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HomeMy WebLinkAbout20080229 Ver 1_Year 2 Monitoring Report Stream_20091022Forrest Creek Mitigation Bank Year 2 Stream Monitoring Report Orange County, North Carolina USGS H UC: 03020201020020 October 2009 t , rf' r r vow, {j g ?CY r?r-. r -9§: f ?'{1l r.', F l.?rV L Jri ? df? ?'?. J ,.; _ ?!:?a.{4 h? 7 r aS} . f A - Fib 'l TABLE OF CONTENTS 1.0 EXECUTIVE SUMMARY PROJECT ABSTRACT 2.0 PROJECT BACKGROUND 2.1 LOCATION AND SETTING 2.2 STRUCTURE AND OBJECTIVES 3.0 PROJECT CONDITION AND MONITORING RESULTS 3.1 VEGETATION ASSESSMENT 3.1.1 Soil Data 3.1.2 Vegetative Problem Areas 3.1.3 Stem Counts 3.1.4 Vegetation Assessment Summary 3.2 CHANNEL STABILITY ASSESSMENT 3.2.1 Cross Sections 3.2.2 Bank Full Events 3.2.3 Longitudinal Profiles 3.2.4 Site Summary and Remedial Actions Figure 1: Project Location Map Figure 2: Monitoring Plan View TABLES Table L Project Mitigation Structure and Objectives Table H. Project Activity and Reporting History Table HI. Project Contacts Table IV. Preliminary Soil Data Table V Installed Plantings Table VI. Stem Counts by Species Table VII. Stem Counts by Plot Table VIII. Bankfull Events 1 3 3 3 6 6 6 7 8 8 11 11 12 12 13 5 5 6 6 7 9 10 12 Forrest Creek Mitigation Bank i Monitoring Year 2 of 5 APPENDICES APPENDIX A. Vegetation Raw Data APPENDIX B. Cross Sections APPENDIX C. Profile Survey Pebble Counts APPENDIX D. Photo Logs APPENDIX E. Bank Full Event Photo Log Rainfall Table Repairs Forrest Creek Mitigation Bank ii Monitoring Year 2 of 5 1.0 EXECUTIVE SUMMARY/PROJECT ABSTRACT The Forrest Creek Mitigation Bank (Bank) is located in Orange County North Carolina within land owned by Milton A. Latta and Sons Dairy Farms, Inc. A permanent conservation easement covers the restored stream and surrounding riparian buffer. This easement defines the Bank's boundaries. The Bank is located on an active dairy farm approximately seven miles northeast of Hillsborough and six miles northwest of Durham in northeastern Orange County, North Carolina. The stream(s) lie within USGS hydrologic unit 03020201020020 in the Neuse River Basin. The North Carolina Division of Water Quality (NCDWQ) classifies the main reach, Forrest Creek, as a WS-II (water supply II), HQW (high quality water), and NSW (nutrient sensitive water). Prior to restoration, pasture land surrounded most of the length of the project reaches and the stream banks lacked strong rooted vegetation (e.g. woody or deep rooted herbaceous vegetation). Due to the lack of bank protection and partially cleared watershed, the stream channels became entrenched within the floodplain and showed signs of high shear stress. In this condition and with regular impacts due to cattle traffic, bank erosion had accelerated and the variety of bed features diminished. Two types of vegetative communities surrounded the stream reaches prior to restoration. The first zone consisted of a mix of woody vegetation that included significant populations of invasive species including privet (Ligustrum sinense), multiflora rose (Rosa multiflora), Japanese honeysuckle (Lonicera japonica), Japanese Stilt Grass (Mircostegium vimineum), Tree-of-Heaven (Ailanthus altissima), and Princess Tree (Paulownia tomentosa). This zone covered the lower section of the Ut Forrest Creek and the upper section of Forrest Creek. The second zone consisted primarily of herbaceous vegetation with scattered woody vegetation. The woody vegetation included a mix of natural, invasive, and succession species. This zone covered the remaining restoration areas. The altered conditions of the stream and the riparian buffer reduced water quality and impaired habitat. Pasture derived nutrients flowing untreated through the riparian zone and fine silts sloughing from the incised banks raised biochemical oxygen demand. This with the lack of sufficient reoxygenating riffle features reduced dissolved oxygen within the water column. Water quality had also diminished due to raised turbidity from bank erosion and elevated water temperatures caused by the lack of tree shading. Habitat potential had been reduced by the diminished water quality and loss of physical habitat such as bed features, undercut banks, and a well developed vegetative community. The Forrest Creek reach was restored within the existing floodplain using a Priority II approach and the Ut Forrest Creek reach bed was raised to the abandoned floodplain using a Priority I approach. A portion of Forrest Creek immediately above the Forrest Creek restoration reach was enhanced by modifying a downstream crossing that had caused ponding upstream of it. The crossing modification reestablished natural flow and will create a natural channel profile. Above the enhancement area, a section of Forrest Forrest Creek Mitigation Bank 1 Monitoring Year 2 of 5 Creek has been placed under a conversation easement to preserve a functional stream channel and riparian buffer. The stream restoration work is regulated under the Forrest Creek Mitigation Bank Mitigation Banking Instrument signed by the Sponsor and the US Army Corp of Engineers (USACE), the US Environmental Protection Agency (USEPA), the NC Division of Water Quality (NCDWQ), and the NC Wildlife Resouces Commission (NCWRC) all comprising the Interagency Review Team (IRT) formerly the MBRT in accordance with Federal guidelines and regulations including the Compensatory Mitigation losses of Aquatic Resources Final Rule, 33 CFR Parts 325 and 332 and 40 CFR Part 230. Restoration work resulted in the restoration of 6,825 linear feet, enhancement (Level I) of 325 linear feet, and preservation of 3,005 linear feet of stream. With the restoration, water quality will be improved due to a decrease in nutrients, turbidity, and moderation in water temperature. Biochemical oxygen demand will be reduced through filtering in the riparian buffer and riverine wetlands. Potential habitats have been added through the creation of bed features and reestablishment of riparian vegetative community. Monitoring Plan The annual monitoring work will assess the Bank's streams, the Forrest Creek main channel and the Unnamed Tributary to Forrest Creek, to determine restoration success. The monitoring plan has been set up based on guidance provided by The Stream Mitigation Guidelines developed by the United States Corps of Engineers - Wilmington District (McLendon, Scott, Fox, Becky et al. 2003), version 1.2 (11/16/2006) of the North Carolina Ecosystem Enhancement Program (EEP) document entitled "Content, Format, and Data Requirements for EEP Monitoring Reports", version 2.0 (3/27/2008) of the EEP document entitled "Mitigation Plan Document Format, Data Requirements, and Content Guidance", and the Forrest Creek Mitigation Bank Mitigation Plan (May 2008). The monitoring will occur annually for five years. The monitoring period should include two separate years with bankfull events. Bankfull events will be verified using an installed crest stage gauge that will be inspected during each monitoring visit. Monitoring reports will be submitted during years 1-5. Monitoring work will include reference photographs, vegetative stem counts, materials sampling, site survey, bankfull event documentation, and visual assessment and mapping of significant features. Mid- Atlantic Mitigation and the MT in coordination with the appropriate regulatory agencies, will determine when stream and riparian restoration have met success criteria. The sections below provide a framework for determining and assessing success criteria. Stream restoration will be considered successful through achievement of stable channel geometry, appropriate channel materials, and lack of significant erosion. The riparian buffer will be monitored for survivability and specific densities of planted vegetation and exclusion of invasive species. The site will be maintained during the monitoring period to allow it to continue on a trajectory that meets project goals and success criteria. Repairs Forrest Creek Mitigation Bank 2 Monitoring Year 2 of 5 will be completed as necessary to reestablish channel stability and the site will be replanted if vegetation shows signs of significant failure or if vegetative density goals contained in the NMI are not achieved. Year 2, 2009 monitoring was completed on September 1st, 2009. Survey work was completed in July. Strategies and methodologies laid out in the Monitoring Plan will be followed for a minimum of five years of monitoring. The stream will be monitored for stability of dimension, pattern, and profile using standard practices including permanent cross sections, longitudinal profile, and pebble counts. Vegetative success of associated plantings will be monitored for species diversity and survival with standardized, permanent (10m by 10m) vegetation plots to be monitored annually for 5 years. Monitoring data will be analyzed to determine what remedial actions, if any, are required. Any remedial actions proposed will be detailed in the following monitoring report. 2.0 PROJECT BACKGROUND 2.1 LOCATION AND SETTING The Forrest Creek Mitigation Bank (Bank) is located in Orange County North Carolina within land owned by Milton A. Latta and Sons Dairy Farms, Inc. A permanent conservation easement covers the restored stream and surrounding riparian buffer. This easement defines the Bank's boundaries. The Bank is located approximately seven miles northeast of Hillsborough and six miles northwest of Durham in northeastern Orange County, North Carolina. The stream(s) lie within USGS hydrologic unit 03020201020020 in the Neuse River Basin. Streams within the Bank consist of two reaches. The larger reach (Forrest Creek) flows through the property from north to south and drains a 3.6 square mile area consisting of predominantly forest and pasture land. The smaller tributary (UT 1) flows from west to east before joining with Forrest Creek and drains a 0.1 square mile area consisting of predominantly pasture land. 2.2 STRUCTURE AND OBJECTIVES The goals of the project relate to providing ecological improvements to the Bank's streams and riparian buffers through beneficial modifications of hydrology, water quality, and habitat. Goals related to hydrology include: ? Re-establishing floodplain connection by raising bed elevations (UT1) or lowering adjacent floodplain (Forrest Creek) ? Increasing flood storage by re-establishing floodplain connection Forrest Creek Mitigation Bank 3 Monitoring Year 2 of 5 Goals related to water quality include: ? Reducing turbidity and pollution by reducing sediment and nutrient inputs (cattle exclusion) ? Reducing water temperatures by providing shading ? Increasing / stabilizing oxygen levels by reducing BOD/COD and increasing reoxygenating turbulence Goals related to habitat include: ? Improving in stream bed habitat by increasing riffle - pool diversity, reducing sedimentdeposition, and improving low flow water depths ? Improving bank habitat by increasing stability and woody biomass ? Improving floodplain habitat by establishing microtopography and hydrology, removing invasive vegetation, and increasing habitat diversity ? Improving food web dynamics by adding biomass (such as detritus, coarse woody debris, and leaf matter) and re-establishing floodplain connection The restoration achieves these goals through the following objectives: ? Stabilizing channel bed and banks through modifying dimension, pattern, and profile using natural channel design ? Installing in-stream structures such as rock vanes, log vanes, and constructed riffles ? Raising stream bed elevations or lowering floodplains ? Restoring soils in riparian buffer by excluding cattle and adding organic components ? Removing invasive vegetation ? Planting native vegetation in riparian buffer ? Fencing out livestock Together, these improvements will provide functional uplift for the watershed as a whole. The dimension, pattern, and profile were restored using Rosgen Priority I and II restoration approaches (Rosgen, David L. 1997). The Priority I approach was used on Ut Forrest Creek to raise bed elevations and reconnect the stream to the abandoned floodplain. The Priority II approach was used on Forrest Creek to reestablish an active floodplain at the existing bed elevation. These