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HomeMy WebLinkAbout20020233 Ver 1_More Info Received_20050520CP J C?O LAX6 E'nV Environmental Consulting Services Inc. April 26, 2005 Ms. Cyndi Karoly NC DENR DWQ Wetlands/401 Unit 1621 Mail Service Center Raleigh, NC 27699-1621 aa-0a2li3 A TF 3764 Rominger Road Banner Elk, NC 28604 Ph/Fax: 828-297-6946 e-mail: wccJv@skybest.com RE: Ginn - LA Laurel Creek, LLLP Resort Golf Development, Watauga County DWQ # 02-0233 USACE Action ID No 200330353 Dear Ms. Karoly: This letter is in reference to the Section 401 Water Quality Certification No. 3429 issued 8-26-2003 for the referenced project. Specifically this submittal refers to permit condition #2.b) viii, which specifies that: "A monitoring plan for stability of the remaining streams and wetlands downstream of the project site to the property boundary must be approved in writing by this office before any of the impacts approved in this certification occur...." Enclosed under this cover is a plan to monitor and evaluate the stability of several stream reaches located downstream of the project area. Please review the plan and let me know as soon as possible if this is approved or if you need modifications or additional information. If you have any questions regarding this request please call me at 828-297-6946, thank you. Sincerely, hn C. Vilas President, E'nV Environmental Consulting Services Inc. Cc: Patrick Warren, PE, McGill and Associates Bob Oelberg Doug Miller Q?c?c?Q?c?Q MAY 1 1 2005 WETI M AND STORM A R BRANCH Ginn Laurel Creek Project Stream Stability Monitoring Plan DWQ Project #: 02-0233, USACE Action ID: 200330353 Background: The Ginn Laurel Creek Project (formally, the Heavenly Mountain Project) will involve the construction of an 18 hole golf course, several miles of subdivision roads and the construction of numerous buildings including single family homes, multi-family condominiums, a club house and several maintenance buildings. An Individual Clean Water Act 404 Permit and Individual 401 Water Quality Certification were applied for and obtained for this project. Sedimentation and subsequent destabilization of the on-site streams and downstream reaches was the most significant threat to water quality mentioned during the permit review process and public comment period. In response to these concerns the U.S. Army Corps of Engineers and NC Division of Water Quality placed a condition on the permit mandating that: "A monitoring plan for stability of the remaining streams and wetlands downstream of the project site to the property boundary must be approved in writing by this office before the impacts approved in this certification occur." The concept of stream stability, as defined by Rosgen, focuses on the existence of a consistent dimension, pattern and profile and the ability of the stream to move sediment and detritus produced from the contributing watershed over time, within the existing climate without either aggrading or degrading. With regard to the Ginn Laurel Creek Project, stream stability concerns arise from two primary activities. The first relates to three proposed stream relocation projects scheduled to occur within the next year and a half on project area streams. The concern with these is that the new sections of channel may not be stable and therefore, may contribute excess sediment to downstream reaches, or that changes in morphological characteristics of the relocated sections will result in stability problems for reaches immediately upstream or downstream. The second activity of concern involves the remaining development proposed over the watershed of these streams and the effects that increased imperviousness associated with residential and golf course development may have on downstream wetlands and streams. Purpose: This plan is intended to set forth a procedure by which the stability of streams and wetlands downstream of project site will be monitored. The intended purpose of the storm water management and erosion control plans currently under development for this project are to maintain a consistent dynamic between the pre and post-construction condition at the site and below the site with respect to stream flow, sediment production and transport, aquatic habitat, stream bank stability and a variety of other morphological and water quality aspects of the streams potentially affected by this project. Given the magnitude of the proposed work, it is unrealistic to assume that at some point there will not be conditions that result in deviations from the consistent dynamic. From the standpoint of stream stability the questions becomes whether or not project induced changes remain within the range of natural variability and if the streams in the area are able to remain in a stable state under this scenario. Heavenly Mountain Resort 1 4/26/2005 Golf Course Stream Stability Monitoring Plan The goal for this plan is to establish a procedure to measure several critical and significant variables of project area streams both before during and after the permitted work is completed. This plan is intended to be initiated during the pre-construction period and will continue until all construction is complete and the site is stabilized. Procedure: The monitoring program for determining stream stability in project area streams will consist of several distinct phases: • Approach • Specific Data Needs • Monitoring Site Selection • Sampling Protocol • Data Evaluation and Reporting Approach: Stream Stability in the project area will be evaluated using four sites located below areas within the project that will experience significant construction activity such as road building, golf course construction and building construction. In addition to these sites there will be a control site established on a reach that will not experience any significant construction activity. The primary goal of this monitoring procedure is to assess current stability in project area streams and associated wetlands, and to track changes over time in any of the parameters closely linked to stream stability. The first step will be to collect preconstruction data at all sampling locations. All sites will be reevaluated approximately every six months for a period not less than 2 years after completion of major constructions activities within the watershed. Specific Data Needs: The protocol for this