Monthly Archives: July 2016

Fact-Checking the History of Coal Ash Regulation in N.C.

July 27, 2016. Misunderstanding history makes it more likely  the same mistakes will be made again. In that spirit, a fact-check of recent DEQ statements1 about the history of coal ash regulation in North Carolina:

“In 2007, a previous administration changed landfill laws and specifically exempted coal-ash ponds from many environmental requirements.”

The statement seems to be referring to the Solid Waste Management Act of 2007 which amended landfill siting and construction standards.  Two provisions related to coal ash landfills, but nothing in the law directly addressed coal ash ponds. Coal ash was not the main focus of the 2007 law, which responded to several controversial applications to construct new landfills for household waste and construction debris. As a result, the law  focused on concerns specific to those  proposals — impacts on wildlife refuges and parks; the size and height of waste disposal areas; separation from groundwater; and guarantees the landfill owner could pay for  environmental remediation.

The first of two provisions in the 2007 law affecting coal ash allowed utilities to construct a lined coal ash landfill on top of an old coal ash disposal site under specific standards. The second provision exempted coal ash landfills on the site of a coal-fired power plant from some of the new landfill siting requirements.   Coal ash landfills located on power plant sites continued to be regulated as industrial landfills under standards that required liners;  groundwater monitoring; and setbacks from waters and wetlands. The Department of Environment of Environment and Natural Resources (“DENR”) did not request either coal ash provision.

“In 2009, the state exempted Duke Energy from having to show that its coal-ash ponds were structurally sound. If that information had been required, the corroded pipe under the Dan River coal ash pond might have been found and the spill avoided.”

In 2009, the General Assembly actually repealed a state Dam Safety Act exemption for coal ash impoundments. See Session Law 2009-390.   Before 2009,  coal ash ponds had been entirely exempt from the dam safety law.  Repeal of the exemption made coal ash impoundments subject to the dam safety law  for the first time — requiring compliance with dam safety standards; regular state inspections; and DENR review/approval of plans for expansion or repair.

DEQ’s statement may be focused on language in the 2009 legislation that allowed existing coal ash impoundments to “… be deemed to have received all of the necessary approvals  from [DENR]  and the Commission for Dam Safety for normal operation and maintenance”. In effect, the law allowed impoundments built before repeal of the exemption to continue to operate as if the state had permitted the original construction.  Those impoundments, however, would be inspected going forward and required to comply with dam safety orders to address structural deficiencies.  On balance, the 2009 legislation greatly increased rather than diminished state oversight of coal ash impoundments under the Dam Safety Act.

The Dam Safety Act amendments did not cause state and federal regulators to miss critical information about the Dan River stormwater pipe that later ruptured. Both the U.S. Environmental Protection Agency (EPA) and DENR dam safety staff became aware of the stormwater pipes at the Dan River impoundment in 2009-2010. Before inspecting N.C. impoundments as part of the federal response to the TVA coal ash disaster,  EPA asked electric utilities to provide information on  structural conditions at each impoundment site in the state. Maps of the Dan River site that Duke Energy provided to state and federal inspectors incorrectly identified the stormwater pipes as concrete rather than corrugated metal.   The error meant state and federal inspectors did not have complete and accurate information as background for the inspections,  but not because the 2009 law allowed electric utilities to shield information about the impoundments — it didn’t.

Note:  It later became clear that internal Duke Energy inspection reports had flagged the metal pipes at Dan River for attention as early as the 1980s. In accepting a plea deal to a large federal penalty for the Dan River spill,  Duke Energy acknowledged a pattern of neglect that included failure to take the advice of its own engineers in 2011 and 2012 to do camera inspections of the stormwater pipes.

“In 2010 federal regulators required leaks from all coal ash ponds to be evaluated. No action was taken in North Carolina for three years.” 

