annual monitoring report AWS

ANNUAL MONITORING REPORT YEAR 5 (2011) CONTRACT D06003-1

LLOYD STREAM AND WETLAND RESTORATION SITE ONSLOW COUNTY, NORTH CAROLINA FULL DELIVERY PROJECT WHITE OAK RIVER BASIN CATALOGING UNIT 03030001

Prepared for: NORTH CAROLINA DEPARTMENT OF ENVIRONMENT AND NATURAL RESOURCES RALEIGH, NORTH CAROLINA Prepared by:

And

Restoration Systems, LLC 1101 Haynes Street, Suite 211 Raleigh, North Carolina 27604

Axiom Environmental, Inc. 218 Snow Avenue Raleigh, North Carolina 27603

November 2011

EXECUTIVE SUMMARY Restoration Systems, L.L.C. has completed restoration of stream and wetlands (riverine and nonriverine) at the Lloyd Stream and Wetland Restoration Site to assist the North Carolina Ecosystem Enhancement Program in fulfilling stream and wetland mitigation goals in the region. The Site is located approximately 1 mile southeast of Richlands and 5 miles northwest of Jacksonville, in Onslow County. The Site is located in United States Geological Survey (USGS) Hydrologic Unit (HU) 03030001010030 (North Carolina Division of Water Quality Subbasin 03-05-02) of the White Oak River Basin and will service the USGS 8-digit CU 03030001. This report serves as the Year 5 (2011) annual monitoring report. Primary activities at the Site included 1) stream restoration, 2) wetland restoration, 3) soil scarification, and 4) plant community restoration. Project restoration efforts provide a minimum of 4750 Stream Mitigation Units, 3.3 riverine Wetland Mitigation Units, and 3.1 nonriverine Wetland Mitigation Units as outlined in the June 2005 Technical Proposal. Five vegetation plots (10 meters by 10 meters in size) were established and permanently monumented. These plots were surveyed in August 2011 for the Year 5 (2011) monitoring season. Based on the number of stems present, the average density of all plots was 680 planted stems per acre surviving in Year 5 (2011). The dominant species identified at the Site were planted stems of sycamore (Platanus occidentalis), sugarberry (Celtis laevigata), and green ash (Fraxinus pennsylvanica). In addition, each individual plot met success criteria with densities ranging from 486 to 850 planted stems per acre. A small area of poor vegetation growth is located near groundwater monitoring Gauge 4, most likely due to a lack of nutrients in the soil after construction. This area is expected to recover naturally. No other vegetation problem areas were noted during the Year 5 (2011) monitoring season. Twelve cross-sections and longitudinal profiles within three reaches totaling 3442 linear feet were measured during Year 5 (2011) monitoring. As a whole, monitoring measurements indicate that there have been minimal changes in both the longitudinal profile and cross-sections as compared to as-built data. The as-built channel geometry compares favorably with the emulated, stable E/C type stream reach as set forth in the detailed mitigation plan and construction plans. Current monitoring has demonstrated dimension, pattern, and profile were stable over the course of the monitoring period. No stream problem areas were noted within the Site during the Year 5 (2011) monitoring year. Nine restoration Site groundwater gauges and one reference groundwater gauge were maintained for the Year 5 (2011) monitoring season. Rainfall for the Year 5 (2011) growing season was below normal with 39.3 inches of rain occurring from January to October 2011 compared to the 30-year historic mean rainfall of 49.1 inches occurring from January to October. Therefore, success criteria of restoration gauges are based on comparisons to reference gauge data, analysis of growing season start date, and all gauges should be considered successful for Year 5 (2011). Wetlands at the Site are developing well despite continued drought conditions with the development of hydrophytic herbaceous vegetation and a presence of recent oxidized rhizospheres within the upper 12 inches of soil. Based on recent field visits, gauge data, rain data, and analyses of growing season start dates, wetlands at the Site should be considered successful. Drought conditions compounded with an uncharacteristically late growing season start have led to data results that don’t consistently meet success criteria; however, jurisdictional wetland delineations completed within the Site would undoubtedly find a surplus of wetlands at the Site beyond minimums outlined in the June 2005 Technical Proposal (3.3

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Executive Summary

Riparian WMUs and 3.1 Nonriparian WMUs). Based on the Site as constructed, restoration activities resulted in 8.2 acres of riparian wetland restoration, 3.1 acres of nonriparian wetland restoration, and 1.9 acres of riparian wetland creation. In summary, the restoration Site achieved success criteria in Year 5 (2011) and should be considered successful over the five-year monitoring period.

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Executive Summary

TABLE OF CONTENTS EXECUTIVE SUMMARY ........................................................................................................................... i 1.0 PROJECT BACKGROUND............................................................................................................. 1 1.1 Location and Setting ..................................................................................................................... 1 1.2 Project Objectives ......................................................................................................................... 1 1.3 Project Structure, Restoration Type, and Approach...................................................................... 1 1.4 Project History and Background ................................................................................................... 4 2.0 PROJECT CONDITION AND MONITORING RESULTS ............................................................ 5 2.1 Vegetation Assessment ................................................................................................................. 5 2.1.1 Vegetation Success Criteria .................................................................................................. 5 2.1.2 Vegetative Problem Areas .................................................................................................... 6 2.2 Stream Assessment ....................................................................................................................... 6 2.2.1 Stream Success Criteria ........................................................................................................ 6 2.2.2 Bankfull Events ..................................................................................................................... 7 2.2.3 Stream Problem Areas .......................................................................................................... 8 2.2.4 Categorical Stream Feature Visual Stability Assessment ..................................................... 8 2.2.5 Quantitative Stream Measurements ...................................................................................... 9 2.3 Wetland Assessment ..................................................................................................................... 9 2.3.1 Wetland Success Criteria ...................................................................................................... 9 2.3.2 Wetland Problem Areas ........................................................................................................ 9 2.3.3 Wetland Criteria Attainment ............................................................................................... 14 3.0 CONCLUSIONS............................................................................................................................. 17 4.0 REFERENCES ............................................................................................................................... 20

FIGURES Figure 1. Site Location ................................................................................................................................. 2 Figure 2. Annual Climatic Data vs. 30-year Historic Data ........................................................................ 15 Figure 3. North Carolina Drought Monitor Maps ...................................................................................... 16 TABLES Table 1. Site Restoration Structures and Objectives .................................................................................... 3 Table 2. Project Activity and Reporting History ......................................................................................... 4 Table 3. Project Contacts Table ................................................................................................................... 4 Table 4. Project Background Table.............................................................................................................. 5 Table 5. Planted Species and Reference Forest Ecosystem ......................................................................... 6 Table 6. Verification of Bankfull Events ..................................................................................................... 7 Table 7A-7C. Categorical Stream Feature Visual Stability Assessment ..................................................... 8 Table 8. Baseline Morphology and Hydraulic Summary........................................................................... 10 Table 9A-9C. Morphology and Hydraulic Monitoring Summary ........................................................ 11-13 Table 10. Summary of Growing Season Start Dates.................................................................................. 17 Table 11. Summary of Defined Success Criteria ....................................................................................... 17 Table 12. Summary of Planted Vegetation Plot Results ............................................................................ 17 Table 13. Summary of Groundwater Gauge Results ................................................................................. 19

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APPENDICES APPENDIX A. VEGETATION DATA 1. Vegetation Survey Data Tables 2. Vegetation Monitoring Plot Photos APPENDIX B. GEOMORPHOLOGIC DATA 1. Tables B1-B3. Visual Morphological Stability Assessment 2. Cross-section Plots and Tables 3. Longitudinal Profile Plots 4. Stream Fixed Station Photos 5. Stream Problem Area Photos 6. Preconstruction Photos APPENDIX C. HYDROLOGY DATA 2011 Groundwater Gauge Data APPENDIX D. MONITORING PLAN VIEW

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1.0

PROJECT BACKGROUND

1.1 Location and Setting Restoration Systems, L.L.C. (Restoration Systems) has completed restoration of stream and wetlands (riverine and nonriverine) at the Lloyd Stream and Wetland Restoration Site (hereafter referred to as the “Site”) to assist the North Carolina Ecosystem Enhancement Program (EEP) in fulfilling stream and wetland mitigation goals in the region. The Site is located approximately 1 mile southeast of Richlands and 5 miles northwest of Jacksonville, in Onslow County (Figure 1). The Site is located in United States Geological Survey (USGS) Hydrologic Unit (HU) 03030001010030 (North Carolina Division of Water Quality [NCDWQ] Subbasin 03-05-02) of the White Oak River Basin and will service the USGS 8-digit Cataloging Unit (CU) 03030001. Directions to the Site from Richlands, North Carolina, are as follows:
Travel east on Highway 24 for approximately 4 miles
Turn left on Northwest Bridge Road and travel approximately 2 miles
The Site is on the left 1.2 Project Objectives The primary components of the restoration project included 1) construction of a stable, riffle-pool stream channel; 2) enhancement of water quality functions within, upstream, and downstream of the Site 3) creation of a natural vegetated buffer along restored stream channels; 4) restoration of jurisdictional riverine and nonriverine wetlands in the Site; 5) improvement of aquatic habitat and species diversity by enhancing stream bed variability; and 6) restoration of wildlife functions associated with a riparian corridor/stable stream. 1.3 Project Structure, Restoration Type, and Approach A 24.3-acre conservation easement has been placed on the Site to incorporate all restoration activities. The Site contains 22.5 acres of hydric soil, two unnamed tributaries (UTs) to the New River (main and eastern tributaries), riparian buffer, and upland slopes. The purpose of this project was to restore stable pattern, dimension, and profile to the UTs; restore hydrology to drained riverine and nonriverine wetlands; and revegetate streams, floodplains, and wetlands within the Site. The Site drainage area encompasses approximately 1.4 square miles of land at the downstream Site outfall that is characterized by agricultural land, forest, and low-density residential development. Prior to construction, the entire Site was characterized by active pasture, fallow fields, and forest stands. Pasture was grazed by livestock including cattle and horses, and livestock had access to the entire Site. No exclusionary barriers were located adjacent to onsite streams or wetlands and livestock contributed to degradation of stream banks, unstable channel characteristics (stream entrenchment, erosion, and bank collapse), degraded water quality, compacted hydric soils, and decreased wetland function. In addition, the eastern tributary didn’t receive natural stream flows. A berm had been placed near the eastern property/Site boundary to redirect stream flows into a linear ditch that drained south along the eastern property boundary into roadside ditches along the southern property boundary. The roadside ditch tied into the main tributary in the southwestern portion of the Site. The primary goals of this stream and wetland restoration project focused on improving water quality, enhancing flood attenuation, and restoring aquatic and riparian habitat and were accomplished by:

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Directions to the Site from Richlands, North Carolina: -> Take Highway 24 east for ~ 4 miles -> Turn left on Northwest Bridge Road (denoted as Gum Branch Road in some gazateers) -> Travel approximately 2 miles; the Site is on the left

Reference Forest

Lloyd Site Location

1:150,000 Source: 2003 North Carolina Atlas and Gazetteer , p.77.