methods will decrease stream bank erosion, establish an active floodplain, reduce channel stress during floods, improve aquatic habitat, and reduce fine sediments. A portion of Forrest Creek immediately above the restoration reach was enhanced by modifying a downstream crossing that had created ponding upstream of it. The crossing modification reestablished natural flow and will create a natural channel profile. Above the enhancement area, a section of Forrest Creek has been placed under conservation easement to preserve a functional stream channel and riparian buffer. The remaining impaired riparian buffer was planted as four (4) zones. Zones 1 and 2 are the stream channel and bank zones consisting of tree and shrub species and native herbaceous seeding typically found along stream banks in the region. Live stakes comprised the bulk of installed species within these zones. Zone 3 is the riparian zone Forrest Creek Mitigation Bank 4 Monitoring Year 2 of 5 consisting of selected tree and shrub species with a range of tolerances to inundation and saturation. Zone 4 is the transitional zone that includes the buffer areas (subject of a separate report prepared for NCDWQ). Pre As Built Mitigation Feature Mitigation Construction Length/ Credit Mitigation Type Length/Area Area Ratio Credits Forrest Creek Restoration 3,405 ft 3,484 ft 1:1 3,484 ft UT to Forrest Creek Restoration 2,436 ft 3,371 ft 1:1 3,371 ft Forrest Creek Enhancement 325 ft 325 ft 1.5:1 217 ft Forrest Creek Preservation 3,005 ft 3,005 ft 5:1 601 ft Total Stream Credits (SMU) 7,673 ft Table II. Project Activity and Reporting History Activity or Report Calendar Year of Completion or Planned Completion MBI Signed March 2007 Buffer Agreement Signed April2008 Construction March to June 2008 Temporary /Permanent seeding March to Jul 2008 Containerized Plantings March to Jul 2008 Mitigation Plan November 2008 Year 1 Monitoring December 2008 Year 2 Monitoring October 2009 Year 3 Monitoring Year 4 Monitoring Year 5 Monitoring Forrest Creek Mitigation Bank 5 Monitoring Year 2 of 5 Table III. Project Contacts Project Manager 1960 Derita Road Mid-Atlantic Mitigation, LLC Concord, NC 28027 Rich Mogensen (704) 782-4133 Designer 3001 Weston Parkway Kimley-Horn and Associates Inc. Cary, NC 27513 Todd St.John & Daren Pait (919) 653- 2950 Construction Contractor Shamrock Environmental Corporation P.O Box 14987 Browns Summit, NC 27214 Mike Granson: 336 708-5930 Planting Contractor 550 E. Westinghouse Blvd. Carolina Wetland Services Charlotte, North Carolina 28273 Joshua Frost (704) 527-1177 ext 102 Monitoring Performers Mid-Atlantic Mitigation, LLC 1960 Derita Road Concord, North Carolina 28027 Christine Cook (704) 782-4140 3.0 PROJECT CONDITION AND MONITORING RESULTS 3.1 VEGETATION ASSESSMENT 3.1.1 Soil Data Table IV. Preliminary Soil Data Series Max Depth in % Clay on Surface K T OM % Chewacla 60 10-27 .28 5 1-4 Forrest Creek Mitigation Bank 6 Monitoring Year 2 of 5 3.1.2 Vegetative Problem Areas The site is stabilized and vegetated with native woody and herbaceous species. Invasive species listed in the executive summary and in the Mitigation Report have not reestablished themselves and will continue to be monitored and noted in future reports. Kudzu, which was previously kept at bay by grazing cattle has began to establish along UT1 between Stations 119 and 127, approximately. This population will be treated this year and annual treatments will be scheduled for this area. The Sponsor is taking this threat very seriously and will begin necessary measures to control the problem immediately. An unidentified species of commelina (Dayflower) has colonized the riffle areas along the main channel somewhat aggressively. It is expected that the plants will die back over- winter. Care will be taken in the spring and summer of 2010 (year 3) to prevent regrowth. A more detailed discussion of the effects of these populations can be found with the Pebble Count analysis in the Forrest Creek Mitigation Bank Stream Monitoring report. As documented in the previously submitted Supplemental Planting Report, supplemental livestaking was done on January 14th and 15th and a supplemental planting of 1,000 gallon size trees was completed on January 29th, 2009 by Carolina Wetland Services. Findings of the 2009 monitoring activities and stems counts are discussed in the following section. Table V. Installed Plantings Bare roots and tublings (2008) Livestakes (2008) Livestakes (2009) Gallons (2009) Asimina triloba 600 Betula nigra 600 200 Cephalanthus occidentalis 600 Cornus amomum 600 3775 500 Fraxinus pennsylvanica 600 200 Ilex opaca 600 Jugulans nigra 600 Platanus occidentalis 600 200 Quercus michauxii 600 200 Quercus palustris 600 Quercus phellos 600 200 Salix nigra 11325 1000 Total 6600 15100 1500 1000 Forrest Creek Mitigation Bank 7 Monitoring Year 2 of 5 3.1.3 Stem Counts Four planting zones were established as follows: Zone 1 - Stream channel; Zone 2- Stream Bank; Zone 3 - Riparian; and Zone 4 - Transitional (including buffer areas). Live stakes were installed along the new constructed channel within Zones 1 and 2. Zones 2 - 4 consist of tublings, gallon and 3 gallon size plants. A reduction in the percentage of nuisance vegetation in areas with existing vegetation to less than 10% will indicate establishment of native wetland vegetation. Study plots show that the composition and density of vegetation in the restoration areas compares closely to the reference areas, indicating restoration success for vegetation. Success will be gauged by stem counts of planted species. Stem counts of over 320 woody stems per acre after 5 years will be considered successful. Presence, numbers and health of desirable volunteers will be considered before a replant will be deemed necessary. Photos taken at established photo points should indicate maturation of riparian vegetation community. Photographs will help to capture the health of the planted vegetation and the severity of any invasive or exotic species that establish within the site. Permanent vegetative plots have been established at 14 locations. The success of vegetation plantings will be measured through stems counts. Height and DBH were measured at baseline and will be measured in years 3 and 5. These plots will be used to sample primarily Zones 2, 3 and 4. Each plot covers 100 square meters for tree counts. Within each plot, a 1 meter plot will be sampled to measure herbaceous coverage. During the counts, the health of the vegetation will be noted. In addition to stem counts, the samples will inventory species diversity to allow for comparison between the reference and restoration wetlands and track the percent cover of nuisance species. The vegetation survey will occur during the growing season. On September 1st, 2009, the second year vegetative monitoring was performed on the established vegetative plots. 3.1.4 Vegetation Assessment Summary The success of riparian vegetation planting will be gauged by stem counts of planted species and an assessment of community composition including (desirable) volunteers. Stem counts of over 320 trees and shrubs per acre after 5 years will be considered successful. The composition of the vegetation community should trend toward a predominance of target species. A majority (80%) of the target species should be present in the reforestation area in numbers and condition conducive to continuing the species through the maturation of the community. The population of invasive species will be kept below 10% of the total population. Photos taken at established photo points should indicate maturation of riparian vegetation community. The Year 2 monitoring numbers indicate approximately 80% survival and 413 stems per acre overall. The Tributary reach maintained an overall stems per acre count of 358 not counting volunteer species. The main channel reach maintained an overall stem per acre count of 468 without including volunteer species. This number (main channel reach) was improved by supplemental plantings done prior to the 2009 growing season. Forrest Creek Mitigation Bank 8 Monitoring Year 2 of 5 Table VI: Total Stem Counts by Suecies -FU > O 0 ? a' L C O ~ O 4, - O N O C VI f6 c I L - N N L U L C ? Q Q z U Species Asimina triloba 10 9 10 7 70 Betula nigra* 7 5 12 12 100 Cephalanthus occidentalis 4 4 4 8 100 Cercis canadensis 3 2 3 1 33 Cornus amomum 12 9 12 8 67 Fraxinus pennsylvanica* 14 11 21 21 100 Ilex opaca 1 1 1 0 0 Jugulans nigra 15 11 15 5 33 Liriodendron tulipifera 1 0 1 0 0 Morus rubra 1 1 1 1 Quercus michauxii* 3 2 11 11 100 Quercus palustris 64 45 64 43 67 Quercus phellos* 1 1 11 11 100 Salix nigra 20 7 22 22 100 Unknown 13 10 - - - Total 168 118 188 150 80 *Species included in 2009 supplemental Planting Forrest Creek Mitigation Bank 9 Monitoring Year 2 of 5 Table VII: Stems per Acre by Plot and Year Replant - Baseline MY1 Year 2 MY2 wi Vol. Vegplot Stems/acre Stems/acre Stems/acre Stems/acre Stems/acre VQ1 283 202 324 445 688 VQ2 364 243 486 445 - VQ3 486 364 364 364 - VQ4 486 364 364 283 364 VQ5 364 202 445 405 647 VQ6 324 81 647 688 850 VQ7 405 81 607 607 - Average stems/acre = (Main Channel) 387 220 462 468 566 Vegplot Stems/acre Stems/acre Stems/acre Stems/acre Stems/acre VQT1 647 283 688 647 728 VQT2 688 607 607 283 - VQT3 647 486 486 324 - VQT4 526 445 445 202 - VQT5 486 324 324 324 - VQT6 607 526 526 607 - VQT7 486 405 405 121 162 Average stems/acre (Tributary) 584 439 497 358 376 Average stems/acre = (Total) 486 330 480 413 471 Along the Main channel only Plot VQ4 indicated a stems per acre count of below 320. 283 stems per acre were counted; however inclusion of 2 volunteer stems of Cottonwood and Smooth Sumac increased the count to 364 stems per acre. Both Cottonwood and Sumac tend to colonize in large numbers, however, this is not currently the case and neither species is classified as invasive. The 2009 supplemental planting covered the main channel only and stem counts on the main channel for 2009 do not indicate the need for a replant. A handful of new individuals will be added to VQ4 to boost stem counts for 2010. However, 2009 stem Forrest Creek Mitigation Bank 10 Monitoring Year 2 of 5 counts indicate a need for supplemental planting on UT I. Plots VQT2, VQT4, and VQT7 all indicated stems per acre counts below 320, while plots VQT3 and VQT5 both indicated stems per acre counts of 324, which is low for this stage (Year 2) in site development. Desirable volunteers do not yet contribute significantly to stems counts along UT1. A second supplemental planting covering only UT1 will be done this winter. Please note a change in the number of individuals labeled as Unknown. Final identifications were made during the 2009 count. Along the main channel of Forrest Creek, herbaceous cover is well established. Sample plots indicated an average of 94 % cover with a range of 80% (VQ6) to 100% cover (VQ3, 4, 5, and 7). VQ1 and 2 tend to hold standing water leaving some areas slightly bare. VQ6 was most recently stabilized with annual rye due to equipment traffic for repairs to the stream bank in winter 2008. Cattle grasses and grasses used for stabilization are beginning to be out competed by natural herbaceous cover such as soft rush and ploygonum in the wet areas; and narrow leaved sunflower, dog fennel and cockle burr in the drier areas. Along the unnamed tributary, herbaceous cover is well established and more mature than on the main channel. Sample plots indicated 100% cover throughout with similar composition to the main channel. Detailed vegetation survey information is located in Appendix A; including herbaceous cover, stressed individuals, and volunteers. 