By 2010,  EPA  had taken several steps to get a better handle on coal ash impoundments. In 2009, EPA  launched the nationwide effort to assess the structural integrity of coal ash impoundments.   Based on information provided by the electric utilities, EPA did on-site inspections of  eight higher risk  N.C. impoundment sites in 2009-2010 including the Dan River facility.  Inspectors from the state’s water quality, waste management and dam safety programs accompanied EPA on most of those inspections.  Also in 2009-2010, state dam safety inspectors did an initial dam safety inspection of every coal ash impoundment as the first step in bringing those impoundments under the Dam Safety Act.

On a different track, EPA  provided new guidance to states on permitting  discharges  from coal ash impoundments under the Clean Water Act ; the new guidance recognized that  discharges could result from seeps and leaks through impoundment walls.  In 2010-2012, the state water quality program began increasing  groundwater monitoring requirements for coal ash ponds and  revising stormwater permits for impoundment sites. It may be that state programs gave higher priority to  structural impoundment problems, groundwater contamination and stormwater permitting in 2010-2012 and lower priority to  addressing the water quality impacts of leaks. It is difficult to know without more information.

“In 2011 the state gave Duke Energy approval to use Sutton lake, a recreational area in Wilmington, as a dumping ground for coal ash.” 

Sutton Lake has not been used for coal ash disposal. Coal ash from the Sutton Power Plant went into one of two coal ash impoundments;  outlets release water from the impoundments to Sutton Lake. Another outlet releases water from Sutton Lake to the Cape Fear River.  The earliest Clean Water Act permit for the Sutton Plant accessible on the DEQ  website (from 1996)  treated the outlet to the Cape Fear River as the permitted discharge point and applied effluent standards there. Although the permit also put water quality limits on discharges from the coal ash impoundments to Sutton Lake, the lake was regulated as a cooling pond — part of the wastewater treatment system — rather than as “waters of the State” protected under the Clean Water Act.  Every renewal of the 5-year Clean Water Act permit from 1996 through  2011 continued that approach. Apparently water quality staff revisited the question of whether Sutton Lake should be treated as a cooling pond or as “waters of the State”  in  2011, but decided to maintain the approach used in earlier permit renewals. In 2014, the department (now the Department of Environmental Quality) looked at the issue again and concluded — correctly, I think — that the permit should be modified to treat Sutton Lake as “waters of the State” and put effluent limits on discharges to the lake. It isn’t clear why the water quality program and the Environmental Management Commission reached a different conclusion in issuing and renewing earlier permits.

“For many years Duke Energy monitored the water under its ponds and found hundreds of samples that did not meet groundwater standards. Again, no action was taken. In fact, the prior administration created a policy instructing regulators not to fine Duke if the company said it would correct the problem.”

The state water quality program  first began requiring comprehensive groundwater monitoring for coal ash constituents in 2009-2010, imposing new groundwater monitoring conditions as Clean Water Act discharge permits for the impoundments came up for renewal.  The new conditions covered key contaminants associated with coal ash and required groundwater monitoring to be done under a state-approved plan to insure monitoring wells would be appropriately placed to detect violations.  Given the  time required to install monitoring wells and collect a full cycle of monitoring results, little data  showing a  groundwater standard violation related to coal ash would have been available before 2010.  None of the groundwater violations cited in DEQ’s  2014 enforcement action concerning the Sutton Power Plant predate 2009;  most come from the period between 2010 and 2014.

Before 2009-2010, most of the state’s coal ash impoundments operated without significant groundwater monitoring for decades.  Electric utilities built many of the impoundments in the 1960s and 1970s  before any environmental regulations applied.  In the late 1970s,  the state began issuing federal Clean Water Act permits for discharges from the impoundments to rivers, lakes and streams. Environmental regulation focused on the quality of water discharged from the upper layers of the ash ponds to surface waters rather than the coal ash itself.  In the 1980s-1990s, the state began putting  groundwater monitoring conditions on the discharge permits, but the monitoring focused on very basic parameters. For the Sutton Plant,  those parameters were:   water level,  pH, chlorides, iron, arsenic, selenium and total suspended solids. Groundwater concerns had not yet focused on contaminants specifically associated with coal ash.