2126 Rowland Pond Drive Willow Spring, NC 27592 (919) 215-1693 (919) 341-3839 fax

Axiom Environmental, Inc.

SITE LOCATION LLOYD STREAM AND WETLAND RESTORATION SITE Onslow County, North Carolina

Dwn. by:

CLF Date:

Project:

NOV 2008 08-007

FIGURE

1

•

•

• •

• •

Removing nonpoint sources of pollution associated with agricultural production including a) removal of livestock from streams, stream banks, and floodplains; b) cessation of broadcasting fertilizer, pesticides, and other agricultural materials into and adjacent to Site streams and wetlands; and c) providing a vegetative buffer adjacent to streams and wetlands to treat surface runoff. Reducing sedimentation within onsite and downstream receiving waters by a) reducing bank erosion associated with hoof shear, vegetation maintenance, and agricultural plowing to Site streams and b) providing a forested vegetative buffer adjacent to Site streams and wetlands. Reestablishing stream stability and the capacity to transport watershed flows and sediment loads by restoring stable dimension, pattern, and profile. Promoting floodwater attenuation by a) reconnecting bankfull stream flows to the abandoned floodplain terrace; b) restoring secondary, entrenched tributaries thereby reducing floodwater velocities within smaller catchment basins; c) restoring depressional floodplain wetlands and increasing storage capacity for floodwaters within the Site; and d) revegetating Site floodplains to increase frictional resistance on floodwaters crossing Site floodplains. Improving aquatic habitat by enhancing stream bed variability. Providing wildlife habitat including a forested riparian corridor within a region of the state highly dissected by agricultural land use.

Primary activities at the Site included 1) belt-width preparation and grading, 2) floodplain bench excavation, 3) channel excavation, 4) installation of channel and ditch plugs, 5) backfilling of the abandoned channel and ditches, 6) ditch rerouting, 7) installation of in-stream structures and a Terracell drop structure at the Site outfall, 8) construction of a piped channel crossing, 9) floodplain soil scarification, and 10) plant community restoration. Table 1 describes the Site restoration structures and objectives, which have provided a minimum of 4750 Stream Mitigation Units, 3.3 riverine Wetland Mitigation Units, and 3.1 nonriverine Wetland Mitigation Units as outlined in the June 2005 Technical Proposal. Site restoration activities included the following. • • • •

Restored 5858 linear feet of stream within two UTs to the New River by constructing meandering, C/E-type channels. Restored 3.3 acres of riverine wetland through filling ditches, removal of spoil castings, eliminating agricultural practices, and/or planting with native forest vegetation. Restored 3.1 acres of nonriverine wetland through filling ditches, removal of spoil castings, eliminating agricultural practices, and/or planting with native forest vegetation. Reforested the entire floodplain with native forest species.

Table 1. Site Restoration Structures and Objectives Restoration Segment/ Station Range Reach ID Tributary 1 0+00 – 27+96 Tributary 2 0+00 – 30+62 Riverine Wetlands -Nonriverine Wetlands -Mitigation Unit Summations Stream Riverine Wetland 5858 SMU 3.3 WMU *PI=Priority 1

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Restoration Type/Approach* Restoration/PI Restoration/PI Restoration Restoration

Designed Linear Footage/Acreage 2796 3062 3.3 3.1

SMU/WMUs 2796 3062 3.3 3.1

Nonriverine Wetland 3.1 WMU

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1.4 Project History and Background Completed project activities, reporting history, completion dates, project contacts, and background information are summarized in Tables 2-4. Table 2. Project Activity and Reporting History

Activity or Report Restoration Plan Construction Completion Site Planting Mitigation Plan/As-builts

Data Collection Completion May 2006 NA NA March 2007

Year 1 Monitoring (2008) Year 2 Monitoring (2008) Year 3 Monitoring (2009) Year 4 Monitoring (2010) Year 5 Monitoring (2011)

November 2007 November 2008 November 2009 November 2010 November 2011

Actual Completion or Delivery June 2006 March 2007 March 2007 May 2007 amended July 2007 December 2007 November 2008 August 2009 November 2010 November 2011

Table 3. Project Contacts Table Full Delivery Provider

Restoration Systems 1101 Haynes Street, Suite 211 Raleigh, North Carolina 27604 George Howard and John Preyer (919) 755-9490

Backwater Environmental PO Box 1654 Pittsboro, North Carolina 27312 Wes Newell (919) 523-4375 Carolina Silvics Planting Contractor 908 Indian Trail Road Edenton, North Carolina 27932 Dwight McKinney (252) 482-8491 Designer and Year 2-5 (2008-2011) Axiom Environmental, Inc. 218 Snow Avenue Monitoring Performer Raleigh, North Carolina 27603 Grant Lewis (919) 215-1693 ARACDIS G&M of North Carolina, Inc. Year 1 (2007) Monitoring Performer 801 Corporate Center Drive, Suite 300 Raleigh, NC 27607 Ben Furr and Keven Duerr (919) 854-1282 Construction Contractor

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Table 4. Project Background Table Project County Drainage Area Drainage impervious cover estimate (%) Stream Order Physiographic Region Ecoregion Rosgen Classification of As-built Cowardin Classification Dominant Soil Types Reference Site ID USGS HUC NCDWQ Subbasin NCDWQ Classification Any portion of any project segment 303d listed? Any portion of project upstream of a 303d listed segment? Reasons for 303d listing or stressor % of project easement fenced

Onslow County, North Carolina 1.4 square miles 170 11.1 11.4 10.2 9.2 9.6 19.3 23.8 21.4 23 23 10.6 1 1.2 1.1 1 1 1.5 1.4 1.8 1.8 1.7 1 1.7 1.6 1.7 1.6 1.6 2.9 3.2 3.2 3.3 3.2 1.7 10.8 8.6 9.2 9.5 10 8.8 ------- ---- ---9.6 10.1 15.2 15.5 16.1 15 17.6 ------- ---- ---16.9 1.0 1.0 1.0 1.0 1.0 1.0 ------- ---- ---1.0 11.5 10.9 10.6 10.2 10.7 14.6 18.8 14.5 15 16 11 1.0 1.0 1.0 0.9 0.9 1.3 1.3 1.5 1.5 1.5 1.0 0.1 1

MY2 12.2 150 13.1 1.1 2.1 11.3 12.3 1.0 13 1.0 -------

MY3 MY4 MY5 MY+ 11 12 9.3 150 150 150 12 12 12 1.1 1 1.3 2 2 2 10 11 7.2 13 13 16 1.0 1.0 1.0 12 13 10 1.0 1.0 1.2 ---- ---- ------- ---- ----

2.3.3 Wetland Criteria Attainment Monitoring results and factors that should be considered when evaluating Site wetlands are discussed below and include regional rainfall and drought analyses, Site landscape position, and the growing season. Regional Rainfall and Drought Analyses A thorough analysis of precipitation and drought conditions at the Site was completed by Restoration Systems (Analysis of Issues Related to the Lloyd Stream and Wetland Mitigation Site), Year 1 (2007) Year 3 (2009). Based on the resulted of the analysis Year 1 (2007) - Year 3 (2009) are considered to be atypically dry years. In addition, rainfall for the Year 5 (2011) growing season was below normal with 39.3 inches of rain occurring from January to October 2011 compared to the 30-year historic mean rainfall of 49.1 inches occurring from January to October (Figures 2 and 3). Therefore, all restoration area gauges are compared to the reference gauge, which is located within a jurisdictional wetland. The value obtained for each restoration area gauge was compared to the value obtained for the reference gauge. If the restoration area gauge value exceeded 75 percent of the value exhibited for the reference gauge for that monitoring year, the restoration gauge was then considered successful. Landscape Position Site tributaries are first- and second-order streams that drain an approximately 1.4-square mile watershed at the Site outfall. Site physiography is characterized by a relatively broad, nearly level alluvial valley and an interstream divide located between Site streams. As a result of the relatively low slope, hydration of wetlands is primarily driven by stream overbank flooding and upland runoff within riparian wetlands, and direct precipitation within nonriparian wetlands. Lateral groundwater migration plays a lesser role than typical within riparian wetlands due to the low slope and a lack of springs and seeps. Therefore, all wetlands within the Site are highly dependent on rainfall and are affected to a greater extent by drought. As documented within Analysis of Issues Related to the Lloyd Stream and Wetland Mitigation Site, the Site has continued to be in a drought since before Site construction. Growing Season According to the Soil Survey of Onslow County, North Carolina, the growing season extends from April 8 to November 5 (212 days). However, the start date for the growing season is not typical for the Coastal Plain region and should start earlier as evidenced by bud development noted consistently in February. The following are photographs taken at the Site on February 15, 2011 showing leaf-out on buttonbush plants (Cephalanthus occidentalis). In addition, soil temperatures were taken on February 22, 2011 by digging multiple pits using a hand trowel. Recorded temperatures ranged from 50-55 degrees at a depth of 12 inches from the soil surface.

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Figure 2. Annual Climatic Data vs. 30-year Historic Data 30%* 70%* 2010** Month 3.88 5.92 2.35 Jan 2.37 4.65 2.42 Feb 3.54 5.31 3.27 Mar Apr 1.84 3.77 0.61 May 2.99 4.69 3.35 Jun 3.2 5.82 4.84 Jul 4.81 7.95 6.11 Aug 4.62 8.15 5.11 Sep 3.28 7.87 17.03 Oct 1.85 4.46 1.28 Nov 2.56 4.42 1.18 Dec 2.33 4.4 3.32 * Hoffman Forest, NC 30-year Historic Data (NOAA 2004)

2011*** 2.91 4.35 2.95 0.68 0.62 3.36 6.5 11.57 2.8 3.55

**Onsite rain gauge data for April-December 2010, a nearby rain gauge at Jarmon's Oaks Restoration Site for March 2010, and from a weather station at the Jacksonville Airport (KOAJ) for January-February 2010 (Weatherunderground 2010) ***Onsite rain gauge data

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Therefore, we have analyzed the gauge data three different ways as follows. 1. Using the Onslow County start date of April 8 2. Based on an average regional start date of March 17 for adjacent counties including Pender, Lenoir, Carteret, Jones, and Duplin (see table below, which gives the growing season start dates for adjacent counties as reported in the corresponding county soil survey) 3. A start date of March 1, which occurred well-after the beginning of the actual growing season for 2011 as noted by bud development and soil temperatures Table 10. Summary of Growing Season Start Dates Growing Season Start Date (28 degrees 5 years in 10) April 8 March 19 March 12 February 27 March 15 April 9

County Onslow Pender Lenoir Carteret Jones Duplin

Utilizing an earlier start date extends the length of the growing season and subsequently the number of days required for success. The following table gives the required number of consecutive days based on the growing season used, wetland type, and percent consecutive inundation/saturation required for success followed by a table outlining gauge results. Table 11. Summary of Defined Success Criteria Growing Season/Total Days Onslow County/212 days Regional/234 days March 1/250 days

