What is a “Waters of the US?” [Dec 2016]

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What is a “Waters of the US?”

This workshop will cover the October 31, 2016 USACOE  Regulatory Guidance Letter 16-1.  We will cover the latest updates to Approved Jurisdictional Determination Letters (AJD) and Preliminary Jurisdictional Determination Letters (PJD) and how final agency actions will be considered in light of USACOE v. Hawkes.

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Wetlands are wetlands and waters are waters but what makes them jurisdictional?

For the past 6 years there have been thousands of pages of reports, regulations, guidance, court decisions, and news headlines all about “waters of the US.” Sorting through the swamp of this has been no easy task.

What is regulated as a “Water of the US” has changed a lot since it was first induced in 1899. In recent days we have seen significant revisions to the definition only leading up to legal challenges resulting in repeals.

The problem we all face is that as project move forward we still need to be concerned with what is and what is not regulated as a “Waters of the US.”  We at the Swamp School have put together a comprehensive online workshop on what are the current rules, how to apply them and how to navigate through the proposed and envisioned changes. We will cover the brand new Jurisdictional Determination Form that was released with RGL 16-1 and some tips on what needs to be included on it.  Join us online on December 2, 2016 at 1 PM EST for a fully interactive online workshop on what the current rules say and how to work with them on your projects.

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Download RGL 16-01 Here

Any questions? Just give us a call at 1-877-479-2673.

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Please be sure to purchase one ticket per student.  Use of the same student account for multiple users is not allowed.  If you wish to purchase tickets for a group please contact us for additional group discount opportunities.

Incorporating Environmental Justice into all Regulatory Efforts

The Swamp Stomp

Volume 16, Issue 28

Historically was limited to NEPA type projects funded by the US government.  However, under NEPA Environmental Justice (EJ) can be brought in as part of any federal environmental government action.  This includes Nationwide permits.  The title of the press release sort of gives away the intent.  Focus on the word “all.”  The following is from the EPA press release.

Jun 7, 2016
Incorporating Environmental Justice into all Regulatory Efforts

By Charles Lee and Kelly Maguire

Today marks an important moment in environmental justice history. The U.S. Environmental Protection Agency issued its first-ever Technical Guidance for Assessing Environmental Justice in Regulatory Analysis (EJ Technical Guidance).  This guidance represents a significant step towards ensuring the impacts of EPA regulations on vulnerable populations are understood and considered in the decision-making process.

spraydriftThe EJ Technical Guidance improves our ability to perform some of the most important work we do. Better integrating environmental justice in EPA’s core regulatory function is essential to ensure that all Americans, regardless of their race, ethnicity, or income level, have access to clean water, clean air, and healthy communities. Technical guidance, reinforced by the meaningful involvement of the public and key stakeholders, helps to ensure that all communities are protected from pollution as the result of EPA rules.

So how does it work? The EJ Technical Guidance equips EPA rule writers with key analytic principles and definitions, best practices, and technical questions to consider potential impacts on communities with environmental justice concerns. Each component helps us take complex issues and think about them in a consistent, step-by-step approach, while ensuring that sound science is the foundation of EPA’s decision-making process.

In fact, the Science Advisory Board (SAB) states “the [EJ Technical Guidance] represents major philosophical and communication steps for the agency and EJ communities with a major goal of the guidance being to incorporate EJ analysis into the framework of regulatory analysis.”  For the first time, EPA analysts will have a coherent set of methods to use when assessing potential environmental justice concerns in national rules.

Pages-from-EJTG_5-6-16_v4-232x300The finalization of the EJ Technical Guidance realizes the last commitment made under Plan EJ 2014, and sets the stage to deliver on key aspects of the draft EJ 2020 Action Agenda, EPA’s next environmental justice strategic plan for 2016-2020.  Through EJ 2020, EPA will use the EJ Technical Guidance to ensure that environmental justice is appropriately analyzed, considered and addressed in EPA rules with potential EJ concerns. This will be accomplished by implementing guidance, training, monitoring, evaluation and community involvement, including periodic assessments of how EPA is conducting EJ analyses. A hallmark of EJ 2020’s approach will be continuous learning and improvement. However, we know we still have much work to do, including development of advanced methods and guidance for analyzing cumulative risks and impacts.

We are excited about this step in the long journey towards ensuring environmental justice for all communities. We fully agree with the Administrator, when she emphasized that “by improving our ability to conduct strong, consistent analysis of environmental justice in regulatory actions, the EJ Technical Guidance marks a major milestone in our continued efforts to ensure environmental justice is considered in all aspects of the agency’s work.  Looking ahead, it offers an important advance that will bring better protection to America’s vulnerable populations for years to come.”

You can find more about this new policy by going to the EPA EJ site.

US Army Corps of Engineers Proposes to Increase Wetland Impact Limits

The Swamp Stomp

Volume 16, Issue 24

The U.S. Army Corps of Engineers (Corps) issues nationwide permits (NWPs) to authorize waters of the US and wetlands activities under Section 404 of the Clean Water Act and Section 10 of the Rivers and Harbors Act of 1899.  The idea of a nationwide permit is that the activity will result in no more than minimal individual and cumulative adverse environmental effects. There are currently 50 NWPs. These NWPs were published in the February 21, 2012, issue of the Federal Register (77 FR 10184) and expire on March 18, 2017. On June 1, 2016 the Corps published in the Federal Register a notice, that they are beginning the process for reissuing the NWPs so that the reissued NWPs will be in effect immediately after the current NWPs expire.