3.2 CHANNEL STABILITY ASSESSMENT 3.2.1 Cross Sections The stream geometry will be considered successful if the cross-section geometry, profile, and sinuosity are stable or reach a dynamic equilibrium. It is expected that there will be minimal changes in the designed cross sections, profile, and/or substrate composition. Changes that may occur during the monitoring period will be evaluated to determine if they represent a movement toward a more unstable condition (e.g. down cutting, erosion, mid-channel bars, etc.) or are minor changes that represent an increase in stability (e.g. settling, vegetative changes, coarsening of bed material, etc.). Deviation from the design ratios will not necessarily denote failure as it is possible to maintain stability and not stay within the design geometry. Additionally, determination of true bankfull will be difficult until the stream has had adequate flooding events to create strong bankfull indicators. Morphological data used for this report was collected in July, 2009 and is shown in Appendix B. Bankfull elevations are still not fully established and determination of true bankfull is still difficult, as noted above. Commelina is present in almost every riffle and throughout Forrest Creek Mitigation Bank 11 Monitoring Year 2 of 5 the tributary, this vegetation in the channel at time of survey creates a slight artificial rise in bed elevation on some cross sections. Overall the cross-section graphs for Year 2 compare well to Year 1 and show stable dimension with normal, minor fluctuations. 3.2.2 Bank Full Events Crest Stage Gages (CSG) are located on Forrest Creek and on the Tributary. Photo documentation is shown in the Bank Full Event Photo Log in Appendix E. Rain fall data is also presented in table form in Appendix E. A total of two bankfull events were documented since the submittal of the Year 1 Monitoring Report as noted in Table VI. Significant rain events were recorded by the on-site rain gage in May, June and July, but the CSG's were not triggered. It is typical for CSG's to be more difficult to trigger in the summer months. At the time of monitoring both gages were found to be water logged, and may have malfunctioned due to debris or vegetation blockage. Repairs were made to the swale area above the confluence of the main channel and UT1 in February. This repair was a hold over from Year 1 storm damage due to Hurricane Hanna. Before and after photos of this repair are located in Appendix E. Exhibit Table VI. Bankfull Events Site Visit Date Associated Rainfall Event Date Rainfall Amount (Inches) Method Documented 12-15-2008 Nov. 30 - Dec. 1st 1.25 CSG/Photos 4-15-2009 March 27 - 29th 1.99 CSG/Photos 3.2.3 Longitudinal Profiles Profiles 1, 2, and 3 are along portions of the UT and Profiles 4 and 5 cover larger sections of Forrest Creek. Commelina is present in almost every riffle and throughout the tributary, this vegetation in the channel at time of survey creates a slight artificial rise in bed elevation in some areas, particularly riffles. Overall the profile graphs for Year 2 compare well to Year 1 and show a stable profile with normal, minor fluctuations. Bed material was also sampled at five riffles throughout the project. Cross Sections T1, T3 and T6 on the UT are located in LP 1, LP 2, and LP 3, respectively. Cross Sections 2 and 4 on Forrest Creek are located in LP 4 and LP 5, respectively. All riffles are currently similar in composition dominated by larger class gravels and small cobble. All riffles show some silt/clay content, especially T3 and T6. Increase in silt content for 2009 is due to the presence of a semi-aquatic plant growing thickly in the riffles of the main channel and throughout UT I. Periodic dry conditions allowed Dayflower to establish in the shallower areas. Once the plant and organic matter was cleared away from the cross section(s) bed material similar to the previous years' count was found. The commelina will be watched this winter to determine if it will die back completely on its own or will need to be removed prior to the start of the growing season. At a minimum, herbicide treatments will be used to prepare cross sections for 2010 pebble counts if necessary. Forrest Creek Mitigation Bank 12 Monitoring Year 2 of 5 Morphological data used for the profiles in this report was collected in July, 2009 and is shown in Appendix C. Pebble count data was collected on September 1st, 2009. 3.2.4 Site Summary and Remeadial Actions The herbaceous vegetative cover has developed a healthy and diverse community throughout most of the site. The planted trees and shrubs in the riparian and buffer areas have also done relatively well and are supplemented by an existing buffer community which will provide a seed source for native volunteers well suited to the current site conditions. Low stem counts along UT1 are likely due to herbaceous competition. Original plantings were done with bare roots and tublings. Tublings, in particular, are not well suited to these competitive conditions. A 2010 replant along UT1 will be done with only gallon size trees, which typically maintain a higher level of success and can be planted in smaller numbers. Approximately 500 to 700 trees will be installed during this replant. Invasive species will be treated with herbicide this year and full scale removal of Kudzu along UT1 near VQT2 will be scheduled for the spring and late summer, with annual treatments thereafter. Beaver activity was not noted in 2009. On-going beaver management will be maintained as part of the monitoring requirements as discussed in the Mitigation Plan. Forrest Creek Mitigation Bank 13 Monitoring Year 2 of 5 Prepared by Jason Diaz ???ruxaia im APPENDIX A. Vegetation Raw Data APPENDIX B. Cross Sections APPENDIX C. Profile Survey Pebble Counts APPENDIX D. Photo Log APPENDIX E. Bank Full Event Log Rainfall Table Vegetation Quad Photo Log LP97vy?-.9 P J{rs?i ?'? - }?C P yry? W _ `iL J { ? E yF f kt b, Atf 0 4ir ryFy?? .{ '"?l ?,; i r 1 v t i b ?Nc:. VQ 1 VQ3 VQ2 M4 R .t L 3Yt ?? '??i sa-:b W, _ ?"• S ,:.' 9I { FJ Fp §D ?} ;? -i t,? 31 VQ4 VQ5 Ij??Yp7'. # ? ? b as • ? r '14 4 i L4 gyp. Nl? r + 1. r VQ6 rr M1'?.. i . n S 3 ' ? 5 ? ?• cif, i s c L ti 5 4 1 VQ7 VQT 1 l yY` ? ? a ?: 7 .f e e Yr. ? xv- rw? V,- a i VQT2 x r 1 yf9}s d - I?t . f? ..:•4 fr i' A',. 3 5 r, :f 1 r v',e ? 5 " t'P r,z a? A ?eix f.'? VQT3 ?A VQT4 f. ? l F ? I! ? `4. 7 '4, ?. ??r Lk,?? ??: 7 l • ? t? '1 /.rig" rye ?5.f `? ,?.s? S alrii - `R• 1 1 4.Vf ._'`.. •,r.?x e ?, t„ s;?:: A: a.. ? ?, ,o-1 s ?t ....k =?.? ... VQT5 t. t t i ) f ? ,l. f f y? w . VQT6 . P f ? t y ? f i ? q 5 VQT7 Baseline Project: Forrest Creek stems = 7 Date: 6/1/2008 plot size (m"2) = 100 Name: VQ1 stems/acre = 283 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name Common Name Condition Comments 4.3 0.5 Unknown sp Unknown sp 9 2.1 Quercus sp. Oak Sp. 6.9 3.9 Quercus sp. Oak Sp. 3.1 3 Quercus sp. Oak Sp. 2.2 6.8 Quercus sp. Oak Sp. 6.4 6.9 Quercus sp. Oak Sp. 10 7.6 Quercus sp. Oak Sp. MY1 Project: Forrest Creek stems = 5 Date: 12/4/2008 plot size (m"2) = 100 Name: VQ1 stems/acre = 202 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name Common Name Condition Comments 4.3 0.5 Unknown sp Unknown sp Stressed 9 2.1 Quercus palustris Pin Oak 3.1 3 Quercus palustris Pin Oak 2.2 6.8 Quercus palustris Pin Oak 10 7.6 Quercus palustris Pin Oak 1.5 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2.4 8.5 Liquidambar styraciflua Sweet Gum Invasive native ddh (mm) Height (cm) 6 47 4 48 3 26 3 38 3 30 3 25 3 36 Replant - Year 2 Project: Forrest Creek stems = 8 stems = Vol. = 9 Date: 5/29/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQ1 stems/acre = 324 stems/acre = 364 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name Common Name Condition Comments 9 2.1 Quercus palustris Pin Oak 3.1 3 Quercus palustris Pin Oak 2.2 6.8 Quercus palustris Pin Oak 10 7.6 Quercus palustris Pin Oak 1.5 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2.4 8.5 Liquidambar styraciflua Sweet Gum Invasive native 1.7 3.5 Betula nigra River Birch 1/29/09 Replant 6.6 8.8 Betula nigra River Birch 1/29/09 Replant 4.9 0 Quercus phellos Willow Oak 1/29/09 Replant 6.8 2.6 Juglans nigra Black Walnut Vol. 1 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2.3 5.1 Liquidambar styraciflua Sweet Gum Invasive native 6.9 3.9 Quercus palustris Pin Oak 0 5.2 Liquidambar styraciflua Sweet Gum Invasive native 4.2 6.2 Liquidambar styraciflua Sweet Gum Invasive native 2 6.8 Liquidambar styraciflua Sweet Gum Invasive native 1.2 9.5 Liquidambar styraciflua Sweet Gum Invasive native MY2 Project: Forrest Creek stems = 11 stems = Vol. = 17 Date: 9/1/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQ1 stems/acre = 445 stems/acre = 688 Size: 10m x 10m Cover: Dog fennel; m ixed cattle grasses = 85% X (m) y (m) Scientific Name Common Name Condition Comments 9 2.1 Quercus palustris Pin Oak 3.1 3 Quercus palustris Pin Oak 2.2 6.8 Quercus palustris Pin Oak 10 7.6 Quercus palustris Pin Oak 1.5 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2 5.1 Liquidambar styraciflua Sweet Gum Invasive native 2.4 8.5 Fraxinus pennsylvanicus Green Ash Replaced Sweet gum 6.6 8.8 Betula nigra River Birch 4.9 0 Quercus phellos Willow Oak 6.8 2.6 Robinia pseudoacacia Black Locust Vol. 1 5.1 Quercus phellos Willow Oak Replaced Sweet gum 2.3 5.1 Quercus michauxii Swamp chestnut Oak Replaced Sweet gum 6.9 3.9 Quercus palustris Pin Oak 0 5.2 Liquidambar styraciflua Sweet Gum Invasive native 4.2 6.2 Liquidambar styraciflua Sweet Gum Invasive native 2 6.8 Liquidambar styraciflua Sweet Gum Invasive native 1.2 9.5 Salix Nigra Black Willow Replaced Sweet gum VQ1 10 9 8 7 6 5 4 3 2 1 0 0 Black Willow River Birch Green Ash Pin Oak Sweet Gum Pin Oak ¦ Sweet Gum Swamp Sweet Gum Sweet Gum Chestnut Oak Willow Oak Sweet Gum Pin Oak ¦ Pin Oak Black Walnut Pin Oak ¦ Willow Oak 1 2 3 4 5 6 7 X (m) 8 9 10 ¦ Baseline ¦ MY1 ¦ Replant (Year 2) MY2 Baseline Project: Forrest Creek stems = 9 Date: 6/1/2008 plot size (m"2) = 100 Name: VQ2 stems/acre = 364 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 2.8 0.4 Quercus sp. Oak sp. 2 22 3.7 3 Quercus sp. Oak sp. 2 30 4.7 7 Quercus sp. Oak sp. 3 35 1.9 9 Quercus sp. Oak sp. 3 34 1.5 5.6 Quercus sp. Oak sp. 3 39 6.9 1.3 Quercus sp. Oak sp. 2 28 9.8 4.1 Quercus sp. Oak sp. 3 36 7.2 4.3 Unknown sp Unknown sp 3 12 8.3 8.3 Quercus sp. Oak sp. 3 32 MY1 Project: Forrest Creek Date: 12/4/2008 Name: VQ2 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name 2.8 0.4 Quercus palustris 4.7 7 Quercus palustris 1.9 9 Quercus palustris 1.5 5.6 Quercus palustris 6.9 1.3 Quercus palustris 8.3 8.3 Quercus palustris stems = plot size (m"2) _ stems/acre = Common Name Pin Oak Pin Oak Pin Oak Pin Oak Pin Oak Pin Oak 6 100 243 Condition Comments Replant - Year 2 Project: Forrest Creek stems = 12 Date: 5/29/2009 plot size (m"2) = 100 Name: VQ2 stems/acre = 486 Size: 10m x 10m Cover: 25% water, 75% grass x (m) y (m) Scientific Name Common Name Condition Comments 2.8 0.4 Quercus palustris Pin Oak 4.7 7 Quercus palustris Pin Oak 1.9 9 Quercus palustris Pin Oak 1.5 5.6 Quercus palustris Pin Oak 6.9 1.3 Quercus palustris Pin Oak 8.3 8.3 Quercus palustris Pin Oak 2.6 1.9 Fraxinus pennsylvanica Green Ash 1/29/09 Replant 1.3 5.9 Betula nigra River Birch 1/29/09 Replant 4.6 7.5 Betula nigra River Birch 1/29/09 Replant 6.8 5.1 Betula nigra River Birch 1/29/09 Replant 9.4 3.2 Quercus phellos Willow Oak 1/29/09 Replant 3.7 3 Quercus palustris Pin Oak MY2 Project: Forrest Creek Date: 9/1/2009 Name: VQ2 Size: 10m x 10m Cover: X (m) 4.7 1.9 1.5 6.9 8.3 2.6 1.3 4.6 6.8 9.4 9.8 stems = plot size (m"2) _ stems/acre = mixed cattle grasses, porcupine sedge, cokleburr = 90% y (m) 7 9 5.6 1.3 8.3 1.9 5.9 7.5 5.1 3.2 4.1 Scientific Name Quercus palustris Quercus palustris Quercus palustris Quercus michauxii Quercus palustris Fraxinus pennsylvanica Betula nigra Betula nigra Betula nigra Quercus phellos Quercus michauxii Common Name Pin Oak Pin Oak Pin Oak Swamp Chestnut Oak Pin Oak Green Ash River Birch River Birch River Birch Willow Oak Swamp Chestnut Oak 11 100 445 Condition Comments VQ2 10 9 8 7 6 5 4 3 2 1 0 0 Pin Oak Pin Oak River Birch Pin Oak River Birch Pin Oak River Birch Swam ¦ Chest Willow Oak Green Ash Pin Oak ¦ A Oak 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 ¦ Replant - Year 2 MY2 Baseline Project: Forrest Creek Date: 6/1/2008 Name: VQ3 Size: 10m x 10m Cover: 60% grass x (m) y (m) 3 0.3 6.4 0.1 9.2 1.6 7.4 4.3 4.5 2.8 0.9 4.8 3 7.3 5.8 6.6 9.7 6.5 8.2 8.7 5.1 9.3 2.3 9.9 Scientific Name Asimina triloba Asimina triloba Asimina triloba Cornus amomum Asimina triloba Cornus amomum Cornus amomum Asimina triloba Fraxinus pennsylvanica Asimina triloba Asimina triloba Cornus amomum stems = plot size (m"2) = stems/acre = Common Name Common Pawpaw Common Pawpaw Common Pawpaw Silky Dogwood