Groundwater concerns increased after 2000 as EPA continued to lay the groundwork for a federal coal ash disposal rule. In 2006, electric utilities began voluntarily  monitoring for contaminants associated with coal ash in the face of pressure from environmental organizations and expected federal rulemaking.  Most of the data from the voluntary monitoring could not be used in state enforcement actions.  Under state groundwater rules, a violation exists only if the impoundment causes an exceedence of groundwater standards at or beyond a compliance boundary around the pond.  (For most N.C.  impoundments, the compliance boundary is set 500 feet from the edge of the pond.)  Wells used by the utilities for the voluntary groundwater monitoring had not been placed to document groundwater standard violations at the compliance boundary.  But based on the voluntary monitoring results,  the state water quality program  put broader groundwater monitoring conditions on impoundment permits and required monitoring to be done under a state-approved well-siting plan to insure the data could be used for future enforcement.

The enforcement policy mentioned in the DEQ statement refers to 2010 groundwater enforcement guidance developed by water quality staff.  Since the expanded groundwater monitoring requirements applied to facilities that had operated for many years without monitoring, the water quality program developed a policy that put the enforcement emphasis on remediation of contamination rather than assessment of penalties for activities that had been unregulated  or lightly regulated for much of the facility’s history.

What the fact-checked history suggests:

It is difficult to contain environmental impacts 20 to 40 years after the fact. Both state and federal regulators struggled to understand and address problems associated with a method of coal ash disposal electric utilities had already invested in and become reliant on by the time environmental impacts became a concern.

The basic arc of state and federal regulation looks like this: In the 1970s,  state and federal regulators focused on discharges from existing coal ash ponds to surface waters. There was a quiet period between issuance of the first Clean Water Act discharge permits for coal ash impoundments in the late 1970s through the 1990s.  Regulators assumed the electric utilities were maintaining the impoundments properly and indicators of  groundwater contamination associated with coal ash had not reached critical mass. EPA began working on a federal coal ash disposal rule in the late 1990s, but abandoned the proposed rule in 2000 in the face of strong political opposition. Between 2000 and 2008, troubling data on groundwater and surface water pollution associated with coal ash ponds accumulated and the 2008 TVA spill undermined confidence in the electric utilities’ maintenance of impoundments.  Both state and federal regulatory efforts accelerated in 2008-2009, leading to state permitting changes and renewed efforts to adopt a federal coal ash disposal rule. (EPA finalized the federal rule in 2015.)

The issues surrounding coal ash have not been the responsibility of any one administration or a single branch of government. The history spans multiple governors of both political parties and legislative as well as executive action.  Coal ash provisions in the 2007 Solid Waste Management Act came out of direct negotiation between the electric utilities and legislators.  In  2009, the General Assembly repealed the Dam Safety Act exemption for coal ash impoundments,  but did not move a bill to set comprehensive state standards for coal ash disposal out of committee.

Leaps in state law on coal ash  management followed specific crises — the coal ash impoundment exemption from the Dam Safety Act survived until the 2008 TVA spill put a spotlight on poor maintenance. In  2009, the  General Assembly had no interest in moving comprehensive coal ash disposal legislation; that only changed after the 2014 Dan River coal ash spill .

By 2009, accumulating evidence of groundwater contamination and other water quality concerns led the state water quality program to use existing permitting authority to require more groundwater monitoring around coal ash impoundments and increase stormwater requirements. Those  efforts to use existing permitting tools more effectively laid the foundation for later groundwater enforcement actions.

 

 1 The statements  in bold appeared in  a recent letter by DEQ Assistant Secretary Tom Reeder to the Raleigh News and Observer.

2016 Legislative Session in Review: Environmental Legislation

July 12, 2016. The 2016 General Assembly session resulted in changes to several environmental laws, but ended without final action on a major regulatory reform bill.  Among the more significant environmental provisions enacted outside the budget bill:

Coal Ash. House Bill 630 eliminated the Coal Ash Management Commission, giving the Department of Environmental Quality (DEQ) authority to make decisions about final closure of coal ash impoundments.  The bill also changed the criteria for prioritizing impoundment closures and required Duke Energy to provide a permanent alternative water supply to  well owners within 1/2 mile of a coal ash impoundments (unless separated from the impoundment by a river or lake) and to other well owners potentially affected by the migration of groundwater contamination from the impoundments. See an earlier post for more detail on H630  changes to the 2014 Coal Ash Management Act.

