV, 2019
2019
English.
In: Atmospheric Environment: X. - : Elsevier BV. - 2590-1621.
  • Journal article (peer-reviewed)
Abstract Subject headings
Close  
  • Traffic related non-exhaust particulate sources and road dust are an increasingly important source for PM10 air pollution as exhaust sources are decreasing due to regulations. In the Nordic countries, the road dust problem is enhanced by use of studded tyres, causing increased road wear and winter road maintenance including gritting. Efforts to reduce road dust emissions requires knowledge on temporal and spatial road dust load dynamics. The city of Stockholm, Sweden, has therefore financed seasonal (October to May) road dust sampling to be able to optimize their winter and spring time street operation measures for reduced road dust emissions. This work describes the outcome of six seasons (2011/2012–2016/2017) of road dust sampling in five central streets using the VTI wet dust sampler (WDS).The results show that road dust load, expressed as DL180 (dust load smaller than 180 μm) has a seasonal variation with the highest loads (up to 200 g/m2) in late winter and early spring and a minimum (down to about 15 g/m2) in early autumn and late spring. The dust load varies between streets and is depending on pavement surface properties. On a smaller scale the dust load has a high variability across streets due to differences in rates of suspension from different parts of the road surface, with low amounts in wheel tracks and higher in-between and outside the tracks. Between 2 and 30% of the DL180 is smaller than 10 μm and could directly contribute to PM10 emissions. In general, higher road surface texture leads to higher dust loads, but the condition of the pavement (e.g. cracks, aggregate loss) might also have an effect. A new, wear resistant pavement accumulated markedly higher road dust amounts than a several years old pavement. This paper closes with a discussion on the complex relation between road dust load and PM10 concentrations and a discussion on the challenges and comparability of road dust sampling techniques and measures.

Subject headings

NATURVETENSKAP  -- Geovetenskap och miljövetenskap -- Meteorologi och atmosfärforskning (hsv//swe)
NATURAL SCIENCES  -- Earth and Related Environmental Sciences -- Meteorology and Atmospheric Sciences (hsv//eng)
NATURVETENSKAP  -- Geovetenskap och miljövetenskap -- Multidisciplinär geovetenskap (hsv//swe)
NATURAL SCIENCES  -- Earth and Related Environmental Sciences -- Geosciences, Multidisciplinary (hsv//eng)
TEKNIK OCH TEKNOLOGIER  -- Samhällsbyggnadsteknik -- Infrastrukturteknik (hsv//swe)
ENGINEERING AND TECHNOLOGY  -- Civil Engineering -- Infrastructure Engineering (hsv//eng)

Keyword

Non-exhaust
sampling
Spatial variation
Temporal variation
Macro texture
PM10
15 Road: Environment

Publication and Content Type

ref (subject category)
art (subject category)

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