ML061020375
| ML061020375 | |
| Person / Time | |
|---|---|
| Site: | Browns Ferry  (DPR-033, DPR-052, DPR-068) |
| Issue date: | 04/07/2006 |
| From: | Morris G Tennessee Valley Authority |
| To: | Hogue G Office of Nuclear Reactor Regulation, US Dept of Interior (DOI) |
| References | |
| Download: ML061020375 (154) | |
Text
.'.;. t-.Y Tennessee Valley Authority, 1101 Market Street, Chattanooga, Tennessee 37402-2801 April 7, 2006 Mr. Gregory Hogue Office of Environmental Policy and Compliance Department of the Interior Russell Federal Building 75 Spring Street, S.W., Suite 1144 Atlanta, Georgia 30303 Gentlemen:
BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE
TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL The purpose of this letter is to submit TVA's response to F&WS' RAI on NRC's Biological Assessment of TVA's applicaton for BFN license renewal.
Specifically, F&WS sent six RAIs to TVA on August 12, 2005, pertaining to BFN license renewal environmental issues.
TVA's draft responses to these RAIs were discussed with F&WS personnel on October 27, 2005, ir, Birmingham, Alabama.
Comments and recommendations received from F&WS during this meeting have been incorporated into TVA's responses.
The Enclosure to this letter provides TVA's responses to the six F&WS questions.
If you have any questions regarding the information in this letter, contact R. M. Brown at (423) 751-7228.
Sincerely, Glenn W. Morris Ins Manager, Corporate Nuclear Licensing A ot and Industry Affairs cc:
See page 2 P-to I on ecyV$W prwr
I'
-i Department of the Interior Page 2 April 7, 2006 Enclosure cc (Enclosure):
U.S. Nuclear Regulatory Commission ATTN:
Document Control Desk 11555 Rockville Pike Rockville, Maryland 20852-2738 Ms. Margaret H. Chernoff, Project Manager U.S. Nuclear Regulatory Commission MS 8G9A One White Flint, North 11555 Rockville Pike Rockville, Maryland 20852-2738 Ms. Harriett L. Nash, Project Manager U.S. Nuclear Regulatory Commission MS ilF1 One White Flint, North 11555 Rockville Pike Rockville, Maryland 20852-2738 Mr. Rob Hurt Fish and Wildlife Biologist Ecological Services 2700 Refuge Headquarters Road Decatur, Alabama 35603
if p.
ENCLOSURE BROWNS PERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL The following provides TVA's responses to F&WS' six RAIs:
F&WS Question No.1:
We request more information regarding when and by whom aquatic/terrestrial survey efforts were conducted along the 160 miles of transmission line rights-of-way.
We would also like to see results of some of these surveys.
If surveys are incomplete, we would like a commitment to complete the aquatic and/or terrestrial surveys prior to any new construction or maintenance activity that may affect listed species known in the respective county or counties.
TVA RESPONSE:
TVA's Heritage staff in Knoxville regularly receives requests t:o review right-of-way (ROW) areas scheduled for vegetation management or other maintenance or modification activities.
There are approximately 19,000 ROW miles in the TVA system and requests are received involving approximately one-third of these miles every year.
Such a large workload means that it is not possible to field-survey miles.
Instead, TVA utilizes the best tools available such as Heritage staffers who "fly" the transmission line corridors (using video available to them on TVA InsideNet computer files) to "see" the kinds of habitats present in the project area.
They then overlay the ROW with records o:f sensitive plants and animals from the Heritage data base and consider the likelihood of any listed plant or animal to inhabit the section of line involved in the project.
The standard criteria and guidelines developed years ago are then applied to make conservative vegetation and/or land management recommendations to the Power System Operations project managers.
In general, the listed species are assumed to be present, and the recommendations are conservatively made with the objective of protecting the species.
Vegetation management recommendations can involve hand-clearing requirements, restrictions on use of herbicide sprays, bush hogging, etc.
If there is ground-distu.rbing work to be done (e.g., pole replacement, lightning arrester installation, etc.), and the video fly-overs indicate likely habitat for a listed plant or animal, field visits are made to those project areas to check for the presence of listed species.
