Tag Archives: Water Quality

Understanding the Court’s Coal Ash Order

Note: This post was updated to link to a different site for a copy of the judge’s order after the original source site became unavailable.

On March 6, 2014,  a  Superior Court judge issued an order reversing part of a 2012 declaratory ruling  by the N.C.  Environmental Management Commission (EMC) concerning regulation of coal ash ponds under state groundwater rules. The declaratory ruling case began in October of 2012 — before the Clean Water Act citizen suits of 2013 and the recent Dan River spill — as a request for an interpretation of state groundwater rules as applied to the coal ash ponds. The declaratory ruling request (filed on behalf of Cape Fear River Watch, Sierra Club, and Western N.C. Alliance) asked the EMC to  rule on three issues:

1. Operators of coal ash  ponds with Clean Water Act discharge permits first issued on or before December 30, 1983 must take corrective action (such as assessment and remediation) when their activity causes a groundwater standard violation — even if the violation occurs inside the compliance boundary around the ash pond;

2. Operators of coal ash  ponds with Clean Water Act discharge permits first issued on or before December 30, 1983 must take immediate action to remove sources of contamination causing a groundwater standard violation; and

3. These same requirements apply to owners of coal ash ponds that are closed and inactive.

Two background notes. State  rules recognize the possibility that waste disposal may cause groundwater contamination.  The rules generally only require corrective action at a permitted waste disposal site  if the waste disposal activity has caused a groundwater standard violation beyond a defined compliance boundary.  Corrective action can include assessment of the extent of contamination, steps to contain or reduce ongoing contamination and groundwater remediation. Landfills built to modern (post-1983) solid waste management standards have a  groundwater compliance boundary  of  250 feet around the perimeter of the waste disposal area or the property  line, whichever is closer.   Older facilities (like the coal ash ponds) generally have a  500-foot groundwater compliance boundary. See a previous post for  more on groundwater compliance boundaries.

December 30, 1983  becomes significant because state rules treat waste disposal sites that first received Clean Water Act permits on or before that date as unpermitted facilities.  (More about the logic of that assumption as applied to ash ponds later.) The rules require a different response to groundwater contamination found at an unpermitted waste disposal  site  as opposed to a permitted facility — presumably because newer facilities  have been built to more environmentally protective standards.

Judge Ridgeway’s Decision. On the first issue, Judge Ridgeway  agreed with the EMC, concluding that state rules only require corrective action if the waste disposal activity causes a violation of groundwater standards beyond the compliance boundary  around the disposal site.  Exceedence of a groundwater standard within the compliance boundary does not require corrective action except in extraordinary circumstances.  Although consistent with past EMC and DENR interpretations,  Judge Ridgeway’s decision leans heavily on new groundwater legislation adopted as part of the Regulatory Reform Act of 2013. (See the  earlier post for  more on the 2013 legislation.) According to the judge’s order, all of the parties to the declaratory ruling case  agreed that the 2013 legislation mooted the compliance boundary issue.

On the other hand, Judge Ridgeway decided the second issue (concerning immediate removal of the source of groundwater contamination) in favor of the petitioners. The  judge  relied on state rules  treating waste disposal  facilities first permitted under the Clean Water Act on or before December 30, 1983 differently from those permitted later.    The rules  classify  older facilities   as  unpermitted  and  a groundwater standard violation at an unpermitted waste disposal site triggers a requirement to immediately remove the source(s) of contamination.    All of the coal ash ponds in the state  first received a Clean Water Act discharge permit before December 30, 1983.

Treating the ash ponds as unpermitted waste disposal  facilities  is  key to the  judge’s ruling  that  the utility companies must immediately remove the contamination source at any ash pond that has caused a groundwater standard violation beyond the compliance boundary.   Removal of the source of groundwater contamination associated with  a coal ash pond clearly has huge implications, since the  primary  source of contamination is the coal ash itself. Under the rules, a groundwater standard violation at a permitted waste disposal facility  may require corrective action, but not  necessarily  removal of  waste causing the contamination.

Judge Ridgeway disposed of the third issue by briefly noting that the laws  and  rules don’t distinguish between active and inactive waste disposal facilities.

Potential confusion.  Judge Ridgeway’s order seems to treat  coal ash ponds as permitted waste disposal sites in deciding the first issue  and as unpermitted waste disposal sites in deciding the  second. The 2013 legislation the judge relies on  to decide  the first issue  clearly  applies to waste disposal systems that require an individual permit under either  water quality or waste management laws. The  new statute language  limiting the EMC’s power to require corrective action  inside the compliance boundary  begins with these words: “When operation of a disposal system permitted under this section results in an exceedance of the groundwater quality standards…”

It seems clear that the 2013 legislation can only benefit operators of waste disposal facilities holding individual  water quality or waste management permits.  Having given  coal ash ponds the benefit of the new law on the first issue, the judge does not explain why the  coal ash ponds are treated as unpermitted waste disposal  facilities in deciding the second.  The judge relies on  state rules that predate the 2013 legislation to identify the kind of corrective required at the ash ponds even though  the new law  also addresses  corrective action —  without making any distinction based on the permitting history of the facility:

“(k) Where operation of a disposal system permitted under this section results in exceedances  of the groundwater quality standards at or beyond the compliance boundary established under subsection (i) of this section, exceedances shall be remedied through cleanup, recovery, containment, or other response as directed by the Commission.”

It is possible that Judge Ridgeway saw no conflict between the new law on corrective action and existing groundwater rules  on corrective action at  older facilities, but the decision does not explain how he reconciled the  two.

Permitted or unpermitted and  does it matter? There may well be an appeal of Judge Ridgeway’s  decision.  By assuming the coal ash ponds have a different permitting status for purposes of the two major issues in the case, the decision awards each side a win and a loss. It is conceivable that at least one party to the case would prefer two wins.

The permitted/unpermitted conflict  just emphasizes again the peculiar regulatory status of coal ash ponds. EMC rules treating pre-December 30, 1983 waste disposal sites as “unpermitted” makes perfect sense  in the context of truly unauthorized waste disposal sites or  older landfills that closed rather than meet new standards for  solid and hazardous waste disposal that went into effect in 1983.  It makes less sense as applied to coal ash ponds that largely fell under the jurisdiction of the Utilities Commission until 2009 and never had an  obligation to comply with solid and hazardous waste regulations.   In fact, the coal ash ponds continued to operate for decades after 1983  — subject only to Clean Water Act permits for discharges from the ponds — with the acquiescence of both state and federal policy makers.  That only began to change in 2009 after the TVA ash spill drew more attention to the risks.  Then,  the state somewhat increased environmental oversight for the ponds — but  failed to  enact comprehensive coal ash disposal legislation  much less demand  immediate closure of the ash ponds.

Since coal ash ponds  operated  outside of  most  environmental regulatory programs for  years,  existing laws and rules don’t fit either operation or closure of the ash ponds very well. As badly as the state needs a solution to the problems surrounding coal  ash ponds, Judge Ridgeway’s order in itself is not likely to be the answer.  A solution will require standards for coal ash disposal;  a process for safe closure of coal ash ponds;  priorities for closure;  and  assessment of environmental damage and ongoing risk at existing facilities. It’s going to require legislation.

Regulatory Reform and the Environment III: The Future

December 4, 2013. Two earlier posts  looked at  the history of regulatory reform in North Carolina and regulatory reform’s  focus on environmental rules.  The current General Assembly has continued  to work on regulatory reform in general and  limiting environmental rules in particular.  Regulatory reform legislation adopted by the N.C. General Assembly since 2011  reflects two basic  ideas: 1. Some number of agency rules are simply unnecessary and should be repealed;  and 2.  If  a federal  environmental standard exists, state and local environmental rules should not go beyond the federal requirement except in extraordinary circumstances. More about the  assumptions behind  recent regulatory reform efforts below.

Assumption: State agencies have unnecessary and overly burdensome rules that should be repealed. There will always be a need to review, update and in some cases repeal outdated rules, but it is not clear that rooting out “unnecessary” rules can  do much to turn down the political heat over regulations. It isn’t for lack of trying. In October 2010, Governor Beverly Perdue issued an executive order on regulatory reform.   Executive Order 70    invited citizens to identify overly burdensome and unnecessary rules and  directed state agencies to  do  an internal review to identify unnecessary and outdated rules.   In 2011, the General Assembly’s  Regulatory Reform Committee   invited the public to identify “outdated,  unnecessary, unduly burdensome, or vague rules…that are an impediment to private sector job creation”  in a series of public meetings. The  legislature also amended the state’s Administrative Procedures Act in 2011 to put the rules review process created under Executive Order 70 into  law.  G.S. 150B-19.2 

The earlier post on the history of regulatory reform describes the somewhat underwhelming results of both efforts to root out unnecessary and overly burdensome rules.  Although state agencies identified several hundred unnecessary rules  through the internal review required under Executive Order 70 , most of those rules related to programs that no longer existed or had been superceded by new standards.  Since the rules were no longer being enforced, repeal  did nothing to ease complaints about regulatory burden. On the other hand, rules identified by citizens as unnecessary or unduly burdensome often turned out to be required  by  state or federal law or the result of a significant  policy  debate and unlikely candidates for  a politically painless  repeal.