The U.S. Army Corps of Engineers (Corps) is soliciting comments for the reissuance of the existing nationwide permits (NWPs), general conditions, and definitions, with some modifications. The Corps is also proposing to issue two new NWPs and one new general condition. The Corps is requesting comment on all aspects of these proposed nationwide permits. The reissuance process has started with this publication of the proposed NWPs in the Federal Register for a 60-day comment period. The comment period ends on August 1, 2016.  The purpose of the Federal Register notice is to solicit comments from the regulated public on the proposed new and modified NWPs, as well as the NWP general conditions and definitions. In addition to the nationwide public notice, each Corps district will publish a separate public notice to solicit comments on its proposed regional conditions for these NWPs.

Fill

There are several significant changes to the existing permits suggested in the notice that include the consideration of expanding the acreage limit allowed under some NWPs to increase up to 2 acres.  It has also been suggested by the Corps that the acreage limits be waived in some circumstances. The notice discusses how the President’s Climate Action Plan and EPA’s proposed Clean Power Plan may be reasons to increase the acreage limits and PCN thresholds of a number of NWPs including the permits related to natural gas and renewable energy production and transmission.

Two new permits specifically used for ecological restoration projects are being considered for 2017.  The removal of low-head dams is one new proposed permit.  This is often associated with stream restoration projects. The construction and maintenance of living shorelines is the other new proposed permit.  This is associated with the use of vegetation as shoreline erosion and control.

Dam Removal

In the past some low-head dam removals may have been authorized by NWP 27, if those dams were small dams located in headwater streams. However, most low-dam removal requires individual permit authorization because it is not covered by an NWP or regional general permit. The proposed NWP will facilitate the removal of low-head dams that are no longer being used for their intended purposes or are too costly to repair. The removal of low-head dams restores ecological processes in rivers and streams and enhances public safety.

The construction and maintenance of living shorelines is a new NWP. Many living shorelines projects require individual permit authorization, and some Corps districts have issued regional general permits to authorize different types of living shorelines. These types of projects are often undertaken by waterfront property owners in areas like the Chesapeake Bay as a way to stabilize the shoreline.  It is often an alternative to using traditional stabilization methods like bulk heading rip-rap placement.  Most of the living shoreline construction methods require significant amounts of fill material to restore the shore bank.  The proposed NWP will provide general permit authorization for the construction and maintenance of living shorelines, which will give landowners a choice in how they can protect their property under erosion mitigation measures authorized by NWP. Bank stabilization activities are authorized by NWP 13 and if the proposed new NWP is issued, it will provide a similar streamlined authorization process as NWP 13. Both of these NWPs will result in decreased processing times and permit application costs associated with obtaining authorization under Section 404 of the Clean Water Act and Section 10 of the Rivers and Harbors Act of 1899.

Public comments are due on August 1, 2016.  There are already some comments posed supporting the expansion of the acreage limits.  We highly encourage you to send in your comments to the Corps.  The direct link to the public comments and the Corps notice is: HERE

US Army Corps of Engineers v Hawkes Co Inc.

The Swamp Stomp

Volume 16, Issue 23

Chief Justice Roberts announces unanimous opinion in U.S. Army Corps of Engineers v. Hawkes Co., Inc. (Justice Alito absent from bench) (Art Lien)
Chief Justice Roberts announces unanimous opinion in U.S. Army Corps of Engineers v. Hawkes Co., Inc. (Justice Alito absent from bench) (Art Lien)

On Tuesday, May 31, 2016 the Supreme Court of the United States (SCOTUS) unanimously ruled in favor of the respondent in the US Army Corps of Engineers (USACOE) v. Hawkes Co., Inc.  The decision ruled that a Waters of the US (WOTUS) Jurisdictional Determination (JD) is a final agency action.  The plaintiff (USACOE) had postulated that it was not and the respondents (Hawkes) argued that it was a final agency action.

Justice Roberts wrote the majority decision for the Court primarily on a Memorandum of Agreement (MOA) between the Corps and the Environmental Protection Agency (which shares authority to enforce the Act).  The MOA states that “final determinations” made pursuant to the MOA “will be binding on the Government and represent the Government’s position in any subsequent Federal action or litigation concerning that final determination.”  This establishes a liability limit, or safe harbor, for the five-year validity period of a negative JD.  Seven of the eight Justices agreed that the MOA was critical to the decision.  Justice Ginsburg did not concur that the MOA was the deciding factor.  However, she did concur with the majority opinion that JD’s are final agency actions.

Justice Anthony Kennedy’s separate but concurring opinion indicated that he had doubts about the government’s power under the Clean Water Act. After observing during oral arguments of this case that the Clean Water Act is perhaps “unconstitutionally vague,” Kennedy wrote in his decision that the law “continues to raise troubling questions regarding the Government’s power to cast doubt on the full use and enjoyment of private property throughout the Nation.”

“The fact that the ruling was unanimous shows that even the liberal justices will not automatically defer to the Obama administration’s Clean Water Act policy interpretations which impact property rights,” said Larry Liebesman, a senior adviser at Dawson and Associates and former Justice Department environmental attorney. “The ruling also suggests that the WOTUS rule will likely face similar scrutiny should it reach the Court.”

The following is from the case brief prepared by the Pacific Legal Foundation (PLF) who is the attorney for the respondent (Hawkes).