Common Pawpaw Silky Dogwood Silky Dogwood Common Pawpaw Green Ash Common Pawpaw Common Pawpaw Silky Dogwood 12 100 486 Condition Comments ddh (mm) Height (cm) 9 89 11 114 10 120 7 84 15 124 5 42 6 65 9 107 4 23 11 106 11 100 4 65 MY1 Project: Forrest Creek stems = Date: 12/4/2008 plot size (m"2) _ Name: VQ3 stems/acre = Size: 10m x 10m Cover: 60% grass x (m) y (m) Scientific Name Common Name 3 0.3 Asimina triloba Common pawpaw 6.4 0.1 Asimina triloba Common pawpaw 9.2 1.6 Asimina triloba Common pawpaw 7.4 5.3 Cornus amomum Silky Dogwood 4.5 2.8 Asimina triloba Common pawpaw 0.9 4.8 Cornus amomum Silky Dogwood 5.8 6.6 Asimina triloba Common pawpaw 9.7 6.5 Fraxinus pennsylvanica Green Ash 5.1 9.3 Asimina triloba Common pawpaw MY2 9 100 364 Condition Comments Project: Forrest Creek Date: 9/1/2009 Name: Size: VQ3 10m x 10m Cover: X (m) 3 6.4 9.2 7.4 4.5 0.9 9.7 5.1 0 stems = 9 plot size (m"2) = 100 stems/acre = 364 mixed cattle grasses, narrow leaved sunflower, soft rush = 100% cover y (m) Scientific Name Common Name Condition 0.3 Asimina triloba Common pawpaw 0.1 Asimina triloba Common pawpaw 1.6 Asimina triloba Common pawpaw stressed 5.3 Cornus amomum Silky Dogwood 2.8 Asimina triloba Common pawpaw 4.8 Cornus amomum Silky Dogwood 6.5 Fraxinus pennsylvanica Green Ash 9.3 Asimina triloba Common pawpaw stressed 7 Quercus palustris Pin Oak Comments not on previous counts but now touching the line VQ3 10 9 8 7 6 5 4 3 2 1 0 ¦ Common pawpaw ¦ Pin Oak ¦ ¦ Green Ash Silky Dogwood Silky Dogwood ¦ Common pawpaw Common pawpaw Common pawpaw Common pawpaw 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = 12 Date: 6/1/2008 plot size (m"2) = 100 Name: VQ4 stems/acre = 486 Size: 10m x 10m Cover: 50% Herbaceous Dicots x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 6.6 0.8 Juglans nigra Black Walnut 8 68 8.1 3.2 Quercus sp. Oak sp. 3 40 3.5 2.7 Fraxinus pennsylvanica Green Ash 9 55 1 5.4 Unknown sp Unknown sp 4 28 6.2 4.6 Quercus sp. Oak sp. 2 27 3.5 6.3 Quercus sp. Oak sp. 4 36 1 8 Quercus sp. Oak sp. 3 36 5.7 7.9 Quercus sp. Oak sp. 3 36 9.5 8.7 Juglans nigra Black Walnut 7 62 0 9.8 Salix nigra Black Willow Livestake 40 15 0.6 9.7 Salix nigra Black Willow Livestake 38 16 1.2 9.5 Salix nigra Black Willow Livestake 17 19 MY1 Project: Forrest Creek stems = 9 Date: 12/4/2008 plot size (m"2) = 100 Name: VQ4 stems/acre = 364 Size: 10m x 10m Cover: 50% Herbaceous Dicots x (m) y (m) Scientific Name Common Name Condition Comments 6.6 0.8 Juglans nigra Black Walnut 8.1 3.2 Quercus palustris Pin Oak 3.5 2.7 Fraxinus Pennsylvanica Green Ash Stressed 1 5.4 Unknown sp Unknown sp 6.2 4.6 Quercus palustris Pin Oak 3.5 6.3 Quercus palustris Pin Oak 1 8 Quercus palustris Pin Oak 5.7 7.9 Quercus palustris Pin Oak 9.5 8.7 Juglans nigra Black Walnut MY2 Project: Forrest Creek stems = 7 (w/vols) stems = 9 Date: 9/1/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQ4 stems/acre = 283 stems/acre = 364 Size: 10m x 10m Cover: Dog fennel, mi xed cattle grasses = 100% X (m) y (m) Scientific Name Common Name Condition Comments 6.6 0.8 Juglans nigra Black Walnut 1 5.4 Populus deltoides Cottonwood vol. 6.2 4.6 Quercus phellos Willow Oak 3.5 6.3 Quercus michauxii Swamp Chestnut Oak 1 8 Quercus phellos Willow Oak 5.7 7.9 Quercus phellos Willow Oak 0.6 9.7 Salix nigra Black Willow Livestake 1.2 9.5 Salix nigra Black Willow Livestake 6.4 0.2 Rhus glabra Smooth Sumac Vol. VQ4 10 I 9 8 7 6 5 4 3 2 1 0 Black Willow Live stakes Pin Oak ¦ Pin Oak Pin Oak Cottonwood Pin Oak ¦ ¦ Black Walnut Smooth Sumac Vol. 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek Date: 6/1/2008 Name: VQ5 Size: 10m x 10m Cover: 80% Broomsed ge x (m) y (m) Scientific Name 0.3 0.2 Quercus sp. 5.9 0.9 Fraxinus pennsylvanica 8.5 0.3 Quercus sp. 4.4 9.4 Unknown sp 5.5 3.7 Quercus sp. 2.6 3.1 Salix nigra 1.3 5.9 Fraxinus pennsylvanica 2.6 8.5 Quercus sp. 7.5 8.7 Fraxinus pennsylvanica stems = plot size (m"2) _ stems/acre = Common Name Oak sp. Green Ash Oak sp. Unknown sp Oak sp. Black Willow Green Ash Oak sp. Green Ash 9 100 364 Condition Comments ddh (mm) Height (cm) 3 41 4 34 2 35 8 28 3 37 4 19 5 33 3 44 2 20 MY1 Project: Forrest Creek Date: 12/4/2008 Name: VQ5 Size: 10m x 10m Cover: 80% Broomsed ge x (m) y (m) Scientific Name 5.9 0.9 Fraxinus pennsylvanica 8.5 0.3 Quercus palustris 1.3 5.9 Fraxinus pennsylvanica 2.6 8.5 Quercus palustris 7.5 8.7 Quercus palustris 1.2 6.3 Unknown sp 2.3 6.8 Unknown sp stems = 5 stems+ Vol. = 7 plot size (m"2) = 100 plot size (m"2) = 100 stems/acre = 202 stems/acre = 283 Common Name Green Ash Pin Oak Green Ash Pin Oak Pin Oak Unknown sp Unknown sp Condition Comments Vol. Vol. Replant - Year 2 Project: Forrest Creek stems = 11 stems+ Vol. = 16 Date: 5/29/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQ5 stems/acre = 445 stems/acre = 647 Size: 10m x 10m Cover: 80% Broomsedge x (m) y (m) Scientific Name Common Name 5.9 0.9 Fraxinus pennsylvanica Green Ash 8.5 0.3 Quercus palustris Pin Oak 1.3 5.9 Fraxinus pennsylvanica Green Ash 2.6 8.5 Quercus palustris Pin Oak 1.2 6.3 Cephalanthus occidentalis Buttonbush 2.3 6.8 Cephalanthus occidentalis Buttonbush 7.7 2.1 Fraxinus pennsylvanica Green Ash 2.4 9.4 Quercus phellos Willow Oak 0.3 0.2 Quercus palustris Pin Oak 5.5 3.7 Quercus palustris Pin Oak 0.7 5.4 Cephalanthus occidentalis Buttonbush 1.4 5.4 Cephalanthus occidentalis Buttonbush 0.5 7.8 Cephalanthus occidentalis Buttonbush 7.5 8.7 Fraxinus pennsylvanica Green Ash 4.4 9.4 Quercus palustris Pin Oak 6.3 9.8 Quercus palustris Pin Oak Condition Comments Vol. Vol. 1/29/09 Replant 1/29/09 Replant Vol. Vol. Vol. 1/29/09 Replant: mis-identified @ nursery? MY2 Project: Forrest Creek stems = 10 stems+ Vol. = 16 Date: 9/1/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQ5 stems/acre = 405 stems/acre = 647 Size: 10m x 10m Cover: dog fennel, narrow leaved sun flower = 100% x (m) y (m) Scientific Name Common Name 5.9 0.9 Fraxinus pennsylvanica Green Ash 8.5 0.3 Quercus palustris Pin Oak 1.3 5.9 Fraxinus pennsylvanica Green Ash 2.6 8.5 Quercus palustris Pin Oak 1.2 6.3 Cephalanthus occidentalis Buttonbush 2.3 6.8 Cephalanthus occidentalis Buttonbush 2.4 9.4 Quercus phellos Willow Oak 0.3 0.2 Quercus palustris Pin Oak 5.5 3.7 Quercus palustris Pin Oak 0.7 5.4 Cephalanthus occidentalis Buttonbush 1.4 5.4 Cephalanthus occidentalis Buttonbush 0.5 7.8 Cephalanthus occidentalis Buttonbush 7.5 8.7 Fraxinus pennsylvanica Green Ash 4.4 9.4 Quercus palustris Pin Oak 6.3 9.8 Quercus palustris Pin Oak 2.6 3.1 Diospyros virginiana Persimmon Condition Comments Vol. Vol. Vol. Vol. Vol. Vol. VQ5 10 9 8 7 6 5 4 3 2 1 0 0 Willow Oak Pin Oak Pin Oak Pin Oak Green Ash Buttonbush Buttonbush Buttonbush Green Ash Buttonbush Buttonbush Pin Oak Persimmon vol. ¦ Green Ash Pin Oak Pin Oak 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 ¦ Replant - Year 2 MY2 Baseline Project: Forrest Creek Date: 6/1/2008 Name: VQ6 Size: 10m x 10m Cover: 90% Annual R ye x (m) y (m) Scientific Name 1.1 1 Juglans nigra 8.7 0.3 Quercus alba 1.5 4.5 Fraxinus pennsylvanica 3.8 3 Quercus alba 7.7 3.1 Juglans nigra 5.8 7.1 Unknown sp 3.8 9.6 Quercus sp. 9.2 7 Quercus sp. MY1 stems = plot size (m"2) _ stems/acre = Common Name Black Walnut White Oak Green Ash White Oak Black Walnut Unknown sp Oak sp. Oak sp. ddh (mm) Height (cm) 8 55 2 19 3 33 4 20 8 51 3 32 2 17 4 38 8 100 324 Condition Comments Project: Forrest Creek Date: 12/4/2008 Name: VQ6 Size: 10m x 10m Cover: 90% Annual Rye x (m) y (m) 1.1 1 3.8 3 2.2 1.6 5 3.1 Scientific Name Juglans nigra Quercus michauxii Unknown sp Unknown sp stems = 2 stems + Vol. = 4 plot size (m"2) = 100 plot size (m"2) = 100 stems/acre = 81 stems/acre = 162 Common Name Black Walnut Swamp Chestnut Oak Unknown sp Unknown sp Condition Comments Vol. Vol. Replant - Year 2 Project: Forrest Creek Date: 5/29/2009 Name: VQ6 Size: 10m x 10m Cover: 90% Annual R ye x (m) y (m) Scientific Name 1.1 1 Juglans nigra 3.8 3 Quercus palustris 2.2 1.6 Juglans nigra 6.3 2.5 Fraxinus pennsylvanica 4.1 5 Fraxinus pennsylvanica 1.5 4.5 Fraxinus pennsylvanica 7.5 6.4 Fraxinus pennsylvanica 3.6 8.2 Betula nigra 3.4 1.9 Betula nigra 4.9 0.5 Sailx nigra 5.6 0.3 Sailx nigra 6.7 0.3 Sailx nigra 8.7 0.3 Sailx nigra 4.2 3.2 Diospyros virginiana 0.5 3.8 Platanus occidentalis 5.8 7.1 Quercus palustris 6.4 7.7 Quercus phellos 3.2 10 Diospyros virginiana 3.8 9.6 Quercus palustris stems = 16 stems +Vol. = 19 plot size (m"2) = 100 plot size (m"2) = 100 stems/acre = 647 stems/acre = 769 Common Name Black Walnut Pin Oak Black Walnut Green Ash Green Ash Green Ash Green Ash River Birch River Birch Black Willow Black Willow Black Willow Black Willow Persimmon Sycamore Pin Oak Willow Oak Persimmon Pin Oak Condition Comments 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant livestake - Replant livestake - Replant livestake - Replant livestake - Replant Vol. Vol. 1/29/09 Replant Vol. MY2 Project: Forrest Creek stems = 17 stems +Vol. _ Date: 9/1/2009 plot size (m"2) = 100 plot size (m"2) _ Name: VQ6 stems/acre = 688 stems/acre = Size: 10m x 10m Cover: narrow leaved sunflower, bare spots where annual rye is gone and not grown over yet = 80% cover x (m) 1.1 3.8 2.2 6.3 4.1 1.5 7.5 3.6 3.4 4.9 5.6 6.7 8.7 1 4.2 0.5 5.8 6.4 3.2 3.8 9.2 Y (m) 1 3 1.6 2.5 5 4.5 6.4 8.2 1.9 0.5 0.3 0.3 0.3 0 3.2 3.8 7.1 7.7 10 9.6 7 Scientific Name Juglans nigra Quercus palustris Juglans nigra Fraxinus pennsylvanica Fraxinus pennsylvanica Fraxinus pennsylvanica Fraxinus pennsylvanica Betula nigra Betula nigra Sailx nigra Sailx nigra Sailx nigra Sailx nigra Sailx nigra Diospyros virginiana Platanus occidentalis Quercus michauxii Quercus phellos Diospyros virginiana Quercus palustris Platanus occidentalis Common Name Black Walnut Pin Oak Black Walnut Green Ash Green Ash Green Ash Green Ash River Birch River Birch Black Willow Black Willow Black Willow Black Willow Black Willow Persimmon Sycamore Swamp Chestnut Oak Willow Oak Persimmon Pin Oak Sycamore Condition Comments Stressed Stressed Stressed Stressed livestake livestake livestake livestake livestake Vol. Vol. Vol. Vol. 21 100 850 previously not counted VQ6 10 9 8 7 6 5 4 3 2 1 0 Persimmon Pin Oak River Birch Willow Oak Swamp Sycamore Chestnut Oak Green Ash Green Ash Green Ash Sycamore Persimmon Pin Oak Green Ash River Birch Black Walnut Black Walnut Black Willow Black Willow Black Willow Black Willow 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 ¦ Replant - Year 2 MY2 Baseline Project: Forrest Creek stems = 10 Date: 6/1/2008 plot size (m"2) = 100 Name: VQ7 stems/acre = 405 Size: 10m x 10m Cover: 100% polygonum and cocklebur x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 0.7 0.7 Quercus sp. Oak sp. 3 31 3.9 2.1 Quercus sp. Oak sp. 5 50 6.7 2.3 Quercus sp. Oak sp. 4 31 9.8 2.5 Quercus sp. Oak sp. 4 45 3.9 2.1 Quercus sp. Oak sp. 3 40 7.5 4.6 Quercus sp. Oak sp. 3 34 4.5 4.5 Quercus sp. Oak sp. 3 42 1.8 7.2 Quercus sp. Oak sp. 3 42 7.5 9 Quercus sp. Oak sp. 3 31 9.8 2.5 Quercus sp. Oak sp. 4 27 MY1 Project: Forrest Creek stems = 2 Date: 12/4/2008 plot size (m"2) = 100 Name: VQ7 stems/acre = 81 Size: 10m x 10m Cover: 100% polygonum and cocklebur x (m) y (m) Scientific Name Common Name Condition Comments 3.9 2.1 Quercus palustris Pin Oak 7.5 4.6 Quercus palustris Pin Oak Replant - Year 2 Project: Forrest Creek stems = 15 Date: 5/29/2009 plot size (m"2) = 100 Name: VQ7 stems/acre = 607 Size: 10m x 10m Cover: 100% polygonum and cocklebur x (m) y (m) Scientific Name Common Name Condition 7.5 4.6 Quercus palustris Pin Oak 1.5 8.2 Fraxinus pennsylvanica Green Ash 1.7 1.6 Fraxinus pennsylvanica Green Ash 6.5 0.2 Betula nigra River Birch 9.5 8.8 Quercus phellos Willow Oak 6.7 2.3 Quercus phellos Willow Oak 9.8 0.8 Quercus michauxii Swamp Chestnut Oak 9.8 2.5 Quercus palustris Pin Oak 6.7 2 Quercus palustris Pin Oak 2.9 9.2 Quercus palustris Pin Oak 1.8 7.2 Quercus palustris Pin Oak 0.7 0.7 Quercus palustris Pin Oak 7.5 9 Quercus michauxii Swamp Chestnut Oak 7.5 6.7 Quercus michauxii Swamp Chestnut Oak 5.1 1.7 Quercus michauxii Swamp Chestnut Oak Comments 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant 1/29/09 Replant: mis-identified @ nursery? 