The  Regulatory Reform Act of 2013 (Session Law 2013-413 ) takes  a  new  approach,  requiring state agencies to review and readopt all existing rules every ten years.  If a rule is not reviewed   on the schedule set by the state’s Rules Review Commission, the rule automatically expires. (Rules needed to carry out a delegated federal program  will not automatically expire,  but  still have to be reviewed and readopted.)   Continuing its preoccupation with environmental rules, the General Assembly directed the  Rules Review Commission to schedule state water quality standards and wetland rules for the first round of review in 2014.  Ten-year review and readoption  may one day settle into a manageable  routine,  but several potential pitfalls  lie ahead:

— Given N.C.’s lengthy rulemaking process,  a 10-year  readoption  schedule could lead to constant churning and little certainty for either regulators or the public.  Nothing in Session Law 2013-413 shortens the process for readoption of an existing rule, so the agency would need to go through all of the usual rule adoption steps: public notice, fiscal analysis, review by the Rules Review Commission, and  possible legislative disapproval.  The Falls Lake nutrient rules took about five years from beginning to effective date and the rules include some requirements that phase-in even later.  Streamlining the process for readoption and starting the ten-year review period at full implementation of a rule (rather than adoption)  could reduce the churning.

— Review and readoption of rules will be even  more disruptive if it is used to constantly revisit policy decisions rather than simply identify outdated, unnecessary rules. The fact that the General Assembly targeted water quality and wetland rules for the first round of review and readoption suggests  a policy agenda.  Public statements by the director of  the state’s water quality programs,  Tom Reeder,   indicate that  the Department of Environment and Natural Resources has already put  stream buffer and  wetland rules  — repeatedly targeted by development interests — in the spotlight for the first round of water quality rule review.

— Complex sets of rules have to be reviewed together. Stream buffer rules, for example,  have  generally been adopted as part of  a larger plan to solve a specific water quality problem. Federal law requires the state to  reduce  pollution causing impaired water quality  (like the nutrient problems in Falls Lake and Jordan Lake), but federal rules do not dictate  the solution.    North Carolina ‘s longstanding  policy has been to create  a solution that shares the burden of pollution reduction among all of the major pollution sources (wastewater treatment plants, industrial dischargers, agricultural runoff and development activity).  In most cases, the final rules also represent a long negotiation process.  Using rule review  to respond to one  interest group could shift  more of the regulatory burden and cost  of pollution reduction to others.  A piecemeal approach to regulatory reform carries the risk of making complex environmental protection programs less effective and less equitable, but no less politically charged.

— The interrelationship of rules has practical implications.  According to Tom Reeder, the legislative  mandate  to review surface water standards and wetland rules in 2013 also  draws in two additional sets of rules.   Mr. Reeder expects the 2014 water quality rule review  to  involve  395 rules.

— Rule review comes without any additional staff resources. The massive water quality rule review will create a new workload for a water quality staff still shrinking under budget cuts and reorganization decisions. Mr. Reeder has already suggested that  rule review may further delay  revisions to state water quality standards  needed to  comply with federal  Clean Water Act requirements.

Assumption: State and local environmental standards should not go beyond federal standards except in extraordinary circumstances.

The Regulatory Reform Act of 2011     ( Session Law 2011-398 )  prohibited  state environmental  agencies — and only environmental agencies — from adopting  a more restrictive standard than a corresponding federal rule.   The  law has exceptions  for  rules to address a “serious and unforeseen threat to public health, safety or welfare” and rules required by state law, federal law, state budget policy or a court order. The same legislation directed all state agencies to provide the General Assembly’s Joint Select Regulatory Reform Committee  with a list of existing rules and indicate for each rule whether the rule was mandated by federal law and whether the  rule was more stringent than an analogous federal regulation. (The session law defined analogous to mean that a federal rule regulated the same conduct or activity.)

An earlier post (originally written about a 2013  Senate  bill)  provides examples of state environmental rules that go beyond  the  corresponding  federal rule.  (The examples come from the 2011 DENR report to the Select Regulatory Reform Committee.)  The post also notes some of the  difficulties in  limiting state environmental rules to  federal standards.  At the most basic level, it turns out to be harder than legislators may think to even figure out whether a state rule is “more stringent” than a corresponding federal rule. It is rarely as easy as comparing two numerical standards; in many cases, federal rules set a framework and goals in the expectation that the state will fill in the detail.  Another  problem is that  federal environmental  statutes and rules set a floor rather than a ceiling on environmental protection — a floor based on national priorities  rather than state needs.   Finally, federal rules rarely   include all of the administrative pieces needed for  a complete environmental protection program. Since the states actually carry out most of these programs, Congress and EPA  left the states a good bit of  flexibility  in setting up permitting and enforcement programs.

Having put limits on new  state environmental rules in 2011, the 2013 General Assembly took on local environmental ordinances.  Session Law 2013-413 puts a one year moratorium on adoption of new local environmental ordinances regulating issues addressed by state or federal environmental rules. An earlier post goes into more detail about the temporary  limit on local environmental ordinances. The one-year moratorium actually represents a compromise to allow time for the legislature’s Environmental Review Commission to look at the appropriate scope of local government authority to adopt environmental standards. The N.C. Senate had proposed to permanently restrict adoption of local environmental ordinances.

Even the one-year moratorium may be a problem for local government.  A number of cities and counties operate environmental infrastructure (like water and wastewater treatment systems) under state-issued permits that require the local government to put  environmental protection measures in place by ordinance.

Behind all of this lies a genuine concern about the layering of federal, state and local requirements. Citizen comments  clearly indicate confusion about where environmental standards come from and how different requirements  fit together.  In spite of everyone’s best efforts, the overlay of federal  rules, state rules  and local ordinances don’t always fit together perfectly.  Conflicts  get  resolved, but the property owner caught up in an unintended consequence of overlapping standards will be understandably frustrated in the meantime.

Which is all to say that there are good reasons to look at the intersection of federal, state and local environmental standards. It is just not as easy as waiving away everything other than the standard adopted by the highest level of government.

Regulatory Reform and the Environment II: Targeting Environmental Rules

November 21, 2013.   In North Carolina,  “regulatory reform” has had a strong focus on environmental rules for  nearly twenty years. An earlier post sketched a very broad history of regulatory reform in N.C. starting with the creation of the Rules Review Commission in 1986. But from 1977 into the early 1980s,  the General Assembly  actually had an Administrative Rules Review Committee made up of legislators. The committee tracked the number of rules adopted by state agencies and reviewed rules for statutory authority. I was able to find committee reports from 1979-1983. (After that, the online  trail went cold.)  The reports list all of the rules the committee objected to for lack of statutory authority and how those objections were resolved. Environmental rules didn’t  receive  much   attention from the committee; some of the most common objections concerned rules assessing fees not authorized by law; state agencies creating criminal penalties by rule;  and professional licensing  boards overstepping their authority.

Environmental rules may have had a lower profile simply because of  the times. Congress  had just adopted the major federal environmental protection laws  in the early to mid-1970s —  the Clean Air Act  in 1970, the Clean Water Act  in 1972, the  Safe Drinking Water Act in 1974 and the Resource Conservation and Recovery Act (regulating hazardous waste)  in 1976.  In the 1970s and early 1980s,  state environmental agencies were  adopting rules  needed to run delegated permitting programs under those federal laws: water quality  and air quality standards; drinking water regulations;  hazardous waste permitting rules;  and regulations for petroleum underground storage tanks. Environmental rulemaking may not have been without controversy, but  there was also significant support for environmental programs and for the most part  the General Assembly seemed to let the  regulatory agencies  handle the controversies.

That started to change as water quality rules in particular began to have a greater impact on development activity. The first generation of  environmental permitting rules largely affected local government and  industry.  In the water quality program, local government wastewater treatment plants  and industries directly discharging wastewater to a stream  needed a Clean Water Act permit.    A developer only needed an environmental permit if the project involved filling wetlands or a segment of stream.  As  the state  began to grapple with the impact of development activity on  coastal resources and water quality in the late 1980s, environmental  permitting came to have a much greater effect on developers and private property owners.

By 1984, the state’s Coastal Resources Commission had adopted the first standards for development on the state’s ocean and inlet beaches. Those rules included oceanfront setbacks and restrictions on use of seawalls and jetties to protect oceanfront structures from erosion.  In the late 1980s, the state’s water quality program  began  work on  rules to address high bacteria levels in coastal shellfish waters.  Those  rules included the first state stormwater management requirements for new development projects.  Since then, a  series of water quality initiatives have used stormwater  standards, density limits and  riparian buffers to reduce the impact of polluted runoff from developed areas. A combination of density limits, buffers and stormwater controls became part of the basic water supply watershed program designed to prevent pollution of drinking water supplies. Those same tools became part of the comprehensive water quality strategies to reduce nutrient over-enrichment in the Tar-Pamlico River, Neuse River,  Falls Lake and Jordan Lake.  In the nutrient  strategies,  development standards represented one part of a much larger set of pollution reduction measures  that also  included  tighter controls on wastewater discharges and  best management practices to limit agricultural runoff.