Several years ago, Hawkes and its partners sought approval to harvest peat on approximately 150 acres of land adjoining their current operations in Minnesota. The Minnesota Department of Natural Resources was consulted because of its regulation of peat extraction and wetland replacement and restoration associated with it. The U.S. Corps of Engineers also undertook a years-long process to determine whether the land was a wetland subject to the Clean Water Act. During this time, the Corps repeatedly tried to persuade Hawkes to abandon its plans. Representatives emphasized that the permitting process was very expensive (the required assessments alone cost over $100,000), would take years, and ultimately might not even allow Hawkes to harvest peat on the land. A Corps representative even told a Hawkes employee that he should start looking for a new job. Nearly five years after first meeting with Hawkes, the Corps concluded that a portion of the land was a “water of the United States” because it had a “significant nexus” or impact on the Red River of the North 120 miles away. Therefore, according to the Corps, the land was subject to the Clean Water Act. Hawkes disagreed and filed an administrative appeal. A Corps review officer concluded that there was insufficient evidence to support the Corps’ original finding of Clean Water Act jurisdiction.

Rather than allow a judge to consider the validity of the Corps’ jurisdictional determination, the federal government claims Hawkes must first go through an expensive, months- or years-long additional process with the Corps to apply for a federal permit to use the property, which might ultimately be futile or come with conditions that are cost-prohibitive. Thus, Hawkes has three options: (1) undergo the long, costly, and potentially futile federal permitting process; (2) abandon the land, with significant financial losses; or (3) use the land without a permit and risk criminal prosecution and steep fines. Represented by Pacific Legal Foundation (PLF), Hawkes argues that it is absurd to spend years and hundreds of thousands of dollars for a permit that wouldn’t be necessary if the Corps is incorrect about its jurisdiction over the property. The property owners also should not have to forgo their business plans, or risk draconian penalties, without an opportunity to make their case in court.

Landowners are generally prohibited from using property regulated by the Clean Water Act without a federal permit. Even though Hawkes can demonstrate the Corps is wrong about the property at issue, the disagreement with the Corps creates a huge risk for Hawkes if it went ahead and used the property without a permit: the Corps could bring criminal charges and seek fines of tens of thousands of dollars per day.

Thus, it would be commercially foolhardy for Hawkes to use the parcel without some reasonable assurance that the Corps will not interfere with that use. Yet, the agency permitting process is time-consuming, expensive, and sometimes futile. Indeed, the Corps warned Hawkes that the permitting process could take years and Hawkes would have to pay over $100,000 just to submit an application. The Corps indicated it might not even issue a permit.

After losing in the district court, Hawkes asked PLF to help represent them in their appeal to the U.S. Court of Appeals for the Eighth Circuit. In April 2015, the Eighth Circuit ruled in favor of Hawkes, declaring that the agency’s issuance of the JD was “final agency action” that Hawkes could challenge in court. This decision created a circuit split because two other circuit courts had previously ruled against landowners raising the same type of challenge. The Solicitor General (representing the Corps) asked the Supreme Court to resolve the split regarding whether a final agency JD is immediately reviewable in court. In December 2015, the Supreme Court accepted the case for review.

On May 31, 2016 the Supreme Court ruled that Jurisdictional Determinations are final agency actions and can be challenged in court.

US Army Corps of Engineers 2017 Nationwide Permits

The Swamp Stomp

Volume 16, Issue 21

On Friday, May 20, 2016 the US Army Corps of Engineers released the pre-publication of the proposed 2017 Nationwide Permits. The purpose of this release is to start the public comment process. This process officially starts when the 2017 nationwide permits are published in the Federal Register. The public comment period ends 60 days from publication in the Federal Register.

There have been a number of significant changes to the existing permits along with the creation of two new permits. The Corps of Engineers lists 52 nationwide permits along with NWP A and NWP B.  NWP A is for the removal of low head dams. Low head dams are dams constructed to pass up stream flows over the entire width of the dam crest on an uncontrolled basis. These types of dams are often associated with stream and river restoration projects.  NWP B is for the construction of living shorelines. These types of projects are often associated with title areas that include the use of vegetation for shore erosion control. Oftentimes fill is required to create a suitable planting substrate.

There are a number of changes to the existing permits.  These are just a highlights of the some of the permit condition changes.  These are explained in more detail in the pre-publication document.

Nationwide Permit number 3 (maintenance) has in the past been used for some stream restoration projects. The new nationwide permit does not authorize maintenance dredging for the primary purpose of navigation; beach restoration; or new stream channelization or stream relocation projects. It would seem that the intention is to move these activities to the new NWP A.

Nationwide Permit 12 (utility line activities) has had some changes. The Corps will allow the use of temporary mats for construction activities. They also added a note referencing the definition of a single and complete linear project. The nationwide permit does authorize inadvertent returns of drilling muds through subsoil fractures better known as frac-outs that might occur during directional drilling operations to install utility lines.

The waters of the US definition debate lingers on in this publication. Currently, the most recent published 2015 version of the waters the US definition remains on hold. However, one of the topics that arose from the definition debate was the increase in wetland disturbance authorized by the new nationwide permits. The Army Corps of Engineers has more or less held the same acreage limits for the new permits. However, in the pre-publication discussion related to acreage limits the Corps appears open to expanding these limits. They specifically request public comment to this end. Some of the comments that were published in the waters the US definition discussion seem to indicate that while the EPA and Army Corps were expanding what would be defined as a waters of the US at the same time they were also indicating that they would allow more impacts through the nationwide permit process.