1/29/09 Replant 1/29/09 Replant MY2 Project: Forrest Creek Date: 9/1/2009 Name: VQ7 Size: 10m x 10m Cover: x (m) 7.5 1.5 1.7 6.5 9.5 6.7 9.8 9.8 6.7 2.9 1.8 0.7 7.5 7.5 5.1 stems = plot size (m"2) _ stems/acre = polygonum, narrow leaved sunflower, cocklebur = 100% y (m) 4.6 8.2 1.6 0.2 8.8 2.3 0.8 2.5 2 9.2 7.2 0.7 9 6.7 1.7 Scientific Name Quercus palustris Fraxinus pennsylvanica Fraxinus pennsylvanica Betula nigra Quercus phellos Quercus phellos Quercus michauxii Quercus palustris Quercus palustris Quercus palustris Quercus palustris Quercus palustris Quercus michauxii Quercus michauxii Quercus michauxii Common Name Pin Oak Green Ash Green Ash River Birch Willow Oak Willow Oak Swamp Chestnut Oak Pin Oak Pin Oak Pin Oak Pin Oak Pin Oak Swamp Chestnut Oak Swamp Chestnut Oak Swamp Chestnut Oak 15 100 607 Condition Comments VQ7 10 9 8 7 6 5 4 3 2 1 0 0 Pin Oak Swamp Chestnut Oak Willow Oak Green Ash Pin Oak Swamp Chestnut Oak Pin Oak ¦ Willow Oak Pin Oak ¦ Green Ash Pin Oak Swamp Chestnut Oak Swamp Chestnut Oak Pin Oak River Birch 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 ¦ Replant - Year 2 MY2 Baseline Project: Forrest Creek stems = 16 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT1 stems/acre = 647 Size: 10m x 10m Cover: 90% cattle grass x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 3 0.7 Quercus sp. Oak sp. 5 32 7.9 1 Quercus sp. Oak sp. 4 46 1.4 3.3 Fraxinus pennsylvanica Green Ash 4 28 0.2 1.6 Salix nigra Black Willow 23 14 0.3 2.2 Salix nigra Black Willow 26 17 0.1 3.1 Salix nigra Black Willow 21 17 0.6 3.7 Salix nigra Black Willow 16 17 0.1 3.9 Salix nigra Black Willow 31 19 0.6 4.6 Salix nigra Black Willow 23 21 0.1 4.9 Salix nigra Black Willow 15 18 0.5 5.8 Salix nigra Black Willow 29 21 0.4 6.7 Salix nigra Black Willow 30 14 8.8 6.3 Quercus sp. Oak sp. 2 18 6.2 7.5 Fraxinus pennsylvanica Green Ash 4 33 0.5 7.3 Quercus sp. Oak sp. 4 47 2.3 9.5 Fraxinus pennsylvanica Green Ash 6 52 MY1 Project: Forrest Creek Date: 12/4/2008 Name: VQT1 Size: 10m x 10m Cover: 90% cattle grass x (m) y (m) Scientific Name 3 0.7 Quercus palustris 7.9 1 Quercus palustris 1.4 3.3 Fraxinus pennsylvanica 8.8 6.3 Quercus palustris 6.2 7.5 Fraxinus pennsylvanica 0.5 7.3 Quercus palustris 2.3 9.5 Fraxinus pennsylvanica stems = plot size (m"2) _ stems/acre = Common Name Pin Oak Pin Oak Green Ash Pin Oak Green Ash Pin Oak Green Ash 7 100 283 Condition Comments Replant - Year 2 Project: Forrest Creek stems = 17 stems + Vol. = 22 Date: 5/29/2009 plot size (m"2) = 100 plot size (m"2) = 100 Name: VQT1 stems/acre = 688 stems/acre = 890 Size: 10m x 10m Cover: 90% cattle grass x (m) y (m) Scientific Name Common Name Condition Comments 3 0.7 Quercus palustris Pin Oak 7.9 1 Quercus palustris Pin Oak 1.4 3.3 Fraxinus pennsylvanica Green Ash 8.8 6.3 Quercus palustris Pin Oak 6.2 7.5 Fraxinus pennsylvanica Green Ash 0.5 7.3 Quercus palustris Pin Oak 2.3 9.5 Fraxinus pennsylvanica Green Ash 7.1 3.8 Quercus michauxii Swamp Chestnut Oak 1/29/09 Replant 7.5 7.8 Quercus michauxii Swamp Chestnut Oak 1/29/09 Replant 0.1 0.8 Salix nigra Black Willow livestake - Replant 0.2 1.6 Salix nigra Black Willow livestake 0.3 2.2 Salix nigra Black Willow livestake 0.5 5.8 Salix nigra Black Willow livestake 0.4 6.7 Salix nigra Black Willow livestake 0.4 7.2 Salix nigra Black Willow livestake - Replant 0.4 8.5 Salix nigra Black Willow livestake - Replant 0.8 8.8 Platanus occidentalis Sycamore Vol. 2.8 5.6 Cephalanthus occidentalis Buttonbush Vol. 3.8 5.6 Cephalanthus occidentalis Buttonbush Vol. 4.2 7.2 Cephalanthus occidentalis Buttonbush Vol. 5.2 4.7 Fraxinus pennsylvanica Green Ash 1/29/09 Replant 6.2 1.1 Cephalanthus occidentalis Buttonbush Vol. MY2 Project: Forrest Creek stems = 16 Date: 9/1/2009 plot size (m"2) = 100 Name: VQT1 stems/acre = 647 Size: 10m x 10m Cover: dog fennel, mixed cattle grasses = 100% X (m) y (m) Scientific Name Common Name Condition 3 0.7 Quercus palustris Pin Oak 7.9 1 Quercus palustris Pin Oak 1.4 3.3 Fraxinus pennsylvanica Green Ash 8.8 6.3 Quercus palustris Pin Oak 6.2 7.5 Fraxinus pennsylvanica Green Ash 2.3 9.5 Fraxinus pennsylvanica Green Ash 7.1 3.8 Quercus michauxii Swamp Chestnut Oak 7.5 7.8 Quercus michauxii Swamp Chestnut Oak 0.1 0.8 Salix nigra Black Willow 0.2 1.6 Salix nigra Black Willow 0.3 2.2 Salix nigra Black Willow 0.5 5.8 Salix nigra Black Willow 0.4 6.7 Salix nigra Black Willow 0.4 7.2 Salix nigra Black Willow 0.4 8.5 Salix nigra Black Willow 2.8 5.6 Cephalanthus occidentalis Buttonbush 5.2 4.7 Fraxinus pennsylvanica Green Ash 6.2 1.1 Cephalanthus occidentalis Buttonbush stems + Vol. = 18 plot size (m"2) = 100 stems/acre = 728 Comments livestake livestake livestake livestake livestake livestake livestake Vol. Vol. VQT1 10 9 8 7 6 5 4 3 2 1 0 Green Ash ¦ Black Willow Swamp Chestnut Oak Green Ash ¦Black Willow ¦ Black Willow Pin Oak Black Willow Buttonbush ¦ ¦ ¦ Green Ash Swamp Chestnut Oak ¦ ¦ Green Ash ¦ Black Willow Black Willow Buttonbush Pin Oak Black Willow Pin Oak 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 ¦ Replant - Year 2 MY2 Baseline Project: Forrest Creek stems = 17 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT2 stems/acre = 688 Size: 10m x 10m Cover: 80% Eupatorium and grass x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 1.2 1.3 Quercus sp. Oak sp. 3 37 7.8 0.2 Quercus sp. Oak sp. 2 36 8.4 2.4 Juglans nigra Black Walnut 6 53 5.5 2.1 Unknown sp Unknown sp 3 28 1.9 3.3 Quercus sp. Oak sp. 8 41 1.5 3.8 Quercus sp. Oak sp. 4 40 3.9 4.1 Betula nigra River Birch 5 62 6.2 4.2 Ilex opaca American Holly 3 34 8 4.9 Cornus amomum Silky Dogwood 7 32 1.9 6.2 Quercus sp. Oak sp. 4 43 4.4 6.3 Juglans nigra Black Walnut 9 20 6.7 6.8 Quercus phellos Willow Oak 7 94 9.2 6.9 Unknown sp Unknown sp 5 40 7.3 9.1 Cornus amomum Silky Dogwood 6 53 4.7 8.9 Cornus amomum Silky Dogwood 10 53 2.7 8.5 Cephalanthus occidentalis Buttonbush 6 73 0.2 8 Betula nigra River Birch 5 49 MY1 Project: Forrest Creek stems = 15 Date: 12/4/2008 plot size (m"2) = 100 Name: VQT2 stems/acre = 607 Size: 10m x 10m Cover: 80% Eupatorium and grass x (m) y (m) Scientific Name Common Name Condition Comments 1.2 1.3 Quercus palustris Pin Oak 7.8 0.2 Quercus palustris Pin Oak 8.4 2.4 Juglans nigra Black Walnut 5.5 2.1 Unknown sp Unknown sp 1.9 3.3 Quercus palustris Pin Oak 1.5 3.8 Quercus palustris Pin Oak 3.9 4.1 Betula nigra River Birch 6.2 4.2 Ilex opaca American Holly 8 4.9 Cornus amomum Silky Dogwood 1.9 6.2 Quercus palustris Pin Oak 4.4 6.3 Juglans nigra Black Walnut 6.7 6.8 Quercus phellos Willow Oak 9.2 6.9 Unknown sp Unknown sp 7.3 9.1 Cornus amomum Silky Dogwood 2.7 8.5 Cephalanthus occidentalis Buttonbush MY2 Project: Forrest Creek stems = 7 Date: 9/1/2009 plot size (m"2) = 100 Name: VQT2 stems/acre = 283 Size: 10m x 10m Cover: Dog fennel = 10 0% Kudzu in plot x (m) y (m) Scientific Name Common Name Condition 1.2 1.3 Quercus palustris Pin Oak 1.9 3.3 Quercus palustris Pin Oak 1.5 3.8 Quercus palustris Pin Oak 3.9 4.1 Betula nigra River Birch 6.7 6.8 Quercus phellos Willow Oak 7.3 9.1 Cornus amomum Silky Dogwood 4.9 0.8 Betula nigra River Birch Comments VQT2 10 9 8 7 6 5 4 3 2 1 0 Silky Dogwood ¦ ¦ Willow Oak ¦ ¦ River Birch Pin Oak ¦ Pin Oak ¦ ¦ Pin Oak River Birch ¦ 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = 16 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT3 stems/acre = 647 Size: 10m x 10m Cover: 95% Solide go sp and cattle grass x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 2.5 0.3 Asimina triloba Common Pawpaw 10 108 6.4 0.9 Quercus sp. Oak sp. 6 45 9.4 0.6 Cornus amomum Silky Dogwood 5 84 2.6 2.5 Juglans nigra Black Walnut 9 74 0 3.1 Unknown sp Unknown sp 12 116 5 3.2 Unknown sp Unknown sp 7 52 9.5 3.5 Cercis canadensis Eastern Redbud 8 84 2 4.8 Cephalanthus occidentalis Buttonbush 6 89 3.7 5.5 Asimina triloba Common Pawpaw 6 82 5.8 5.4 Quercus sp. Oak sp. 6 65 8.3 5.5 Unknown sp Unknown sp 5 61 6.4 8 Cercis canadensis Eastern Redbud 8 107 4 7.6 Liriodendron tulipifera Tulip Poplar 7 54 2 7.3 Unknown sp Unknown sp 9 177 1.8 9.9 Cephalanthus occidentalis Buttonbush 7 93 3.3 9.9 Quercus sp. Oak sp. 4 55 MY1 Project: Forrest Creek stems = 12 Date: 12/4/2008 plot size (m"2) = 100 Name: VQT3 stems/acre = 486 Size: 10m x 10m Cover: 95% Solidego sp and cattle grass x (m) y (m) Scientific Name Common Name Condition 2.5 0.3 Asimina triloba Common Pawpaw 6.4 0.9 Quercus palustris Pin Oak 9.4 0.6 Cornus amomum Silky Dogwood 2.6 2.5 Juglans nigra Black Walnut 0 3.1 Unknown sp Unknown sp 5 3.2 Unknown sp Unknown sp 2 4.8 Cephalanthus occidentalis Buttonbush 3.7 5.5 Asimina triloba Common Pawpaw 6.4 8 Cercis canadensis Eastern Redbud 2 7.3 Unknown sp Unknown sp 1.8 9.9 Cephalanthus occidentalis Buttonbush 3.3 9.9 Quercus palustris Pin Oak MY2 Project: Forrest Creek stems = 8 Date: 9/1/2009 plot size (m"2) = 100 Name: VQT3 stems/acre = 324 Size: 10m x 10m Cover: Dog Fennel, narrow leaved sunflower = 100% x (m) y (m) Scientific Name Common Name Condition 2.5 0.3 Asimina triloba Common Pawpaw 6.4 0.9 Quercus palustris Pin Oak 9.4 0.6 Cornus amomum Silky Dogwood 2.6 2.5 Juglans nigra Black Walnut 5 3.2 Unknown sp Unknown sp 6.4 8 Cercis canadensis Eastern Redbud 3.3 9.9 Quercus palustris Pin Oak 3.5 4 Quercus palustris Pin Oak Comments Nyssa? Cornus? Morus rubra? River Birch? Comments Morus rubra? VQT3 10 9 8 7 6 5 4 3? 2 1 0 ¦ Pin Oak Eastern Redbud ¦ ¦ ¦ Pin Oak Red Mulberry ¦ Black Walnut Pin Oak Common Pawpaw Silky Dogwood 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = 13 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT4 stems/acre = 526 Size: 10m x 10m Cover: 95% Solide go sp and cockleburs x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 0.6 0.6 Cercis canadensis Eastern Redbud 6 85 2.8 0.3 Quercus sp. Oak sp. 3 35 7.4 0.5 Quercus sp. Oak sp. 3 39 9.1 2.4 Quercus sp. Oak sp. 2 35 6.3 2.3 Quercus sp. Oak sp. 4 24 3.4 2.5 Quercus sp. Oak sp. 3 36 7.2 5.1 Cephalanthus occidentalis Buttonbush 7 75 4.7 5.2 Quercus sp. Oak sp. 4 24 2.1 5.5 Unknown sp Unknown sp 4 57 0.2 6.1 Quercus sp. Oak sp. 3 30 2.7 7.7 Cornus amomum Silky Dogwood 5 54 5.2 7.6 Asimina triloba Common Pawpaw 7 72 0.3 8.5 Unknown sp Unknown sp 4 48 MY1 Project: Forrest Creek stems = Date: 12/4/2008 plot size (m"2) _ Name: VQT4 stems/acre = Size: 10m x 10m Cover: 95% Solidego sp and cockleburs x (m) y (m) Scientific Name Common Name 0.6 0.6 Cercis canadensis Eastern Redbud 2.8 0.3 Quercus palustris Pin Oak 7.4 0.5 Quercus palustris Pin Oak 6.3 2.3 Quercus palustris Pin Oak 3.4 2.5 Quercus palustris Pin Oak 7.2 5.1 Cephalanthus occidentalis Buttonbush 4.7 5.2 Quercus palustris Pin Oak 0.2 6.1 Quercus palustris Pin Oak 2.7 7.7 Cornus amomum Silky Dogwood 5.2 7.6 Asimina triloba Common Pawpaw 0.3 8.5 Quercus sp Oak sp MY2 11 100 445 Condition Comments Project: Forrest Creek stems = Date: 9/1/2009 plot size (m"2) _ Name: VQT4 stems/acre = Size: 10m x 10m Cover: cocleburr, dog fennel = 100% x (m) y (m) Scientific Name Common Name 7.4 0.5 Quercus palustris Pin Oak 7.2 5.1 Cephalanthus occidentalis Buttonbush 4.7 5.2 Quercus palustris Pin Oak 2.7 7.7 Cornus amomum Silky Dogwood 5.2 7.6 Asimina triloba Common Pawpaw 5 100 202 Condition Comments VQT4 10 9 8 7 6 5 4 3 2 1 0 0 ¦ Silky Dogwood Common Pawpaw ¦ ¦ Pin Oak Buttonbush ¦ Pin Oak ¦ ¦ 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = Date: 6/1/2008 plot size (m"2) _ Name: VQT5 stems/acre = Size: 10m x 10m Cover: 95% Solidego sp and cockleburs x (m) y (m) Scientific Name Common Name 0.4 1 Fraxinus pennsylvanica Green Ash 7.9 0.1 Juglans nigra Black Walnut 6.6 2.6 Betula nigra River Birch 3.1 2.3 Quercus alba White Oak 1.6 4.6 Betula nigra River Birch 4.8 5.1 Juglans nigra Black Walnut 7.6 5.6 Quercus sp. Oak sp. 0.8 3.2 Juglans nigra Black Walnut 3.1 7.6 Quercus sp. Oak sp. 6 7.9 Betula nigra River Birch 8.9 8.5 Betula nigra River Birch 1.6 10 Betula nigra River Birch 12 100 486 Condition Comments ddh (mm) Height (cm) 6 42 8 42 6 59 3 35 6 66 8 40 4 54 8 58 2 24 6 53 7 71 5 55 MY1 Project: Forrest Creek stems = 8 Date: 12/4/2008 plot size (m"2) = 100 Name: VQT5 stems/acre = 324 Size: 10m x 10m Cover: 95% Solidego sp and cockleburs x (m) y (m) Scientific Name Common Name Condition 0.4 1 Fraxinus pennsylvanica Green Ash 7.9 0.1 Juglans nigra Black Walnut Stressed 6.6 2.6 Betula nigra River Birch 3.1 2.3 Quercus alba White Oak 1.6 4.6 Betula nigra River Birch 3.1 7.6 Quercus palustris Pin Oak 8.9 8.5 Betula nigra River Birch 1.6 10 Betula nigra River Birch Stressed