Commissions.  House Bill 630 responded to the Governor’s constitutional objections to three state regulatory commissions — the Coal Ash Management Commission, the Oil and Gas Commission, and the Mining Commission. The Governor successfully challenged  the laws creating  all three commissions as violating separation of powers; in part, the Governor objected to the legislature’s power to appoint a majority of each commission’s members.  A post on the N.C. Supreme Court decision can be found here.  The Governor vetoed an earlier bill (Senate Bill 71)  attempting to resolve the separation of powers issue by giving the Governor a majority of commission appointments.  The Governor’s position  on Senate Bill 71 suggested an ongoing objection to any  commission exercising executive powers unless the Governor had authority to appoint a majority of the members without legislative confirmation;  direct the actions of the commission;  and remove commissioners at will.

The Governor’s Office reportedly accepted H630 as a compromise. The  bill eliminates the Coal Ash Management Commission,  but retains the Oil and Gas Commission and the Mining Commission under conditions the Governor had previously objected to — legislative confirmation of appointees and the ability to remove commissioners only for cause. [Note: Although there have been indications that the Governor’s Office agreed to H630, the Governor has not yet signed the bill.]

Renewable Energy. Two provisions in Senate Bill 770 (N.C. Farm Act of 2016) amended laws related to renewable energy specifically to benefit agricultural sources, such as swine waste-to-energy projects. Sec. 10 of the bill extends the state’s renewable energy tax credit (25% of project costs)  to projects in service by January 1, 2020 (previously January 1, 2017) as long as the facility began construction by December 31, 2013.  The extension will likely benefit some swine waste-to-energy projects that have been in the works for several years, but are not yet generating electricity. Sec. 18 of the same bill gives  poultry and swine waste-to-energy projects priority over other renewable energy generation projects in connecting to electric utility delivery systems.

Sediment Pollution. Sec. 14 of Senate Bill 770 amends G.S. 113A-52.01 to add production of  “[m]ulch, ornamental plants, and other horticultural products”  to the list of agricultural activities exempt from the state’s Sedimentation Pollution Control Act (or “Sediment Act”). The Sediment Act otherwise requires activities disturbing an acre or more to maintain a stream buffer and use erosion barriers to keep sediment out of rivers, lakes and streams. The addition of ornamental plants will not raise many questions, but mulch is not an agricultural product similar to the others. Including mulch production in the Sediment Act exemption will raise two questions:

1. What kinds of operations will be covered by the mulch exemption?  Mulch operations include  large-scale municipal  waste disposal facilities that mulch yard waste and have no relationship to agriculture.

2. How will the mulch exemption affect Clean Water Act permitting? The exemption seems to go beyond the federal stormwater exemption for agriculture. That is important because most land-disturbing activities in N.C.  meet federal construction stormwater requirements by complying with the state Sediment Act.  If the Sediment Act exempts activities that don’t also fall under a Clean Water Act stormwater exemption, the activity may require  a separate federal stormwater permit.

What didn’t happen.   Several efforts to enact legislation significantly restricting wind energy development  failed, although Sen. Harry Brown has already indicated an intent to reintroduce a bill prohibiting erection of wind turbines in designated military air corridors in 2017. Proposals to repeal the ban on landfill disposal of electronics and to end the state’s electronics recycling program also failed.  Legislators apparently could not reach agreement on bills attempting to clarify the protocol for advising well owners on the heath effects of well contamination — an issue sparked by controversies over conflicting advice given to well owners near coal ash impoundments; those bills never got to a floor vote. The Senate received House Bill 593 (Amend Environmental Laws 2)  from the House and expanded the bill to include a number of additional  provisions on stormwater, beach nourishment, stream mitigation and other issues. The House did not concur in the Senate changes, leaving those proposals to die with adjournment.