Legislative  Disapproval of  Environmental Rules.  Legislative action on regulatory issues can  take other forms, but tracking disapproval bills gives a fair indication of where legislative attention has been  focused. For the first few years after the General Assembly amended the Administrative Procedure Act to allow for legislative disapproval of rules, virtually all of the disapproval bills concerned environmental rules.  The first disapproval bills introduced in the General Assembly (in 1998) targeted the Neuse River stream buffer rules and the Tar-Pamlico nutrient  rules (which also included buffer and stormwater requirements).   Based on a  search of the General Assembly bill database, legislators introduced bills to disapprove at least 41 state agency rules between 1998 and 2012.   Sixteen of the disapproval  bills  targeted environmental protection rules;  in some cases, a single bill  covered multiple rules. Another four bills proposed to disapprove Wildlife Resource Commission regulations. All of the other regulatory programs in state government (public health, worker safety, building code, occupational licensing boards, food safety, insurance regulation, etc.)  accounted for just another 16 disapproval bills during the same period. (See Legislative Disapproval Bills for a complete  list of the disapproval bills that I  found.)

Of the 16  bills to disapprove environmental  rules, ten concerned water quality rules.  The list  includes the Neuse River  buffer rules, the Tar-Pamlico River nutrient rules, coastal stormwater rules, rules classifying streams as trout waters or Outstanding Resource Waters,  water quality standards for municipal storm sewer systems,  and the Falls Lake and Jordan Lake nutrient management strategies. That list of water quality rules includes  the most debated (and negotiated) environmental rules adopted in the last 15 years, addressing some of the state’s most complicated water quality  problems. One common thread  is that all of those regulations  use development standards as one tool to address a water quality problem. The other common (and related) factor is that all encountered opposition from realtors,  developers, and owners of waterfront property.

Amending the APA to make environmental rulemaking more difficult. There has also been an effort to make environmental rulemaking more difficult by putting limits or requirements on environmental rules that don’t apply to other kinds of regulations. In 2005, the General Assembly  amended G.S. 150B-21.4 ( fiscal notes on rules) to require a special fiscal analysis of environmental rules — and only environmental rules — affecting state highway projects. The change responded in part to expansion of   stormwater  requirements,  which affected state highway projects as well as conventional building projects.

In 2009, several House and Senate bills proposed to put a moratorium on  rulemaking by the state’s Environmental Management Commission (the citizen commission  that adopts air quality and water quality rules).  House Bill 1335 actually passed the House and received a favorable report from a Senate committee before being pulled off the Senate floor without a vote.  But the 2011 Regulatory Reform Act, Session Law 2011-398, picked up the effort to restrain environmental rulemaking  and put new  limits on environmental rules that do not apply to other state rules.   G.S. 150B-19.3 prevents a state environmental agency from adopting a rule that is more stringent than a corresponding  federal environmental rule except in very limited circumstances.  As a practical matter,  the new law  will  be much more difficult to apply than legislators may have expected. Many federal environmental rules  provide  a framework for regulation rather than comprehensive standards and permitting procedures, making the “more stringent than” comparison difficult to impossible — although it should provide fertile ground for argument.  More about the policy implications of handcuffing state environmental regulations to federal rules in  a future  post.

The focus on environmental regulations continued in the  2013 Regulatory Reform Act, Session Law 2013-413.  The  most recent  legislation requires review of existing rules every ten years causes rules to automatically expire if the review does not occur. Although the review requirement  applies  to all state regulatory programs, the legislation specifically directs the  Rules Review Commission to schedule existing state water quality and wetland rules for the first round of review in 2014. The legislation also puts a one-year moratorium  on adoption of local government ordinances that address environmental issues  covered  by state and federal environmental rules. During that year,  the legislature’s Environmental Review Commission will study local government authority to adopt environmental ordinances. Like the 2011 limitation on state environmental rules, the moratorium on local ordinances almost certainly has some unintended consequences. More about that in a future  post as well.

Why has regulatory reform come to focus so heavily on water quality rules?   In one way, water quality rules seem  to be an odd focus for so much regulatory reform activity since federal requirements drive so many of the rules.  But while  federal law requires the state to  reduce  pollution causing impaired water quality  (like the nutrient problems in the Tar Pamlico River, Neuse River, Falls Lake and Jordan Lake), federal rules do not dictate the remedy.  The legislative disapproval bills have targeted the remedy —  a comprehensive strategy that reduces direct discharges of the pollutant (from wastewater treatment plants and industrial dischargers) and indirect runoff from agriculture and developed areas.

In these instances, things happening under the banner of “regulatory reform” are not so much about eliminating unnecessary and burdensome regulations. It is really about how the state will  solve complicated environmental problems and whether  the burden of pollution reduction will be shared by all of the sources contributing to the problem.  Since  2013  legislation also delayed further implementation of the Jordan Lake rules to  convene a  legislative study committee on Jordan Lake water quality (see Session Law 2013-395), the current General Assembly will have  a chance to  struggle with  those questions.

The Direction of the State’s Water Quality Program

September 19, 2013.  Earlier posts talked about two unusual recent  decisions by the Department of Environment and Natural Resources (DENR) on Section 401 water quality certifications  under the Clean Water Act — one concerning  Cleveland County’s proposal to build a new dam on the First Broad River to create a reservoir and the other for federal relicensing of Alcoa’s existing hydroelectric power dams on the Yadkin River.  You can find the Cleveland County  post here and the Alcoa post here.  The question is what those two decisions  say about the current direction of the water quality program.

The  decision to waive the water quality certification for the proposed Cleveland County reservoir — the first deliberate waiver in the history of the N.C. water quality program — cited  a state rule requiring  a decision on a 401 application within 60 days. But  the Cleveland County application was not complete and DENR made no effort to go through the review process (which would have  required an environmental impact statement and a public notice).  As reported in the Charlotte Observer, Division of Water Resources Director Tom Reeder gave a different explanation of the waiver: “The state of North Carolina looked at all of this and said there’s really no value added to us getting involved in this whole thing. Cleveland County would have had to spend more money that would not go to any good purpose.”  The implication was that a state water quality review would add more time and cost when the U.S. Army Corps of Engineers (as the federal permitting agency) opposed the project — even though the state water quality review and the federal permit review usually go hand in hand and rely on the same environmental studies.

Where the Cleveland County project  proposed construction of a new dam;  Alcoa applied for a state water quality certification to cover continued operation of four existing dams on the Yadkin River that were built between 50 and 100 years ago to generate power for the now-closed Alcoa aluminum smelting plant. After nearly a year of review and a public hearing, DENR suddenly denied the Alcoa 401 Certification. The denial letter cited a state rule requiring the  applicant to have title to the project site, the permission of the property owner or the  ability to acquire the property by condemnation.  DENR relied on a lawsuit (filed the same day) claiming state public trust ownership of  the bed of the Yadkin River under the Alcoa dams to conclude that Alcoa  could not show title to the land  under the dams. According to the letter, the lack of either title or permission from the state would make it difficult to assure that Alcoa could meet water quality conditions on operation of the dams.

The earlier posts talked about a number of questions raised by the two decisions. There are also a few things to take away:

DENR has waived a 401 Certification without clearly explaining the reason for the waiver or how waiver decisions will be made in the future.   The decision letter suggests the waiver resulted from DENR’s inability to make a decision within 60 days, but the record shows no attempt to get the additional information needed to make the application complete, provide a public notice of the application or do a complete review.  The  Division of Water Resources director later suggested that  state review would have served no purpose given the Corps of Engineers’ objections to the project. Either reason could also easily apply to other 401 applications.

As to the first explanation,  DENR denied the Alcoa 401 application one month later  after nearly a year of review  with no suggestion that water quality rules required a waiver.  The second reason offered for the waiver (U.S. Army Corps of Engineers opposition) also applies to other projects. The Corps of Engineers often presses federal permit  applicants to look at other alternatives with fewer environmental impacts.   The Corps expressed similar skepticism about the City of Raleigh’s  proposal to build a reservoir on the Little River, but in that case DENR has continued to work with  Raleigh and the Corps of Engineers to look at alternatives and  address the Corps’ concerns.  The same has been true for other large commercial development projects.

DENR treated the Cleveland County reservoir project differently, but has not provided a consistent explanation of the decision or criteria for future 401 Certification waivers.

Denial of  a 401 Certification based on an unresolved claim of public trust ownership of the river bed under the project has implications well beyond Alcoa.   If there is a case to be made for public trust ownership of the upper reaches of the Yadkin River,  the same will be true for  many of the state’s inland rivers. The decision may have implications for  dam  sites proposed by Cleveland County and the City of Raleigh (on the First Broad River and the Little River respectively).

Title to the bed of the Yadkin River under the Alcoa dams  has not yet been determined by the courts, but DENR issues both Individual and general 401 Certifications for a wide range of projects  known to be on state-owned  public trust lands — including mining activities, utility and energy infrastructure, marinas, aquaculture operations, shoreline stabilization projects, water intakes, and dams.  The justification for denial of the Alcoa 401 Certification — that lack of ownership or permission from the state to apply  calls into question the applicant’s ability to comply with water quality conditions — would apply equally to those projects.