3.0

Riparian Wetland (8 percent) 17 days 19 days 20 days

Nonriparian Wetland (10 percent) 21 days 23 days 25 days

CONCLUSIONS

Stream monitoring has demonstrated dimension, pattern, and profile were stable over the course of the fiveyear monitoring period. In addition, all vegetation plots across the Site were above the required 260 stems per acre with an average of 680 tree stems per acre in the Fifth Monitoring Year (Year 2011) (Table 12). Table 12. Summary of Planted Vegetation Plot Results Plot 1 2 3 4 5 Average of All Plots (1-5)

Planted Stems/Acre Counting Towards Success Criteria Year 1 (2007) Year 2 (2008) Year 3 (2009) Year 4 (2010) Year 5 (2011) 728 607 607 607 647 728 809 769 850 850 809 769 891 688 647 445 445 810 769 769 364 364 364 405 486 615

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

599

688

656

680

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Success criteria of restoration gauges are based on comparisons to reference gauge data, analysis of growing season start date, and all gauges should be considered successful for Year 5 (2011). Hydrographs containing groundwater and precipitation data for each gauge can be found in Appendix C. A summary of groundwater gauge data is included in Table 13. As documented in Section 2.3.3, all monitoring years are considered to be atypically dry; therefore, restoration area gauges are compared to the reference gauge located within a jurisdictional wetland. Consecutive inundation or saturation within 12 inches of the soil surface was analyzed for each gauge for three separate growing season start scenarios. The longest period of consecutive inundation/saturation during the growing season is reported in Table 12 as a number of days followed by a percentage of the total growing season. The value obtained for each restoration area gauge was compared to the value obtained for the reference gauge. If the restoration area gauge value exceeded 75 percent of the value exhibited by the reference gauge for that monitoring year, the restoration gauge was then considered successful. In addition, the success of each restoration gauge is given based on consecutive days alone followed by comparisons to the reference gauge. Wetlands at the Site are developing well despite continued drought conditions with the development of hydrophytic herbaceous vegetation and a presence of recent oxidized rhizospheres within the upper 12 inches of soil. Based on recent field visits, gauge data, rain data, and analyses of growing season start dates, wetlands at the Site should be considered successful. Drought conditions compounded with an uncharacteristically late growing season start have led to data results that don’t consistently meet success criteria; however, jurisdictional wetland delineations completed within the Site would undoubtedly find a surplus of wetlands at the Site beyond minimums outlined in the June 2005 Technical Proposal (3.3 Riparian WMUs and 3.1 Nonriparian WMUs). Based on the Site as constructed, restoration activities resulted in 8.2 acres of riparian wetland restoration, 3.1 acres of nonriparian wetland restoration, and 1.9 acres of riparian wetland creation. Hydric soils with a presence of recent oxidized rhizospheres adjacent to Gauge 3 (Nonriparian).

Hydric soils and algal mats adjacent to Gauge 4 (Riparian).

Typical reduced soils with redoximorphic features within riparian wetland areas.

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Table 13. Summary of Groundwater Gauge Results Success Criteria Achieved/Success Criteria based on Reference Achieved Max Consecutive Days During Growing Season (% Max Consecutive Days of Growing Season)

Gauge

March 1

Year 1 (2007)1 March 17

April 8

Year 2 (2008)2 March 1 March 17

April 8

Year 3 (2009)3 March 1 March 17

April 8

Year 4 (2010)4 March 1 March 17

April 8

Year 5 (2011)5 March 1 March 17

April 8

No/Yes 8 days (3.4 %)

No/No 5 days (2.3 %)

No/No 17 days (6.8 %)

No/Yes 12 days (5.1 %)

No/Yes 12 days (5.7 %)

Yes/Yes 38 days (15.2 %)

No/Yes 22 days (9.4 %)

No/Yes 14 days (6.6 %)

Yes/Yes 37 days (14.8 %)

Yes/Yes 25 days (10.7 %)

Yes/Yes 25 days (11.8 %)

Yes/Yes 60 days (24.0 %)

Yes/Yes 44 days (18.8 %)

Yes/Yes 22 days (10.4 %)

2 Nonriverine

No/Yes 16 days (6.8 %)

No/Yes 10 days (4.7 %)

Yes/Yes 24 days (9.6 %)

No/Yes 12 days (5.1 %)

No/Yes 11 days (5.2 %)

Yes/Yes 24 days (9.6 %)

No/Yes 9 days (3.8 %)

No/Yes 9 days (4.2 %)

Yes/Yes 39 days (15.6 %)

Yes/Yes 23 days (10.8 %)

No/No 1 days (0.5 %)

Yes/Yes 45 days (18.0 %)

Yes/Yes 29 days (12.3 %)

No/Yes 7 days (3.3 %)

No/No 2 days (0.9 %)

No/No 2 days (0.9 %)

No/No 11 days (4.4 %)

No/No 11 days (4.7%)

No/No 6 days (2.8 %)

No/No 3 days (1.2 %)

No/No 3 days (1.3 %)

No/No 3 days (1.4 %)

Yes/Yes 21 days (8.4 %)

Yes/Yes 18 days (8.5 %)

Yes/Yes 18 days (8.4 %)

No/Yes 16 days (6.4 %)

No/Yes 8 days (3.4 %)

No/Yes 8 days (3.8 %)

No/No 12 days (4.8 %)

No/Yes 12 days (5.1 %)

No/Yes 8 days (3.8 %)

Yes/Yes 33 days (13.2 %)

No/Yes 17 days (7.3 %)

No/Yes 9 days (4.2 %)

No/No 10 days (4.0 %)

No/No 10 days (4.3 %)

No/No 10 days (4.7 %)

No/Yes 14 days (5.6 %)

No/No 6 days (2.6 %)

No/Yes 5 days (2.4 %)

Yes/Yes 113 days (45.2 %)

Yes/Yes 97 days (41.5 %)

Yes/Yes 75 days (35.4 %)

Yes/Yes 64 days (25.6 %)

Yes/Yes 64 days (27.4 %)

Yes/Yes 64 days (30.2 %)

Yes/Yes 49 days (19.6 %)

Yes/Yes 33 days (14.1 %)

No/Yes 13 days (6.1 %)

Yes/Yes 48 days (19.2 %)

Yes/Yes 32 days (13.7 %)

Yes/Yes 23 days (10.8 %)

Yes/Yes 36 days (14.4 %)

No/No 20 days (8.5 %)

Yes/Yes 20 days (9.4 %)

No/Yes 19 days (7.6 %)

No/Yes 13 days (5.6 %)

No/Yes 13 days (6.1 %)

Yes/Yes 60 days (24.0 %)

Yes/Yes 44 days (18.8 %)

Yes/Yes 39 days (18.4 %)

Yes/Yes 69 days (27.6 %)

Yes/Yes 53 days (22.6 %)

Yes/Yes 31 days (14.6 %)

Yes/Yes 67 days (26.8 %)

Yes/Yes 51 days (21.8 %)

Yes/Yes 41 days (19.3 %)

Yes/Yes 27 days (10.8 %)

Yes/Yes 27 days (11.5 %)

Yes/Yes 27 days (12.7 %)

Yes/Yes 40 days (16.0 %)

Yes/Yes 24 days (10.3 %)

No/Yes 14 days (6.6 %)

Yes/Yes 24 days (9.6 %)

Yes/Yes 18 days (7.7 %)

No/Yes 7 days (3.3 %)

52 days** (20.8 %)

36 days** (15.4 %)

14 day** (6.6 %)

17 days (6.8 %)

9 days (3.8 %)

0 days (0 %)

3 Nonriverine

4 Riverine

5 Riverine

6 Riverine

7 Riverine

8 Riverine

Gauges were installed on March 8, 2007; therefore, this data is not available.

1 Riverine

Not available

No/Yes 18 days (7.7 %)

No/Yes 18 days (8.5 %)

These gauges were installed at the beginning of the Year 4 (2010) monitoring season.

9 Riverine

Reference

8 days (3.4 %)

8 days (3.8 %)

26 days (10.4 %)

15 days (6.4 %)

9 day (4.3 %)

13 days (5.2 %)

8 days (3.4 %)

8 day (3.8 %)

1 Regional rainfall from January through October for the Year 1 (2007) was 33.04 inches, 17.94 inches (35.2%) below the WETS mean of 50.98; therefore, success criteria are based on the reference gauge. 2 Regional rainfall from January through October for the Year 2 (2008) was 42.58 inches, 8.40 inches (16.4%) below the WETS mean; therefore, success criteria are based on comparisons to reference gauge data. 3 Regional rainfall from January through October for the Year 3 (2009) was 41.31 inches, 9.67 inches (19.0%) below the WETS mean; therefore, success criteria are based on comparisons to reference gauge data. 4 Site rainfall from January through October for the Year 4 (2010) was 46.37 inches, 4.61 inches (9.0%) below the WETS mean with > 17 inches occurring in September 2010; therefore, success criteria are based on comparisons to reference gauge data. 5 Site rainfall from January through October for the Year 4 (2010) was 39.29 inches, 11.69 inches (22.9%) below the WETS mean with > 11 inches occurring in August 2011; therefore, success criteria are based on comparisons to reference gauge data. ** The reference gauge malfunctioned at the beginning of the growing season; therefore, the maximum possible period of inundation/saturation was reported and is most likely greatly overestimated.

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4.0

REFERENCES

Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual. Technical Report Y87-1. United States Army Engineer Waterways Experiment Station, Vicksburg, Mississippi. Lee, Michael T., R.K. Peet, S.D. Roberts, and T.R. Wentworth. 2006. CVS-EEP Protocol for Recording Vegetation, Version 4.0. (online). Available: http://cvs.bio.unc.edu/methods.htm National Oceanic and Atmospheric Administration (NOAA). 2004. Climatography of the United States No. 20; Monthly Station Climate Summaries, 1971-2000. National Oceanic and Atmospheric Administration, National Environmental Satellite, Data, and Information Service, National Climatic Data Center, Asheville, North Carolina. Rosgen, D. 1996. Colorado.

Applied River Morphology.

Wildland Hydrology (Publisher).

Pagosa Springs,

Weakley, Alan S. 2007. Flora of the Carolinas, Virginia, Georgia, and Surrounding Areas (online). Available: http://www.herbarium.unc.edu/WeakleysFlora.pdf [February 1, 2008]. University of North Carolina Herbarium, North Carolina Botanical Garden, University of North Carolina, Chapel Hill, North Carolina. Weather Underground. 2010. Station at Jacksonville Airport (KOAJ), North Carolina. (online). Available: http://www.wunderground.com/weatherstation/WXDailyHistory.asp?ID=KOAJ [November 9, 2010]. Weather Underground.