There are also a set of classes that apply to certain types of waters. A number of the nationwide permits are applicable only to certain types of waters. These include:

  • navigable waters of the US
  • all waters of the US
  • nontidal waters of the US
  • nontidal wetlands
  • coral reefs
  • special aquatic sites

 

Finally, the current 2012 nationwide permits included renewable energy projects. These were either land-based or water-based. A significant amount of change has been proposed for these permits.

We at the Swamp School are in the process of preparing an easy to follow guide to the new nationwide permits. If you would like to download a free copy of this guide please click the button below and will be happy to send you one as soon as it’s ready. In addition please keep an eye on the Federal Register to find out when the public comment period opens. We will be posting this information to our Facebook page as soon as it’s available.

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Point-Intercept Sampling Procedure for Determining Hydrophytic Vegetation

The Swamp Stomp

Volume 16, Issue 20

The Hawkes v. US Army Corps of Engineers case brings up some interesting problems for us in the wetland delineation business. The main issue relates to the accuracy of the data submitted to the US Army Corps of Engineers. Currently the US Supreme Court is debating whether or not a jurisdictional determination is a final agency action. If the Court decides that a jurisdictional determination is a final agency action then an applicant can challenge the Corps of Engineers determination in court.

Just how accurate are vegetation inventories? Currently, we are allowed to do a visual estimate of percent cover of a given plant species. Based upon the 2016 US Army Corps of Engineers National Wetland Plant List we can determine whether a site has a hydrophytic plant community. Two issues arise from this methodology. The first of course is the proper identification of the plant species. Most wetland biologists put forth a tremendous effort in trying to correctly identify both the genus and species of a given plant. However, the second issue is the estimate of percent cover. This is highly subjective and prone to large error.

The procedure for determining percent cover is a simple guesstimate of looking up into the sky and estimating how much cover each species occupies. Similarly, we also look downwards and estimate the aerial cover of smaller species. The problem lies in the fact that it’s a guess. If you were to have a dozen wetland biologists on a given site I can almost guarantee that you will have a dozen sets of data. The problem is exasperated by the fact that it is entirely possible for one group of individuals to identify a plant community as being hydrophytic and another group looking at the exact same plant community and finding it to be upland.

How is this possible? Well quite simply the problem lies in the data collection itself. The current methodology can have variances in excess of 20 to 30%. If you were to go to court and had to defend your data what would be your comfort level given this type of variance?

Fortunately, the US Army Corps of Engineers has published another plant collection methodology. Buried deep in the back of the regional supplements in what is usually appendix B is the procedure called the point intercept sampling method. This procedure is highly accurate and can have a variance of less than 1% amongst numerous data collectors. As you might suspect it takes a bit longer to do this type of procedure but the data is rock solid.

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The following procedure is taken directly from US Army Corps of Engineers regional supplements for wetland delineations. It is highly recommended that you consider incorporating this procedure into your routine wetland delineation methods. As part of our wetland delineation programs we are now offering training using this methodology.  Please review the methodology outlined below and let us know your comments.

Appendix B: Point-Intercept Sampling Procedure for Determining Hydrophytic Vegetation

The following procedure for point-intercept sampling is an alternative to plot-based sampling methods to estimate the abundance of plant species in a community. The approach may be used with the approval of the appropriate Corps of Engineers District to evaluate vegetation as part of a wetland delineation. Advantages of point-intercept sampling include better quantification of plant species abundance and reduced bias com- pared with visual estimates of cover. The method is useful in communities with high species diversity, and in areas where vegetation is patchy or heterogeneous, making it difficult to identify representative locations for plot sampling. Disadvantages include the increased time required for sampling and the need for vegetation units large enough to permit the establishment of one or more transect lines within them. The approach also assumes that soil and hydrologic conditions are uniform across the area where transects are located. In particular, transects should not cross the wetland boundary. Point-intercept sampling is generally used with a transect-based prevalence index (see below) to determine whether vegetation is hydrophytic.

In point-intercept sampling, plant occurrence is determined at points located at fixed intervals along one or more transects established in random locations within the plant community or vegetation unit. If a transect is being used to sample the vegetation near a wetland boundary, the transect should be placed parallel to the boundary and should not cross either the wetland boundary or into other communities. Usually a measuring tape is laid on the ground and used for the transect line.  Transect length depends upon the size and complexity of the plant community and may range from 100 to 300 ft (30 to 90 m) or more. Plant occurrence data are collected at fixed intervals along the line, for example every 2 ft (0.6 m). At each interval, a “hit” on a species is recorded if a vertical line at that point would intercept the stem or foliage of that spe- cies. Only one “hit” is recorded for a species at a point even if the same species would be intercepted more than once at that point. Vertical intercepts can be determined using a long pin or rod protruding into and through the various vegetation layers, a sighting device (e.g., for the canopy), or an imaginary vertical line. The total number of “hits” for each species along the transect is then determined. The result is a list of species and their frequencies of occurrence along the line (Mueller-Dombois and Ellenberg 1974, Tiner 1999). Species are then categorized by wetland indi- cator status (i.e., OBL, FACW, FAC, FACU, or UPL), the total number of hits determined within each category, and the data used to calculate a transect-based prevalence index. The formula is similar to that given in Chapter 2 for the plot-based prevalence index (see Indicator 3), except that frequencies are used in place of cover estimates. The community is hydrophytic if the prevalence index is 3.0 or less. To be valid, more than 80 percent of “hits” on the transect must be of species that have been identified correctly and placed in an indicator category.

