Damage cost of the Dan River coal ash spill
Graphical abstract
Introduction
On February 2, 2014 two large stormwater drainpipes (36″ and 48″ diameter) underlying a coal ash disposal impoundment at Duke Energy's Dan River Plant collapsed, spilling approximately 39,000 tons of coal ash (Duke Energy revised figure, originally estimated at 82,000 tons) and about 27 million gallons of untreated ash wastewater into the Dan River at Eden, North Carolina (Duke Energy, 2014, NCDENR, 2014, Fig. 1). This event was the third largest coal ash spill ever recorded in the USA (Waterkeeper Alliance, 2014).
The volume of ash and wastewater, and its rapid release, overwhelmed the river's natural flow. The spill coated the river banks and left ash deposits on the river bottom several feet thick in some places, and changed the chemistry of the entire flow of the river due to poisonous metals and trace elements such as selenium, arsenic, and copper. Within days, the US Fish and Wildlife Service detected floating ash and benthic ash deposits at the mouth of Kerr Reservoir in Virginia, some 70 miles downstream (USFWS, 2014). The North Carolina Department of Environment and Natural Resources called the spill “an environmental disaster” (Zucchino, 2014).
In addition to chemical hazards from waterborne toxins, the physical habitat degradation (blanketing and smothering) caused by coal ash deposited after a spill is extremely damaging to benthic animals like mussels, clams, insects, snails, worms, crayfish, frogs, toads, salamanders, turtles, etc. A portion of the more mobile species such as fish may be able to escape the initial “ash tsunami” by moving long distances up or downstream (in the Dan River, only downstream movement is possible due to a large weir dam just upstream of the spill site), but this doesn't really prevent damage to the greater animal community. Some fish will stay and ingest toxic ash and be chemically poisoned (Tuberty, 2009). Many will leave, which causes mass exodus of populations and severe disruption of the natural ecosystem balance (Arcadis, 2012). The ash deposits will persist and some of their contaminants will move up the benthic food chain into fish and wildlife (Ruhl et al., 2010, Arcadis, 2012). In addition to direct impacts on animals and their habitat, there is a cascade effect of the ecological damage that influences human-related factors such as recreation, public health, consumptive uses, and property values. The environmental damage from coal ash spills into rivers can be catastrophic and the effects can be long-lasting. Research shows that when a riverine aquatic ecosystem is severely damaged from coal ash pollution, it may never fully recover to its “pre-pollution” biological condition and ecological balance. For example, a spill of smaller size in 1967 on the Clinch River in VA resulted in destruction of benthic communities and displacement of resident fish populations for over 70 miles (Lemly and Skorupa, 2012a, Lemly and Skorupa, 2012b). Natural recovery coupled with extensive restoration efforts (stocking) for endangered and threatened mussels carried out by the US Fish and Wildlife Service have not been able to restore the native river fauna to its pre-pollution condition after more than 30 years (Jones et al., 2000). Other examples of extensive, long-term damage of coal ash spills on water quality and river fauna include the Delaware River, PA and the Emory River, TN (Arcadis, 2012, Carriker et al., 2013, Lemly and Skorupa, 2012a, Lemly and Skorupa, 2012b, Ruhl et al., 2010).
The type of pollution and associated fish and wildlife impacts that have taken place in the Dan River due to coal ash results in diminished natural resource values that have both short-term and long-term negative economic effects at the local, state, and regional levels (Kopp and Smith, 1993, King, 1998). These values include (1) ecological costs (poisoning and blanketing/smothering of animals, displacement of animals, destruction of aquatic habitat and ecosystem function, associated animal replacement and aquatic habitat restoration costs), (2) sport/recreational costs (impacts to fishing, camping, hiking, boating, swimming, and associated costs including outfitters, guides, licenses, food, clothing, tackle/gear, bait, gasoline, vehicles, and other provisions), (3) human health and consumptive use costs (food value of poisoned or displaced edible fish, human health risks from elevated pollutants in edible fish, physical stress and anxiety), (4) property damage costs (lost/depreciated real estate values of waterfront property due to pollution), and (5) esthetic costs (inherent value of a clean and healthy ecosystem to non-users/recreators). Spatial extent of the damage and duration in time both add substantially to these costs.
Section snippets
Damage cost of the Dan River spill after 6 months
The cost calculations presented here were derived based on valuation parameters established by NC State Statute for fish and wildlife replacement, US Fish and Wildlife Service Natural Resource Damage Assessment principles and procedures, and case examples taken from the scientific and technical literature (Lemly and Skorupa, 2012a, Lemly and Skorupa, 2012b, NOAA, 2013). Because a large part of the environmental impact and associated economic costs of riverine coal ash spills can be long-term,
Physically and chemically altered benthic aquatic habitat
Coal ash that spilled into the Dan River coated the bottom for a distance of 70 miles, according to the US Fish and Wildlife Service and US Environmental Protection Agency (USFWS, 2014, USEPA, 2014). Deposits ranged from several feet deep near the spill site, to 5 inches at 2 miles downstream, 2 inches at 9 miles downstream, and one-half inch at 62 miles downstream. It is possible to analyze the nature of ash deposits themselves to ascertain the degree of habitat degradation that took place in
Damage element two – recreational impacts
From the time of the spill, recreational use of the Dan River decreased. This is evidenced by news reports and interviews with local individuals and businesses (e.g., News-Record 2014, Catanoso, 2014a, Visit-NC, 2014), and by the impacts due to issuance of a Recreational Water Advisory and Fish and Shellfish Consumption Advisory for the Dan River spill zone by the North Carolina Department of Health and Human Services on February 14 (NCDHHS, 2014a). These advisories recommended no direct water
Damage element three – human health and consumptive use
The hazard of coal ash to human health from eating contaminated fish or shellfish is clear from the consumption advisory for the Dan River issued by NCDHHS (NCDHHS 2014a). The hazard to human health from coal ash pollutants through direct contact with water is evident from the NCDHHS Recreational Water Advisory (NCDHHS 2014a). The damage cost from water contact is mostly captured in the lost recreational usage figure given above, as it includes those activities which would expose humans to
Damage element four – property damage and real estate values
The damage cost of coal ash spills on property values can be assessed through comparative market valuations before and after spill events, and by realtor comparisons of market prices of “equivalent properties” for waterfront parcels or acreages in a spill zone versus reference locations. This has not been done yet along the Dan River. The results of such an investigation would be valuable and essential for compiling a complete long-term cost determination of the Dan River spill. Property
Damage element five – esthetic values
Esthetic valuation is an important part of the damage cost of pollution impacts on the aquatic environment. It does not directly measure habitat degradation, poisoned animals, or human health effects. Rather, it captures the essence of the inherent value of a healthy ecosystem and what it means to the “greater good” of a healthy environment to our society and our planet. Esthetic values were given a high priority in a recent report used in support of efforts to designate the Dan River as a
Conclusions
A 6-month damage cost analysis for the Dan River coal ash spill breaks down as follows: Ecological Impacts = $113,412,000; Recreational Impacts = $31,507,500; Human Health and Consumptive Use = $75,565,500; Property Damage and Real Estate Values = Not Calculated; Esthetic Values = $75,000,000. The grand total 6-month damage cost is $295,485,000. This total will likely increase substantially as additional information on poisoning and chemical contamination of fish and wildlife becomes available
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