F i
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE ro FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL The criteria and guidelines used by TVA's Heritage staff for protection of listed species potentially affected by power line work activities were shared with the F&WS when they were first developed, and again in a February 2005 demonstration session Eor visiting F&WS personnel.
In both reviews, F&WS personnel concurred that these were reasonable methods to perform this work. If there is further interest by other F&WS personnel in reviewing this process, the Heritage staff would be pleased to sched.ule another session. contains a list of biologists, both TVA personnel and contractors that work directly on transmission line projects (such as re-clearing or pole replacement) that involve consideration of potential impacts on threatened and endangered species, wetlands, or natural areas.
Included are staff personnel that do the desk-top reviews and/or field reviews, if necessary.
Included with this list are three examples presented wherein actual field work was required because the database flagged potentially impacted species.
F&WS Question No.2:
Prov;:de river bottom dissolved oxygen data for both winter and summer months under low and high flow conditions at and below BFN's diffuser pipes within the mixing zone and at the mixing zone edge, and describe any changes anticipated with the addition of Unlit 1.
TVA RESPONSE: (Wheeler Profiles 1990-2005 Revl.xls) contains profiles collected from Wheeler Reservoir at Tennessee River Mile (TRM:
locations 277.0 (Wheeler Dam Forebay) and 295.9 (Transition zone -2 miles upstream of BFN).
Beginning in 1990, the sampling was conducted annually, but it was changed to every other year in 1995 to about 1998, and now it is back to annual monitoring due to the drought conditions of recent past years and the implementation of the River Operations study.
The sampling was usually done once a month from April through September as part of the Vital Signs Monitoring program which targets the phytDplankton productive months and coincides with natural dissolved oxygen (DO) variability due to warming water temperatures and potential thermal stratification.
The profiles are collected with a Hydrolab profile at the deepest part of the main channel at the given river mile.
In general, data is taken starting at the reservoir bottom, followed by taking measurements
A.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL about every two meters to the surface.
At TRM 295.9, the only DO recorded at <5mg/L (approximately 4.8 mg/L) was in the lower 3 meters of the water column in June 2001.
Overall, DO conditions for the years monitored appear to be very good at this location.
Attachments 4 and 5 show special Hydrolab profiles for BFN collected on August 31, 2005, and September 14, 2005, at three locations: Below (i.e., downstream of) the BFN mixing zone at TRM 293.3, approximately 250 to 300-feet downstream from the river water temperature monitoring station; in the mixing zone at TRY.'
293.9, approximately 250 to 300-feet downstream from the diffusers; and at TRM 295.9, the normal transition zone monitoring location for Wheeler Reservoir, which is upstream from the m'.xing zone.
On August 31, 2005, and September 14, 2005, Units 2 and 3 were operating at full power with no cooling towers in operation.
These data further support the above conclusion that DO is very unlikely to be an issue in the river reach near BFN.
In addition to not having any significant impact on the measured DO levels in, and downstream of, the mixing zone, the warmer water exiting the BFN diffusers is buoyant and rises to the surface rather than moving along the bottom of the reservoir, so its impact on benthic species is also minimal.
Some historical data are also available from monitoring conducted after Browns Ferry Unit 1 achieved initial criticality on August 17, 1973.
Unit 1 began initial operation on October 15, 1973, and Units 2 and 3 began initial operation on August 28, 1974, and September 12, 1976, respectively.
DO data are contained in reports of Water Quality and Biological Conditions in Wheeler Reservoir during operation of BFN from August 17, 1973, through December 31, 1980.
During the period of operation covered by these reports, it was concluded that there was no apparent long-term alteration of water quality in Wheeler Reservoir due to the operation of BFN.
This conclusion was based on statistical comparison of the quarterly means of water quality parameters from upstream and downstream stations, including DO.
Additional information regarding the anticipated impact of Unit: 1 on DO is found in Section 4.3.6.3 of the Final Supplemental Environmental Impact Statement (FSEIS) for Operating License Renewal of the Browns Ferry Nuclear Plant in Athens Alabama, 2002, which describes the results of computer simulations using a two-dimensional water-quality model of Wheeler Reservoir.
In general, the model predicts that the startup of Unit 1 will not:
have an adverse impact on DO.
In fact, the model predicts that:
in areas downstream of the plant, the minimum level of DO will increase.