The transect-based prevalence index is calculated using the following formula:

PI = FOBL + 2FFACW + 3FFAC + 4FFACU + 5FUPL

FOBL + FFACW + FFAC + FFACU + FUPL

where:

PI  =  prevalence index

FOBL   =  frequency of obligate (OBL) plant species;

FFACW  =  frequency of facultative wetland (FACW) plant species;

FFAC   =  frequency of facultative (FAC) plant species;

FFACU   =  frequency of facultative upland (FACU) plant species;

FUPL   =  frequency of upland (UPL) plant species.

2016 National Wetland Plant List Update

The Swamp Stomp

Volume 16, Issue 18

39179966

On Monday, April 18, 2016 the US Army Corps of Engineers published (Federal Register Vol.  81, No.  74) the final 2016 National Wetland Plant List (NWPL). The NWPL is used to determine whether the hydrophytic vegetation parameter is met when conducting wetland determinations under the Clean Water Act and the Wetland Conservation Provisions of the Food Security Act. Other applications of the list include wetland restoration, establishment, and enhancement projects. The list will become effective on May 1, 2016 and will be used in any wetland delineation performed after this date. Delineations received prior to May 1, 2016 may still use the 2014 NWPL, or you may choose to use the 2016 list.

The latest review process began in 2015 and included the review by Regional Panels (RPs), the National Panel (NP), and the public, whom provided input on changes to the wetland indicator status of 1,689 species. Four groups of species were examined during this update. The first group consisted of rating changes for 25 species (including six new additions) that the public requested on the NWPL Web site (November 10, 2014 to January 31, 2015) and during the Federal Register Comment Period (September 14, 2015 to November 13, 2015). The second group consisted of 166 species with highly variable ratings spanning more than three ratings categories nationally (e.g., rated FACW in the Arid West and UPL in the Caribbean).  The third group consisted of five nationally problematic species. Initially, the public requested a rating change for these five species in one region. However, their ratings were re-examined in all regions where they occur, based on a NP request (a total of 21 ratings). Seven species occurred in more than one of these three groups. The fourth group consisted of input received on the wetland ratings of 1,500 species that occur in the South Pacific Islands (SPI) subregion. In group one, based on public requests for rating changes, 88% of the wetland ratings for 25 species were changed on the 2016 NWPL. In group two, species with highly variable ratings, the ratings of all of the species were changed to some degree. In group three, the nationally problematic species, 76% of the 21 ratings were changed for five species. In group four, the SPI species, 12.6% of the ratings were changed.

The 2014 update contained 8,061 species (Lichvar et al. 2014). Four were rated UPL in all regions where they occur, so there were a total of 8,057 species that occur in wetlands. This update contains 8,092 species, a net change of 35 more species (39 species added in the SPI, six new species in the Continental U.S. (CONUS), and removal of ten UPL species). These 8,092 species have 27,984 unique ratings since each can occur in more than one of the ten regions.

The 2016 list includes changes in plant indicator status (OBL, FACW, FAC, FACU and UPL designations) from the 2014 list for 186 species found in the CONUS. Since these 186 species can occur in multiple Corps delineation regions, each having a unique rating, there were a total of 306 rating changes. The indicator status (rating) represents the likelihood that a particular plant occurs in a wetland or upland. The specific breakout of the 306 rating changes was: 49 percent (150 ratings) were assigned wetter indicator ratings and 51 percent (156 ratings) species were assigned drier indicator ratings. Ratings for 41 species were wetter in one region and drier in another region and ratings of three species did not change. In the SPI, there were 189 ratings changes, for a grand total of 495 rating changes in the entire list.

In response to the September 14, 2015, Federal Register notice, a total of 18 comments were received and reviewed on 50 species from eight Corps wetland delineation regions and one subregion. The Corps received seven written comments in response to the September 14, 2015, Federal Register 80 CFR number 177.

The comments were mostly related to species specific rating changes.  There were also comments about invasive species, habitat descriptions and the difficulty and cost of the comment process.  One commenter was concerned about the inclusion of non-governmental, private- sector and academic experts on the NWPL panels, stating that government- only membership prevents the public from benefiting from expertise of botanists and other experts who are not federal employees. The Corps responded that they do not feel that private sector or academic representatives should serve on the
interagency regional or national panels as voting members. They further encourage outside entities to provide input into the ratings process by providing scientific information, field data, literature reviews, and the like during the Federal Register notice process and by providing comments on the NWPL Web site.

The last bit of news relates to the ratings themselves.  The Corps has updated the interpretation of the wetland indicator ratings in the table below.  Be sure to update your wetland reports to reflect these descriptions.  We are not using the US Fish and Wildlife percent occurrence in wetlands (1988, Reed) any longer.

2016 Indicator Status Ratings

Indicator Status Symbol Definitions – Short Version

( ERDC/CRREL TN-12-1 )

Obligate OBL   Almost always occur in wetlands.
Facultative Wetland FACW   Usually occur in wetlands, but may occur in non-wetlands.
Facultative FAC   Occur in wetlands and nonwetlands.
Facultative Upland FACU   Usually occur in non-wetlands, but may occur in wetlands.
Upland UPL   Almost never occur in wetlands.