DENR has not explained what evidence of title will be required of applicants proposing to construct a project in navigable waters.    A deed to submerged lands may or may not be valid. See the earlier post on public trust doctrine for more explanation of public trust ownership and the way title to state-owned public trust lands can be transferred.   But the existence — or absence — of a state lawsuit claiming title under the public trust doctrine cannot be the deciding factor either.  Public trust ownership does not arise because of a state lawsuit; it is not negated by the absence of one.  Having made public trust ownership a factor in the issuance of 401 Certifications, DENR needs a clear and consistent approach to resolving questions of title to lands under coastal waters and navigable rivers; otherwise the outcomes will be arbitrary and subject to political influence.

The Alcoa denial letter suggests that Alcoa needs specific state permission to apply for a 401 Certification to continue operating the Yadkin hydropower dams, but does not indicate what form that permission must take. Some  activities on state-owned public trust lands have individual submerged lands leases from the State Property Office, but many do not. The state has often relied on environmental permits as the permission to develop on state-owned submerged lands.  It isn’t even clear whether a previous  lease to construct on state-owned public trust lands would be sufficient, since the state’s lawsuit claiming ownership of the Yadkin river admits that Alcoa had permission to build the four dams.

The precedent set by the Alcoa denial could apply to a number of  ongoing commercial activities in coastal waters and state rivers.  One of the (several) interesting things about the Alcoa decision is that it dealt with renewal of an operating license for dams built decades ago with state permission. The DENR denial letter suggests that the state must give express permission for the renewal of licenses and permits for ongoing operations on state-owned public trust lands — activities that could include aquaculture, marina operations, sand mining and other commercial activities. The criteria for granting or denying permission will be another question.

The troubling thing about the Cleveland County and Alcoa decisions is the reliance on rule interpretations that not only break with past practice, but are inconsistent with each other.  With respect to the waiver of a 401 Certification under the 60-day rule, DENR needs to reconcile the Cleveland County and Alcoa decisions. If opposition by the Corps of Engineers was the real reason for the Cleveland County waiver, DENR should explain the criteria for waiver in situation where the Corps has pressed an applicant for alternatives. DENR also needs to  provide  guidance to applicants proposing projects in coastal waters and inland rivers.  Otherwise,  applicants will have little assurance of a clear, consistent and predictable water quality review.

The Uses of a Water Quality Certification: Alcoa

September 9, 2013.   On August 2, 2013, DENR’s Division of Water Resources denied a Section 401 water quality certification for the relicensing of Alcoa’s four hydroelectric dams on the Yadkin River.   (See an  earlier post  for background on  401 Certifications.) The denial letter did not cite any water quality basis for denying the 401 Certification. Instead, the letter  referred to a lawsuit filed the same day by the N.C. Department of Administration  that: 1.  claimed title to the bed of the Yadkin River under the Alcoa dams as public trust land;  and 2. asked the court to   recognized State ownership of the Alcoa dams  based on public trust ownership of the riverbed under the dams.  The significance of the Alcoa 401 Certification denial is that  many projects requiring 401 Certifications are located  in waters that may be covered by the public trust doctrine. The Alcoa  denial raises  some interesting questions about   issuance of  401 Certifications for  activities in rivers and streams in particular.   First, some history on Alcoa’s dams and  the public trust doctrine.

History.  Alcoa operates four dams on the Yadkin River to generate electricity.  Alcoa bought an  unfinished aluminum smelting plant in the town of Badin from a French company in 1915, completed the plant and began operation in 1917 powered by the newly constructed Narrows Dam on the Yadkin River.  As power demand increased, Alcoa  built three more hydroelectric dams on the Yadkin  —  at the Falls (1919),  High Rock (1927)  and Tuckertown (1962).   After Congress strengthened the federal role in permitting hydroelectric power projects,  Alcoa received  a 50-year federal  license to operate the dams (together  known as the “Yadkin Project”) in 1958.  In 2002, Alcoa  began the process of renewing the federal license.

For two years, a group  of North Carolina local governments, state agencies (including DENR), federal  agencies, lakefront homeowners associations, and environmental organizations met  to develop recommended license conditions for the Yadkin Project.  The   group  reached agreement on measures to protect water quality and habitat; provide public access; maintain lake levels and adequate  downstream flows; and create a drought management system for the area affected by the Yadkin Project.  The group submitted the proposed conditions to the Federal Energy Regulatory Commission (FERC) in 2007.  You can find a description of the 2007  relicensing settlement agreement  here.

Shortly after the settlement agreement had been signed,  Alcoa stopped all production at the Badin aluminum works and eliminated the last 30 jobs at the plant.  At its height, the Badin aluminum works employed about 1,000 people, but production had declined over a ten-year period.  As the demand for power at the Badin works lessened, Alcoa  started selling electricity from the Yadkin Project on the wholesale market.  Complete shutdown of the Badin plant set off a backlash. Stanly County, which  did  not sign the relicensing settlement agreement, demanded that Alcoa compensate the county for jobs lost  in the  shut down of the  Badin works and raised concerns about industrial contamination in the area of Alcoa’s Badin plant.  Stanly County  and others opposed to  renewal of Alcoa’s  FERC license  persuaded Gov. Beverly Perdue to intervene in the FERC relicensing and  request transfer of the  Alcoa  license to the State of North Carolina. FERC’s decision on relicensing of the Yadkin Project has now been on hold for several years waiting for the state to make a decision on issuance of a  401 Certification for operation of the dams.

In 2009, DENR   issued a  401 Certification for the Yadkin Project. The certification required   Alcoa to upgrade the hydroelectric generation facilities and make operational changes to improve downstream water quality and  restore flow to streams affected by operation of the dams.  DWQ revoked that  401 Certification in late 2010 after discovering that  information submitted by  Alcoa during the application review  may have been misleading.  After resolving DWQ’s  concerns, Alcoa reapplied for a 401 Certification last  year.   DWQ was  moving toward issuing a new 401 Certification  for the Alcoa dams — there was  a public hearing on a draft 401 Certification  in  May  — when DENR suddenly reversed direction and denied the 401 Certification on August 2, 2013 citing the McCrory administration lawsuit filed the same day. You can find documents related to Alcoa’s recent 401 application (including the denial letter and the complaint in the McCrory administration lawsuit) here.

Public Trust Doctrine. Under ancient law brought to the American colonies from England,  lands under navigable waters are owned by the sovereign and held in trust for the public.  The “public trust doctrine” protects the right of  the public to use the  waters for navigation, fishing, and recreation.  After independence, the states acquired title to public trust lands previously held by the King. Since the state holds lands under navigable waters in trust for the use of the public,  the state rarely transfers ownership of  those lands  outright.  On the other hand, the state  allows many private activities on  state-owned public trust lands — both commercial and non-commercial. Most of the docks, piers, marinas, and fish houses in  coastal waters have been built on state-owned public trust lands.   You will  find  other commercial activities in  coastal waters, rivers and streams including  aquaculture operations,  mining,  commercial recreation facilities,  and  dams (used for various purposes).

The  McCrory administration lawsuit admits  that  Alcoa had state permission to build hydroelectric dams on the Yadkin River. In the late 18th and early 20th century,  the General Assembly allowed a number of companies to build hydroelectric dams and mill dams on state rivers by  special legislation.  It is not clear that the state claimed ownership of the bed of the Yadkin River at the time.  Some early laws authorizing construction of dams on the Yadkin  refer to construction on “non-navigable” sections of the  Yadkin River  and a number of  state court decisions  recognized private ownership  of the bed of the Yadkin River  at  specific locations.   In Rose v. Franklin, 216 N.C. 289, 4 S.E.2d 876 (N.C., 1939), the N.C. Supreme Court noted that the parties to a title dispute admitted that the Yadkin River was a non-navigable stream as it passed through the town of Elkin and found that the plaintiff owned to the center of the river.

Until the 1990s,  court decisions recognized state ownership of lands under: 1. tidal waters (like the waters of the Atlantic Ocean and the coastal bays and sounds); and 2.   other waters that were navigable by sea-going vessels. The second category covered rivers that were below the fall line and deep enough to  be navigated  by large boats.    The public trust cases  appeared to allow private ownership of  the beds of  other rivers and streams,  but recognized a public trust easement on those that could be navigated by  shallow-draft boats or used to float logs downstream.   Decisions like Rose v. Franklin  fit this understanding of the law.

A  1995 N.C. Supreme Court decision, Gwathmey v. State, 464 S.E.2d 674, 342 N.C. 287,   abandoned the use of tidal influence as a factor and stated a simple rule: the public trust doctrine applies to any water body that, in its natural condition, can be navigated by “useful vessels, including small craft used for pleasure”.   It isn’t clear whether  Gwathmey completely abandons the old distinction between waters navigable by sea-going vessels and those  floatable by canoe for purposes of state ownership of the bed. One  problem with the Gwathmey case is that it  involved tidal  waters and marsh where public trust ownership had historically been recognized. The court just substituted one grounds for public trust ownership (navigability) for another (tidal influence).  The decision never  addressed the  impact of the  new rule  on  inland rivers where state courts had  recognized  private ownership of the river bed.  The McCrory administration lawsuit claiming title to the Alcoa dams may require the court to explain how the Gwathmey decision  applies to  interior rivers and streams.