This is primarily due to higher levels of
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL photosynthesis, induced by warmer water temperatures, created by the addition of heat from Unit 1. For example, at TRM 292.0, about: 2 miles downstream of the diffusers, the model predicts that for a hot, dry year such as 1988, the minimum daily DO will increase by about 0.8 mg/L after the startup of Unit 1.
Other processes influencing DO are related to mixing induced by the plant diffusers.
Bottom diffusers usually help to increase DO ill bottom layers of the reservoir immediately downstream of the plant.
This is due to upwelling of the river water as it flows up and over the diffuser pipes, and due to turbulence created by the jets from the diffuser ports.
These processes mix oxygen-rich water in the surface region of the reservoir with water of lower DO in the bottom of the reservoir.
These phenomena have been documented in studies performed for the TVA Sequoyah Nuclear Plant, located on the Tennessee River in the Chickamauga Reservoir (TVA, 1990).
The startup of Unit 1 will increase reservoir mixing by the action of the diffuser jets.
Any changes in DO created by these processes, however, will likely be small compared to the action of photosynthesis, as discussed above.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE To FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL F&WS Question No. 3:
Provide modeling data depicting the thermal plume within Wheeler Reservoir when all 3 nuclear plants are operating at full capacity (120% of their originally licensed power production capacity).
Describe any differences expected in the extent of effects on bottom and top waters before and after startup of Unit 1.
TVA RESPONSE: contains a copy of a Power Point presentation showing the results of a three-dimensional simulation of the diffuser thermal effluent with all three units operating at extended power uprate (120 percent of originally licensed thermal power).
The presentation is the same as that shown to F&WS in the meeting of October 27, 2005.
The river flow is 10,000 cubic feet per second, the minimum daily average flow at BFN for the summer heating season, as targeted by TVA River Operations.
The upstream ambient river temperature is 870F, the approximate maximum temperature allowing sustained operation of BFN at full power without exceeding the maximum river temperature downstream of the plant specified in the NPDES permit.
At higher ambient temperatures the plant would have to initiate a derate to protect the NPDES limit.
The results of the three-dimensional simulation represent the worst case scenario for conditions including all three BFN units operating at max generation with extended power uprate.
Compared to the operation of Unit 2 and Unit 3, the startup of Unit 1 will increase the volume of waste heat in Wheeler Reservoir.
- Thus, with Unit 1, the spatial extent of the thermal discharge will be larger, both at the bottom and at the surface of the reservoir.
However, the magnitude of the temperature extremes along the downstream boundary of the mixing zone will not change significantly, because of the plant requirements to maintain compliance with the NPDES river temperature limits.
A ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL F&WS Question No.4:
Provide some discussion on the thermal plume produced by BFN and whether the thermal plume will/will not affect the host fish for listed mussel species within Wheeler Reservoir.
TVA RESPONSE:
Host Fish Impacts on Glochidia (mussel larvae)
The four threatened and endangered freshwater mussels (pink mucket, rough pigtoe, orangefoot pimpleback and fanshell) found in Wheeler Reservoir are all primarily located in the riverine sect:.on below Guntersville Dam (Figure 1).
Known fish hosts for the pink mucket and rough pigtoe are all common reservoir species and are primarily sportfish except for freshwater drum and rosefin shiner (TVA 2005a) (Table 1).
The orangefoot pimpleback and :anshell fish hosts are logperch, darters, and sculpins (IVA 2005a).
Mettee (1996) reported no records of mottled sculpin, tangerine darters, or blotchside logperch in the highland rim region of Alabama.
Rosefin shiners, greenside darters, and banded sculpins are found in tributary streams to Wheeler Rese:voir; snubnose and banded darters are only found in the headwaters of the Elk River.
All of the reservoir fish species, acting or serving as mussel.
hosts, have the ability to detect temperature increases and avoid the river channel affected by BFN's diffusers.
The thermal model illustrates that the left descending bank opposite of BFN is riot affected by the thermal plume and provides passage for migrating host species.
Baxter and Buchanan (1998) tracked sauger with radio telemetry and found that sauger did not have a channel location preference in the vicinity of BFN, and migration was not affected by the thermal plume.
BFN's thermal variance of 90 E'
(32.2 C) does not exceed most of the fish host species upper lethal temperature limits.