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MT Man Convicted of Clean Water Act Violations and Destruction of US Property

The Swamp Stomp

Volume 16, Issue 16

22873752

MISSOULA – On April 7, 2016 a federal Montana jury found Mr. Joseph David Robertson, 77, guilty on two counts of unauthorized discharge of pollutants into waters of the United States and one count of injury or depredation of United States property.  He now faces up to 15 years in prison and a $250,000 fine.  The sentencing phase is pending.  Mr. Robertson was indicted by a grand jury in May of 2015 as a result of illegal ponds he built on two parcels of land near Basin, Montana, one on Beaverhead-Deerlodge National Forest land and the other on adjacent private property.  The ponds resulted in the discharge of dredged and fill material into a tributary stream and adjacent wetlands and caused widespread damage to both properties.

At trial, the government introduced evidence that in October of 2013, a United States Forest Service (USFS) Special Agent visited the National Forest property to determine whether Mr. Robertson had complied with previously issued conditions of probation for misdemeanor violations of USFS regulations.  The Agent testified at trial that during the site visit, she observed multiple ponds dug into an existing stream on both USFS and adjacent private property.

Mr. Robertson lives on the White Pine Lode patented mining claim that he owns. In 2013 and 2014, he dug ponds that discharged dredged and fill materials into an adjacent tributary of Cataract Creek and into nearby wetlands. A U.S. Forest Service agent discovered the ponds when she went to the property to see whether Mr. Robertson had complied with a judge’s previous order to remove structures he had built on federal lands without permission.

Mr. Robertson dug the ponds to protect his property from fire and to water his horses, his federal public defender said in court filings. Mr. Robertson acknowledged at the time that he didn’t have a permit to do the work, but he said a Montana Fish, Wildlife and Parks official had given him permission to dig.

Cataract Creek flows into the Boulder River, which empties into the Jefferson River. The U.S. Army Corps of Engineers sent Robertson a notice in 2014 that he was discharging pollutants without a permit, but Mr. Robertson’s wife threw the certified mail notice into the trash at the post office, federal prosecutors said.

The U.S. Attorney’s Office filed a criminal indictment against Mr. Robertson in May 2015, charging him with unauthorized discharge of pollutants into U.S. waters and malicious mischief for injuring the property of the United States. Government officials estimated it will cost nearly $70,000 to repair the damage, and that the value of the wetlands lost in the 1.2-acre area is estimated between $25,000 and $40,000 per acre.

During a subsequent site visit in November of 2013, Mr. Robertson admitted to Environmental Protection Agency (EPA) and USFS Criminal Special Agents that he had performed the work on the National Forest property using an excavator.  State and federal officials visited the site again in May of 2014, and observed that Mr. Robertson had done additional work.  The site was now approximately 1.2 acres in size, and extended beyond the National Forest property to a private property that he did not own.  The work consisted of nine ponds of varying sizes, including some as large as approximately 4900 square feet that were placed directly in the stream and wetlands area.  Unconsolidated dredged material from the ponds had been used to create the berms and had been placed in and around the stream and wetlands.  Mr. Robertson admitted that he had completed the additional work.  Additional investigation revealed that Mr. Robertson continued to construct ponds on the USFS property after May of 2014, despite being told repeatedly that he had no legal right to do so.

One of the central legal issues at trial was whether the waters polluted by Mr. Robertson were “waters of the United States” for purposes of the Clean Water Act.  The United States introduced evidence and expert testimony from the Army Corps of Engineers and the EPA that the stream and wetlands had a significant nexus to traditional navigable waters, and therefore were “waters of the United States.”  Fishery biologists from the Montana Fish, Wildlife and Parks (FWP) and the USFS testified that this headwater and wetland complex provided critical support to trout in downstream rivers and fisheries, including the Boulder and Jefferson Rivers.

“This verdict sends a message that the United States will not stand by and allow streams and wetlands of the United States to be polluted, or National Forest lands to be injured,” said United States Attorney for the District of Montana Mike Cotter.  “Clean and healthy waterways are a critical resource for all forms of life and are a Montana value.  It is imperative that we protect this increasingly scarce resource.  The collaborative efforts of multiple state and federal agencies in cases like this help ensure that individuals who seek to degrade it will be held accountable.”

“Rivers, streams and wetlands provide essential habitat for fish and wildlife which must be protected, and EPA and its law enforcement partners are committed to protecting these invaluable natural assets as well as the communities around them,” said Jeffrey Martinez, Special Agent in Charge of EPA’s criminal enforcement program in Montana.  “The defendant’s illegal activity took place not only on public land but also on private property he didn’t own.  Today’s guilty verdict demonstrates that polluters will be held accountable for their actions.”

The case was prosecuted by Assistant U.S. Attorney Bryan Whittaker and Special Assistant U.S. Attorney Eric Nelson from the United States Environmental Protection Agency.  This case was investigated by multiple state and federal agencies including the United States Forest Service, the Environmental Protection Agency Criminal Investigation Division, the Army Corps of Engineers, and the Jefferson County Sheriff’s Office.    Other agencies that assisted the investigation included Montana Fish, Wildlife and Parks and the Jefferson Valley Conservation District.

Sources:

https://www.justice.gov/usao-mt/pr/basin-man-convicted-clean-water-act-violations-and-destruction-us-property

http://www.washingtontimes.com/news/2015/oct/6/trial-underway-for-man-charged-with-breaking-clean/

USFW/NMFS Publish Final Changes for Critical Habitat Under the ESA

The Swamp Stomp

Volume 16, Issue 15

The US Fish & Wildlife Service and National Marine Fisheries Service (the “Services”) have promulgated major changes to their critical habitat regulations. The result will be more designation of state, local and private land as critical habitat, and increased regulatory burdens and costs on land activities. Effects will be felt by a wide range of public and private sector entities across government and industry sectors, including energy, land and mineral development, real estate, banking, commercial transactions and agriculture. The changes take effect on March 14, 2016.