The 401 Certification Decision.  The letter denying the Alcoa 401 Certification offers only one grounds for the denial — the state’s claim of ownership of the Yadkin River bed and the Alcoa dams built there. Citing a water quality rule, 15A NCAC 02H.0502 (f),  the letter says that “signature on the [401] application ‘certifies that the applicant has title to the property, has been authorized by the owner to apply for certification or is a public entity and has the power of eminent domain’. The required ownership certification ensures that the applicant owns the project’s dams and powerhouses and is fully capable of implementing all protections of water quality that may be imposed as conditions in a 401 Certification.”

The  rule applies to  all 401 applicants, raising the question of what will  now be required of applicants proposing development in public trust waters or in rivers and streams where public trust ownership may be in question.   It  is not a standard that seems to have been applied before to projects  on rivers and streams– even in the very recent past.  Just one month earlier, DENR waived a 401 Certification for the proposed Cleveland County dam without requiring the county to  show ownership of the bed of the First Broad River or obtain state permission to apply for a federal Clean Water Act permit  to build a dam.  Beyond dam construction,   a  401 Certification may be required for other commercial activities like in-stream mining; aquaculture;  construction of recreation facilities;  and  water intake structures for industry or agriculture.  Having invoked the requirement for Alcoa’s hydroelectric dams, DENR will need to  explain how the requirement applies to other applicants and permit holders:

— Does the standard set in the Alcoa denial letter apply to all  projects  in navigable  waters that require a 401 Certification?  This is not a trick question;  the letter indicates that  ownership  or  some form of state permission  will be necessary to satisfy DENR that  the applicant  has  sufficient control over  a project  on public trust lands  to  meet water quality conditions on a 401 Certification.

— What  will an applicant have to do to show  private ownership of land under a river or stream? Deciding whether a river or stream is navigable can require a boat trip — literally.  Answering the question of public trust ownership  will be  further complicated by uncertainty about how  the Gwathmey decision  applies to  rivers (or parts of rivers)  that  had  never been considered navigable by sea-going vessels.  In the past, many of those riverbeds had been recognized as  private property subject to a public trust easement for  navigation.

— Without proof of private ownership of the river or stream bed, what  kind of  state permission will be needed?  In the 19th and early 20th century, the General Assembly  often authorized activities in rivers and streams by special legislation  — as it did for  construction of  hydroelectric dams on the Yadkin River.  The state issues leases and easements in public trust lands for some purposes, but  those   programs developed fairly late in the 20th century and have been used for the most part in coastal waters.  The easement criteria in G.S. 146-12  lend themselves more readily to piers and docks  than to more intensive uses such as mining or dam construction.

In something of a reverse of the Alcoa 401 denial,  the state has   often relied on environmental permits as the vehicle for approving  activities in public trust waters.  Under G.S. 146-12, issuance of a  Coastal Area Management Act (CAMA) permit for development in  coastal waters  also  gives  the applicant a state  easement.  (The State Property Office  has an opportunity to review those CAMA applications.)   Outside the coastal counties, it is hard to find consistent application of the easement requirement.  For projects that don’t require a CAMA permit,  there will likely be more uncertainty about  public trust ownership and a less well-trod  path to state approval if the state does own the submerged lands.

— What standards will be applied in granting or denying state permission for activities on public trust lands?  The McCrory administration lawsuit suggests an intent to tie Alcoa’s operation of the Yadkin dams to generate electricity for sale on the wholesale market to compensation for use of the public trust resources.  Outside of leases to mine on  submerged lands, state law has not generally taxed  revenue from commercial  use of public trust resources.

— What happens when Congress has given a federal agency authority  to permit an  activity in navigable waters?  Under the Federal Power Act, FERC  has the authority to license hydroelectric projects in navigable waters of the United States. The U.S. Army Corps of Engineers has authority to permit other types of structures in navigable waters under the  Rivers and Harbors Act of 1899 and  issues Clean Water Act permits to fill navigable waters.  The Section 401 Certification has generally served as the state approval for  federally permitted projects in navigable waters. I don’t know that  the state has previously required a separate easement or lease. I also don’t know whether the federal  agencies believe any other state approval is needed given  Congressional authority  to permit these activities in navigable waters.

Many questions. The answers will be interesting.

The Uses of a Water Quality Certification: Cleveland County Reservoir

September 3, 2013.  First a disclaimer: This post will be the first of  a series  on two recent decisions by the Department of Environment and Natural Resources (DENR)  on water quality certifications requested under  Section 401 of the Clean Water Act.   Both  decisions  have been appealed; these posts should not be taken as legal advice to  parties  in these or other cases.

This post explains  how  Section 401  of the Clean Water Act works  and describes DENR’s decision to waive the 401 Certification for a Cleveland County reservoir project. The next  post will cover DENR’s denial of a 401 Certification for Alcoa’s hydroelectric dams on the Yadkin River. The last  post in the series will  talk about the implications of the  Cleveland County and Alcoa decisions for  DENR’s water quality certification program.  Individually, the decisions are unprecedented; together, the decisions send a very confusing message about DENR’s implementation of Section 401 of the  Clean Water Act.

First, a little background on water quality certifications. Under Section 401 of the Clean Water Act, an applicant for a federal license or permit that involves any discharge to navigable waters   must  provide the federal  agency with a certification that the activity  will comply with the water quality standards of the state where the project will be built.  Examples of a “discharge” include piping  wastewater  to a stream or river;  putting fill material in the water to build a structure like a dam or bulkhead; and releasing water through a hydroelectric dam.  A number of  federal permits can trigger the need for a “401 Certification”; the most common may be permits under Section 404 of the Clean Water Act to  fill navigable waters;  permits issued under Section 10 of  the Rivers and Harbors Act of 1899  for structures in navigable waters; and Federal Energy Regulatory Commission (FERC) licenses  to build or operate  hydroelectric dams.

One important thing to know about a 401 Certification: the state water quality  review does not simply duplicate the federal  permitting process.  The federal  permit decision often focuses on one part of the  project and may or may not include consideration of water quality impacts.  Under Section 401 of the Clean Water Act,   the state is charged to look at all of the  activity’s   water quality impacts — including impacts beyond the scope of the federal permit — in deciding whether  the activity will meet water quality standards.  The U.S. Supreme Court  confirmed  the broad scope of a state  401 Certification  in  PUD #1 of Jefferson County v. Washington State Dept. of Environmental Quality, 114 S.Ct. 1900, 128 L.Ed.2d 716 (1994).    The state rarely stamps a 401 application “approved” as submitted. More often, the  state’s 401 Certification identifies operating conditions and mitigation measures needed to prevent  a water quality violation. The federal permit then incorporates  the state’s water quality conditions and mitigation requirements.

Cleveland County Reservoir.   Cleveland County has been  trying to get a  Section 404 permit from the U.S. Army Corps of Engineers to  dam the First Broad River and create a reservoir since at least 2005.  To  issue a  Section 404 permit,   the Corps of Engineers has to find that there is no less environmentally damaging alternative that can  meet the project’s intended purpose. Cleveland County has  argued that the reservoir project is necessary to supply drinking water for the county, but the  Corps of Engineers has not been persuaded that a reservoir is the least environmentally damaging alternative.  There appear to be other drinking water sources available to Cleveland County —  including the purchase of water from existing water systems with excess supply.

The Corps expressed  concerns about the Cleveland County reservoir project from the beginning, but entered into an agreement with the county describing how a  federal permit application would be processed.  An early step would have to be preparation of an Environmental Impact  Statement (EIS) in consultation with the Corps of Engineers to satisfy  the National Environmental Policy Act (NEPA).  Since 2005,  little progress has been made on the federal permit application and EIS, but in late April Cleveland County sent DENR’s Division of Water Quality an application for a 401 Certification for the reservoir project.

Soon after receiving the Cleveland County  application on May 2, DENR’s water quality  staff  concluded that the application was incomplete; among other things, the application  did not identify mitigation  for stream and wetland impacts.  The state also has an  environmental  law  similar to NEPA.   The state Environmental Policy Act (SEPA)  requires an  EIS before  a state agency approves a project involving: 1. expenditure of public money or use of public land; and 2. the potential for significant impacts on the environment.  See N.C.G.S. 113A-4.  Although the Cleveland County reservoir project met all of the SEPA triggers,  the county did not submit an EIS with the permit application –another reason to find the application incomplete.  (Usually,  the state and federal reviews  are  coordinated so a single  EIS can be used for both. )

Although water quality staff  decided that the Cleveland County application was incomplete,  DENR  did not notify  Cleveland County of deficiencies in the application. On the other hand, DENR    did not  acknowledge the application as complete and  publish  notice of the application as required under federal law. After the  early  exchange  of emails among DENR staff about the incomplete application,  radio silence (at least in terms of email communication) for several weeks. Then, on  July 2, 2013 the new  director of DENR’s reorganized water programs, Tom Reeder,  sent a letter  to Cleveland County  waiving the requirement for a 401 Certification on the reservoir project. The letter gave one reason: under state rules, DENR  must act on an application for a  401 Certification within 60 days or the certification is waived. (See 15A NCAC 02H.0507.

