Mining legacy across a wetland landscape: high
mercury in Upper Peninsula (Michigan) rivers, lakes,
and fish
W. Charles Kerfoot,
*
a
Noel R. Urban,
b
Cory P. McDonald,
b
Huanxin Zhang,
c
Ronald Rossmann,
d
Judith A. Perlinger,
b
Tanvir Khan,
b
Ashley Hendricks,
b
Mugdha Priyadarshini
b
and Morgan Bolstad
b
A geographic enigma is that present-day atmospheric deposition of mercury in the Upper Peninsula of
Michigan is low (48%) and that regional industrial emissions have declined substantially (ca. 81%
reduction) relative to downstate. Mercury levels should be declining. However, state (MDEQ) surveys of
rivers and lakes revealed elevated total mercury (THg) in Upper Peninsula waters and sediment relative to
downstate. Moreover, Western Upper Peninsula (WUP) fish possess higher methyl mercury (MeHg) levels
than Northern Lower Peninsula (NLP) fish. A contributing explanation for elevated THg loading is that
a century ago the Upper Peninsula was a major industrial region, centered on mining. Many regional ores
(silver, copper, zinc, massive sulfides) contain mercury in part per million concentrations. Copper
smelters and iron furnace-taconite operations broadcast mercury almost continuously for 140 years,
whereas mills discharged tailings and old mine shafts leaked contaminated water. We show that mercury
emissions from copper and iron operations were substantial (60–650 kg per year) and dispersed over
relatively large areas. Moreover, lake sediments in the vicinity of mining operations have higher THg
concentrations. Sediment profiles from the Keweenaw Waterway show that THg accumulation increased
50- to 400-fold above modern-day atmospheric deposition levels during active mining and smelting
operations, with lingering MeHg effects. High MeHg concentrations are geographically correlated with
low pH and dissolved organic carbon (DOC), a consequence of biogeochemical cycling in wetlands,
characteristic of the Upper Peninsula. DOC can mobilize metals and elevate MeHg concentrations. We
argue that mercury loading from mining is historically superimposed upon strong regional wetland
effects, producing a combined elevation of both THg and MeHg in the Western Upper Peninsula.
Environmental signicance
The manuscript addresses the enigma of low atmospheric mercury deposition and falling emissions in modern-day Upper Peninsula environments, yet elevated
THg and MeHg in rivers, lakes, and sh. For the rst time, we reconstruct 140 years of historical mercury emissions from copper and iron mining, showing how
mercury was broadcast broadly around regional environments up to the present. We compare historical deposition rates with a combination of modeling and
sediment core studies. Mining discharges (smelter emissions, tailing releases, mine sha seepage) appear superimposed upon high wetland methylation. With
forest recovery, wetlands are becoming even more abundant. Rather than mercury concentrations in piscivorous sh declining due to reduced atmospheric
inputs, we observe 1–3% increases. We show historically how the substantial mining inputs are superimposed upon wetland rebound with time delays in MeHg
production, helping explain some of the curious reversals.
Introduction
Mercury contamination of the environment from human
activity continues to be a global problem.
1–3
In 2015, 36 state-
wide mercury advisories were issued in the United States for
freshwater sh from lakes or rivers.
4
The extent of the problem
is pervasive, as the 2010 National Listing of Fish Advisories
included 4598 advisories that covered around 7.16 million
hectares of lake area and 2.09 million km of river stretches,
equivalent to 42 percent of the nation's total lake area and 36
a
Department of Biological Sciences, Michigan Technological University, Houghton, MI
49931, USA. E-mail: wkerfoot@mtu.edu
b
Department of Civil & Environmental Engineering, Michigan Technological
University, Houghton, MI 49931, USA
c
Department of Geological & Mining Engineering & Sciences, Michigan Technological
University, Houghton, MI 49931, USA
d
Visiting Scientist, U.S. EPA, Mid-Continent Ecology Division, Large Lakes Research
Station, Grosse Ile, MI 48138, USA
Cite this: Environ. Sci.: Processes
Impacts, 2018, 20, 708
Received 31st October 2017
Accepted 30th January 2018
DOI: 10.1039/c7em00521k
rsc.li/espi
708 | Environ. Sci.: Processes Impacts, 2018, 20, 708–733 This journal is © The Royal Society of Chemistry 2018
Environmental
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