The fanshell and orangefoot pimpleback have not been reported since 1978 and are considered very rare.
The fish host species found in the Wheeler Reservoir are tolerant of high ambient r:.ver temperatures.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL tNFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL Table 1 below lists the federally-threatened and endangered freshwater mussel species, corresponding fish host species, and water thermal tolerances of the host species found in Wheeler Reservoir (TVA 2005b).
Based on this information, TVA concludes that water temperatures at BFN do not adversely affect freshwater mussels or their fish hosts.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&.WS) REQUEST FOR ADDITIONAL I:NFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL Guntersvillc Darn Naot Rock I t
Ath e
'h04 Q2k Imu"
' At Creek Decatur
, Fx Ceek crQek Species Codes:
o Lamrpsilis abrupta O Plearobema plenum O Cyprogcria :iogarla o Pkt.holasu r cooperiantis Wvheeler Darn Figure 1. Survey Results of Threatened and Endangered Fresh Water Mussel Species Conducted in Wheeler Reservoir since 1978.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TrO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL Table I.. Fish Host Species, Distribution and Upper Temperature Tolerances of Four Threatened and Endangered Freshwater Mussel Species found in Wheeler Reservoir.
Common Name Host Species Distribution of
- Upper Limit Fish host species Temperature C Lampsil.Ls abrupta Aplodinotus Pink Mu4:ket grunniens Reservoir Sp.
32.8-34.0 Freshwater Drum Micropterus dolomieu Smallmouth Bass Reservoir Sp.
35.0-36.3 Micropterus punctulatusR Spotted Bass Reservoir Sp.
36.0 Micropterus salmoides Largemouth Bass Reservoir Sp.
30.6-36.4 Pomoxis annularis White Crappie Reservoir Sp.
32.0-32.8 Stizostedion canadense Sauger Reservoir Sp.
30.4-33.9 Stizostedion vitreum Walleye Reservoir Sp.
31.6-35 Pleurokema plenum Lythurus ardens Rough Pigtoe Rosefin shiner Tributaries to no records Wheeler Reservoir.
Lepomis Macrochirus Bluegill Reservoir Sp.
3S.5-37.3 Plethobasus Stizostedion cooperianus canadense Orangefoot Sauger Reservoir Sp.
30.4-33.9 pimpletack Cyrogeria stegaria Cottus bairdi Not found in Al Fanshell Mottled Sculpin Highland Rim 29.6-33.8 Cottus carolinae Banded Sculpin Tributaries to no records Wheeler Res.
Etheostoma blenniodes Tributaries to 32.2 Greenside darter Wheeler Res.
Etheostoma simoterum Elk River no records Snubnose darter Tributaries Etheostoma zonale Elk River no records Banded darter Tributaries Percina aurantiaca Not found in Al no records Tangerine Darter Highland Rim Percina burtoni Perchin b onpe rc Not found in Al no records Blotchside Logperch Highland Rim Percina carrodes Reservoir Sp.
26.0**
Logperch
- The upper thermal limits for fish were taken from the report for the ORSANCO Temperature Criteria Re-evaluation, Appendix Table Z.1 database, C. 0. Yoder, 2005.
- Denotes data endpoint derived from collected data for upper temperature limit for larvae.
Logpsrch survive ambient water temperatures in Wheeler Reservoir higher than the reported endpoint temperature limit.
Logperch have been collected in annual Vital Signs surveys downstream of BFN at Tennessee River Mile 292.5 (Baxter and Lowery 2005).
A ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL Impa:ts On Reproductive Rates Via Impacts To Host Fish And Temperature Mortality Data For Larval Fishes, Not Just Adult Fish Mortality Two species of special interest, sauger and yellow perch, were the focus of TVA's BFN thermal variance studies because both are considered coolwater species and are theoretically more susceptible to elevated water temperature.
Based on results of the studies conducted from 1985 through 1992 (Baxter and Buchanan 1998), operation of BFN had no significant adverse impact on the reproductive success of either species, or the annual spawning migration of sauger past BFN.
However, Maceina et al. (1998) found that sauger-spawning success was adversely impacted by over fish.ng and drought conditions (e.g., low flows and decreased turb.dity) in the Tennessee Valley during 1985 through 1988.