MY2 Project: Forrest Creek Date: 9/1/2009 Name: Size: Cover: X (m) 0.4 6.6 3.1 1.6 3.1 8.9 3.8 9.5 VQT5 10m x 10m narrow leaved sunflower, mixed grasses = 100% stems = plot size (m"2) _ stems/acre = Y (m) Scientific Name Common Name 1 Fraxinus pennsylvanica Green Ash 2.6 Betula nigra River Birch 2.3 Quercus palustris White Oak 4.6 Betula nigra River Birch 7.6 Quercus palustris Pin Oak 8.5 Betula nigra River Birch 0.5 Fraxinus pennsylvanicus Green Ash 6.5 Quercus palustris Pin Oak 8 100 324 Comments Condition Comments not previously counted not previously counted VQT5 10 9 8 7 6 5 4 3 2 1 0 River Birch ¦ Pin Oak Pin Oak ¦ ¦ River Birch ¦ White Oak River Birch Green Ash Green Ash ¦ 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = 15 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT6 stems/acre = 607 Size: 10m x 10m Cover: 97% Solidego sp and cockleburs x (m) y (m) Scientific Name Common Name Condition Comments ddh (mm) Height (cm) 8.6 2.9 Quercus sp. Oak sp. 3 41 5.6 2.1 Fraxinus pennsylvanica Green Ash 4 20 3 1.9 Fraxinus pennsylvanica Green Ash 4 29 0.4 2.7 Juglans nigra Black Walnut 7 58 4.5 4.5 Quercus sp. Oak sp. 4 35 6.9 5.3 Fraxinus pennsylvanica Green Ash 3 33 0 5.4 Salix nigra Black Willow Livestakes 36 25 0 6 Salix nigra Black Willow Livestakes 18 22 0 6.7 Salix nigra Black Willow Livestakes 13 30 0 7.3 Salix nigra Black Willow Livestakes 20 27 0 7.8 Salix nigra Black Willow Livestakes 29 24 0 8.4 Salix nigra Black Willow Livestakes 20 25 3 6.6 Fraxinus pennsylvanica Green Ash 4 29 9.3 7.6 Quercus sp. Oak sp. 3 35 1.9 9.5 Quercus sp. Oak sp. 3 40 MY1 Project: Forrest Creek stems = 13 Date: 12/4/2008 plot size (m"2) = 100 Name: VQT6 stems/acre = 526 Size: 10m x 10m Cover: 97% Solidego sp and cockleburs x (m) y (m) Scientific Name Common Name Condition Comments 8.6 2.9 Quercus palustris Pin Oak 5.6 2.1 Fraxinus pennsylvanica Green Ash 3 1.9 Fraxinus pennsylvanica Green Ash 0.4 2.7 Juglans nigra Black Walnut 4.5 4.5 Quercus palustris Pin Oak 0 5.4 Salix nigra Black Willow Livestakes 0 6 Salix nigra Black Willow Livestakes 0 6.7 Salix nigra Black Willow Livestakes 0 7.3 Salix nigra Black Willow Livestakes 0 7.8 Salix nigra Black Willow Livestakes 0 8.4 Salix nigra Black Willow Livestakes 3 6.6 Fraxinus pennsylvanica Green Ash 9.3 7.6 Quercus palustris Pin Oak MY2 Project: Forrest Creek Date: 9/1/2009 Name: VQT6 Size: 10m x 10m stems = 15 plot size (m"2) = 100 stems/acre = 607 Cover: cokleburr, dog fennel, narrow leaved sunflower = 100% x (m) y (m) Scientific Name Common Name 8.6 2.9 Quercus palustris Pin Oak 5.6 2.1 Fraxinus pennsylvanica Green Ash 3 1.9 Fraxinus pennsylvanica Green Ash 0.4 2.7 Juglans nigra Black Walnut 4.5 4.5 Quercus palustris Pin Oak 0 5.4 Salix nigra Black Willow 0 6 Salix nigra Black Willow 0 6.7 Salix nigra Black Willow 0 7.3 Salix nigra Black Willow 0 7.8 Salix nigra Black Willow 0 8.4 Salix nigra Black Willow 3 6.6 Fraxinus pennsylvanica Green Ash 9.3 7.6 Quercus palustris Pin Oak 1.9 9.5 Quercus palustris Pin Oak 5.1 7 Quercus palustris Pin Oak Condition Comments Livestakes Livestakes Livestakes Livestakes Livestakes Livestakes not previously counted VQT6 10 9 8 7 6 5 4 3 2 1 0 Pin Oak Black Willow Black Willow Pin Oak Black Willow I Pin Oak Black Willow Green Ash Black Willow Black Willow Pin Oak Pin Oak Black Walnut Green Ash Green Ash 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Baseline Project: Forrest Creek stems = 12 Date: 6/1/2008 plot size (m"2) = 100 Name: VQT7 stems/acre = 486 Size: 10m x 10m Cover: 95% Solidego sp x (m) y (m) Scientific Name Common Name Condition 1.1 0.7 Cornus amomum Silky Dogwood 6.8 1 Juglans nigra Black Walnut 8.3 3.5 Quercus sp. Oak sp. 5.1 3.2 Cornus amomum Silky Dogwood 0 3.2 Quercus sp. Oak sp. 9.8 6.1 Juglans nigra Black Walnut 5.4 6.2 Cornus amomum Silky Dogwood 0.9 6.4 Juglans nigra Black Walnut 0 7 Salix nigra Black Willow 2.7 8.7 Quercus sp. Oak sp. 8 7.5 Juglans nigra Black Walnut 0.1 9.3 Quercus sp. Oak sp. Comments ddh (mm) Height (cm) dbh = 0.5 cm 21 155 7 41 3 27 dbh = 0.6 cm 26 175 4 36 7 42 9 132 5 47 30 32 3 32 5 62 3 26 MY1 Project: Forrest Creek Date: 12/4/2008 Name: VQT7 Size: 10m x 10m Cover: 95% Solidego sp X (M) Y (M) 1.1 0.7 6.8 1 5.1 3.2 0 3.2 5.4 6.2 0.9 6.4 0 7 2.7 8.7 8 7.5 0.1 9.3 MY2 Scientific Name Cornus amomum Juglans nigra Cornus amomum Quercus palustris Cornus amomum Juglans nigra Salix nigra Quercus palustris Juglans nigra Quercus palustris stems = plot size (m"2) _ stems/acre = Common Name Silky Dogwood Black Walnut Silky Dogwood Pin Oak Silky Dogwood Black Walnut Black Willow Pin Oak Black Walnut Pin Oak 10 100 405 Condition Comments Project: Forrest Creek Date: 9/1/2009 Name: VQT7 Size: 10m x 10m Cover: dog fennel, soft rush = 100% X (M) Y (M) Scientific Name 1.1 0.7 Cornus amomum 5.1 3.2 Cornus amomum 5.4 6.2 Cornus amomum 3.4 8.7 Salix nigra stems = 3 (w/ vols.) stems = 4 plot size (m"2) = 100 plot size (m"2) = 100 stems/acre = 121 stems/acre = 162 Common Name Silky Dogwood Silky Dogwood Silky Dogwood Black Willow Condition Comments vol. VQT7 10 9 8 71 6 5 4 I 3 2 1 0 ¦ ¦ Black Willow Vol. ¦ ¦ Silky Dogwood ¦ Silky Dogwood ¦ Silky Dogwood 0 1 2 3 4 5 6 7 8 9 10 X (m) ¦ Baseline ¦ MY1 MY2 Exhibit Table VII: Stems per Acre by Plot and Year Replant - Baseline MY1 Year 2 MY2 W/ Vol. Vegplot Stems/acre Stems/acre Stems/acre Stems/acre Stems/acre VQ1 283 202 324 445* 688 VQ2 364 243 486 445 - VQ3 486 364 364 364 - VQ4 486 364 364 324 364 VQ5 364 202 445 405 647 VQ6 324 81 647 688 850 VQ7 405 81 607 607 - Average stems/acre = (Main Channel) 387 220 462 468 566 Vegplot Stems/acre Stems/acre Stems/acre Stems/acre Stems/acre VQT1 647 283 688 647 728 VQT2 688 607 607 283 - VQT3 647 486 486 324 - VQT4 526 445 445 202 - VQT5 486 324 324 324 - VQT6 607 526 526 607 - VQT7 486 405 405 121 162 Average stems/acre = (Tributary) 584 439 497 358 376 Average stems/acre = (Total) 486 330 480 413 471 * replaced 4 sweet gum trees with transplants stems = 146 (w/ vols.) stems = 165 plot size (m"2) = 1400 plot size (m"2) = 1400 stems/acre = 422 stems/acre = 477 XS 1 stream left s b x t t I {{ 7 Y, I Ikk i"N ?t F J •. 5! ?A 9 ? r '.? @p'F k b a S ?? ??8 s Ls f` r f ', ?' n tt ° k XS 1 stream right i![{r? rte. Q ¢ - D ? •F !? r1? i f I ra s' F -et ?" b I t XS 1 upstream XS 1 downstream ( w < r is a s x:.; y' ?C, f Y t Fs t f:: ?' r'` ? ? ' 3f AA:" ?F ryl ? SI 'd ?J YI I(R fry tl Z ,?, ,.3?`,?,??.£?s.??.kv c-u..-k`Y.{,A.'???`?.'.s .tir,.? rl?r(h?Y$.t. "?„r? ,..,,.,. t?:• XS2 downstream qw,r { ??? a 1 S Y y i : ' 4 '? a f sr i:' W t a ,. ? ? Ir 4 7a 'd M- i 1 , N V ??It x ' 1' ?' g e vF ! y # r 4o- t r 1} r 3G fn?K j tMa. 6 ''?•'., ? ? •:.f' r _:, ..??; ? ? .? l.rlR^_u3. v? ;•?., .t .<.? • Ira,s{9Y?rlu" ?,'se;i,a ?1 `??'.r XS2 stream right M _ r3. s .fir _ v ??ti l? 1 k XS2 stream left t ti? G ? • L ?. q ?F F a `? `? 0. r ,t C J v4i 1 ti a XS2 upstream p, I .. it ;? ?F 3 ? ?iwp?r x M L ? 21 y? rr a XS3 downstream . ?' i'y!'. ( f k 1•' i ? - r I + fit' , + y ! { Pf o I ? f ? I f ,ll?, ' ? kn'!!°-a ??••,F?,?•-.?'c ¢M:+ H ? Y ?-^? wfy r, h ? ?'s>???Ca.§ ? .... y,s.5? ?'Sti:i, ; } r..3 `S-cam' } x ern ` 3 #? $3 Y " ?i5 = I q ':!YY° Ylk?4?ay tt% ,. m(a1-zA?i?:^1e,i?ltrn kl..' S?, ?n ..,- ?,Ma ?'?J?'T•. .e S!fc.? XS3 stream right 71, ?' i & zfi fe ? « a'•. r - m2 Off , y ?, '? ( §.`? _ ? ? f rse? y ?sy? t ' ? a r' r "! j ,Fr4 u t^ F k r A 12 ? : ? I{. t a r i i I t ri 8.?1 R 9 . f ?? I f - it rJ1Y - ?/9/ i ?( - 44 al ? "Y` ? X51 ???• ?1 ?=5 f Y b_' x) ti'tf, ,? T4 AY rv? M 4`? . r , a.. ;? ` ?'w+ ,+,??`,. ?e ? • 'v..tn ' XS3 stream left !,, ?'? S rj 4 ?1lEZrf .'iprr-? 1... rl -.^' '? "s.r '^ .'• " ?4 III :. I -- ,? ! .t r.{ x a i;.srf Ci?7cp r a "Ap + ' c+ J l J ? ? E.a Ar,?? 1 c r XS3 upstream rays a #Ykd:. Ak z s XS4 downstream r " t t'+ rt iH +. ? ?S+-p 7 T b ? ! ? ? ? _ r? ?? .? fi T? V -• p 1 h'K+Ki J'?1?}? iN 1'? !` ?'y ? }1 ? alpd p V C 7-? x ?'fk ?rT. ,1 9d`:?dr FJ7 B ,ri i ?.' 3i y .' .... Y; .ru } -? wd .,:w1 k f y 'i 4,R i t r.' k 7 .. xr "7?? ?'"' ? • .d'?`°b"srP '?`??"????? e?,ry?2 r( ? '??. ` k ;I'F ? i , 1 . + tar' j ?9 y } a b l fi , ? " tom' +iArz? ?} ? r' ff??? ?• ?8a- ¢ f a ?yj /,i ?. _ a Y L F 4 ?,a __h r , XS4 stream right XS4 stream left h ? ,Wi3f_ ? r yyyy •d' Y 3 F ., 'k ?b r?? r 1 q 4 cwt ? iw- V 1 t. ,i k 5? s'. XS4 upstream .P 1 A l , f ya .? Y?? ?r `lt Sim. a 5 ?? ?? ? ,•? _ ?.. y. F. XS5 downstream ? n ???? i??e Li:???? 31 °1?r? ?,? +C.:• ? ?$ ?ae?r `.? t? ?`w ?:w'1': ,I l ZI, Y F9 -M eu ? ?+• ? P f` I elr . °^??''t? ?? do ? ?vj, ?yyl Pt$@?, XS5 stream right t a f "' I ? at 1 v a e A6 1 d ' ? ?+' i . ?P' r' ?!. 1?? ? q a Ier r= n,g ? lf? ft?.,Y`:J: t XS5 stream left s ! affrt$ ky?i4r41G 1'} pry rr k?k? ?i 'Ar Ik- XS5 upstream aw 4? y,w 3 fir- XS6 downstream XS6 stream left 14 y - 6 4 L.i;d,1.t .. n XS6 stream right XS6 upstream f N, T? ..n R? Ft 4 p ;i '?F' -y1!r`tr s? r ?*? t sa 1 al J Y N, v4, ` °.. a ? s tq? pSS 3? ye & A:,° ?, a zd:; PLr ? ? r s "j" h., 's c s .,, !fit. .., ?.da' i j T 4 }'?, 1. >rs_ "?• XSTI downstream r S I I F, ?Y t 4 ?16 z'! i €S t :/ F ! L Y.F"e 'a 4 a +Y.. 1 4 r% -. St?3f + !a ?„ s AF" r. s 4. ?i ` s w?L jj' +? 4 -.r '°?' : .,"" h+a7r ? r'r-4 J s i+t f .• ?y i•.. •6 .?, i XSTI stream right a Wi off S '? ! 15 K ?'?i.# YS1 ?Y } ? r? (6L? ? 5 k ??9i/? d l ? f t .46 # . r s ? .• t? d s I .: 1M rir t i 'v? x? a{ Y 3 '1 ! d 1'? ! F i 1f? t.? ! '? .t 1 t f.: R Fi r 4.°? ; § fi k ;j r es' t' f k 01 ?? t .jig-` aa, ,a ,f ,r n iL f r II Tf''P 7 ?4r: I'Y k ' a ? is S.•'?..? /?^`'?b? l ?i ? ?? .k:J ? Af?..?Ta ? ,i r????? _,,. ? '? ' f S?'yF Rf XSTI stream left 1 , h ? ; XSTI upstream F 1 IA +?}b t? ? - b 'h M? •.jl ? ?'µ?? a xW r r a 7 dE 4s, Cap "? * _x ?, ?T ;` XST2 downstream -?? a ? _ p v, de ,. ? a of dr•. as _ ? ? ji 4. i r3 l ? ? f ! =F pp '. y { s F f i ? .t t ,. I f l ' t le, { ,'7I1 ?? f x'.12 ;.; ??^^ ! qq ` v? F-? A ? Ph; v C as °: k X 4 as j l p 4 p ; a XST2 stream right M Yr u ?, ?' 1 ? •??1,y?MkStM1 ? ?t ?IY S }?i1??? "i, ? !1 ???' ?"' ? (` q ?. h, Q ? l? t 1 ? ? y ? v I 4? r ? y? jr wk :ai:4 y? ; t '`k`Cr' ? ?(r '.? 1•?.. §,t *?M $^t z'Y ?rh?d 'q, , t ? tY? ?3.r = ? a? a 4.. XST2 stream left P- *1 r? q ? ? h t t ?' ? 11 ? ?i4i }S R ! ? r n ? f [ 1FL" Y - ] { '? A y . j t £ ? w? .., 1 •i ??: r3 !fir ?, ?. 1 w qqr ;i A71 . # :sb, >3C. .9ti'_'{Yl4eF T!a, r,t ?'st ?p.fln rs. 1'et:: . . "` ?T ,'yte:F? XST2 upstream ?F. ? 6t? z' li f. r . ?! i? - 13rwt Y fhb f? ?1?4??i` IS. .yi „• rl S I?A /' -1. ? E ! 1 . XST3 downstream 11,16 ,. "Y z ? F r rsR f 'Y\ + j{4"? k`? ?. ',i`3 kip. 1s . ? ?. ! Iii 1 r 3 0 k ' tr, f XST3 stream right XST3 stream left XST3 upstream XST4 downstream e l ! ' 3iy 3 M.L 7 4 ?+' b i • ,? yr ? e ?, e??7t I „5 _ ?' 3 -: F F . F.'.. 7# 1 s. 7 A x 7 gti' f i S j?. z z XST4 stream right N G • ?t L' • : ? a y , 1 1 #YC*.' .k, ' I ? P t ?.1 b r l( i` y, `1 ,.Y r n 1N d i? > A LS s, ? N a x t .? ? r f \ r S`I .} ? ? M*PA A}r s { el'' XST4 stream left XST4 upstream XST5 stream right XST5 upstream XST5 downstream XST5 stream left 711 d f ?',• A ? T V / -N .7 ??y5y?iRt 8 XST6 stream left f f a?f_ I ?v r /+ ed ?`?ed?"? ( . Ell? ( , $ s L;^ tea, r. ct r all. 'fix .4? ?Sr 4 ?T i k"y '. r < r i / ? 1? ,ff Y } XST6 stream right XST6 upstream XST6 downstream XSR1 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 591.08 591.05 13.09 590.35 590.60 17.41 589.73 589.75 29.50 BKF 589.34 589.10 35.70 588.53 588.29 43.60 586.38 586.30 45.80 586.19 586.10 48.74 TW' 585.89 585.98 52.24 TWZ 586.25 585.73 62.27 589.16 588.90 78.47 BKF 588.85 589.06 88.59 590.12 590.15 103.41 BM 590.21 590.28 XSR2 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 592.06 592.10 13.24 591.71 591.60 34.89 590.70 590.50 42.91 BKF 589.96 590.00 49.50 587.64 587.80 50.83 587.43 587.50 56.08 587.44 587.50 61.03 TW 587.36 587.40 62.18 587.56 587.60 69.14 BKF 590.09 589.90 77.97 590.13 590.70 90.05 591.67 591.40 115.70 BM 591.80 591.90 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 48.97 48.97 Dbkf 3.45 3.37 Abkf 132.62 129.55 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 26.23 26.23 Dbkf 2.60 2.60 Abkf 53.54 53.54 592.00 591 00 XSP1 . 590 00 . 589.00 588 00 . 587 00 ° . 586 00 - . 585 00 . 584 00 . 583 00 . 582 00 . 0.0 13.1 17.4 29.5 35.7 43.6 45.8 48.7 52.2 62.3 78.5 88.6 103.4 +2008 X2009 593.00 592 00 XSR2 . 591 00 . 590 00 . 