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

page 20

APPENDIX A VEGETATION DATA 1. Vegetation Survey Data Tables 2. Vegetation Monitoring Plot Photos

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

Report Prepared By Date Prepared

Corri Faquin

database name database location computer name file size

RestorationSystems-2011-A_Sept20.mdb C:\Axiom\Business\CVS CORRI-PC 70189056

10/4/2011 9:02

DESCRIPTION OF WORKSHEETS IN THIS DOCUMENT-----------Metadata Description of database file, the report worksheets, and a summary of project(s) and project data. Proj, planted Each project is listed with its PLANTED stems per acre, for each year. This excludes live stakes. Each project is listed with its TOTAL stems per acre, for each year. This includes live stakes, all planted stems, and all Proj, total stems natural/volunteer stems. Plots List of plots surveyed with location and summary data (live stems, dead stems, missing, etc.). Vigor Frequency distribution of vigor classes for stems for all plots. Vigor by Spp Frequency distribution of vigor classes listed by species. Damage List of most frequent damage classes with number of occurrences and percent of total stems impacted by each. Damage by Spp Damage values tallied by type for each species. Damage by Plot Damage values tallied by type for each plot. Planted Stems by Plot and Spp A matrix of the count of PLANTED living stems of each species for each plot; dead and missing stems are excluded. A matrix of the count of totalliving stems of each species (planted and natural volunteers combined) for each plot; dead and missing stems are excluded. ALL Stems by Plot and spp PROJECT SUMMARY------------------------------------Project Code Lloyd project Name Lloyd Restoration Site Description Stream and Wetland Restoration Site in Onslow County River Basin White Oak

Living planted stems, excluding live stakes, per acre Project Code Project Name River Basin Lloyd Lloyd Restoration Site White Oak

Year 5 679.87

0 2 5 1 0

21 51 29 4 7

37 72 45 23 19

37 72 45 23 19

647 850 647 769 486

647 850 647 769 486

850 2064 1174 162 283

# species

Dead/Missing Stems

16 21 16 19 12

Total Living Stems EXCLUDING Live Stakes PER ACRE

Planted Living Stems

7/2/2010 7/2/2010 7/2/2010 7/2/2010 7/2/2010

Total Living Stems PER ACRE

Date Sampled

NAD83/WGS84 NAD83/WGS84 NAD83/WGS84 NAD83/WGS84 NAD83/WGS84

Natural (Volunteer) Stems PER ACRE

Datum

77º 30.441' 77º 30.531' 77º 30.697' 77º 38.651' 77º 30.621'

Planted Living Stems EXCLUDING Live Stakes PER ACRE

Longitude/ Easting

34º 51.949' 34º 52.036' 34º 51.877' 34º 51.794' 34º 51.658'

Planted Living Stems per ACRE

Latitude/ Northing

5 5 5 5 5

Total Living Stems EXCLUDING Live Stakes

Year

2 2 2 2 2

Total Living Stems

Plot Level

LV1 LV2 LV3 LV4 LV5

Natural (Volunteer) Stems

plot

Total stems, including planted stems of all kinds (including live stakes) and natural/volunteer stems: River Project Code Project Name Basin Year 5 Lloyd Lloyd Restoration Site White Oak 1586.367721

1497 2914 1821 931 769

1497 2914 1821 931 769

3 4 6 4 5

Vigor vigor 0 3 4 Missing

Count 1 25 59 7

Vigor by Species Species Betula nigra Celtis laevigata

Percent 1.1 27.2 64.1 7.6

Cephalanthus occidentalis Fraxinus pennsylvanica Nyssa aquatica Nyssa sylvatica Quercus nigra Quercus pagoda Quercus phellos Salix nigra Carya Platanus occidentalis Ulmus Ulmus americana 14

Damage Damage (no damage) Deer Insects

Count 73 17 2

Percent Of Stems

79.3 18.5 2.2

CommonName river birch sugarberry common buttonbush green ash water tupelo blackgum water oak cherrybark oak willow oak black willow hickory American sycamore elm American elm 14

Damage by Plot

plot LV1 LV2 LV3 LV4 LV5 Total

Count of Damage Categories 6 3 0 5 5 19

(no damage) Deer Insects 10 6 20 2 1 21 15 5 7 4 1 73 17 2

4 6 6

3

2

1 0 Missing

6

5 7 3 1 6 1 5 1 1 1 1 8 12 3 5 2 4 59 25

1

1

1

1 2 1 1

1

7

Damage by Species

Species Betula nigra Carya Celtis laevigata Cephalanthus occidentalis Fraxinus pennsylvanica Nyssa aquatica Nyssa sylvatica Platanus occidentalis Quercus nigra Quercus pagoda Quercus phellos Salix nigra Ulmus Ulmus americana 14

CommonName river birch hickory sugarberry common buttonbush green ash water tupelo blackgum American sycamore water oak cherrybark oak willow oak black willow elm American elm 14

Count of Damage (no Categories damage) Deer Insects 0 6 0 9 5 8 5 0 5 1 9 1 3 4 3 1 1 1 1 11 1 0 5 1 1 1 0 3 0 3 4 5 4 3 3 3 19 73 17 2

Species Betula nigra Carya Celtis laevigata Cephalanthus occidentalis Fraxinus pennsylvanica Nyssa aquatica Nyssa sylvatica Platanus occidentalis Quercus nigra Quercus pagoda Quercus phellos Salix nigra Ulmus Ulmus americana 14

CommonName river birch hickory sugarberry common buttonbush green ash water tupelo blackgum American sycamore water oak cherrybark oak willow oak black willow elm American elm 14

plot Lloyd-BNF-LV5year:3

plot Lloyd-BNF-LV4year:3

plot Lloyd-BNF-LV3year:3

plot Lloyd-BNF-LV2year:3

Total avg# Planted # Stems plots stems 6 2 3 8 1 8 12 3 4 5 1 5 10 1 10 7 2 3.5 1 1 1 12 2 6 5 2 2.5 2 1 2 1 1 1 1 1 1 8 2 4 6 2 3 84 14

plot Lloyd-BNF-LV1year:3

Planted Stems by Plot and Species

4

2

1

4

8 7

5 10 4

3 1 8 4

4 1

7

1

19

12

2 1 1 5 16

21

1 16

plot Lloyd-BNFLV5-year:3

3

3

27 2

plot Lloyd-BNFLV4-year:3

# avg# Total Stems plots stems 31 3 10.33 8 3 2.67 6 2 3 8 1 8 12 3 4 5 1 5 1 1 1 10 1 10 2 1 2 33 5 6.6 4 1 4 7 2 3.5 1 1 1 15 3 5 22 2 11 1 1 1 5 2 2.5 2 1 2 2 1 2 6 1 6 10 2 5 6 2 3 197 22

plot Lloyd-BNFLV3-year:3

Acer rubrum Baccharis halimifolia Betula nigra Carya Celtis laevigata Cephalanthus occidentalis Cercis canadensis Fraxinus pennsylvanica Juglans nigra Liquidambar styraciflua Liriodendron tulipifera Nyssa aquatica Nyssa sylvatica Pinus taeda Platanus occidentalis Prunus serotina Quercus nigra Quercus pagoda Quercus phellos Salix nigra Ulmus Ulmus americana 22

CommonName red maple eastern baccharis river birch hickory sugarberry common buttonbush eastern redbud green ash black walnut sweetgum tuliptree water tupelo blackgum loblolly pine American sycamore black cherry water oak cherrybark oak willow oak black willow elm American elm 22

plot Lloyd-BNFLV2-year:3

Species

plot Lloyd-BNFLV1-year:3

All Stems by Plot and Species

4

1 3 2

1

4

8 7

5 1 10 2 13

11

5 4

4 3

3

1

3 1 11

1 18

4 1 4

1

7

3

23

19

2 2 6 5 37

72

1 46

Lloyd Stream and Wetland Restoration Site Year 5 (2011) Annual Monitoring Vegetation Plot Photos Taken August 2011

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

APPENDIX B GEOMORPHOLOGIC DATA 1. Tables B1-B3. Qualitative Visual Stability Assessment 2. Cross-section Plots and Tables 3. Longitudinal Profile Plots 4. Stream Fixed Station Photos

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

Cape Fear/White Oak Lloyd Property XS - 1, Pool 0.67 2/15/2011 Dean, Perkinson

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 25.39 25.56 25.53 24.96 24.90 24.56 24.14 23.28 23.17 23.49 24.28 25.51 25.63 25.74

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

25.5 17.6 13.2 2.3 1.3 E/C

Stream Type

Cape Fear/White Oak River Basin, Lloyd Property, XS - 1, Pool

26 Elevation (feet)

Station 16.88 22.61 24.67 26.32 27.65 28.80 29.63 32.30 33.59 35.74 36.56 37.95 46.31 52.52

Bankfull Flood Prone Area

24

MY-01 9/7/07 MY-02 11/7/08 MY-03 6/30/09

22

MY-4 4/7/10

0

10

20

30 Station (feet)

40

50

MY-05 2/15/11

60

Cape Fear/White Oak Lloyd Property XS - 2, Riffle 0.67 2/15/2011 Dean, Perkinson

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 25.23 25.26 25.35 24.64 24.13 24.17 24.29 24.75 25.55 25.50 25.49 25.48

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

25.3 7.0 9.8 26.5 150.0 1.2 0.7 13.7 15.3 1.0 Stream Type

E/C

Cape Fear/White Oak River Basin, Lloyd Property, XS - 2, Riffle 27

Elevation (feet)

Station 32.16 37.26 39.80 42.73 45.52 46.83 47.60 48.71 50.37 55.01 59.63 62.13

25

Bankfull Flood Prone Area MY-01 9/7/07 MY-02 11/7/08 MY-03 6/30/09

23

MY-04 4/7/10

30

40

50 Station (feet)

60 MY-05 2/15/11

Cape Fear/White Oak Lloyd Property XS - 3, Pool 0.67 2/15/2011 Dean, Perkinson

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 23.45 23.70 23.42 23.06 22.57 21.59 21.88 22.46 23.25 23.50 23.86 24.01

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

23.5 11.7 10.2 1.9 1.1 Stream Type

C

Cape Fear/White Oak River Basin, Lloyd Property, XS - 3, Pool 26

Elevation (feet)

Station 21.49 33.85 35.63 36.25 36.59 39.04 40.95 43.55 44.82 45.81 56.14 65.31

24

Bankfull MY-01 9/7/07

22

MY-02 11/7/08 MY-03 6/30/09

20 20

30

40 Station (feet)

50

MY-04 4/7/10 MY-05 2/15/11

60

Cape Fear/White Oak Lloyd Property XS - 4, Riffle 0.67 2/15/2011 Dean, Perkinson

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 22.48 22.53 22.65 22.69 21.52 21.41 21.35 21.33 22.30 22.65 22.58 22.52

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

22.5 5.6 7.4 23.7 150.0 1.2 0.8 9.8 20.3 1.0 E/C

Stream Type

Cape Fear/White Oak River Basin, Lloyd Property, XS - 4, Riffle

Elevation (feet)

Station 32.41 35.98 37.21 41.01 42.83 44.13 45.05 45.78 47.24 48.96 52.24 57.30

23

Bankfull Flood Prone Area MY-01 9/7/07 MY-02 11/7/08 MY-03 6/30/09

21 30

40

50 Station (feet)

MY-04 4/7/10 MY-05 2/15/11

60

Station 4.5 6.6 11.9 16.3 20.1 25.3 29.5 31.3 32.9 33.6 34.9 35.9 37.2 38.4 39.0 40.0 41.7 42.7 43.9

Elevation 22.86 22.65 22.03 21.57 21.24 21.21 21.19 21.35 20.37 20.14 20.07 20.12 20.27 20.42 20.89 21.19 21.1 21.0 21.0