You can find  DENR documents on the Cleveland County reservoir project, including the waiver letter,   here. (Be prepared to try  the link more than once; the connection sometimes sends an error message.)

Several things about DENR’s decision on the Cleveland County 401 Certification:

—  DENR has always interpreted the  60-day time period in state rules as  starting when DENR receives a complete application for the 401 Certification and in this case it seems clear that the Cleveland County application was not complete.

— The Clean Water Act  only assumes the 401 Certification has been waived if the state fails to act within  one year after receiving a 401 application.

— Starting the review time based on an incomplete application is inconsistent with DENR’s past interpretation of the rule and inconsistent with DENR’s  application of the rule to other projects currently under review.

— Given the inconsistency with past interpretation, current practice  and the absence of any effort to put the Cleveland County application through a normal 401 Certification review,  DENR seems to have made a deliberate decision to waive the state’s 401 authority for this particular project. The waiver did not happen by operation of  either state or federal law.

—  A deliberate waiver of a 401 Certification appears to have  no precedent in the N.C. water quality program and means the state has  forfeited the opportunity to influence permit conditions and  mitigation requirements for the Cleveland County reservoir project to protect water quality.

—  Other applicants will  question the  criteria for  a state waiver of the 401 Certification.  (The City of Raleigh, which has also proposed a controversial reservoir project, has already asked for a copy of the Cleveland County waiver letter.) Unfortunately, the waiver letter raises more questions than it answers, since it cites the 60-day rule to waive the 401 Certification for an incomplete application.

On August 21, 2013, Southern Environmental Law Center (SELC) sent a letter asking the U.S. Environmental Protection Agency  to designate the  area  of the First Broad River in Cleveland County proposed for reservoir construction as unsuitable under Section 404(c) of the Clean Water Act. Since then, SELC has filed an appeal of the state’s waiver of the 401 Certification on behalf of American Rivers.

Reorganization and Review of N.C. Water Programs

August 7, 2013. An earlier post talked about reported plans for reorganization of water programs in the Department of Environment and Natural Resources and legislation directing DENR to combine the Division of Water Resources and the Division of Water Quality.  Since then,  DENR’s plans have become public and the General Assembly  adopted budget provisions related to the reorganization. On  August 1, 2013,  Secretary John Skvarla announced that all of the stormwater programs in the Division of Water Quality would move to the Division of Mineral, Energy and Land Resources effective that same day and the remaining water quality programs would become part of a reorganized Division of Water Resources. You can find the press release here.

Stormwater. Transfer of the stormwater programs significantly  changes the responsibilities of the Division of Mineral, Energy and Land Resources.  The Division of Water Quality  managed a number of different state and federal stormwater programs, including: a state coastal stormwater  program  designed to protect shellfish waters from bacterial contamination;  stormwater control requirements associated with the Neuse River, Tar-Pamlico River, Falls Lake and Jordan Lake nutrient strategies;  federal  stormwater programs (delegated to the state by EPA)  that issue permits for municipal and industrial stormwater discharges and for  stormwater generated by active construction sites. The Division of Energy, Mineral and Land Resources (DEMLR)  has no stormwater experience other than a supporting role in  construction stormwater  permitting   (through the DEMLR sedimentation program)  and no experience managing  federal  Clean Water Act programs. Taking on a much broader range of stormwater programs and responsibility for delegated federal programs could make for a steep learning curve.

Transfer of the stormwater programs to DEMLR separates NPDES stormwater permitting from NPDES permitting for wastewater discharges.  (National Pollutant Discharge Elimination System — or “NPDES”– permits are the federal  Clean Water Act permits required for discharge of pollutants to surface waters.)  The move also separates programs that  work together to reduce pollution loading to water bodies — like Falls Lake and the Neuse River estuary — that have become impaired by  pollutants coming from both point sources and nonpoint sources.

One  footnote on the stormwater move — legislation  that directs DENR to combine programs in the Division of Water Quality and the Division of Water Resources  assumes that  stormwater programs will remain in the reorganized Division of Water Resources.  The section of House Bill 74 (Regulatory Reform Act) that directs DENR to  reorganize the water programs also makes changes in a number of water quality laws to reflect the reorganization and substitutes  “Division of Water Resources” for “Division of Water Quality”   in state stormwater laws. I am guessing that reflects a lapse in communication rather than a conflict between DENR and the General Assembly – but in the short term, several state laws seem to  identify the Division of Water Resources as the stormwater permitting agency.

Other Water Quality Programs.  Remaining Division of Water Quality (DWQ) programs will move into the reorganized Division of Water Resources (DWR) under director Tom Reeder. The state budget  attached a $2 million budget reduction to the water program reorganization.  Using the reorganization to cut programs and people has risks. After four years of budget cuts, it will be difficult to reduce the combined water programs by another 12.4%  without hurting critical functions. In reality,  there has been little overlap in the activities of the two divisions; DWQ had responsibility for water pollution programs and DWR focused on water supply  — quantity rather than quality. It is not clear that the additional budget reduction will leave the state with effective water quality and water supply programs.  DENR will also need to be sure program  cuts don’t threaten its  ability  to meet federal requirements for delegated permitting authority under the Clean Water Act and Safe Drinking Water Act.   Those  requirements go beyond simply having people to issue permits. In addition to  meeting regulatory and planning standards set in federal law,  the federal grant agreements  link to specific performance measures for  state permitting and compliance activities. The earlier post on reorganization proposals talked about some of the  program requirements linked to delegation of Clean Water Act permitting.

A July  video  message from Division of Water Resources director, Tom Reeder,  to  staff in the Water Resources and Water Quality divisions provides some insight into  next steps for the water  programs.  New information about the reorganization was limited, although Reeder said the new organization of around 700 employees would have fewer managers (and no deputy director).  After briefly talking about the reorganization, Reeder described plans for a review of water programs and rules that will begin right away and be completed by the end of December. The purpose of the review goes beyond identifying duplication of programs in the newly combined divisions. Reeder describes it as an effort to eliminate rules and programs that  are overly burdensome or  ineffective.

In the  video, Reeder  specifically mentions riparian buffer rules as a program area needing review. It isn’t clear whether  that means minor adjustments or wholesale revision of the buffer rules, but  the  buffer rules are a good example of  one potential pitfall in  the review process — some rules are part of larger water quality strategies and  the burdens and benefits need to be looked at in that context. Buffer rules put an additional burden on real estate developers and property owners, but  using  buffers  as part of a broader  nutrient reduction strategy can   lower  the  cost  to  other nutrient sources  (including municipal wastewater treatment plants and agricultural operations).  Continuing to balance the burden among point and nonpoint sources will be particularly important where buffer rules rules account for some of the  load reduction required to meet an  EPA-approved Total Maximum Daily Load for impaired waters.

The Division of Water Resources has formed an outside involvement committee to help with the review of water programs and rules. You can find the Reeder video on YouTube. Discussion of the reorganization and review of water rules begins around the 7-minute mark.

Legislative Wrap-up I: Water Quality

July 30, 2013:  A summary of legislative action on water quality-

Budget-  The final budget directs the Department of Environment and Natural Resources (DENR) to combine programs in the Division of Water Quality (DWQ)  and the Division of Water Resources DWR) and reduces the budget for the reorganized programs by $2 million.  The $2 million cut amounts to a 12.4% reduction to the combined programs. The budget also make two specific  program cuts  that reduce appropriations for water resource and water quality programs by another $735,257.  Total reductions may go even  higher than $2.7 million if water resource/water quality  programs also share in the  2% department-wide reduction required by  the final budget.   Although both the Division of Water Resources and the Division of Water Quality deal with water, the two have very different responsibilities and little overlap in functions; it  will be  difficult for  the reorganized programs to absorb another 12.4 % cut  without hurting program delivery.

Division of Water Quality (DWQ) has responsibility for preventing and reducing water pollution in the state’s rivers, lake, streams and groundwater supplies.  By delegation of authority from the U.S. Environmental Protection Agency, DWQ  issues federal Clean Water Act permits to wastewater and stormwater  dischargers. DWQ also issues state water quality permits for animal waste management systems, injection wells, and for land application of waste.

Division of Water Resources monitors water supply – the amount of water in rivers, lakes, streams and aquifers rather than its quality. DWR has responsibility for state and local water supply planning; drought monitoring and drought response; and approval of  water transfers from one river basin to another (for example, taking water from an intake on the Neuse River to provide drinking water to a city  in the Cape Fear River basin).  The Public Water Supply section in DWR enforces the federal Safe Drinking Water Act, which regulates drinking water systems to ensure that the water coming out of the tap is safe to drink.

Both divisions have river basin planning programs –  DWR water supply plans  use data on water use to model for future water supply  and DWQ  water quality plans track data on pollutant levels,  identify sources of  pollution and provide a foundation for addressing water  quality  problems.  The two types of planning complement each other, but neither can take the place of the other.  It will be important to continue to have strong water quality and water supply planning programs if the state is to have a scientific and technical basis for good water policy decisions.