589 00 . 588 00 . 587 00 . 586 00 . 585 00 . 584 00 . 583 00 . 0.0 13.2 34.9 42.9 49.5 50.8 56.1 61.0 62.2 69.1 78.0 90.1 115.7 + 2008 X2009 XSP3 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 592.56 592.60 26.22 BKF 591.69 591.80 40.88 590.83 590.80 52.18 589.36 589.50 61.56 TW 588.14 588.20 67.76 589.26 589.30 75.16 BKF 591.94 591.80 106.73 BM 592.65 592.70 XSR4 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 595.92 595.80 6.31 595.64 595.70 13.34 594.67 594.80 24.61 BKF 594.57 594.30 31.17 592.74 592.90 32.66 592.58 592.80 34.64 592.50 592.70 42.92 TW' 592.21 592.70 45.39 TWZ 592.59 592.60 46.13 592.67 592.70 53.15 BKF 594.23 594.30 64.31 594.94 595.00 74.00 594.87 595.00 76.95 595.53 595.30 91.94 BM 595.55 595.60 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 48.94 48.94 Dbkf 3.55 3.60 Abkf 136.38 138.30 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 28.54 28.54 Dbkf 2.36 1.70 Abkf 52.87 38.09 594.00 593 00 XSP3 . 592 00 . 591 00 . 590 00 . 589 00 . 588 00 . 587 00 . 586 00 . 585 00 . 584 00 . 0.0 26.2 40.9 52.2 61.6 67.8 75.2 106.7 + 2008 X2009 597.00 596 00 XSR4 . 595.00 - r 594 00 . 593 00 . 592 00 . 591 00 . 590 00 . 589 00 . 588 00 . 587 00 . 0.0 6.3 13.3 24.6 31.2 32.7 34.6 42.9 45.4 46.1 53.2 64.3 74.0 77.0 91.9 ? + 2008 X2009 XSP5 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 598.01 598.10 14.50 597.01 597.10 23.06 595.58 595.90 31.85 595.43 595.20 31.96 BKF 595.39 595.20 43.68 593.70 594.20 45.54 592.96 593.30 50.72 591.72 592.20 50.74 592.10 592.20 52.77 TW 592.02 592.20 54.96 592.57 592.90 56.07 593.90 594.10 62.41 BKF 596.14 596.20 88.18 596.59 596.60 95.75 597.31 597.10 99.32 597.77 597.20 106.66 BM 597.60 597.70 XSR6 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 598.74 598.90 2.85 598.41 598.40 7.10 BKF 597.60 597.90 19.52 597.47 597.50 24.91 595.71 596.00 31.42 TW 595.57 595.78 36.94 595.67 596.04 45.45 BKF 598.10 597.94 73.93 BM 598.89 599.07 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 30.45 30.45 Dbkf 3.37 3.00 Abkf 80.55 71.71 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 38.35 38.35 Dbkf 2.03 2.12 Abkf 61.11 63.82 XSP5 599.00 598 00 . 597 00 . 596 00 . 595 00 . 594 00 . 593 00 - . 592 00 . 591 00 . 590 00 . 589 00 . 00 1?1h o^ ^* ?o 01 ?h o1 01 ti? ?o ?^ Roti ?w o? 0A ti o o rx a ? o o o +2008 X2009 600.00 599 00 XSR6 . 598 00 . 597 00 . 596.00 595 00 . 594 00 . 593 00 . 592 00 . 591 00 . 590 00 . 0.0 2.9 7.1 19.5 24.9 31.4 36.9 45.5 73.9 + 2008 X2009 XSRT 1 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 619.82 619.60 0.00 619.73 619.60 9.63 619.52 619.40 14.46 BKF 619.56 619.40 18.44 618.71 618.50 20.17 TW 618.65 618.50 23.05 619.07 618.74 26.48 BKF 619.69 619.41 40.54 619.88 619.80 53.14 620.28 620.23 53.14 BM 620.43 620.23 XSPT2 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 619.63 619.63 0.00 619.49 619.40 9.86 619.51 619.23 33.21 618.88 618.55 33.47 618.81 618.54 35.84 BKF 618.76 618.40 42.36 617.71 617.56 44.87 TW 617.32 617.26 44.91 617.34 617.28 46.72 617.74 617.65 46.80 617.78 617.57 50.14 BKF 618.80 618.78 50.25 618.85 618.80 61.17 618.98 618.89 72.34 620.06 619.84 72.34 BM 620.07 619.84 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 12.02 12.02 Dbkf 0.91 0.90 Abkf 8.59 8.49 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 14.30 14.30 Dbkf 1.44 1.14 Abkf 16.16 12.80 621.00 620 00 XSRT1 . 619 00 . 618 00 . 617 00 . 616 00 . 615 00 . 614 00 . 613 00 . 612 00 . 611 00 . 0.0 0.0 9.6 14.5 18.4 20.2 23.1 26.5 40.5 53.1 53.1 + 2008 X2009 621.00 620 00 XSPT2 ' . 619 00 / ------ . 618 00 . 617 00 . 616 00 . 615 00 . 614 00 . 613 00 . 612 00 . 611 00 . 0.0 0.0 9.9 33.2 33.5 35.8 42.4 44.9 44.9 46.7 46.8 50.1 50.3 61.2 72.3 72.3 +2008 X2009 XSRT3 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 609.93 609.95 8.97 BKF 609.51 609.50 14.42 609.48 609.38 16.15 608.90 609.00 17.16 TW 608.58 608.69 18.49 608.92 608.95 22.39 BKF 609.66 609.65 29.60 609.38 609.45 37.90 BM 610.10-1 -610.11 XSPT4 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 608.76 608.80 3.45 607.30 607.86 15.04 606.59 606.72 20.54 606.18 606.06 22.91 BKF 605.42 605.57 25.68 TW 604.24 604.03 32.76 BKF 605.43 605.55 39.73 605.61 605.45 40.38 605.34 605.45 46.80 605.44 605.58 52.36 605.50 605.75 62.62 606.02 606.19 66.65 606.22 606.42 73.54 BM 606.78 606.78 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 13.42 13.42 Dbkf 0.93 0.81 Abkf 9.80 8.53 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 9.85 9.85 Dbkf 1.18 1.54 Abkf 9.12 11.91 611.00 610 00 XSRT3 . 609 00 . 608 00 . 607 00 . 606 00 . 605 00 . 604 00 . 603 00 . 602 00 . 601 00 . 0.0 9.0 14.4 16.2 17.2 18.5 22.4 29.6 37.9 + 2008 f 2009 610.00 609 00 XSPT4 . 608 00 . 607 00 . 606 00 . 605 00 . 604 00 . 603 00 . 602 00 . 601 00 . 600 00 . 0.0 3.5 15.0 20.5 22.9 25.7 32.8 39.7 40.4 46.8 52.4 62.6 66.7 73.5 + 2008 X2009 XSRT5 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 602.21 602.20 0.86 601.56 601.89 11.30 601.64 601.85 20.76 BKF 601.79 601.85 24.15 600.65 601.36 25.81 TW 600.53 600.92 27.67 600.87 601.25 31.88 BKF 601.70 601.68 47.49 601.84 601.84 60.60 601.24 601.40 74.71 601.87 602.50 74.93 BM 602.52 602.50 XSRT6 Survey Data Station Notes Year 1 Year 2 Year 3 Year 4 Year 5 0.00 BM 595.81 595.97 0.09 595.33 595.96 14.85 595.57 595.62 22.22 BKF 595.57 595.50 25.92 594.60 594.70 27.91 TW 594.41 594.30 29.88 594.65 594.87 34.31 BKF 595.77 595.55 40.31 595.68 595.90 53.93 595.68 595.89 53.93 BM 596.22 596.30 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 11.12 11.12 Dbkf 1.26 0.93 Abkf 11.00 8.12 Year 1 Year 2 Year 3 Year 4 Year 5 Wbkf 12.09 12.09 Dbkf 1.16 1.20 Abkf 11.01 11.39 603.00 602 00 - XSRT5 . - 601.00 600 00 . 599 00 . 598 00 . 597 00 . 596 00 . 595 00 . 594 00 . 593 00 . 0.0 0.9 11.3 20.8 24.2 25.8 27.7 31.9 47.5 60.6 74.7 74.9 +2008 X2009 597.00 596 00 XSRT6 . 595 00 . 594 00 - . 593 00 . 592 00 . 591 00 . 590 00 . 589 00 . 588 00 . 587 00 . 0.0 0.1 14.9 22.2 25.9 27.9 29.9 34.3 40.3 53.9 53.9 + 2008 X2009 LP 1 622 621 620 619 618 617 616 I 15 65 115 165 215 265 315 365 415 465 -*- 2008 f 2009 B KF LP2 611 r 610 609 608 1 k ? 607 606 605 604 ' d 603 1050 1150 1250 1350 1450 1550 1650 1750 2008 2009 B KF LP3 597 596 5 . 596 595 5 . 595 594.5 -IN 594 593 5 . 593 592 5 . 2650 2700 2750 2800 2850 2900 2950 --0-2008 --m-2009 B KF LN 596 595 594 593 592 II 591 ? >i 590 - 589 588 600 800 1000 1200 1400 1600 1800 2008 f 2009 B KF LP5 591 590 589 588 587 q R 586 585 584 350 450 550 650 750 850 950 1050 1150 2008 --m- 2009 B KF XS4 Particle Size 2008 2009 2010 2011 2012 0.062 16 17 0.13 0.25 0.5 1 2 4 6 10 8 10 11 3 16 4 4 22 7 7 32 13 8 45 15 10 64 15 14 90 19 12 128 8 5 180 5 256 1 362 512 1024 2048 4096 20 18 16 14 12 10 8 6 4 2 0 ooort, ono ooh N tK o w NN No ti? oti ?h o°` oo New N?o ??o Doti ?op eo ? 2008 ¦ 2009 XS2 Particle Size 2008 2009 2010 2011 2012 0.062 10 25 0.13 0.25 0.5 1 2 4 6 3 11 8 7 5 11 4 9 16 10 8 22 10 10 32 3 4 45 15 5 64 12 6 90 13 10 128 10 6 180 2 256 2 362 512 1024 2048 4096 30 1 25 20 15 10 5 0 ooo? ono ooh o``' N o w NN Nb o°` oo Np Np rho oon, 4 ?N lvp Op ? 2008 ¦ 2009 XST1 Particle Size 2008 2009 2010 2011 2012 0.062 1 20 0.13 3 0.25 2 0.5 1 2 2 4 2 1 6 3 3 8 13 8 11 19 10 16 22 9 22 18 16 32 12 12 45 5 4 64 6 3 90 2 6 128 1 180 256 362 512 1024 2048 4096 25 20 15 10 5 0 o o ooti no ooh Ip N ti IK o o NN No ti? oti ?h o? :P Np Noo ?ooo ? 2008 ¦ 2009 XST3 Particle Size 2008 2009 2010 2011 2012 0.062 36 63 0.13 0.25 0.5 1 2 4 2 1 6 3 5 8 1 3 11 3 6 16 4 3 22 4 5 32 12 2 45 13 4 64 14 3 90 11 5 128 180 256 362 512 1024 2048 4096 70 60 50 40 30 20 10 0 ?? oh Oh N `L NN Nb bp, co N?) "'b", b ooo?l.O O ? 2008 ¦ 2009 XST6 Particle Size 2008 2009 2010 2011 2012 0.062 40 53 0.13 0.25 0.5 1 2 4 2 6 3 2 8 1 11 4 3 16 6 2 22 4 5 32 8 6 45 16 11 64 18 12 90 15 5 128 1 180 256 362 512 1024 2048 4096 60 50 40 30 20 10 0 oooti oN ooh N o o NN No ti? oti ?h o°` oo NI) Noo ??o Doti AV?o ?ooo ? 2008 ¦ 2009 reruiaueut ruutu ruuit i,u • ' i „? ?,.. ark ? t - > -???? ?..;:??:? r. f •$P 1 y ,# ?yJ??+. ,-.. s?.?•?* ;? ACV. -?.'?' ???`' d '7 .'?:. ???g^,.. 5Z°? Y- r?§ N. ? ? • . ? '. I ,!- °.. l?, I Iril'1?. _/} f 0. 'Sp tv`p.° `• ?.r`?J' . • . ? ? ?p ?.O'' ? a'yK? Wit` l'Sd i( '?{ • ? 4 n t kg?? t e: } u z t'+I,? P .r yak'- YL,?.: 15, 4 Photo Point 1 - Looking downstream from cattle crossing upstream of Edmund Latta Road (STA 200+00). Photo Point 2 - Looking upstream from Edmund Latta Road bridge (STA 203+75). a ?, ?. y} y .l f . z 4 V A' a ?,a i -a e P• ?, r p ? s5ak Cqp } f:? 4 +}x F r? y, pr ? s ,M [ tic y?-r J44 { ?° {?.?r •x1,'e' a,lx2°' JJa?i,, r f . ' +• ' "Yad "+t1FC .:: r'` y f yT..y'ty. [Yi- g,, ?1 ybyf pv 44 X '. iiff y{y'. rt J %y6 +\ a r7 ?1?0.'r A [j?.?.ifeL?§;f 44 rF Yd i Photo Point 3 - Looking upstream from cattle crossing below the confluence of FC and UT (STA 223+00). IE y d g r e S r {_yFl t yy y .. J ?v t x, ', r f t ?# %q y A' f?, T?f ?,?,;•? yl +? ,'r a F,,d ti"^ F r. ? ? rt s ?? p i q'"r ? A.aT 5?? 4? x, ? ?. - ?...-•"y? 41?j K"?• ?i?.F?,'-??'* ?'. F! sJ? F{':? ?t?l?[-" "?" r 1+. ,r, a ? ?Sa k t?N ?i?tR?L yn :.'` ? ?+ 4d1 rt.?[t?ai { 'r[ } ?. ?ea ? ?'}t t - >< a [? ? r?Y'i "•'}, ! } r '? ry!;•? r s J ? '? sa x dish"i y; ?:: Photo Point 4 - Looking downstream from cattle crossing below the confluence of FC and UT (STA 223+00). r R R+FT i ? ! ??:. l ?. + oaf a ar 4 ? s'.k j? ? max ??b 5a +1? ?x V6S _ x. 4+a M4, 1 rR S€' ?i h}h f V Y +? Y Sr ? 4 ¢? t A 31 41 a ; = -tr r} * 4 ?i. r'. eu ? r X I' i iv a •,ara Photo Point 5 - Looking upstream from London Lane (STA 232+00). Photo Point 6 - Looking upstream (UT) from the cattle crossing above the confluence (STA 126+50). Y`-..` V ! j `?' +[ ?,- 3 n tr1C ^'g'T tS 9ti "?„.' r _ ? ? ? hti rte- ? ? -. ? y ? C???:: ,.?' A Y S fir- i k •, i r ? ? : / F ? x Aas - ' v lii f4.?r? Photo Point 7 - Looking downstream (UT) from cattle crossing above Edmund Latta Road (STA 106+25). Photo Point 8 - Looking upstream (UT) from cattle crossing above Edmund Latta Road (STA 106+25). f !.•y?s ,F ? ?'#' '44?.. ?, by ?`' ,"? 1 i (? t _'v ? f r } •? ; f, ? I ??: q ?.. ? ?tt',y ti?r. I+, r # •"£1*i I cif r?f ?1 ? la J.?? aF• f ?? •. c?''fA ? J. (? y r'N .: rr. ? r ' ?a ,,: rd t y1?'?YP f? ! K'.'y''?i ??f . e•. r? `1F: f '? hr ;? t ?? iI u ..! ,. •? f ,, ? a ` ? ?,?+°'° r r 7 i ?r ? F f r ?.5 ? ? : ? t a t ,` ? Gr- 4 ,?}, ^y? ?i '? ? ? ; }? r`} c `Y a- ? ? R ?y r gv 734? f.:J fr'F?f'S,.P +! s , 1 4 X, t a? t 1T {r M1 lt' ?? yt a?'}wo yt 4ti ?$, a e, { :}*' ! a x, -j, ?.y ?$s r. riS?R ?? ,''t' a?4 i9"•??'?:? 3+ Y #-??i? ? ? '7'? y!*?r S y? C ff .y.} M 1 I[?'?I§'$' "J' .! =Se 'tq'?R ' " M ?5`{?.IiF,? .+s 7 •.' i?????,?F?, ? e,. .,?', .•.. .°'*"`+t•t ;1 ,r ...? »?, .: .?Mr..?7V.5:•?i??'.? '•? +?$?,.x.. ...a rh':v'" ,r:•'??.:. .ar`_?s i... `+ M 1. Vs.. ', y' Str Tow '.'}* tkagk ?t ?'+4't•]r - { Yr ' r r ! F i r. ., ? . J ' ? 9 .?. !• r?' T J 1? ! ?. ?1'' SFSV.2e nnL'- ?s '?ei' Via. A f4 Photo Point 9 - Looking downstream (UT) from Edmund Latta Road (STA 110+50). W? . S ? i r P a .u 1_..l Photo Point 10 - Looking upstream (UT) from Edmund Latta Road (STA 110+00). BANKFULL EVENT LOG Ti . 4 Event not documented in 2008 Monitoring Report. Event most likely took place November 30th and Dec 1st, onsite rain gage logged 1.25 inches. lI d 'l 79 0 i J .po •S .'?% ? . i .. I 14, Kvil-i y # ??'. - r 04 1 t P I?f?y fA! I! r ?, f'. r Art r f/1 P i f !? 7 Y l Several potential bankfull events took place in March 2009. 