Partitioning of Mercury into Several Size
Fractions in Highway Runoff
Marcia Ferreira, Ph.D., P.E.
1
; Mi-Hyun Park, Ph.D.
2
; Jenny A. Jay, Ph.D.
3
;
Peter G. Green, Ph.D.
4
; and Michael K. Stenstrom, Ph.D., P.E., F.ASCE
5
Abstract: Due to their large impervious coverage, highways are ideal sites for the transport of pollutants to either treatment units or direct
discharge to waterways. Mercury, a highly toxic and ubiquitous environmental contaminant, is rarely studied in stormwater runoff. Removal
of particulate-bound mercury in a dry detention basin was analyzed for the five size fractions: <0.45 μm, 0.45–8 μm, 8–20 μm, 20–100 μm,
and >100 μm. The highest concentration of mercury for both influent and effluent is observed in the 8–20 μm size fraction. Treatment units
are often characterized by suspended solids removal efficiency and particle-bound pollutants correlated to suspended solids removal; how-
ever, different suspended solids removal efficiency may occur in specific particle size fractions. Therefore, the benefits of treatment units may
be different than originally anticipated, especially if the particle-bound concentrations are greater in fractions more efficiently removed. For
sedimentation-based treatment units, the removal is dependent on size fraction, and when one size fraction is captured more efficiently,
the removal rate calculated using the entire sample might indicate particle-bound pollutant removal quite different than actually occurring.
DOI: 10.1061/(ASCE)EE.1943-7870.0001838. © 2020 American Society of Civil Engineers.
Author keywords: Stormwater control measures; Highway runoff; Mercury fractionation; Particle size distribution; Size fractionation;
Stormwater runoff.
Introduction
Mercury is a rarely studied contaminant in stormwater runoff. In
fact, out of approximately 500 studies reported to the International
Stormwater Best Management Practice [BMP Database (Jones and
Strecker 2020)], only two studies reported mercury concentration in
dry detention basins. Furthermore, neither of them makes a distinc-
tion between concentrations in dissolved and particulate phases,
which is necessary when dealing with sedimentation-based treat-
ment units, such as dry detention basins. The absence of mercury
studies in stormwater is surprising, since mercury in its inorganic
form is present in every ecosystem due to long-range atmospheric
transport (Ullrich et al. 2001). The sources of atmospheric mercury
range from volcanic eruptions to combustion processes, such as
burning of coal and wildfires (Mason et al. 1995; Schroeder and
Munthe 1998; Biswas et al. 2008; Burke et al. 2010; Pirrone et al.
2010).
Even though volcanic eruptions are responsible for about 20%–
40% of all the mercury (Hg) released into the atmosphere by natural
emissions (Pyle and Mather 2003), the contribution from natural
sources to the global atmospheric Hg pool is decreasing. Until
the 1970s, chlor-alkali plants were the largest anthropogenic source
of atmospheric Hg, but their impact has been reduced due to stricter
regulations (Schroeder and Munthe 1998). Currently, burning of
fossil fuels, artisanal gold mining, nonferrous metals manufactur-
ing, cement production, waste disposal, and caustic soda produc-
tion are the major sources of atmospheric Hg (Pirrone et al. 2010).
Locations with a Mediterranean climate, such as southern
California, are prone to wildfires due to their long dry summers
and the occurrences of high-speed warm dry winds during the Fall
(Mensing et al. 1999). In the year 2006, the state of California saw
4,805 fires burn 222,896 acres (State of California 2020), which is
below the 5-year average (2002–2006) for the number of fires
(average number of fires is 5,674 fires) but above the average
for the burned area at 688 km
2
(170,126 acres). The past seasons
(2017 and 2018) saw the largest wildfire in California history.
These wildfires release contaminants into the atmosphere, which
can either travel across the globe or settle nearby via ash depo-
sition. Rothenberg et al. (2010) have shown that for two relatively
close lakes (40 km apart), the accumulation of Hg in the lakes’
sediment was greater on the lake affected more frequently with
wildfires. Thus, besides long-range atmospheric transport, an im-
portant source of mercury to watersheds might be wildfires (Burke
et al. 2010; Rothenberg et al. 2010).
Mercury is often found in stormwater runoff from urban water-
sheds (Lawson and Mason 2001; Eckley and Branfireun 2008;
McKee and Gilbreath 2015), and land uses with no obvious local
mercury sources such as highways may have elevated mercury con-
centrations because it is a global pollutant. Typical concentration of
mercury in urban runoff was found to be 200 ng=L, and the range
1
Associate Engineer, Water Resource Management, Metropolitan Water
District of Southern California, 700 Alameda St., Los Angeles, CA 90012.
Email: mferreira@mwdh2o.com
2
Dept. of Civil and Environmental Engineering, Univ. of California,
Los Angeles, 420 Westwood Plaza, Los Angeles, CA 90095 (corresponding
author). Email: parkmh@ucla.edu
3
Professor, Dept. of Civil and Environmental Engineering, Univ. of
California, Los Angeles, 420 Westwood Plaza, Los Angeles, CA 90095.
Email: jennyjay@ucla.edu; jjay@seas.ucla.edu
4
Professional Research Engineer, Dept. of Civil and Environmental
Engineering, Univ. of California, Davis, One Shields Ave., Davis, CA
95616. Email: pggreen@ucdavis.edu
5
Distinguished Professor, Dept. of Civil and Environmental Engineer-
ing, Univ. of California, Los Angeles, 420 Westwood Plaza, Los Angeles,
CA 90095. ORCID: https://orcid.org/0000-0001-6157-0718. Email:
stenstro@seas.ucla.edu
Note. This manuscript was submitted on February 21, 2020; approved
on September 10, 2020; published online on November 20, 2020. Discus-
sion period open until April 20, 2021; separate discussions must be sub-
mitted for individual papers. This paper is part of the Journal of
Environmental Engineering, © ASCE, ISSN 0733-9372.
© ASCE 04020146-1 J. Environ. Eng.
J. Environ. Eng., 2021, 147(2): 04020146
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