The Endangered Species Act directs the Services, at the time they list a threatened or endangered species, to designate “any habitat of such species which is then considered to be critical habitat” where prudent and determinable, and based on the best scientific data available.1 Congress designed critical habitat to play a more modest role than the listing of a species. Specifically, the prohibition on “destruction or adverse modification” of critical habitat does not apply to private activities generally, but instead is implemented through application of ESA Section 7 consultation on federal agency actions, including the issuance of federal permits. Federal agencies are required, through Section 7 consultation, to “insure”  that any activity funded, carried out or authorized by that agency is not likely to “result in the destruction or adverse modification” of designated critical habitat.2

The Services issued two rules and a policy that significantly reshape decades-old regulations governing the designation of — and Section 7 consultation on — critical habitat. First, the Services issued a rule to revise the criteria for designation of critical habitat, 81 Fed. Reg. 7,414 (Feb. 11, 2016). Second, the Services promulgated a revised definition of “destruction or adverse modification” of critical habitat, 81 Fed. Reg. 7,214 (Feb. 11, 2016). Finally, the Services adopted a final policy regarding the implementation of ESA Section 4(b)(2) for exclusion of areas from critical habitat designation, 81 Fed. Reg. 7,226 (Feb. 11, 2016).

Taken together, the rules increase the likelihood that the Services will make adverse modification findings (the equivalent of a jeopardy finding and prohibited by the ESA), and could make it more likely that the Services will designate critical habitat and do so across larger areas of land than in the past, impacting landowners and project proponents alike. These changes will lead to increased costs for project proponents who require federal permit authorizations or licenses, and significant restrictions on land use and activities.

Final Rule Defining “Destruction or Adverse Modification”

ESA Section 7(a)(2) requires every federal agency to insure that actions “authorized, funded, or carried out” by the agency do not “jeopardize the continued existence of” listed species or destroy or adversely modify designated critical habitat. A wide range of projects require federal authorization and can trigger the consultation requirement.

The final rule broadens the definition of “destruction or adverse modification,” raising the concern that the Services will be more likely to determine that a federal agency action will destroy or adversely modify critical habitat. The final rule defines “destruction or adverse modification” as “a direct or indirect alteration that appreciably diminishes the value of critical habitat for the conservation of a listed species. Such alterations may include, but are not limited to, those that alter the physical or biological features essential to the conservation of a species that preclude or significantly delay development of such features.” The final rule also broadens its interpretation of the term “appreciably diminish,” thus allowing the Services to find adverse modification based on any measurable effect.3 While the Services state that they will exclude minor adverse effects, their broad interpretation of “appreciably diminish” will afford themselves significant discretion.

Final Rule Amending Criteria for Critical Habitat Designations

The ESA defines “critical habitat” as “the specific areas within the geographical area occupied by the species, at the time it is listed …, on which are found those physical or biological features (I) essential to the conservation of the species and (II) which may require special considerations or protection.”4 As a further limitation, the statute states that “critical habitat shall not include the entire geographical area which can be occupied” by the species, “[e]xcept in those circumstances determined by” the Services to be appropriate.5

The final rule amends and broadens the Services’ regulations governing the designation of critical habitat, and includes three major changes from the previous designation process:

  • The final rule broadly defines “geographic area occupied by the species” (a term not defined in the current regulations) to include a wider area around the species’ occurrences at the time of listing and areas that are used only periodically or temporarily by the species. The Services’ definition allows for designation of habitat as occupied “even if not used on a regular basis.” See 79 Fed. Reg. at 27,069 (emphasis added). This would include areas not (and which may never be) occupied by the species.
  • The final rule eliminates the concept of “primary constituent elements” in determining whether to designate critical habitat. Instead, the Services will now use a broader, more subjective requirement to identify “physical and biological features essential to the conservation of the species,” which can include “ephemeral or dynamic” habitat features and features that allow for development of habitat characteristics usable by the species.
  • The final rule departs from the Services’ prior approach to unoccupied habitat, which required the Service to first determine it could not recover the species with the inclusion of only the “geographical area presently occupied” by the species. The final rule removes this step and allows the Services to consider occupied and unoccupied areas concurrently.

These new provisions provide an especially broad basis for designating critical habitat, potentially leading to much larger critical habitat designations. More landowners could have their land designated as critical habitat, and the Services could be more likely to find, during their review of a permit application, that the proposed activity or project will result in a prohibited destruction or adverse modification of critical habitat.

Final Critical Habitat Exclusions Policy

The Act provides that the Services may exclude an area from critical habitat designation if the benefits of such exclusion outweigh the benefits of designation, i.e., on economic or other public interest grounds.6 The Services’ final policy, which they emphasize is “nonbinding,” sets forth how the Services will consider partnerships and conservation plans, conservation plans permitted under ESA Section 10, tribal lands, national-security and homeland-security impacts and military lands, federal lands and economic impacts in the critical habitat exclusion process. The policy indicates that areas subject to permitted conservation agreements and plans will generally be excluded from critical habitat designation.

Implications

Taken together, the final rules and policy will reshape and complicate the critical habitat designation process and adverse modification determinations.