TVA 2002, Chapter 4 Section 4.4.10.4, pages 4-46 through 4-48 stated that the flow studies conducted by TVA at BFN have indicated that the majority of water entrained originates from the right side of the main river channel.
This pelagic area contains significantly lower densities of drifting fish larvae than found in the overbank areas (Figure 4.3.10-1).
Higher dens:ities of fish eggs (primarily freshwater drum eggs) are transported in the channel portion of the river, but entrainment of drum eggs (and larvae) has not resulted in noticeable decreased abundance of this species; nor is it expected to, under the increased condenser cooling water flow rates.
The thermal plume model illustrates that the plume rises rapidly towards the surface mixing with the ambient water.
Very little bottom channel area is exposed to high temperatures.
Larval sauger and eggs drifting past BFN would have very limited exposure to high temperatures due to their demersal nature of drifting close to the bottom.
During the spring when saugers spawn, ambient temperatures would be much cooler compared to the worst: case scenario temperature model.
Based on the information, TVA concludes that BFN does not adversely affect migration, reproductive rates, larval, juvenile, or adult fish host species in Wheeler Reservoir.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL Biological (Vital Signs) Monitoring After 3 Units Are Operating At EPU TVA 2002, Chapter 4, Section 4.4.10.4, page 4-47, last paragraph, stated that TVA will confirm the expected levels of impingement and entrainment by monitoring under current 2-unit operation and following the return of Unit 1 to service.
TVA's vital signs monitoring program will also continue to assess aquatic ecological communities in Wheeler Reservoir. Although not expected, if based on these monitoring studies it is determined that increased impingement and entrainment are resulting in unacceptable environmental impacts, TVA would assess the technologies, operational measures, and restoration measures that could be undertaken to remedy this and institute appropriate measures in consultation with appropriate federal and Alabama agencies.
All entrainment and impingement monitoring is conducted with the same procedures used during the pre-operational monitoring for BFN.
Literature cited Tennessee Valley Authority.
1983.
Impingement Counts.
Quality Assu:rance Procedure No. NR OPS-FO-ER-23.11, Rev 0. TVA Natural Resource Operations, Field Operations, Norris, TN. 11 pgs.
Mettee, M. F, P. E. O'Neil, and J. M. Pierson, 1996.
The Fishes of ALabama and the Mobile Basin, Oxmoor House Publishing, 820 pp.
Maceina, M. J., P. W. Bettoli, S. D. Finely, and V. J. DiCenzo.
1998.
Analyses of the sauger fishery with simulated effects of a minimum size limit in the Tennessee River of Alabama.
North American Journal of Fisheries Management 18:
66-75.
Baxter, D.S. and J.P. Buchanan.
1998.
Browns Ferry Nuclear Plan: Thermal Variance Monitoring Program including Statistical Analyses -
Final Report.
Tennessee Valley Authority, Water Management, Aquatic Biology Lab, Norris, Tennessee.
Revised August 1998. 64pp.
TVA 2002.
Final Supplemental Environmental Impact Statement (FSEIS) for Operating License Renewal of the Browns Ferry Nuclear Plant in Athens Alabama, 2002.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL TVA 2005a.
Routine Operations and Maintenance of TVA's Control Structures in the Tennessee River Watershed, Biological Assessment, Appendix J: Possible Fish Host of Mussels, July 2005.
TVA 2005b. Tennessee Valley Authority Natural Regional Heritage Project Database.
Resource Stewardship, Knoxville, TN.
Baxter, D. S. and D. L. Lowery. 2005.
Biological Monitoring of the Tennessee River Near Browns Ferry Nuclear Plant Discharge, 2002.
Tennessee Valley Authority, Resource Stewardship, Aquatic Monitoring and Management, Knoxville Tennessee, 27pp.
C. 0. Yoder, 2005.
ORSANCO Temperature Criteria Re-evaluation, Appendix Table Z.1 database, 2005 Unpublished.
F&WS Question No. 5:
For future in-stream work involving any construction likely to affect listed aquatic species or streams with suitable habitat:
for listed aquatic species (but no survey data), indicate whether TVA is willing to conference and possibly consult on their effects determinations and conduct needed surveys prior to effects determinations.