1.38 inches March 2nd and 3rd 2.31 inches March 14th through 17th 1.99 inches March 27th through 29th At the time of monitoring (9-1-09), both CSG's were water logged as shown above. The largest storm event s recorded between April 16th and September 1st were: May 6 - 8: 1.89 in. June 5 - 6: 2.39 in. July 6 and 7: 2.02 in It is typical for the CSG's to be more difficult to trigger in the summer months when vegetation is in full growth, the CSG's may have also malfunctioned due to debris or vegetation. User Name Data Acquired Next Measurement Serial Number User Message Batt. Installed Batt. Voltage Batt. Capacity Alarm Interval Readings per Day Measurements Amt. to Log: Memory Wrap Latitude Longitude ************ Date dd-mmm-yyyy ************ 8/30/2008 8/31/2008 9/1/2008 9/2/2008 9/3/2008 9/4/2008 9/5/2008 9/6/2008 9/7/2008 9/8/2008 9/9/2008 9/10/2008 9/11/2008 9/12/2008 9/13/2008 9/14/2008 9/15/2008 9/16/2008 9/17/2008 9/18/2008 9/19/2008 9/20/2008 9/21/2008 9/22/2008 9/23/2008 9/24/2008 9/25/2008 9/26/2008 9/27/2008 9/28/2008 9/29/2008 FCRG 01-Sep-2009 10:12:00 02-Sep-2009 00:00:00 N48660DD 31 character message 6/08 5.95 90 24 h r(s) 1 368 0 24-Apr-2020 00:00:00 29 59.999 N 81 59.999 W ********** Rainfall inches ********** 0 0 0.16 0 0 0 0 0.66 4.71 0 0 0.03 0.29 0.01 0 0 0 0 1.01 0 0 0.04 0.01 0 0 0 0.01 0.24 1.7 0.02 0.01 1.94 9/30/2008 0 10/l/2008 0.65 10/2/2008 0.08 10/3/2008 0 10/4/2008 0 10/5/2008 0 10/6/2008 0 10/7/2008 0.01 10/8/2008 0 10/9/2008 0.01 10/10/2008 0.03 10/11/2008 0.01 10/12/2008 0 10/13/2008 0 10/14/2008 0 10/15/2008 0.01 10/16/2008 0.01 10/17/2008 0 10/18/2008 0.4 10/19/2008 0.01 10/20/2008 0 10/21/2008 0 10/22/2008 0.01 10/23/2008 0 10/24/2008 0 10/25/2008 0 10/26/2008 0.18 10/27/2008 0.01 10/28/2008 0 10/29/2008 0 10/30/2008 0 10/31/2008 0.02 11/l/2008 0 11/2/2008 0 11/3/2008 0 11/4/2008 0.15 11/5/2008 0.63 11/6/2008 0 11/7/2008 0 11/8/2008 0 11/9/2008 0.01 11/10/2008 0 11/11/2008 0 11/12/2008 0.04 11/13/2008 0.01 11/14/2008 0.08 11/15/2008 0.72 11/16/2008 0.01 11/17/2008 0 11/18/2008 0 11/19/2008 0 11/20/2008 0 11/21/2008 0 11/22/2008 0.06 11/23/2008 0 11/24/2008 0 11/25/2008 0.26 11/26/2008 0.01 11/27/2008 0 11/28/2008 0 11/29/2008 0 11/30/2008 0.28 12/l/2008 0.97 12/2/2008 0 12/3/2008 0 12/4/2008 0.01 05-Dec-2008 0.03 06-Dec-2008 0 07-Dec-2008 0.05 08-Dec-2008 0 09-Dec-2008 0 10-Dec-2008 0.01 11-Dec-2008 0.02 12-Dec-2008 0 13-Dec-2008 0 14-Dec-2008 0 15-Dec-2008 0.01 16-Dec-2008 0 17-Dec-2008 0.01 18-Dec-2008 0 19-Dec-2008 0 20-Dec-2008 0 21-Dec-2008 0 22-Dec-2008 0 23-Dec-2008 0 24-Dec-2008 0 25-Dec-2008 0 26-Dec-2008 0.01 27-Dec-2008 0 28-Dec-2008 0.01 29-Dec-2008 0 30-Dec-2008 0 31-Dec-2008 0 01-Jan-2009 0 02-Jan-2009 0 03-Jan-2009 0.07 04-Jan-2009 0.01 05-Jan-2009 0.25 06-Jan-2009 0 07-Jan-2009 0.64 08-Jan-2009 0.39 09-Jan-2009 0.08 10-Jan-2009 0 11-Jan-2009 0 1.25 1.11 12-Jan-2009 0.01 13-Jan-2009 0 14-Jan-2009 0 15-Jan-2009 0 16-Jan-2009 0 17-Jan-2009 0 18-Jan-2009 0 19-Jan-2009 0 20-Jan-2009 0 21-Jan-2009 0.03 22-Jan-2009 0 23-Jan-2009 0 24-Jan-2009 0 25-Jan-2009 0 26-Jan-2009 0 27-Jan-2009 0 28-Jan-2009 0.27 29-Jan-2009 0.23 30-Jan-2009 0.14 31-Jan-2009 0.06 01-Feb-2009 0.01 02-Feb-2009 0 03-Feb-2009 0.14 04-Feb-2009 0.15 05-Feb-2009 0 06-Feb-2009 0 07-Feb-2009 0 08-Feb-2009 0 09-Feb-2009 0 10-Feb-2009 0 11-Feb-2009 0 12-Feb-2009 0 13-Feb-2009 0 14-Feb-2009 0 15-Feb-2009 0 16-Feb-2009 0 17-Feb-2009 0.06 18-Feb-2009 0.03 19-Feb-2009 0.57 20-Feb-2009 0 21-Feb-2009 0 22-Feb-2009 0 23-Feb-2009 0 24-Feb-2009 0 25-Feb-2009 0 26-Feb-2009 0 27-Feb-2009 0 28-Feb-2009 0.04 01-Mar-2009 0.87 02-Mar-2009 1.25 03-Mar-2009 0.13 04-Mar-2009 0.03 1.38 05-Mar-2009 0.03 06-Mar-2009 0 07-Mar-2009 0 08-Mar-2009 0 09-Mar-2009 0 10-Mar-2009 0 11-Mar-2009 0 12-Mar-2009 0 13-Mar-2009 0 14-Mar-2009 0.36 15-Mar-2009 0.78 16-Mar-2009 0.8 17-Mar-2009 0.37 18-Mar-2009 0 19-Mar-2009 0.01 20-Mar-2009 0.32 21-Mar-2009 0.01 22-Mar-2009 0 23-Mar-2009 0 24-Mar-2009 0 25-Mar-2009 0 26-Mar-2009 0.09 27-Mar-2009 0.41 28-Mar-2009 0.52 29-Mar-2009 1.06 30-Mar-2009 0 31-Mar-2009 0 01-Apr-2009 0 02-Apr-2009 0.04 03-Apr-2009 0.54 04-Apr-2009 0.46 05-Apr-2009 0 06-Apr-2009 0 07-Apr-2009 0.38 08-Apr-2009 0 09-Apr-2009 0 10-Apr-2009 0 11-Apr-2009 0.53 12-Apr-2009 0.01 13-Apr-2009 0 14-Apr-2009 0.04 15-Apr-2009 0.08 16-Apr-2009 0.07 17-Apr-2009 0 18-Apr-2009 0 19-Apr-2009 0 20-Apr-2009 0.01 21-Apr-2009 0.85 22-Apr-2009 0.08 23-Apr-2009 0 24-Apr-2009 0 25-Apr-2009 0 2.31 1.99 26-Apr-2009 0 27-Apr-2009 0 28-Apr-2009 0 29-Apr-2009 0 30-Apr-2009 0 01-May-2009 0 02-May-2009 0.05 03-May-2009 0 04-May-2009 0 05-May-2009 0.2 06-May-2009 0.69 07-May-2009 0.29 08-May-2009 0.91 09-May-2009 0 10-May-2009 0.16 11-May-2009 0 12-May-2009 0.23 13-May-2009 0.01 14-May-2009 0 15-May-2009 0.01 16-May-2009 0.08 17-May-2009 0 18-May-2009 0.18 19-May-2009 0.04 20-May-2009 0 21-May-2009 0.01 22-May-2009 0 23-May-2009 0 24-May-2009 0.29 25-May-2009 0.11 26-May-2009 0 27-May-2009 0.24 28-May-2009 0 29-May-2009 0.13 30-May-2009 0.07 31-May-2009 0 01-Jun-2009 0.04 02-Jun-2009 0 03-Jun-2009 0 04-Jun-2009 0 05-Jun-2009 1.08 06-Jun-2009 1.31 07-Jun-2009 0 08-Jun-2009 0.01 09-Jun-2009 0 10-Jun-2009 0.84 11-Jun-2009 0.03 12-Jun-2009 0.7 13-Jun-2009 0 14-Jun-2009 0 15-Jun-2009 0 16-Jun-2009 0.1 1.89 2.39 17-Jun-2009 0.28 18-Jun-2009 0.12 19-Jun-2009 0.04 20-Jun-2009 0 21-Jun-2009 0 22-Jun-2009 0 23-Jun-2009 0 24-Jun-2009 0.01 25-Jun-2009 0 26-Jun-2009 0 27-Jun-2009 0 28-Jun-2009 0 29-Jun-2009 0 30-Jun-2009 0 01-Jul-2009 0 02-Jul-2009 0 03-Jul-2009 0 04-Jul-2009 0 05-Jul-2009 0 06-Jul-2009 0.89 07-Jul-2009 1.13 08-Jul-2009 0.01 09-Jul-2009 0 10-Jul-2009 0 11-Jul-2009 0 12-Jul-2009 0.03 13-Jul-2009 0 14-Jul-2009 0.16 15-Jul-2009 0 16-Jul-2009 0 17-Jul-2009 0 18-Jul-2009 0.87 19-Jul-2009 0 20-Jul-2009 0 21-Jul-2009 0.11 22-Jul-2009 0.08 23-Jul-2009 0.34 24-Jul-2009 0 25-Jul-2009 0 26-Jul-2009 0 27-Jul-2009 0 28-Jul-2009 0 29-Jul-2009 0 30-Jul-2009 0.24 31-Jul-2009 0.31 01-Aug-2009 0.46 02-Aug-2009 0.01 03-Aug-2009 0.28 04-Aug-2009 0 05-Aug-2009 0 06-Aug-2009 0.72 07-Aug-2009 0 2.02 1.3 08-Aug-2009 0 09-Aug-2009 0 10-Aug-2009 0 11-Aug-2009 0 12-Aug-2009 0.65 13-Aug-2009 0.03 14-Aug-2009 0 15-Aug-2009 0 16-Aug-2009 0 17-Aug-2009 0 18-Aug-2009 0 19-Aug-2009 0 20-Aug-2009 0 21-Aug-2009 0.74 22-Aug-2009 0 23-Aug-2009 0.37 24-Aug-2009 0 25-Aug-2009 0 26-Aug-2009 0 27-Aug-2009 0 28-Aug-2009 0 29-Aug-2009 1.17 30-Aug-2009 0.02 31-Aug-2009 0.02 01-Sep-2009 0.12 Problem Area Before: t7 ? yy ! Y 7` `any ;'? ? + si E?' e? ' i i \ ?,\m .. .i.13 ? L ?' t .i J} y I F ? „? ?'. i4 k' M,• +._ Y _ k 7'"7 a . ?, r fe .,fir . ? ytY+ ? kY I'd yA .. P IwS4 EyrYYk '? tx bs. 4'a c?5. Jf4T.. r:. F"?7^?E•. q do f'?.lw,?..«.> A ty i} ? U. F + Yg9.K f?$ ?Sl'.t .ft? .ytl . '• +it?6'fY:. a, ? 4.gX•, § tijwwS{?r? .? ?{?d??? Tn? f Problem Area After: r pp t ??y,?? _, yY ??p?,Y?i, {'i V+V : Y Y Y•" V .. M1y ,x+4*i f,:'? S ? ? 4 f{ yl L4. [I Mo WKI, in, Oik }y '"'J{py .C I . ?? YS .?? 4 ??? L ? .?_ 13 ?? •',.1??i.?y?p??Y3 ;? h•ai ?' h1r t.?-. •?y?{ I?. '?:... i t `i'e f?"+,:? "?? ".• wC ?'..w S - d 'Y ?4 l { f, a f e1. I., j t ?. @f, r _+„ a ,r,. Mry ?,Sy, 3 bl„ ale a r,r "Nar.,L't _+! .?.;_ a r ? ,. _'i. , .1 i t ti .. ?+.?3 ?LM A•'i?:'tr{!?'i,d X 7:1§f. Y Jr LY "'?OT° t,EN i 7PT'TFUT"f'I7. , PLAIT . HOLY R I- [ON TNIBERAN] .,THIS. H'. K . ALC ALLEXIYN, PLS 1. SLl NOTE. EXISTING TOPOGRAPHICAL INFORMATION AND C'ONTTROL DATA INFORMATION TAKEN FROM SURVEY ENTITLED"LATTA-EARTH_MARKDATED JULY-DECEMBER, 200" BY ALOIS CALLEMYN, PLS. M=M LATOI A0. SIR T ALL NEWT DATA SHOGUN ON THIS SURVEY IS TIED TI-I NORTH CAROLINA STATE PLANTE COORDINATE SYST NAD 1983 M (HORIZONTAL) AND NA VD-29 (VERTIC 57 EXISTING CENTERLINE OF FORREST CREEK, UPSTREAM OF CONSTRUCTION B /IGG +D 00 ITOB -------------------- CONSTRUCTED N RIFFLE, TYP. + 0 O e CULMERTEO A CROSSING G QUAD 7 CONSTRUCTED RIFFLE, TYP. N07E A" ALL DISTANCES ARE HORIZONTAL GROUND, EXCEPT THOSE SHOWN AS GRID AND AREA BY COORDINATE COMPUTATION. NOTE $' EXCEPT AS SPECIFICALLY STATED OR SHOWN, THIS SURVEY DOES NOT REPORT ANY OF THE FOLLOWING, EASEMENTS, OTHER THAN THOSE VISIBLE DURING HELD EXAMINATION, BUILDING SETBACKS, RESTRICTIVE COVENANTS, ZONING OR LAND USE RECULATTONS AND ANY FACTS WHICH A SHE SEARCH MAY DISCLOSE. NOTE 'C' THE LOCATION OF UNDERGROUND URLRES ARE NOT SHOWN, LOCATION OF UNDERGROUND UULJOES AGO STRUCTURES MAY VARY FROM LOCARONS SHOWN HEREON, AND AWIRONAL BURIED VALUES MAY EXIST CONTACT RB APPROPRIATE URLTY COMPANIES FOR INFORMATION REGARDING BURIED URLITIEE r 2 J 5TA 206+83 TO / STA 218+13 f \ 2C16x ? ..-.-` ... TGB \ i a r \ \Li LIMINARY L Not for Recordation, Conveyance or Sales d Xtri HEW 1, ALOIS CALLEMYN, N.C.P.L.S.#2544, CERTIFY THAT THE N.C. GRID COORDINATES AND BEARINGS SHOWN ON THIS PLAT OR DOCUMENT WERE DETERMINED BY AN ACTUAL GIGS SURVEY PERFORMED BY ME. THAT THIS SURVEY WAS PERFORMED TO CLASS C FGCC SPECIFICATIONS AND THATI ROCK CROSS USED GPS-RTK SURVEY FIELD PROCEDURES COORDINATES WERE VANE, TYP. DETERMINED BY LEAST SQUARES ADJUSTMENT THAT THIS SURVEY WAS PERFORMED USING ONE (1) TOPCOAT GPS "VIPER" RECEIVER LOGGED INTO NOSS RTK NETWORK. ALL COORDINATES ARE BASED ON HAD 83(2007) AND ALL ELEVATIONS ARE BASED ON NAND 88. NOTE '0' THIS SURVEY WAS DONE WMOUT A THE SEARCH AND IS BASED ON REFERENCES INFORMAROV. THERE MAY EXIST OTHER DOCUMENTS OF RECORD AMICH COULD AFFECT MIS PROPERTY NOTE 'C WERANGS, JURWOCTCNAL WRITERS OR OTHER CONDITIONS WHICH MAY BE REGULATED BY FEDERAL OR STATE OR LOCAL AGENCIES WERE NOT INNESRGARD DURING GiIS SURVEY RIPARIAN SUFFERS AND OTHER RESTRICDONS ON DEVELOPMENT MAY BE REOU.WED. NOTE 'F' TOW ZONES OR BASE FLOW ELEVATORS HERE NOT INVESTING,= DURING THIS SURVEY. NOTE 'G° EXCEPT AS LABELED OTHERWISE, ALL CORNERS SHOWN AS SET ARE 0.625 INCH COPPER COATED WTON ROSS 'PK" NAILS ARE SET M ALL ASPHALT ROADS. moTTNStALL TYP. VANE, AS-BUILT BANKFULL, TYP. /-AS-BUILT 4 / CENTERLINE, TYP. B KEN QUAD ?a FFL 5 ,Vppx .LEW \ ?? r LTOB ""'11 x0 / B ?W // a8 HEtiN ',a ` ' e a 05 L HEW ./ G QUA aax \ LTC' X00 4E4W A Pe GB 6 00 L e. 00 Jr, REW LE ??(? Q? ?._ ame.`4 e Ftt0. \ ^. / REw L7oBBww "'?Q7° t,EM1! i 7PT'I?FU?"f'I7. , °LA'L . [7 ''1 us 5? - ZIGINAL -LLKE R L'i- H: J E,: " . A. --. - LICBNSHN0.. L -544 \ QUAD s Y \ 4 ag Y? TRIBUTARY l 94\ PRELIMINARY Not for Recordation, Conveyance or Sales NOTE: EXISTING TOPOGRAPHICAL INFORMATION AND CONTROL DATA INFORMATION TAKEN FROM SURVEY ENTITLED"LATTA-EARTHMARKDATED JULY-DECEMBER, 2007 BY ALOIS CALLEMYN, PLS. ALL NERD DATA SHOGUN ON THIS SURVEY IS TIED D-1 NORTH CAROLINA STATE PLANE COORDINATE SYSTEM, NAD 1981-2007 (HORIZONTAL: AND NAVD-29 (VERTIC m m a r r r 226+00 > VfG QUA 3 REW 6 "' r hk s? CULVERTED AGRICULTURAL CROSSING "'?C)I° t,F.N i 7NT'I-FN"f'I7 , nLA1 [7 ''' Rs 51 - 21GINAL -PLRE R L'i- H: J E,: " . A. --. - LICBNSHN0.. L -544 hk s? NOTE: EXISTING TOPOGRAPHICAL INFORMATION AND CONTROL DATA INFORMATION TAKEN FROM SURVEY ENTITLED"LATTA-EARTHMARKDATED JULY-DECEMBER, 2007 BY ALOIS CALLEMYN, PLS. ALL NEW DATA SHOGUN ON THIS SURVEY IS TIED D-1 NORTH CAROLINA STATE PLANE COORDINATE SYSTEM, NAD 1981-2007 (HORIZONTAL: AND NAVD-29 (VERTIC BOULDER WALL (VEGETATED) BEGIN LONGITUDINAL PROFILE 5 STA 224+41 TO STA 231+40 r r r l a?P PRELLV___-4-A1KY PLAT Not for Recordation, Conveyance or Sales NN! _. .BFI L..cI 51 - UGINALSIC_ -.1`Rr- 1 , TH_ i 1[ A. --. LICBNSHNO. L -544 E NOTE. EXISTING TOPOGRAPHICAL INFORMATION AND CONTROL DATA INFORMATION TAKEN FROM SURVEY ENTITLED"LATTA-EARTHMARKDATED JULY-DECEMBER, 2007 BY ALOIS CALLEMYN, PLS. ALL NEW' DATA SHOGUN ON THIS SURVEY IS TIED D-1 NORTH CAROLINA STATE PLANE COORDINATE SYST NAD 1983 ,M (HORIZONYAL) AND NA VD-29 (VERTIC 1, ALOIS CALLEMYN, N.C,P.L.S.#2544, CERTIFY THAT THE N.C. GRID COORDINATES AND BEARINGS SHOWN ON THIS PLAT OR DOCUMENT WERE DETERMINED BY AN ACTUAL CPS SURVEY PERFORMED BY ME. THAT THIS SURVEY WAS PERFORMED TO CLASS C FGCC SPECIFICATIONS AND THAT I USED GPS-RTK SURVEY FIELD PROCEDURES. COORDINATES WERE DETERMINED BY LEAST SQUARES ADJUSTMENT. THAT THIS SURVEY WAS PERFORMED USING ONE (1) TOPCON CPS "HIRER" RECEIVER LOGGED INTO NCGS RTK NETWORK. ALL COORDINATES ARE BASED ON NAD 83(2007) AND ALL ELEVA BONS ARE BASED ON NA VD 88. a'T a?r 60• ?Y Q O 4.0 Q --- --- --- --- ANGFRJDINAL G QUAD "E 1 ?GQUAD T3 00+25 wa BEGIN./ LONGITUDINAL PROFILE 2 STA 111+35 TO STA 117+55 AGRICULTURAL FORD GROSSING PRELIMI AT Not for ecordatio ,Convey Tce or Sales SPRING - EASEMENT FOR WATER SUPPLY 4 y 4 n "'?QI° t,EM1! i 7PT'I?FU1"f'I7. , °LA'L ? . _. .BFI L..cI 51 - 2IGINALSIL..'_1`Rr- I , TH_ i 1[ A. --. LICENSE NO. L -541 NOTE EXISTING TOPOGRAPHICAL INFORMATION AND CONTROL DATA INFORMATION TAKEN FROM SURVEY ENTITLED "LATTA-EARTHMARK", DATED JULY-DECEMBER, 2007 BY ALOIS CALLEMYN, PLS. ALL NEW' DATA SHOWN ON THIS SURVEY IS TIED D-1 NORTH CAROLINA STATE PEANE COORDINATE SYST NAD 1983 HORIZONI'AL) AND NA VD-29 (VERTIC BEGIN " z LONGITUDINAL m END PROFILE 3 LONGITUDINAL STA 127+68 TO PROFILE 3 STA 130+09 STA 127+68 30" pAP _ _ _ STA 130+09 ' VFf. VIA n1 ENO LONGITUDINAL PROFILE 2 _ ----°"-"' STA 111+35 TO _ " - ---- TA 1i7+55 ,®---®- S UEG m QUAD T2 x r 4 1 7?B -0 rrr r r - r o 0 a s ?e PRELIMINAR'x'_ Not for Recordation, Conveyance or Sales ,? TRIBUTARY