Designation of critical habitat can cause immediate and significant restrictions on otherwise lawful uses of the land, create expensive and time-consuming new procedural requirements on ongoing and future projects, increase litigation risk and cause significant diminution in the value of property. If critical habitat designations increase, and additional swaths of land become too expensive or otherwise too difficult to use for commercial or other productive activities, affected entities are likely to find fewer comparable sites available for their projects, particularly if numerous regulatory constraints bear on site selection. Where federal authorization or funding is required for projects and activities, the potential for a prohibited “adverse modification” determination can result in substantial costs, delays and restrictions.

Litigation over these rules is likely.

Source:  Hunton & Williams (https://www.hunton.com/files/News/5a27ed15-5f4d-4181-9b07-b361e860310c/Presentation/NewsAttachment/681a23e2-e205-4f71-899d-b3654e8ab515/major-changes-to-endangered-species-act-critical-habitat-rules-will-cause-substantial-impacts-to-.pdf)

United States Corps of Engineers v. Hawkes

The Swamp Stomp

Volume 16, Issue 14

This past Thursday, (March 31) the Pacific Legal Foundation presented a case to the United States Supreme Court (United States Corps of Engineers v. Hawkes). This is an important case because it is has a direct relationship for getting jurisdictional determinations of wetlands. The main focus of the case is whether jurisdictional determinations (JD) are final agency actions and thus appealable in court.

Up to this point jurisdictional determinations could only be challenged through the permitting process or in an enforcement action. Historically, jurisdictional determinations could not be challenged and the landowner would have to go through an expensive review process in order to challenge the extent of wetlands on their property.

The Hawkes case is precedent-setting largely because there are no permits involved at this point. The Hawkes Company provides peat for golf courses and other sports turf applications. There are two other organizations also enjoined in this case namely Pierce Investment and LPF properties which also own some peatland in Minnesota.

Mr. M. Reed Hopper of the Pacific legal foundation has stated, “this is a case that affects millions of property owners across the country who face the potential of having their property designated as ‘waters of the United States.’  “Everyone who questions a wetlands jurisdictional determination should have the right to go to court to make their case.  So this is a case about property rights, it’s a case about the rule of law, it’s about fairness and it’s a case about whether jurisdictional determinations under the Clean Water Act should get immediate judicial review.”

peatland
Photo credit: Caudata.org, the Newt & Salamander Information Portal

So why is this case important to us?  At issue is the importance of what a jurisdictional determination means. In the Hawkes case it is fairly evident that the peatlands are wetlands at least from an ecological perspective. However, the issue of whether these are “waters of the United States” wetlands and theretofore subject to regulation is in question.

The Hawkes peatlands are more than 100 miles from a traditional navigable waterway. Using the US Army Corps of Engineers jurisdictional determination guidance that arose from the Rapanos case in 2006 it is debatable if these peatlands are jurisdictional. The important test be be addressed is if there is a significant nexus to a traditional navigable waterway. Given the distance it seems unlikely.  However, the Corps has ruled that there is therefore they are jurisdictional.

Using the new Clean Water Rule interpretation of waters United States it is likely that these peatlands would be jurisdictional. Under the “old rules”, the US Army Corps of Engineers has declared them jurisdictional. It is for this reason that the JD is being challenged. The Corps maintains that jurisdictional determinations are not challengeable in a court of law because they are not final agency actions.

If the Supreme Court decides that the jurisdictional determination process is a final agency action then anyone who disagrees with a Corps interpretation of wetlands can bring it before a judge. If the court determines that jurisdictional determinations are not a final agency action then the extent of wetlands can only be challenged as it is currently done through the permit process or in an enforcement action.

The Corps of Engineers is not under any obligation to provide jurisdictional determinations outside of a permit process or agency enforcement action. They only provide JD’s when they can and at their discretion.  There if no fee for a JD nor is there any set time-frame that they Corps must comply with like there are for permits.  Consequently, if the court sides with Hawkes it is unlikely that we will ever see a jurisdictional determination again. It is unfortunate that this may be the case as it is often good planning to establish where wetlands are so as to avoid them. However, one can see the the position Corps would be in and opening itself up for innumerable court cases just for issuing an unfavorable JD.

Furthermore, if this case goes for the Hawkes this could expand the role of the private wetland consultant. Many consultants now perform wetland delineations for the sole purpose of identifying wetlands so that they may be avoided. This is often capped with a request from the Corps of Engineers for a jurisdictional determination. However, if a jurisdictional determination cannot be obtained in a reasonable time-frame or ever, applicants would need to proceed “at risk.” This is currently occurring in many areas where demand for JD’s exceeds the Corps ability to process them.  This  underscores the need for a qualified wetland investigator so as to avoid future enforcement actions as a result of a disputed wetland determination.

The biggest issue that may arise from this case goes back to what makes a water a “waters of the US.”  To date there is no clear answer to this.  We sill await the 6th Circuit Court ruling on the 2015 Clean Water Rule that speaks directly to this.  Without a clear and consistent definition of what is a jurisdictional water any wetland delineation can be challenged in court with the end result of every single one of them ending up before the Supreme Court.  Assuming of course that you have an extra $100K or more to go there.  However, at the end of the day we still do not get an answer because as Justice Alito stated in the 2012 Sackett v. EPA case, “Real relief requires Congress to do what it should have done in the first place: provide a reasonably clear rule regarding the reach of the Clean Water Act.”

We expect to hear from the Supreme Court sometime in June and will be watching this case closely.