TVA RESPONSE:
During the planning of all transmission line construction activities, including new construction and subsequent maintenance operations, TVA attempts to avoid in-stream work.
If in-stream work appears unavoidable, TVA assesses the potential for effects on listed species.
If there is inadequate existing information to conduct this assessment, TVA will conduct surveys in the project area.
If the result of TVA's assessment is the determination that the proposed in-stream work may affect listed species, TVA will consult with the U.S. F&WS.
In the past, the need for such consultation has been very rare and TVA does not anticipate it occurring often in the future.
The following briefly summarizes the environmental compliance review process TVA Heritage Resources use for maintenance and modifications of transmission lines and proposed construction of new transmission lines.
The review processes are presented below by resource area.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE To FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL TVA Heritage Resources Review Process For TVA Transmission Rights-Of-Way Vegetation Maintenance, Line And Pole Maintenance, And New Transmission Line Construction Overview Of Environmental Compliance Process For Transmission Line Maintenance And Modifications The TVA PSO organization routinely conducts maintenance activities on transmission lines in the TVA Power Service Area (PSA).
These activities include, but are not restricted to, ROW re-clearing (removal of vegetation), pole and crossarm replacements, installation of lightning arrestors and counterpoise, and upgrading of existing equipment. Regular vegetation maintenance activities are conducted on a cycle of :3-5 years.
Prior to these maintenance activities, the transmission line area including the ROW is reviewed by technical specialists in the TVA Regional Natural Heritage Project to identify any natural resource issues that may occur along that transmission line.
The TVA Regional Natural Heritage Project maintains a database of some 35,000+ (as of November 2005) occurrence records for protected plants, animals, caves, heronries, eagle nests, and natural areas for the entire TVA PSA, including 201 counties in a sever, state area.
The TVA Heritage database is dynamic, with updates and additions taking place throughout the year.
Only credible records are included in the database, and the sources include the results of field surveys by TVA biologists, publications, museum and herbarium specimens, unpublished reports from biologists outside TVA, data exchanges with the seven state heritage programs overlapped by TVA's coverage area (AL, GA, KY, MS, NC, TN, and VA), and data exchanges with five offices of U.S.
F&WS (Cookeville, TN, Asheville, NC, Athens, GA, Daphne, AL, and Jackson, MS).
Wetland information is maintained by TVA Heritage Resources and includes National Wetland Inventory wetland maps for the entire TVA PSA.
Soil survey maps are also used to identify potential wetland areas.
All records of listed plants or animals, caves, wetlands, or natural areas that are present, or are potentially present, in the transmission line ROWs are taken into consideration when conducting these transmission line reviews.
Other sources considered in reviews include county lists of federally-protected species, the TVA Natural Heritage database described above, aerial photographs and USGS topographical maps.
In addition, high-quality videos taken during low-altitude
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE To FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL flyovers of the transmission corridors are used to estimate the ecological community types present on the ROW.
Using these available data sources, Heritage biologists identify sensitive habitats where rare plants or animals are known, or likely to occur.
If potential impacts of maintenance activities to plants or animals on the Endangered Species Act are identified, field surveys may be conducted to document presence of the listed species in the ROW, especially if the proposed actions include pole replacement or some other action that would result in ground disturbance.
However, in many other cases where the available data indicate the possibility of listed species being present on the ROW, Heritage specialists assume the species is present and work with PSO staff to avoid impacts to the listed species.
For example, if maintenance activities in the ROW could affect a cave inhabited during part of the year by a bat colony, a restriction may be indicated for the time of year the maintenance activities could take place.
Within streamside management zones, hand clearing, or backpack herbicide application reduce impacts to streams and listed aquatic species.
The width of the streamside management zones vary according to the slope of the surrounding area, the type of stream, and the particular resources that may be present in the stream (listed species).
However, if avoidance is not possible, Heritage specialists consult, as appropriate, with the U.S. F&WS.
Also included in this document is the explanation of class definitions and associated table of mapping polygon colors and the restrictions indicated by those designations used in the cGIS product transmitted to PSO.