Cape Fear/White Oak Lloyd Property XS - 5, Riffle 0.55 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

21.2 6.5 8.4 22.3 38.0 1.1 0.8 10.9 4.5 1.0 Stream Type

E/C

Cape Fear/White Oak River Basin, Lloyd Property, XS - 5, Riffle 23

22 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

21 Bankfull Flood Prone Area

20

MY-01 9/7/07 MY-02 11/18/08 MY-03 6/29/09

19

MY-04 4/7/10

20

30

40 Station (feet)

MY-05 4/26/11

50

Station 3.21 13.83 21.67 24.32 25.67 27.39 28.77 32.55 34.26 37.17 41.30 45.92

Elevation 23.75 21.63 21.49 21.05 19.99 19.27 19.59 20.40 20.90 21.07 21.15 21.01

Cape Fear/White Oak Lloyd Property XS - 6, Pool 0.55 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

21.0 11.6 12.3 1.7 0.8 Stream Type

C/E

Cape Fear/White Oak River Basin, Lloyd Property, XS - 6, Pool 23

22 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

Bankfull

21

Flood Prone Area MY-01 9/7/07

20

MY-02 11/7/08 MY-03 6/29/09

19 10

MY-04 4/7/10 MY-05 2/2011

20

30 Station (feet)

40

50

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 22.31 21.74 21.35 21.45 21.63 21.73 21.52 21.20 21.07 20.92 20.34 20.02 19.67 19.43 19.43 19.63 20.33 20.67 21.42 21.23 21.41

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

21.2 16.9 17.1 1.8 1.0 E/C

Stream Type

Cape Fear/White Oak River Basin, Lloyd Property, XS - 7, Pool

22 Elevation (feet)

Station 0.7 14.19 22.53 26.23 28.39 31.35 35.83 39.12 41.27 42.30 43.93 45.28 46.82 48.85 50.96 52.04 53.31 54.50 56.32 60.36 66.46

Cape Fear/White Oak Lloyd Property XS - 7, Pool 0.55 2/15/2011 Dean, Perkinson

Bankfull Flood Prone Area

20

MY-01 9/7/07 MY-02 11/7/08 MY-03 6/29/09

18 20

30

40

50 Station (feet)

60

MY-04 4/7/10 70 MY-05 2/15/11

Cape Fear/White Oak Lloyd Property XS - 8, Riffle 0.55 2/15/2011 Dean, Perkinson

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew: Elevation 21.59 20.99 20.99 20.85 21.07 20.92 20.73 20.13 19.89 19.82 20.29 20.66 20.86 20.82 21.03

SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

20.9 4.9 7.9 21.9 80.0 1.0 0.6 12.7 10.1 1.0 Stream Type

E

Cape Fear/White Oak River Basin, Lloyd Property, XS - 8, Riffle 23

Elevation (feet)

Station 16.26 21.69 25.74 29.77 34.42 37.61 38.94 39.82 41.50 42.27 44.51 45.44 45.93 50.61 56.37

21 Bankfull Flood Prone Area MY-01 9/7/07 MY-02 11/7/08

19 20

30

40

50

MY-03 6/29/09 60 MY-04 4/7/10

Station (feet)

MY-05 2/15/11

Station 149.0 156.9 162.6 163.7 164.7 165.5 166.1 166.3 167.0 167.3 167.7 168.2 169.2 169.8 170.4 171.7 173.0 174.2 175.1 176.0 177.0 179.7 183.6

Elevation 20.8 20.6 20.7 20.7 20.2 19.7 19.3 19.1 18.9 18.8 18.6 18.5 18.3 18.3 18.5 18.8 19.1 19.4 19.6 19.9 20.1 20.7 20.9

Cape Fear/White Oak Lloyd Property XS - 9, Pool 1.2 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

20.8 20.3 17.1 2.3 1.2 Stream Type

E/C

Cape Fear/White Oak River Basin, Lloyd Property, XS - 9, Pool

21 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

Bankfull Flood Prone Area

19

MY-01 9/7/07 MY-02 11/7/08 MY-03 7/1/09 MY-04 4/20/10

17 145

MY-05 2/2011

155

165 Station (feet)

175

185

Station 61.95 71.94 75.85 77.56 78.70 79.71 80.18 80.53 81.09 81.90 82.54 83.39 85.04 85.97 86.63 86.90 87.32 88.30 90.62 92.79 98.85 104.64 109.48

Elevation 20.45 20.68 20.99 20.61 20.37 19.96 19.79 19.54 18.97 18.73 18.81 18.75 18.86 19.14 19.45 19.74 20.06 20.29 20.31 20.34 20.37 20.45 20.60

Cape Fear/White Oak Lloyd Property XS - 10, Riffle 1.2 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

20.3 9.6 10.0 21.9 150.0 1.6 1.0 10.4 15.0 1.0 Stream Type

E/C

Cape Fear/White Oak River Basin, Lloyd Property, XS - 10, Riffle 23

22 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

21

20

Bankfull Flood Prone Area

19

MY-01 9/7/07 MY-02 11/7/08

18

MY-03 7/1/09

60

MY-04 4/20/10 MY-05 2/2011

70

80 Station (feet)

90

100

Station 119.14 123.41 126.10 127.93 128.81 129.48 130.33 131.05 131.54 133.07 133.98 134.62 134.97 135.41 136.34 137.23 137.89 139.07 140.67 142.08 146.57 150.1 152.9

Elevation 18.84 18.72 18.82 18.92 18.85 18.61 17.14 16.66 16.06 15.64 15.49 15.48 15.76 15.91 16.24 16.86 17.56 17.79 18.17 18.69 19.00 19.1 19.3

Cape Fear/White Oak Lloyd Property XS - 11, Pool 1.2 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

18.7 23.1 13.4 3.2 1.7 -

StreamLloyd Type Property, XS -E/C Cape Fear/White Oak River Basin, 11, Pool 22 21 20 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

19 18 Bankfull

17

Flood Prone Area MY-01 9/7/07

16

MY-02 11/7/08 MY-03 7/1/09

15 120

130

140

MY-04 4/20/10 MY-05 2/2011

Station (feet)

150

Station 65.0 73.2 77.4 78.2 78.9 79.5 80.2 80.9 81.7 82.1 82.4 82.9 84.2 85.0 85.8 86.4 86.7 87.6 88.0 89.2 91.6 94.8 100.1

Elevation 18.5 18.5 18.7 18.6 18.5 18.3 17.9 17.5 17.4 17.3 17.0 16.8 16.7 16.7 16.9 17.3 17.4 17.7 18.1 18.4 18.8 18.8 18.8

Cape Fear/White Oak Lloyd Property XS - 12, Riffle 1.2 2/15/2011 Dean, Perkinson SUMMARY DATA Bankfull Elevation: Bankfull Cross-Sectional Area: Bankfull Width: Flood Prone Area Elevation: Flood Prone Width: Max Depth at Bankfull: Mean Depth at Bankfull: W / D Ratio: Entrenchment Ratio: Bank Height Ratio:

18.7 11.9 9.3 20.7 150.0 2.0 1.3 7.3 16.1 1.0 E/C

Stream Type

Cape Fear/White Oak River Basin, Lloyd Property, XS - 12, Riffle 21

20 Elevation (feet)

River Basin: Watershed: XS ID Drainage Area (sq mi): Date: Field Crew:

19

18

Bankfull Flood Prone Area

17

MY-01 9/7/07 MY-02 11/7/08 My-03 7/1/09

16 65

75

85 Station (feet)

95MY-04 4/20/10 MY-05 2/14/2010

Project Name Reach Feature Date Crew

Elevation (feet - arbitrary)

Station 0.0 6.5 17.2 25.3 31.9 39.3 50.1 60.3 69.6 76.7 94.9 110.2 117.7 146.3 160.1 184.4 194.6 206.2 232.2 238.6 247.7 253.7 272.8 280.4 288.5 299.7 304.4 333.1 340.6 347.8 354.5 363.8 369.0 21.5 391.9 404.6 417.7 21.0 421.1 439.6 444.7 454.2 20.5 466.1 478.1 501.9 20.0 508.5 517.2 540.9 571.5 19.5 602.1 633.6 649.2 19.0 665.2 677.8 691.6 18.5 700.1 709.4 716.4 732.2 18.0 746.5 762.0 769.9 17.5 790.8 798.5 808.6 819.4 826.3 839.1

Lloyd Property - Year 5 (2011) Monitoring 1 Profile 3/22/11 Perkinson, Dean

2007 Year 1 Monitoring \Survey Bed Elevation Water Elevation 20.0 19.4 20.0 20.1 20.0 19.5 19.9 20.0 19.8 19.6 19.8 20.1 19.6 19.9 20.0 19.6 19.0 19.8 19.4 18.8 19.4 19.9 19.9 19.0 18.6 19.6 19.8 19.2 19.8 18.9 18.7 19.6 19.9 19.5 19.0 20.1 20.0 20.0 19.7 19.0 19.9 19.9 20.2 19.5 19.1 19.9 19.5 19.9 19.5 19.9 19.6 19.9 19.7 19.3 19.7 20.0 19.4 19.0 19.5 19.8 19.9 19.4 0 18.9 19.5 19.9 19.5

Station 1030.4 1022.0 1014.4 1005.5 997.6 979.5 959.4 941.2 936.3 925.3 915.6 897.7 892.8 888.0 871.3 865.3 859.3 845.3 837.9 828.5 820.4 808.7 802.8 787.4 776.7 763.0 749.3 741.5 732.9 716.4 697.4 678.6 652.9 634.8 621.6 613.3 592.7 579.1 572.6 565.1 554.7 517.0 511.0 502.7 493.8 470.8 462.0 453.5 443.7 426.2 417.7 410.8 400.2 393.2 376.5 353.5 345.9 335.7 322.3 300.1 294.4 288.1 282.3 264.0 254.5 250.0

2008 Year 2 Monitoring \Survey Bed Elevation Water Elevation 19.957963 19.089303 19.098657 19.306372 21.0 19.880162 21.0 19.586749 19.224303 19.67157 21.1 19.210102 21.0 19.049415 21.0 19.711067 21.0 19.527771 19.332744 21.0 19.171506 20.9 18.833257 19.127383 20.9 19.724494 21.0 19.648321 20.9 19.043837 21.0 19.229998 21.1 19.746595 21.0 19.526244 21.0 19.01968 21.1 19.267396 21.1 19.971358 21.1 19.629819 19.482602 21.1 19.24716 21.1 19.056765 21.1 19.734946 21.1 19.457002 19.609162 19.696389 19.454421 19.346965 19.328667 19.67811 19.672349 21.1 19.338267 21.1 19.135175 21.0 19.746199 21.1 19.697563 21.0 19.201772 21.1 19.002121 21.1 19.630113 21.0 19.845283 21.0 18.814558 21.1 18.939948 21.0 19.359837 21.0 19.7145 19.825686 21.1 19.08973 21.1 18.685871 21.1 19.605619 21.1 19.74924 19.568656 21.1 18.947777 21.1 18.730318 21.1 19.964931 21.0 19.415097 21.0 19.012956 21.1 21.1 200 19.029393 19.586876 21.0 19.530477 19.495435 Year21.0 1 (2007) 19.1293 21.0