2016 Legislative Session in Review: The Budget

July 7, 2016. A few notes on how the General Assembly allocated state funds for the environment.

A New Trend Toward Funding Environmental Studies at UNC-CH   The legislature directed (and in most cases funded) the University of North Carolina at Chapel Hill to study  or convene stakeholder groups on  environmental and natural resource policies rather than assigning those projects to the Department of Environmental Quality (DEQ)  or to a legislative study committee:

♦  The budget directs UNC to create a North Carolina Policy Collaborative  to “facilitate the dissemination of the policy and research expertise of UNC for practical use by State and local government”. The Collaborative will focus on research related to natural resource management, including “research related to the environmental and economic components of the management of the natural resources within the State of North Carolina and of new technologies for habitat, environment and water quality improvement.” The legislature appropriated $1 million to the UNC Board of Governors for the N.C. Policy Collaborative for the 2016-2017 fiscal year.

♦ A UNC-led stakeholder group will study efforts to “ecologically restore and achieve economic sustainability” the state’s shellfish aquaculture industry.  The budget provision directs the UNC-Chapel Hill Chief Sustainability Officer (Brad Ives, former Assistant Secretary in DEQ) to lead the stakeholder group. The legislature did not appropriate funds for the effort.

♦ The budget creates a new study of water quality programs to reduce nutrient pollution focused on the Falls Lake and Jordan Lake nutrient reduction strategies. See an earlier post for more detail on the substance of this  budget provision and the effect on enforcement of the Falls Lake and Jordan Lake water quality rules. The legislation gives the UNC-CH Chief Sustainability Officer responsibility for this study as well and provides funding  at $500,000 per year for six years. (The budget provision allocates an additional $1.3 million to DEQ in 2016-2017 to  study  in situ technologies to reduce nutrient impacts.)

These represent unusually large and extended state investments in environmental studies. The combined UNC/DEQ  appropriations for environmental research, collaboration and water quality studies total  $2.8 million just for FY 2016-2017. The UNC nutrient study will be  funded at $500,000 per year for  another five years beyond that. By comparison,  the legislature appropriated only $100,000  for a one-year study of another high profile environmental issue —  hydraulic fracturing — in 2011-2012.  Another reference point may be the annual budget of  $4.1 million for the state’s  non-point source water pollution program; the 2016-2017 appropriations for environmental studies represent 2/3 of the annual operating budget for the non-point source water pollution program.

Earmarked Funds for Water and Wastewater Infrastructure.  Most new funding  for DEQ’s Water Infrastructure Division to support local government water and wastewater projects has been earmarked for specific projects. Of the approximately  $18.8 million in water/wastewater funding added to DEQ’s  2016-2017 budget, the legislature directed approximately $16.6 million to the following projects:

$400,000 to an unnamed municipality  (population < 100) for wastewater improvements needed to eliminate illegal wastewater discharges.

$1,000,000 to Duplin County for improvements to the on-site wastewater system at an elementary school

$700,000 to the Town of Fontana Dam for wastewater system upgrades

$14.5 million to fund extension of water lines to cities and counties in an as-yet unformed Regional Water and Sewer Authority intended to include Guilford County, Rockingham County and one or more municipalities. If the Regional Water and Sewer Authority is not formed by June 30, 2017, the funds revert back to the state’ General Fund. (In other words, the funds cannot be allocated to other water and wastewater projects.)

Restoration of Funds for Commercial UST Cleanups and the Water and Air Quality Account:  Some  transportation-related environmental programs have long been funded by a small portion of the state’s gas tax.  Those programs include the Commercial Underground Storage Tank Fund, (which pays to clean up petroleum contamination from leaking underground storage tanks at convenience stores, gas stations and other businesses) and the N.C. air quality program. In 2015, the legislature replaced the on-going gas tax allocation to these two  programs with a one-time appropriation and ordered a program review.  The main purpose of the review was to look at the diversion of gas tax money from the Highway Fund to non-highway uses — a legislative concern for several years. The 2016 budget restores the gas tax allocation to both programs, putting them back on a stable (although not necessarily adequate)  funding source.