Managed areas (MA), ecologically significant sites, and National Rivexrs Inventory for maintenance activities in TVA transmission line ROW MAs are lands held in public ownership that are managed to protect and maintain certain ecological features. Ecologically Significant Sites (ESS) are tracts of privately-owned land that are identified by resource biologists as containing significant environmental resources. National River Inventory (NRI) streams are free-flowing river segments that are recognized by the National Park Service as possessing remarkable natural or cultural values. The TVA Natural Heritage Project maintains a database of all such lands and streams occurring within the seven-state TVA PSA.
As described above, this information is added to and updated frequently.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL ROW maintenance activity reviews for MA's, ESS's, and NRI streams are completed by utilizing computerized mapping ArcMap graphics software.
If a MA, ESS, and/or NRI stream is located within the 0.5-mile buffer of the subject transmission line, a polygon designating the known or likely extent of that occurrence is drawn on an ArcMap electronic topographic map, and appropriate class restrictions are applied (see table of Class Definitions and Associated Polygon Colors of Sensitive Areas) that represents the area's boundaries within the buffer. A description of the area that includes contact information for the manager of the natural area and also for the appropriate TVA contact, restrictions for maintenance methods, and the subject transmission line name is listed in the corresponding attribute table.
ROW vegetation maintenance and transmission line maintenance are reviewed for potential of these activities to affect natural areas. If all or any portion of a MA, ESS, and/or NRI stream lies within the buffer of the subject transmission line, a polygon is drawn depicting the boundary of such areas. Restrictions on proposed activities (See Attachment 7, Table 1) are determined by the type and location of the MA, ESS, and/or NRI streams, as well as consultation with the area manager or resource specialist. he class and contact restrictions, definitions, and polygon color for both activities are listed in the included table.
After determining the particular class restriction associated with the area, special instructions or comments are added to indicate the importance of the restriction and why it was assigned.
For example, when a portion of a national forest is within the 0.5-mile buffer or crossed by the subject transmission line, a Class 3 restriction is assigned and a comment is added indicating the area manager must be contacted and herbicide use is restricted.
Table 2, in Attachment 7, provides the types of restrictions assigned to transmission line maintenance projects for natural areas. Transmission line projects such as lightning mitigation, counterpoise activities, conveyances, line relocations for state highway department work, and providing delivery points and switches for substations are separate projects and are reviewed for potential impacts to MA's, ESS's, and NRI streams based on the amount and type of disturbance required. A three-mile radius of the project site(s) is reviewed for MA's, ESS's, and NRI streams that might be affected by the proposed activity.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL (Botany) - State and federal protect plant restrictions for maintenance activities in TVA transmission line ROW Botanical assessments are performed for proposed ROW vegetation maintenance and transmission line maintenance activities.
During the review, botanists identify state and federally listed plants or rare plant community types that occur, or are likely to occur on or near the transmission line ROW.
Identifying the occurrences gives TVA the ability to identify habitats within a proposed project area that are sensitive and potentially require restrictions for particular vegetation management activities.
To identify rare plant and sensitive habitat locations, TVA utilizes the U.S. F&WS' county lists of protected plants, the TVA Natural Heritage database, aerial photographs and USGS topographical maps.
In addition, TVA also have access to videos taken during low-altitude flyovers of the transmission corridors.
These high-quality videos are used to determine the type of plant habitats available on the ROW.
The review process for ROW vegetation maintenance and transmission line maintenance activities is different since they potentially impact vegetation in different ways.
ROW vegetation maintenance consists of vegetation clearing with both herbicides (unless otherwise specified) and mechanical methods.
Any vegetation present in the ROW that is sprayed by herbicides could be acversely affected.
Mechanical clearing has less of an impact since many plants can usually tolerate being cut.
Transmission line maintenance projects like pole replacements potentially impact vegetation when vehicles and equipment drive on (and in) the vicinity of the ROW and the soil and the vegetation are disturbed.
If sensitive plants are likely, field work is often required to confirm their presence.
Frequently however, we assume their presence and make recommendations for different access routes to be taken and TVA notifies appropriate staff about. sensitive areas to avoid.
Restrictions are determined by knowledge of the habitat requirements for rare plants and rare plant. communities that occur within the vicinity of the ROW.
Once a sensitive area is located, a polygon designating the known or likely extent of that occurrence is drawn on an ArcMap electronic topographic map, and appropriate class restrictions are applied (see table of Class Definitions and Associated Polygon Colors of Sensitive Areas).