2009 Year 3 Monitoring \Survey Station Bed Elevation Water Elevation 1199.4 19.4 20.0 1195.8 19.6 20.0 1188.0 19.0 20.0 1183.8 19.1 20.0 1178.9 19.6 20.1 1172.6 19.4 20.0 1166.5 19.2 20.0 1161.2 19.2 20.0 1145.5 19.1 20.0 1144.0 19.1 20.1 1134.7 18.8 20.0 1131.8 19.2 20.0 1124.4 18.1 20.0 1117.0 18.3 20.0 1113.7 18.5 20.0 1106.9 19.3 20.0 1097.4 19.5 20.0 1089.9 18.8 20.0 1082.6 18.8 20.0 1080.2 19.0 20.0 1076.0 19.5 20.0 1071.6 19.6 20.1 1066.9 19.6 20.1 1064.6 19.2 20.0 1062.0 19.1 20.0 1060.1 19.8 20.1 1045.1 19.2 20.3 1030.9 19.7 20.4 1021.4 18.9 20.4 1013.8 19.1 20.3 1002.9 19.8 20.4 995.5 19.8 20.3 985.5 19.7 20.4 979.6 19.6 20.3 974.0 19.1 20.3 964.6 19.0 20.3 960.3 19.1 20.3 949.8 19.6 20.3 941.9 19.7 20.4 935.4 19.1 20.4 930.3 19.0 20.4 923.7 19.3 20.4 917.8 19.7 20.3 909.6 19.7 20.4 899.5 19.6 20.3 885.2 19.0 20.3 873.4 19.0 20.3 865.7 19.1 20.3 860.1 19.7 20.4 851.3 19.6 20.4 847.2 19.7 20.4 839.5 19.2 20.3 834.3 19.0 20.4 827.1 19.2 20.4 821.5 19.8 20.4 812.8 19.6 20.4 809.8 19.5 20.3 802.6 18.9 20.4 793.6 18.7 20.3 790.0 19.0 20.4 782.3 19.7 20.4 769.0 19.7 20.3 400 762.7 19.9 20.3 746.8639259 18.999948 20.324484 20.4 Year 3 Bed 739.1 Year 2 19.2 (2008) Bed 728.6 19.3 20.3

2010 Year 4 Monitoring \Survey Station Bed Elevation Water Elevation 1217.3 19.5 20.1 1211.4 19.2 20.1 1205.8 19.3 1200.0 19.4 20.1 1192.8 19.1 20.1 1183.7 19.6 20.1 1175.0 19.4 20.1 1168.7 18.7 20.1 1161.2 19.1 20.1 1154.0 19.3 20.1 1150.8 19.2 20.1 1144.8 18.9 20.1 1132.4 18.7 20.1 1124.0 18.3 20.1 1119.3 18.3 20.1 1111.2 19.2 20.2 1096.6 19.3 20.1 1089.7 18.6 20.1 1085.6 18.6 20.1 1081.0 19.3 20.1 1071.1 19.6 20.1 1067.0 19.0 20.2 1062.6 20.1 20.3 1054.7 20.1 20.4 1041.4 19.8 20.5 1035.0 19.8 1028.8 19.1 20.5 1019.9 19.0 20.5 1005.9 19.8 20.5 996.0 Profile -19.8 Lloyd Reach 1 20.5 989.2 19.7 20.5 978.1 19.2 20.5 970.8 19.0 20.5 964.6 19.0 20.5 956.0 19.5 20.5 945.6 19.5 20.5 938.5 19.0 20.5 933.6 19.0 20.4 923.8 19.4 20.5 908.1 19.8 20.5 894.8 19.3 20.5 887.0 19.0 20.5 877.4 19.0 20.5 870.1 19.0 20.5 863.6 19.6 20.4 848.8 19.6 20.4 840.9 19.0 20.4 834.7 19.1 20.4 826.0 19.7 20.5 812.9 19.5 20.5 803.2 18.9 20.5 795.9 18.9 20.5 789.0 19.3 20.5 767.0 20.3 20.8 756.5 19.5 20.8 746.7 19.3 20.8 738.0 19.0 20.7 732.1 19.3 20.7 722.8 19.4 20.8 705.9 19.8 20.8 696.0 19.5 20.8 686.6 19.1600 20.8 678.3 19.7(feet) 20.9 Distance 662.6 19.5 20.8 656.4Bed 19.5 (2009) Year 4 (2010)20.8 Bed 652.4 19.8 20.8

Station 1186.3 1159.8 1151.5 1142.7 1134.7 1114.9 1111.3 1100.4 1086.9 1081.1 1078.2 1067.7 1062.3 1058.3 1055.3 1053.6 1039.0 1026.5 1016.6 1003.6 993.3 982.2 969.9 955.9 947.7 936.6 927.7 915.6 902.8 886.0 877.7 866.4 854.5 842.2 831.9 822.6 813.6 804.9 794.6 789.0 778.0 759.8 748.0 732.8 726.2 709.8 701.2 694.3 688.1 679.3 671.3 656.3 650.4 640.1 627.0 617.7 602.4 593.6 584.7 578.1 574.0 567.2 559.8 554.0 547.1 5 Year 544.0

2011 Year 5 Monitoring \Survey Bed Elevation Water Elevation 19.3 20.4 19.3 19.3 20.4 19.3 20.4 19.0 20.4 18.5 20.4 18.6 20.4 19.4 20.4 19.3 20.5 18.9 20.4 18.9 20.4 19.5 20.4 19.6 20.4 19.0 20.4 19.3 20.4 20.0 20.5 20.2 20.7 19.9 20.7 19.2 20.8 19.3 20.7 19.7 20.8 19.8 20.8 19.3 20.8 19.1 20.8 19.5 19.7 20.9 19.2 20.8 19.5 20.9 19.8 20.9 19.2 20.9 19.1 20.9 19.1 20.9 19.7 20.9 19.7 20.9 19.2 20.9 19.3 20.9 19.8 20.9 19.6 20.9 19.0 20.9 19.1 20.9 19.8 20.9 20.2 21.0 19.3 20.9 18.9 20.9 19.2 20.9 19.7 20.9 19.8 20.9 19.5 20.9 19.4 20.9 19.4 20.9 19.8 20.9 19.8 21.0 19.6 20.9 19.8 20.9 19.6 20.9 19.6 21.0 19.5 20.9 19.5 21.0 19.7 21.0 19.6 21.0 19.7 21.0 19.5 20.9 800 19.4 21.0 19.6 20.9 20.6 (2011) Bed Year 521.2 (2011) Water 20.0 21.2

Avg. Water Surface Slope Riffle Length Avg. Riffle Slope Pool Length Avg. Pool Slope

1000 Surface

2007 ---18.0 ----22.0 -----

2008 0.0002 32.0 0.0005 24.0 0.0020

2009 0.0003 17.0 0.0000 10.0 0.0022

2010 0.0008 15.6 0.0000 25.8 0.0007

2011 0.0008 14 0.0011 15 0

1200

Project Name Reach Feature Date Crew

Lloyd Property - Year 5 (2011) Monitoring 2 Profile 3/23/11 Perkinson, Dean

Elevation (feet - arbitrary)

2007 Year 1 Monitoring \Survey Station Bed Elevation Water Elevation 0.0 24.0 19.7 23.6 38.4 23.9 49.4 23.5 69.9 24.0 81.1 23.4 92.7 23.0 103.2 23.8 118.1 24.0 118.7 22.8 135.2 22.3 145.5 23.1 150.6 23.5 165.8 23.4 173.0 23.1 179.8 22.7 187.8 23.3 193.6 23.5 207.7 23.3 231.8 23.6 238.1 23.1 243.3 23.1 249.4 23.3 257.7 23.6 276.9 23.5 283.3 23.1 290.7 22.9 301.1 23.7 314.8 22.1 325.5 22.0 330.6 22.5 334.7 22.8 25.0 349.4 23.0 372.7 22.6 379.3 22.3 391.0 22.6 24.0 396.3 23.1 436.9 22.4 450.6 21.6 463.5 22.0 23.0 471.6 22.5 498.6 23.0 512.0 21.2 533.2 22.1 22.0 542.7 22.6 550.2 22.4 563.6 21.6 575.7 22.1 21.0 581.7 22.6 589.8 22.3 596.0 21.8 624.4 20.3 20.0 636.8 21.6 647.0 22.4 674.6 22.0 682.6 21.4 19.0 691.8 21.2 697.8 21.9 705.4 22.1 729.0 21.4 18.0 736.7 20.8 0 743.2 21.7 752.6 22.0 770.3 21.1 777.0 20.9 788.3 21.5

2008 Year 2 Monitoring \Survey Station Bed Elevation Water Elevation 1346.9 19.4 20.1 1335.0 19.3 20.2 1326.9 18.7 20.1 1317.6 18.7 20.1 1309.5 19.4 20.2 1276.6 20.0 1268.6 19.8 20.2 1262.8 19.2 20.3 1252.6 19.1 1243.5 19.0 20.2 1233.7 19.7 20.2 1217.3 19.8 20.5 1212.7 19.4 20.5 1197.6 19.4 20.5 1188.4 19.9 20.4 1165.1 19.9 20.7 1161.2 19.5 1145.4 20.1 20.6 1129.1 20.3 20.9 1122.0 19.5 21.0 1112.7 19.8 21.0 1101.3 20.2 21.0 1094.3 20.0 21.0 1091.1 19.8 21.0 1080.9 20.5 20.9 1067.4 20.6 1053.8 20.3 1044.3 20.8 1026.6 20.7 21.2 1022.1 20.5 21.2 1016.3 20.4 21.3 1008.8 20.8 21.1 997.3 21.1 987.3 20.8 21.4 983.2 20.5 21.4 977.9 20.5 21.4 971.1 21.1 21.5 953.2 21.2 946.7 21.2 21.6 942.1 20.8 21.7 936.8 20.8 21.8 931.1 21.3 21.8 923.4 21.4 900.8 21.2 21.8 895.5 21.0 21.9 891.2 21.0 21.9 884.1 21.5 21.9 873.1 21.4 21.9 870.3 21.2 21.9 864.9 20.9 21.9 860.2 21.7 22.0 835.3 21.5 22.1 829.1 21.2 22.1 823.7 20.9 22.1 815.0 21.5 22.1 793.2 21.5 22.1 788.9 21.5 22.1 780.7 21.2 769.7 20.9 22.0 763.4 21.7 22.2 743.6 21.7 22.2 738.6 200 21.1 22.2 731.7 20.8 22.2 720.5 21.6 22.2 Year 1 (2007) Bed 698.5 21.7 22.3 694.1 21.6 22.3