The budget will test DENR’s  ability to continue to deliver good science, timely permit reviews, compliance assistance, and enforcement with fewer resources. The department will also have to keep an eye on the effect of reduced state appropriations on  federal grants supporting programs in the two divisions. The state receives a significant amount of  federal grant money to support activities required under the delegated Clean Water Act and Safe Drinking Water Act programs.  Those grants require a certain level of state “match” money — which is often provided in the form of state-funded positions in those programs.

Jordan Lake –  Legislation delays further implementation of the Jordan Lake Nutrient Strategy for three years  (Senate Bill 515).  The General Assembly had already delayed  the original Jordan Lake compliance dates for reducing  the amount of  nitrogen and phosphorus in wastewater discharges (until 2016) and for implementing new development stormwater programs (until 2014). The practical effect of the bill will be to  push those dates out three more years.  A number of local governments in the Jordan Lake watershed have already started implementing  local stormwater ordinances and can continue with those programs. The purpose of the delay is to allow the state to “[explore]  other measures and technologies to improve the water quality of the Lake”.  A related budget provision  earmarks   $1.35 million from the 2013-2014 appropriation for the Clean Water Management Trust Fund  for a pilot project to test the use of technology to improve water quality in Jordan Lake.   The budget provision describes the technology to be tested very specifically in three pages of bill text and seems  to direct funds to a particular product.  Both in committee and on the floor of the House, legislators identified the technology as SolarBee— a technology used to aerate water tanks and raw water reservoirs.  The bill exempts the pilot project from normal state contract procedures, which means DENR will not be required to advertise for bids.

Prospects for the success of the pilot project are already in doubt. A  prominent North Carolina scientist, Professor Emeritus Kenneth H. Reckhow of Duke University, has said that aeration technologies are not effective in large water bodies like Jordan Lake.  Even if the  technology can improve in-lake conditions, the U.S. Environmental Protection Agency  has put the state on notice that  in-lake treatment cannot substitute for pollution reductions required under the Clean Water Act (7_10_2013 Letter to Rick Glazier re B Everett Jordan Reservoir TMDL-1).  If EPA holds to that position, the technology  will fail its primary purpose — which is to relieve upstream communities in the Jordan Lake watershed  of the need to  invest in wastewater treatment plant upgrades and stormwater controls on new development.

Groundwater (and possibly coal ash) – Section 46  of  House Bill 74 (Regulatory Reform Act)  seems to narrow DENR’s ability to address groundwater contamination caused by a permitted waste disposal site.  When the state issues a  permit for land application of  waste or for  waste disposal in a landfill, the permit sets a groundwater compliance boundary. Some degree of groundwater contamination will be allowed inside the compliance boundary,   but the permit holder cannot cause groundwater  standards to be violated outside the compliance boundary.   The new language in House Bill 74  continues to allow the Environmental Management Commission (EMC) to set compliance boundaries by rule and by permit, but creates  a presumption that the compliance boundary will be the property line. (By comparison, landfill permits have  generally set the groundwater compliance boundary at 250 feet from the actual waste disposal area.)

The bill then goes on to limit the circumstances in which  DENR can require  “cleanup, recovery, containment, or other response” to groundwater contamination inside the compliance boundary. Before requiring any action inside the compliance boundary, DENR would have to show that the groundwater contamination: 1. has already caused a violation of water quality standards in nearby surface waters or can reasonably be predicted to cause a water quality standard violation; 2. presents an imminent threat to the environment or to public health and safety; or 3.causes a violation of groundwater standards in bedrock (which seems to mean contamination of deep groundwater).

The presumption that the property line will be the compliance boundary  will likely create pressure on the EMC to allow much larger compliance boundaries  than in the past. Expansion of the compliance boundary carries with it the possibility of  larger areas of groundwater contamination. The new law also makes it more difficult for  DENR   to require  a permit holder to take action inside the compliance boundary –even to contain or reduce the flow of contaminated groundwater off site.   DENR could only require steps to contain contaminated groundwater by showing that the groundwater contamination had caused –or will cause — a specific water quality violation or an imminent threat to health, safety or the environment. The fact that the contamination has moved beyond the compliance boundary (and perhaps already migrated off  the property and toward a river or lake) will not be enough. The clear risk will be that  acting only  after a problem already exists will create a larger and more expensive problem to remedy in the future.

The provision appears to be linked to an ongoing controversy and threatened litigation over groundwater contamination and seeps from ponds where coal-fired power plants have disposed of coal ash. The Catawba Riverkeeper has filed a notice of intent to sue under the Clean Water Act over contamination from two coal ash disposal sites — a  Duke Energy  coal ash pond associated with the Riverbend Steam Station and a Progress Energy coal ash pond in Asheville. The Duke Energy coal ash pond is located on the banks of Mountain Island Lake and near a water intake for the City of Charlotte.  Monitoring around the coal ash pond has detected contaminants in groundwater that exceed groundwater standards, but the Division of Water Quality has not yet decided whether corrective action will be necessary. The Riverkeeper’s complaint claims that contaminants from the coal ash are reaching the lake in seepage from the impoundment and through a groundwater connection to the lake. The House Bill 74 language means that groundwater violations alone –even beyond the compliance boundary — would not necessarily require  steps  to  contain  an ongoing flow of contaminated groundwater to the lake.  DENR would first have to show that the groundwater contamination is causing or will cause an actual water quality standard violation in the lake or  an imminent threat to health, safety or the environment.

Regulatory Reform – More on regulatory reform in a later post, but House Bill 74 includes a requirement that agencies review and readopt existing rules of “substantive public interest”   every ten years.  The bill defines “substantive public interest” so broadly that it will  cover  every environmental rule of any real substance. The state’s Rules Review Commission will set the initial schedule for review of rules, but the bill directs the commission to schedule surface water and wetland standards for review in the first round of rule review.

Miscellaneous – This post only covers the most significant water quality legislative. House Bill 74 contains a number of other minor changes, including technical amendments to the laws on permitting animal waste management systems and an exemption from riparian buffer requirements for agricultural ponds.

Failed Water Quality Legislation – One major change did not happen. The N.C. Homebuilders Association had pushed legislation to eliminate state water quality permitting requirements for wetlands that do not fall under federal Clean Water Act permitting jurisdiction. An earlier post provides some background on the difference between federal and state wetlands jurisdiction.  The language first appeared in a Senate farm bill (Senate Bill 638), but was dropped from the bill once it reached the House. The Senate agreed to the change — possibly because farmers already have broad exemptions from wetland permitting requirements. During the last few days of the legislative session, the exemption language popped up again  in a Senate committee substitute for House Bill 938. The House sent the bill to committee and never took it up for a concurrence vote. The bill will still be eligible for consideration next year when the General Assembly reconvenes in May.

Compromise Budget: Effect on Environmental Programs

July 24, 2013: Today, both the Senate and the House will take final votes on the compromise state budget.

Money (Summary)

Although  the  total budget for the Department of Environment and Natural Resources (DENR) appears to  grow, the final budget bill actually cuts the DENR budget for existing programs by  5% over the two-year budget period.  The reductions are not evenly distributed; water quality and water resource programs will take the largest cuts — at least 12.4 % compared to the 2012 budget for those programs.

The apparent increase in the DENR budget  mostly  comes from  moving money for programs being transferred into DENR from other departments (such as the State Energy Office); creation of  a new grant program for water and wastewater infrastructure; and replacement of dedicated funding sources with year to year appropriations.

The overall 5% reduction does not  include the reduction in funds  available to  the Parks and Recreation Trust Fund by shifting deed stamp tax revenue to the General Fund and replacing the dedicated funding with an  appropriation. See an earlier post  for more detail on the amount of revenue that the deed stamp tax had generated for the Parks and Recreation Trust Fund and Natural Heritage Trust Fund.

More detail below.

Department-wide spending reductions: The budget bill requires the Department of Environment and Natural Resources to reduce department spending by 2% from 2012 spending levels ( just over  $2.227 million department-wide).  DENR  can decide where to reduce spending to meet the 2% target. DENR’s 2012  budget already represented a nearly  40%  reduction from 2008 spending levels as a result of budget cuts in earlier years.

Other Reductions: In addition to the department-wide reduction of 2%, the budget makes additional cuts to specific programs. The largest of the targeted reductions requires  DENR to cut an additional $2 million out of the budget for water resources and water quality programs in the second  year of the  two-year budget  (2014-2015). That represents a 12.4% reduction from 2012  funding for water quality and water resource programs. The budget assumes the additional savings can be found by combining water resource and water quality programs into a single division. See an earlier post for more on the water quality/water resource budget cut.

Elimination of dedicated funding sources: The budget eliminates a number of dedicated funding sources for environmental protection and conservation programs, including the earmark of revenue from the state’s deed stamp tax for parks and recreation. All revenue from the deed stamp tax will go to the General Fund and the legislature will appropriate money for parks and recreation on a year to year basis. The budget also eliminates dedicated funding sources for the Bernard Allen Emergency Drinking Water Fund, the Solid Waste Management Trust Fund and the Inactive Hazardous Sites Fund.   Replacing dedicated  revenue from the deed stamp tax with an appropriation significantly reduces funds available for parks and conservation programs.