analysis will consist of similar procedures used for a basic "Rosgen" stream classification. • Cross Sections: Two permanent cross sections will be set up at each sampling site. Cross sections will be used to determine if the stream is aggrading or degrading, or if there is any measurable lateral migration. • Profile: A survey of the stream bed along the entire length of the sample reach will be performed at each location. The purpose of the profile survey is to establish the relative elevation of the thalweg through several pools and riffles within the sample reach. This survey will also establish the relative position and length of pools, glides, riffles and runs longitudinally along the profile. Once established these parameters will be reevaluated during each monitoring visit. • Pebble Count: Pebble counts will be performed at each site and are useful to evaluate sediment transport and delivery characteristics of the reach. Changes in mean particle size in a particular reach are often reflective of changes in the contributing watershed such as significant grading activities or increases in impervious area or the effectiveness of measures designed and constructed to mitigate these changes. Heavenly Mountain Resort 2 4/26/2005 Golf Course Stream Stability Monitoring Plan • Vegetation Community Type: Riparian vegetation serves numerous stability, water quality, and habitat functions. Observable changes to the riparian plant community may be indicative of stability problems within the reach or contributing watershed. Monitoring Site Selection: A total of five monitoring sites are proposed, four will be located below areas that will be disturbed in the course of the golf course construction and one that will remain undisturbed (see Stream and Wetland Stability Monitoring Plan, Site Location Map). The selected sites were chosen with two objectives in mind. First, that all permitted impact areas will be monitored and second, that a range of impact intensity will be represented in the data. Of the four disturbed area monitoring sites, two are located on Flat Branch, one on Swift Ford Branch and one on Pine Knob Branch. The control site is located on Swift Ford Branch. The two sites along Flat Branch were selected because this drainage area is the most heavily impacted by the project. The stream monitoring site is located at the lower end of the eastern fork of Flat Branch, the stream/wetland site is located approximately 1200 feet upstream on the western branch in an area below proposed grading for golf holes 3 and 4. The site proposed along Pine Knob Branch is located downstream of 390 linear feet of pipe impact and extensive grading activities proposed to construct the 5d' hole; this site contains wetlands. The site proposed along Swift Ford Branch is located below extensive grading activities that will occur during construction of the 15th hole. While there are no direct wetland, stream or buffer impacts located on Swift Ford Branch, the grading on the 15th hole will come to the edge of the stream buffer. Sampling Protocol: The preconstruction sampling will involve the establishment of permanent, monumented cross sections, elevation reference points, initial profile, pebble count, vegetation and stability assessments, and photo reference points. Details of the assessment are outlined below: Stream Sites: 1. Establish a sampling reach that is approximately 24 bankfull widths long and consists of at least 2 meander wavelengths. Reach boundaries will be clearly marked in the field. 2. Determine location of permanent cross sections. These shall consist of at least one pool and one riffle at each assessment site. Sections should be located in an area where the stream is free to adjust its boundaries. Each cross section shall be clearly marked in the field. 3. Prepare a profile plot of the entire reach, this plot shall contain thalweg, water surface, and bankfull elevations sufficient to describe facet lengths, depths and other characteristics throughout the reach. 4. Perform a reach pebble count to determine the reach D50 and other significant stream bed characteristics. This count shall Heavenly Mountain Resort 3 4/26/2005 Golf Course Stream Stability Monitoring Plan consist of 100 samples taken from 10 transects proportionately determined based on the reach profile. 5. Perform a vegetation assessment along the reach. This shall consist of a description species composition and community type, as well as an assessment of function and relative vigor of the riparian zone. 6. Evaluation of stream bank stability over the reach. This shall be determined by measuring the length of bank with visible sloughs, exposed roots or other clear signs of channel migration or bank failure. 7. Complete a NCDWQ Habitat Assessment Form (Mountain Region) for the reach, this form shall be reevaluated at each visit. Wetland Sites: 1. Establish the boundaries of the wetland area and install semi- permanent markers to delineate the margin 2. Install one groundwater monitoring well and monitor level periodically, correlate with site rain gage data 3. Monitor the vegetation community throughout the wetland and in particular those species in the boundary region for indications of stress or changes in community structure Data Evaluation and Reporting: All data collected in the field will be downloaded and worked up in the office. Profiles and cross sections will be plotted, pebble counts will be reported graphically, vegetation assessments, stability analysis and habitat forms will be reported in table or text format. The initial or preconstruction evaluation of each site will be reported as baseline and each subsequent evaluation will be compared to the baseline for evidence of instability or indications that the stream is adjusting to changes in flow or sediment regime. Reports will be submitted to the NCDWQ and USACE annually and not later than 60 days following the collection of all field data. _ Heavenly Mountain Resort 4 4/26/2005 Golf Course Stream Stability Monitoring Plan Ginn - LA Laurel Creek, LLLP Stream and Wetland Stability Monitoring Plan Site Location Map PIN B ANCH PUNCHEON EK Site 2, Stream b it 4 6 trea an Wetla 7 6 FLA BRANCH 4 ciA t e 3 LAUREL S ream d Wet 1 U ! CREEK 4 9 P 1 0' R SE VATION BUFFER (ZONE 4) o P ° z 12 ELK CREEK 16 ROAD 4 ELK !6 CREEK o SW T FORD RANCH DUGGER CREEK ontrol Site Site 1, ream