2009 2010 2011 Year 3 Monitoring \Survey Year 4 Monitoring \Survey Year 5 Monitoring \Survey Station Bed Elevation Water Elevation Station Bed Elevation Water Elevation Station Bed Elevation Water Elevation 1353.9 19.5 20.2 1351.4 19.6 20.2 1338.6 19.2 20.3 1340.8 19.3 20.2 1339.4 19.5 20.2 1333.3 18.8 20.2 1335.2 18.9 20.2 1332.9 19.0 20.2 1324.7 18.4 20.3 1325.7 18.7 20.2 1324.7 18.4 20.2 1314.2 19.1 20.3 1317.1 19.3 20.2 1312.6 19.3 20.2 1299.5 19.5 20.2 1298.7 19.7 20.2 1293.0 19.7 20.2 1269.6 19.6 20.3 1280.9 20.0 20.2 1267.0 19.5 20.3 1261.6 19.4 20.3 1271.0 19.9 20.3 1254.4 18.8 20.3 1250.9 19.0 20.3 1259.5 19.4 20.4 1249.4 18.3 20.3 1239.2 19.6 20.4 1249.9 19.0 1242.8 19.0 20.3 1221.7 19.6 20.4 1239.8 19.9 20.3 1237.5 19.7 20.3 1208.9 19.4 20.4 1220.5 19.9 20.5 1225.2 20.0 20.4 1203.3 19.6 20.4 1212.2 19.7 20.5 1216.8 19.4 20.4 1195.2 19.8 20.4 1203.7 19.6 20.5 1199.3 20.0 20.5 1175.5 19.7 20.6 1196.6 20.0 20.5 1168.1 20.1 20.6 1165.7 19.7 20.6 1168.4 20.2 20.7 1161.9 19.7 20.5 1155.5 19.3 20.7 1159.7 19.4 20.7 1153.8 19.3 20.6 1145.4 19.8 20.6 1155.7 19.3 20.7 1145.0 20.3 20.7 1133.7 20.5 21.0 1148.8 20.3 20.7 1131.9 20.4 21.1 1121.2 19.6 21.0 1134.9 20.6 21.0 1126.2 19.9 21.1 1114.0 19.8 21.0 1125.9 19.8 21.0 1117.6 19.6 21.1 1106.9 20.0 21.0 1119.3 19.8 20.9 1107.6 19.7 21.1 1100.3 19.9 21.0 1105.3 20.2 21.0 1104.0 20.1 21.2 1093.5 19.7 21.0 1097.8 19.9 21.0 1102.0 20.2 21.1 1083.5 20.3 21.1 1093.7 20.0 21.0 1096.0 19.7 21.2 1064.6 20.4 21.0 1085.5 20.5 21.0 1083.0 20.4 21.2 1055.0 20.1 21.1 1070.7 20.7 21.0 1066.1 20.5 21.2 1046.9 20.5 21.1 1061.7 20.8 21.0 1055.9 20.2 21.2 1028.1 20.5 21.2 1056.3 20.4 21.0 1050.4 20.2 21.2 1020.2 20.2 21.2 1049.2 20.7 21.0 1042.7 Profile20.9 1013.1 20.6 21.2 Lloyd - Reach 2 21.2 1033.5 20.8 21.2 1029.4 20.6 21.4 1001.2 20.7 21.3 1024.1 20.5 21.2 1019.6 20.4 21.5 991.9 20.7 21.4 1019.5 20.4 21.3 1014.6 20.7 21.4 982.5 20.3 21.4 1015.6 20.8 21.3 1006.2 21.0 21.4 974.3 20.8 21.4 1002.4 21.1 21.4 993.6 21.0 21.4 960.1 21.0 21.6 993.0 20.9 21.4 984.2 20.6 21.6 953.8 21.0 21.7 985.8 20.6 21.4 977.6 20.6 21.5 947.3 20.7 21.7 976.8 21.1 21.4 967.3 21.4 21.5 940.1 20.3 21.6 967.1 21.3 21.7 953.7 21.3 21.8 934.3 21.0 21.6 955.5 21.4 21.7 944.1 20.9 21.8 921.0 21.0 21.6 952.6 21.2 21.7 931.0 21.3 21.9 904.6 20.7 21.7 941.2 20.9 21.7 921.6 21.5 21.9 899.7 20.7 21.7 935.5 21.4 21.7 905.9 21.3 22.0 893.2 20.6 21.7 927.7 21.5 21.8 893.5 20.9 22.0 888.4 21.4 21.7 907.8 21.5 21.8 884.4 21.6 22.2 884.3 21.2 22.3 898.4 21.0 21.9 876.7 21.4 22.1 878.3 21.0 22.3 894.0 21.1 21.9 871.9 20.9 22.2 868.2 20.5 22.2 887.4 21.5 21.9 867.6 21.0 22.1 862.8 21.3 22.3 878.4 21.5 22.0 858.1 21.8 22.1 852.2 21.2 22.3 870.9 20.9 22.0 848.8 21.6 22.2 837.6 21.0 22.3 865.5 21.5 22.0 839.3 21.6 22.3 830.2 20.6 22.2 860.3 21.8 22.0 831.1 21.0 22.2 822.1 21.1 22.4 852.5 21.7 22.1 826.3 21.1 22.2 812.4 21.3 22.4 840.9 21.6 22.1 812.0 21.6 22.2 791.9 21.4 22.4 832.2 21.3 22.1 798.3 21.6 22.2 784.2 21.1 22.4 826.8 21.1 22.1 786.1 21.2 22.2 775.4 20.8 22.4 820.2 21.5 22.1 780.5 21.0 22.2 766.2 21.5 22.5 809.6 21.7 22.1 772.5 21.0 22.2 747.6 21.4 22.4 798.5 21.7 22.1 763.8 21.8 22.3 739.0 20.9 22.5 787.2 21.3 22.1 750.0 21.9 22.3 732.9 20.9 22.5 778.4 21.0 22.1 741.0 21.4 22.3 725.1 21.5 22.5 400 600 800709.5 1000 772.4 21.1 22.1 735.1 21.0 21.6 22.5 767.5 21.8 22.1 721.1 21.6 (feet) 22.3 700.1 21.5 22.5 Distance 759.8 21.9 22.2 702.6 21.6 22.3 692.5 21.4 22.5 Year 2 (2008) Bed Year 3 (2009) Bed Year 4 (2010) Bed Year 2 (2011) Bed Year 5 (2011) Water 750.6 22.0 22.3 695.8 21.4 22.2 683.9 21.3 22.5 Surface 740.7 21.2 22.3 684.6 21.3 22.3 673.8 21.6 22.5

2007 Avg. Water Surface Slope0.0033 20.0 Riffle Length Avg. Riffle Slope 0.0110 22.0 Pool Length ----Avg. Pool Slope

1200

2008 0.0033 26.0 0.0084 24.0 0.0014

2009 0.0032 19.7 0.0006 23.7 0.0005

2010 0.0032 18.6 0.0067 31.2 0.0019

2011 0.0029 21.0 0.0025 11.0 0.0007

1400

Project Name Reach Feature Date Crew

Elevation (feet - arbitrary)

Station 0.0 9.3 17.1 24.6 30.1 34.2 53.0 61.5 74.4 85.9 93.6 112.3 126.6 133.0 146.1 151.9 163.9 180.8 193.3 206.8 216.7 230.7 249.0 273.5 291.8 302.4 315.9 320.9 353.7 361.9 374.7 388.1 21.0 406.2 414.5 421.3 428.3 20.0 447.3 460.6 473.8 19.0 482.3 493.8 502.6 515.5 18.0 530.7 541.2 562.0 17.0 569.7 591.0 594.8 609.9 16.0 635.7 644.3 649.8 15.0 665.1 672.7 687.5 695.8 14.0 702.5 716.4 717.3 13.0 730.1 749.9 759.5 767.0 780.3 785.2

Lloyd Property - Year 5 (2011) Monitoring 3 Profile 3/23/11 Dean, Perkinson

2007 Year 1 Monitoring \Survey Bed Elevation Water Elevation 19.2 18.6 19.2 19.7 19.1 19.3 19.2 18.0 17.8 18.5 19.2 19.7 18.8 18.6 18.9 19.4 18.7 17.6 19.2 18.8 18.3 17.3 18.7 18.3 17.9 18.0 18.6 19.2 18.8 18.1 17.9 18.9 18.3 17.6 18.2 18.7 17.9 17.3 17.4 18.1 18.3 18.2 17.9 17.0 16.8 17.6 18.2 16.5 16.0 18.0 17.2 16.7 16.2 16.9 17.3 16.8 16.4 15.9 16.9 16.2 14.6 15.9 0 100 16.6 16.9 15.9 14.9

Station 932.0 878.4 863.1 855.2 844.7 831.3 820.8 816.1 802.7 796.2 784.1 777.2 763.5 755.4 742.2 729.8 719.4 712.0 705.9 702.2 696.8 673.6 668.8 659.3 650.0 640.4 617.1 611.5 603.5 593.4 587.7 569.1 552.6 542.8 534.6 524.9 498.3 484.4 475.0 467.4 456.1 443.7 426.1 414.5 410.3 402.1 385.5 379.2 365.4 350.6 321.1 305.0 295.7 284.0 267.6 246.5 238.6 229.6 221.9 209.9 192.0 181.2 171.4 158.4 147.8 138.8

2008 Year 2 Monitoring \Survey Bed Elevation Water Elevation 16.0 17.0 16.4 17.3 15.8 17.3 15.8 17.3 16.6 17.3 16.7 17.3 15.1 17.3 15.2 17.3 16.8 17.3 15.8 17.3 15.1 17.3 16.8 17.3 17.0 17.4 16.3 17.5 16.1 14.9 17.4 17.7 17.1 17.5 16.1 17.6 16.2 17.5 16.6 17.5 17.2 17.2 17.9 16.6 17.9 16.3 17.9 17.3 17.9 17.8 17.9 18.3 16.9 18.3 16.4 18.4 18.0 18.5 18.4 18.9 17.5 18.9 17.0 17.0 18.9 17.7 18.9 18.1 18.3 18.3 19.0 17.7 19.0 17.5 17.5 19.0 18.5 19.0 18.8 19.3 17.7 19.3 17.7 19.3 18.8 19.3 18.8 19.5 17.9 19.5 18.2 19.5 18.7 19.5 19.2 19.7 18.2 19.7 18.0 18.3 19.7 18.9 19.7 18.8 19.8 18.0 19.7 17.7 17.8 19.7 19.1 19.8 19.2 19.9 18.0 200 19.9 18.4 19.9 19.5 19.8 Year 1 19.4 19.9 18.5 19.9