Clean Water Management Trust Fund: $10.4 million is appropriated for the Clean Water Management Trust Fund in 2013-2014 and $13.6 million in 2014-2015.

At-Sea Observer Program (Division of Marine Fisheries): The budget provides a one-time appropriation of $1.1 million to monitor the number of endangered sea turtles caught  in commercial fishing nets. The sea turtles, which  are protected under the federal  Endangered Species Act, sometimes get caught in gill nets  used by commercial flounder fishermen. The  monitoring program  is required as a part of an agreement between the state Division of Marine Fisheries and the  National Marine Fisheries Service that allows North Carolina commercial fishermen to continue to use gill nets.

Program increases: The  budget increases funding for shale gas and offshore energy staff (+$400,000) and  for  investigation of hazardous waste contamination (+ $250,000).

Grant Funds for Water/Wastewater Infrastructure: The General Assembly appropriates $3.5 million in 2013-2014 and $5 million in 2014-2015 for water and wastewater infrastructure grants. The new grant program partially offsets the fact that the budget provides zero funding for  infrastructure grants  through the N.C. Rural Economic Development Center.

Programs Eliminated: The budget eliminates the  Fisheries Resource Grant Program,  Sustainable Communities Task Force, Uwharrie Regional Resource Commission,   Adopt a Trail program, and the Division of Water Quality’s Groundwater Investigation Unit well drilling services.

Jordan Lake Cleanup

$1.35 million from the 2013-2014 appropriation for the Clean Water Management Trust Fund is earmarked for a pilot project to test the use of technology to improve water conditions in Jordan Lake. The appropriation appears to be partner to Senate Bill 515 which (as amended in the House) delays further implementation of the Jordan Lake rules for three years to test technology  to  reduce the water quality impacts of nutrient pollution. The budget bill describes the technology to be tested very specifically and appears intended to  direct the funds to a particular product.  The bill exempts the pilot project from normal state contract procedures, which means DENR will not be required to advertise for bids.

Environment Commissions

The budget bill includes changes in appointments to the state’s major environmental regulatory commissions — the  Environmental Management Commission (water quality, air quality and water resource rules) and the Coastal Resources Commission (coastal development rules).  The bill reduces the  number of members on each commission, but the most significant change gives Governor McCrory and current legislative leadership an opportunity to replace nearly all of the members immediately. Terms for  all  Environmental Management Commission (EMC)  members will end July 31, 2013.    Four Coastal Resources Commission (CRC)  members will continue to serve until June 30, 2014 (the specific seats on the commission  are identified in the bill); the terms of  all other CRC members will end July 31, 2013. Until now, members of both commissions served staggered terms of four or six years. Each new governor and legislature had an opportunity to appoint new members as their terms ended. The changes will recreate the staggered appointments, but only after giving the current governor and legislature  unprecedented power to replace all  of the members of each commission.

The final language on EMC appointment includes conflict of interest language intended to address conflict of interest requirements in federal law.

Noncommercial Underground Storage Tanks

The bill changes state law to require owners of  noncommercial underground petroleum storage tanks to pay a deductible of $1,000 and a 10% co-payment for environmental cleanup  if the tank leaks. The bill caps the total contribution required from the tank owner at $2,000 for the combined deductible and co-payment.  Until now, the state’s Noncommercial Underground Storage Tank Trust Fund paid the full amount of cleaning up soil and groundwater contamination from a noncommercial tank and the tank owner only paid for removal of the leaking tank. (“Noncommercial” tanks include home heating oil tanks and farm or residential motor fuel storage tanks that hold less than 1,100  gallons.)

Reorganization

Conservation Programs:  Clean Water Management Trust Fund staff will be transferred to DENR. The bill eliminates the Natural Heritage Trust Fund (NHTF) and amends the CWMTF statute to allow that fund to be used for conservation projects previously funded by the Natural Heritage Trust Fund.  Existing NHTF obligations  will be honored and any remaining funds will be transferred to the  Clean Water Management Trust Fund.

Water/Wastewater Infrastructure Programs: The budget creates a new Division of Water Infrastructure in DENR by combining existing staff for the Drinking Water State Revolving Fund and   Clean Water State Revolving Fund and  transferring some number of infrastructure staff from the Community Development Block Grant program in Department of Commerce. (The actual number to be negotiated between the two departments.)  Infrastructure grant and loan decisions will be made by a new Water Infrastructure Authority.

State Energy Office: The State Energy Office moves from the Department of Commerce to DENR.

Compromise Budget Significantly Cuts Water Quality/ Water Resource Programs

July 22, 2013:  The House and Senate have released a compromise budget proposal to be voted on by both chambers this week. The budget comes in two pieces: 1. The report on continuation, expansion and capital budget (the “money report”) shows the proposed changes up or down in appropriations for state agencies. The money report also shows funds set aside for state capital improvement projects. You can find a copy of the money report here; 2. The conference committee report on the budget bill (Senate Bill 402) has the text of statute changes being adopted as part of the budget. Some of the statute changes are needed because of appropriations decisions; others pop up in the budget bill  for more strategic reasons and have very little relationship to budgeting. Another post will provide an overview of budget decisions affecting environmental programs. This post focuses on one of the most significant — the reorganization of water quality and water resources programs and a large budget cut associated with the reorganization.

The money report shows a $2 million cut to water quality and water resource programs beginning the second year of the biennium (2014-2015)  from  savings to be realized by combining the Division of Water Quality (DWQ) and the Division of Water Resources (DWR). The $2 million dollar reduction represents 12.4% of state appropriations to programs in the two divisions in 2012 and comes on top of a department-wide budget reduction of 2% also required in the compromise budget. An earlier post talked about DENR’s plans to reorganize the state’s water quality programs and anticipated some reduction in positions as part of the reorganization. The questions raised in the earlier post become more important given the magnitude of the cut proposed in the budget bill.

The challenge comes from the fact that the two divisions do very different things.  The Division of Water Quality  has responsibility for  the quality of water in rivers, lakes, streams and aquifers. DWQ develops and enforces state  water quality standards. DWQ also carries out federal Clean Water Act  programs, including permitting programs for wastewater discharges, stormwater discharges and development activities affecting streams and wetlands.  The Division of Water Resources deals with water quantity — the amount of water available in rivers, lakes, streams and underground aquifers;  water supply planning;   drought response;  and regulation of  public water systems. Functions of the two divisions  intersect at points (and there may well be some efficiencies there), but do not overlap. The kind of data needed to monitor water quality in a river is different from the data needed to  understand the volume of water in the same river. Water supply planning and water quality planning are not exactly the same thing – it may well make sense to marry the two, but the marriage will only work  if there are still  sufficient resources to look at both water quality and quantity. After four years of budget cuts, it will be difficult to achieve the  12.4% reduction required in the budget without compromising either the level of service provided to permit applicants or water quality/water supply monitoring and planning activities.

When the earlier post was written in June, the word on the street had been that DENR planned to transfer all of the state’s stormwater programs to the Division of Energy, Mineral and Land Resources (DEMLR) effective August 1 and move remaining Division of Water Quality programs into the Division of Water Resources. About the time word began to get out about the department’s reorganization plans, the Senate put language in House Bill 94  (and later in House Bill 74)  directing DENR to combine the Division of Water Quality and Division of Water Resources. The Senate language seemed to anticipate that stormwater programs would  go to the Division of Water Resources with other DWQ programs. (Both bills made changes to a number of state stormwater statutes to substitute “Division of Water Resources” for “Division of Water Quality”.)  Those bills are still waiting for final action and until that happens, there may be lingering questions about exactly what form the reorganization will take.

See the earlier post  for  more about the implications of moving stormwater programs to the Division of Energy, Mineral and Land Resources. Whatever the final configuration of the state’s water quality programs, the budget cut will be a challenge. The  sedimentation pollution control program  in  DEMLR  (the only water quality -related program in that division)  has already been decimated by budget cuts  that  reduced sedimentation program staff by 35% over  the last four years. As the  number of sedimentation program staff declined, the number of  open construction sites  to be monitored for sedimentation and erosion control did not.  (“Open” construction sites includes sites actively under construction  and sites where construction stopped before completion of the project.) There are now 40 state sedimentation staff to manage an inventory of 8,000 open construction sites across the state. The gap between open  construction sites and state staff to enforce the Sedimentation Pollution Control Act will only become larger as new development activity picks up.  There are no efficiencies left to wring out of  the sedimentation program and it isn’t clear that DWQ  stormwater programs  could help given other state and federal stormwater responsibilities.

The question for DENR is whether any combination of programs can absorb the additional reduction without damaging essential water quality programs. After the budget reductions of the last four years, can the department continue to do all of the things required for delegated Clean Water Act and Safe Drinking Water Act programs, maintain water quality and water supply planning functions, enforce the state Sedimentation Pollution Control Act, and provide good customer service with  another  12.4% budget cut targeting water quality and water resources programs?

NOTE: The original post was modified to make it clear that the $2 million cut begins in the second year of the biennium (2014-2015).