2009 2010 Year 3 Monitoring \Survey Year 4 Monitoring \Survey Station Bed Elevation Water Elevation Station Bed Elevation Water Elevation 1017.0 15.3 17.0 918.0 15.9 1009.4 15.3 16.9 917.1 15.9 17.0 992.2 16.3 16.9 912.8 16.6 17.1 978.7 16.3 17.0 891.0 16.6 17.1 971.4 16.2 17.0 880.9 16.4 17.2 964.2 15.7 17.0 865.9 15.7 17.2 952.4 14.8 16.9 859.3 15.9 17.2 943.4 15.2 17.0 848.5 16.7 17.2 935.4 16.1 17.0 836.0 16.5 17.3 920.2 16.1 16.9 830.4 15.9 17.3 906.8 16.7 17.0 823.7 14.8 889.7 16.6 17.1 814.9 15.7 17.4 875.1 16.3 17.1 806.7 16.7 17.3 868.5 16.1 17.1 798.9 15.8 17.1 860.2 15.8 17.1 789.1 15.0 17.3 857.9 16.0 17.1 780.6 16.7 17.2 850.6 16.6 17.1 763.8 16.7 17.5 837.5 16.7 17.1 751.6 16.1 17.5 826.9 15.4 16.7 736.5 14.5 17.5 820.3 14.7 16.8 730.1 15.0 17.5 817.1 15.1 16.8 722.8 17.4 17.5 806.8 16.5 16.8 721.4 16.6 17.5 799.7 16.2 16.9 714.1 16.8 17.5 792.3 15.3 17.0 708.2 15.9 17.5 786.8 14.9 17.2 696.4 16.8 17.5 781.4 16.4 17.1 678.4 17.2 17.6 764.5 14.8 17.2 662.9 16.5 17.8 741.6 15.7 17.3 653.9 16.3 17.7 733.8 14.8 17.2 648.1 17.2 17.7 Lloyd Reach 3 18.0 722.8 17.8 17.2 631.7 Profile -17.5 721.0 16.8 17.3 613.1 17.8 18.3 713.0 16.8 17.3 600.4 16.1 18.2 708.9 16.1 17.3 593.4 18.0 18.3 706.1 16.2 17.3 587.0 18.3 18.6 696.9 16.9 17.3 572.3 18.2 18.7 686.5 17.1 17.4 556.1 17.4 18.8 672.7 17.3 17.6 545.6 16.8 18.8 662.1 16.6 17.7 538.1 16.8 18.8 659.6 16.5 17.6 531.0 17.8 18.7 651.9 16.4 17.6 507.9 18.5 18.8 645.4 17.2 17.6 501.5 17.9 18.7 636.4 17.2 17.6 491.6 18.2 18.8 623.2 17.7 18.0 472.7 18.7 611.9 17.7 18.1 463.1 17.4 18.7 603.2 16.8 18.1 447.6 18.3 18.7 598.6 16.2 18.1 432.1 18.6 19.0 596.1 16.3 18.1 422.9 17.8 19.1 591.9 17.9 18.2 414.0 17.7 19.1 580.7 18.2 18.4 407.4 18.5 19.2 571.5 18.3 18.5 400.0 18.4 19.2 564.6 17.7 18.6 387.7 18.2 19.4 557.0 17.7 18.6 374.8 17.7 19.4 546.6 17.0 18.6 363.5 18.3 19.4 537.6 16.7 18.5 341.1 18.8 19.3 529.7 17.9 18.6 322.8 19.1 19.6 519.9 17.8 18.6 311.0 18.3 19.6 505.9 18.5 18.7 301.4 18.1 19.6 498.7 18.2 18.7 290.4 18.1 19.7 490.1 18.2 18.7 282.0 18.1 19.7 478.4 17.8 18.7 270.7 18.9 19.6 469.3 17.4 18.7 249.2 18.8 19.7 459.6300 17.5 18.7400 237.8 15.6500 19.8 453.8 17.7 18.7 226.4 Distance 17.7 19.7 (feet) 443.5 18.6 18.8 220.8 18.0 19.6 (2007) Bed Year 2 (2008) Bed Year 3 (2009) Bed Year 4 (2010) Bed 428.3 18.8 19.0 211.5 18.9 19.6 417.8 18.0 19.0 195.0 19.2 19.7

2011 Year 5 Monitoring \Survey Station Bed Elevation Water Elevation 1021.7 16.5 1013.5 14.7 17.4 1011.2 14.6 17.5 1004.6 15.7 17.4 989.8 16.0 17.4 972.8 16.4 17.5 958.8 15.1 17.4 947.3 14.6 17.4 943.7 14.8 17.4 935.4 16.1 17.5 915.4 16.1 17.5 893.6 16.8 17.5 882.3 16.5 17.5 867.4 15.8 17.5 861.8 15.7 17.5 855.8 16.0 17.5 838.8 17.1 17.6 830.2 16.0 17.6 820.1 15.0 17.6 815.5 15.3 17.6 806.0 16.7 17.7 796.5 15.8 17.6 792.7 15.3 17.6 787.2 14.4 17.6 775.4 17.0 17.6 761.4 16.9 17.9 756.3 16.2 17.9 746.7 16.0 17.9 734.2 14.7 17.9 727.8 14.8 17.8 722.0 17.4 714.3 16.9 17.8 708.1 16.1 17.9 703.0 16.1 17.9 693.7 17.0 17.8 677.7 17.4 18.1 665.3 16.8 18.0 653.9 16.5 18.0 642.2 17.3 18.1 617.2 18.0 18.5 603.2 16.8 18.6 597.4 16.2 18.5 586.0 18.2 18.7 572.5 18.4 18.9 560.3 17.9 19.0 547.4 17.1 19.0 538.8 16.9 19.0 529.0 17.9 18.9 507.3 18.5 19.1 491.3 18.2 19.0 480.3 17.9 19.0 469.1 17.6 19.1 456.9 17.5 19.1 445.7 18.4 19.2 429.8 18.9 19.4 418.1 17.9 19.3 414.4 17.7 19.3 399.9 18.6 19.5 388.5 18.8 19.6 381.6 17.8 19.6 366.2 18.3 19.6 353.2 17.8 19.6 600 700 341.9 19.0 19.6 326.5 19.2 19.7 Year 5 (2011) Bed Year 5 (2011) Water Surface 314.4 18.4 19.7 302.5 18.2 19.7

2007 Avg. Water Surface Slope0.0034 19.0 Riffle Length 0.0001 Avg. Riffle Slope 29.0 Pool Length ----Avg. Pool Slope

800

2008 0.0036 24.0 0.0091 38.0 0.0011

2009 0.0033 19.2 0.0059 32.6 0.0001

900

2010 0.0037 18.0 0.0063 34.1 0.0014

2011 0.0032 18.0 0.0043 13.0 0.0019

1000

Appendix B: Preconstruction Photographs

Looking upstream on abandoned channel

Looking downstream on abandoned channel from Site infall.

at Site infall.

Looking downstream on abandoned channel.

Looking upstream on abandoned channel.

Looking across the abandoned channel toward the main tributary adjacent to the tree line.

Appendix B: Preconstruction Photographs (continued)

Looking across the abandoned channel toward the area of Rains soils proposed for nonriverine wetland restoration.

Looking upstream at the main channel adjacent to

Looking towards the abandoned channel

the tree line.

near the location of the culverted crossing that will bisect the easement.

Looking downstream at the confluence of the main channel and the abandoned channel.

Looking upstream towards the confluence of the main channel and the existing eastern channel/roadside ditch.

Lloyd Stream and Wetland Restoration Site Year 5 (2011) Annual Monitoring Stream Fixed Photo Stations Taken November 22, 2011

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

Lloyd Stream and Wetland Restoration Site Year 5 (2011) Annual Monitoring Stream Fixed Photo Stations Taken November 22, 2011 (continued)

Photo from 4/12/10. No photo available for 2011.

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

APPENDIX C HYDROLOGY DATA 2011 Groundwater Gauge Graphs

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

44 days

5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/21/2011

3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG1 Year 5 (2011 Data)

March 17 November 5 End of Growing Season 8

60 days 7

22 days 6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17

29 days

5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/21/2011

3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG2 Year 5 (2011 Data)

November 5 End of Growing Season 8

45 days 7

7 days 6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17

8 days

5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

16 days

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

3/21/2011

16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG3 Year 5 (2011 Data)

November 5 End of Growing Season 8

7

6 days 6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17

5 days

6 days 5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

20 18 16 14 12 10 8 6 4 2 0 -2 14 days -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 -36

3/21/2011

3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG4 Year 5 (2011 Data)

November 5 End of Growing Season 8

7

6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17

23 days

10 days 5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

32 days

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/21/2011

3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG5 Year 5 (2011 Data)

November 5 End of Growing Season 8

7

48 days

6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17 November 5 End of Growing Season

19 days 13 days

Gauge thought to be struck by lightning 5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

3/21/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG6 Year 5 (2011 Data) 8

7

6

March 17

8 November 5 End of Growing Season

April 8

7

Gauge thought to be struck by lightning. Base on data this gauge likely would have remained

69 days

27 days

24 days

6

53 days

5

31 days 4

3

2

1

Date

11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

3/21/2011

3/11/2011

0

Precipitation (inches)

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG7 Year 5 (2011 Data)

Date 11/6/2011

10/27/2011

March 17 November 5 End of Growing Season

5

4

3

2

1

0

Precipitation (inches)

21 days

10/17/2011

10/7/2011

Gauge thought to be struck by lightning

9/27/2011

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

24 days

4/20/2011

4/10/2011

3/31/2011

3/21/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG8 Year 5 (2011 Data) 8

7

6

27 days

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17 November 5 End of Growing Season

7 days

6 days 5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

18 days

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

3/21/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/11/2011

3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge LG9 Year 5 (2011 Data) 8

7

24 days 6

Date 11/6/2011

10/27/2011

10/17/2011

10/7/2011

9/27/2011

March 17 November 5 End of Growing Season

9 days 5

4

3

2

1

0

Precipitation (inches)

April 8

9/17/2011

9/7/2011

8/28/2011

8/18/2011

8/8/2011

7/29/2011

7/19/2011

7/9/2011

6/29/2011

6/19/2011

6/9/2011

5/30/2011

5/20/2011

5/10/2011

4/30/2011

4/20/2011

4/10/2011

3/31/2011

3/21/2011

3/11/2011

20 18 16 14 12 10 8 6 4 2 0 -2 -4 -6 -8 -10 -12 -14 -16 -18 -20 -22 -24 -26 -28 -30 -32 -34 3/1/2011

Water Level (inches)

Lloyd Restoration Site - Groundwater Gauge REF Year 5 (2011 Data) 8

7

17 days 6

APPENDIX D MONITORING PLAN VIEW

Annual Monitoring Report Lloyd Stream and Wetland Restoration Site

Appendices

0

215

430

860

³

Feet 1,720

1,290

3 2! ( 3

# *

2 ! (

# *

1

Prepared for:

6 ! (

# *

8

# *

4

1

# *

2

1 ! (

Project:

# *

# *

9

LLOYD STREAM AND WETLAND MITIGATION SITE

5

3

Onslow County, NC # *

6

7

Title:

! (

9 ! (

4

# * # *

7

MONITORING PLAN VIEW

10

5

Drawn by:

! (

# *

11! (

4

CLF Date:

NOV 2011

Legend Conservation Easement = 24.26 acres 8 ! (

# * # *

15

# *

Riparian Wetland Restoration = 8.2 acres

12

1:3600 Project No.:

10-001

Nonriparian Wetland Restoration = 3.1 acres

5

14

Restored Stream # *

Scale:

13

FIGURE

Riparian Wetland Creation (floodplain bench) = 1.9 acres Vegetation Plots ! (

Groundwater Gauges

# *

Photo Points

D1