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO
- FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL (Terrestrial Animals) - State and federal-protected terrestrial animal restrictions for maintenance activities in TVA transmission line ROW The TVA Regional Natural Heritage Program keeps track of state and federal-protected species reported from the seven state region.
The terrestrial animal portion of the data base includes all listed birds (breeding and large wintering aggregations),
mammals, reptiles, and amphibians, and some invertebrates (land snails, insects and cave obligate invertebrates).
In addition to certain species of animals, the terrestrial portion of the database also includes records of heronries and caves as they often are used by multiple species, and thus are sensitive habitats.
Each :ransmission line maintenance project is reviewed for the presence of protected terrestrial animals, heronries, and caves.
A database search of the listed animals known from the county (or counties) included in the project area is performed.
The zoologists, using these county lists and animal occurrences from the TVA Heritage database, look for habitats appropriate for these species in their review of the ROW videos.
Heronries and caves within a 3-mile radius from the ROW restrictions will be listed, as appropriate, for likely occurrences of federal and state listed species.
A polygon designating the known or likely exten: of that occurrence is drawn on an ArcMap electronic topographic map and appropriate restrictions are applied (Tables 1 and 2).
Special comments or instructions accompany each entry, as appropriate.
For instance, if a cave located along a power line corridor is scheduled for vegetative maintenance, a 200-fcoot buffer is indicated around the opening of the cave and a "Hand Clearing Only" restriction is applied within the buffer.
If the cave is used by a summer or hibernating colony of bats, appropriate time restrictions, as designated in specific recovery plans for each species, may also be applied.
(Aqua;tic Animals) - State and federal protected aquatic animal restrictions for maintenance activities in TVA transmission line ROW Each proposed transmission line maintenance or ROW vegetation maintenance project is reviewed for the known or likely occurrence of protected aquatic animals in streams, in or adjacent to the transmission line ROW, or in a stream drained by the ROW corridor.
A database search of the listed aquatic animals known from the county (or counties) included in the
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL project area is performed.
The aquatic biologists, using these county lists and animal occurrences from the TVA Heritage database, look for habitats appropriate for these species in their review of the ROW videos.
Once an occurrence or likely occurrence is identified, class restrictions are applied and the appropriate colored polygon is drawn around the resource area on an ArcMap electronic topographic map (Tables 1 and 2).
All transmission line maintenance activities are currently conducted using Best Management Practices as outlined in Muncy (1999).
Special comments or instructions (including designation of specific Streamside Management Zones, as identified by Muncy 1999) accompany each entry, as appropriate.
(Wetlands) - Wetlands review for maintenance activities in TVA transmission line ROW Prior to the performance of any maintenance activities in TVA transmission line ROWs, office-level reviews are conducted by Natural Heritage wetland biologists.
This review includes review of the National Wetland Inventory (NWI) map, county soil surveys, and IVA photos and videos of transmission line structures and ROW.
Potential wetland areas, not indicated on the NWI map, are identified based on interpretation of topographic features, water bodies, soil information, TVA photos and videos and proximity to NWI features. All NWI wetlands or potential wetland areas are superimposed as layers on an ArcMap electronic topographic map (see included maps).
These ArcMap images are sent to PSO, and are accompanied by the Excel spread sheet which lists areas that have been included with the NWI data as areas of potential wetlands and what specific guidelines are to be used in each situation to avoid adverse impacts.
The YWI wetlands are indicated on the ArcMap drawings for both the ROW and a 1-mile diameter buffer area around the ROW.
Poter.tial wetland areas are identified in the ROW, but are not identified in the buffer area, parts of which may be used for ROW access.
If the access route follows an existing road that does not require any repair or upgrading, no further wetland reviews are needed. Repair and upgrading includes, but is not limited to, grading, fill addition, new or upgraded stream crossings, and vegetation removal.
If a new or upgraded access route is necessary, environmental reviews of those particular access areas are conducted as required by the National Environmental Policy Act (NEPA).
The NWI data was compiled using high-altitude aerial photography, some of which is now over 15-years old, with very limited field
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL verification.
Because of this, some of the NWI data may be inaccurate.
The limitations of the NWI data are considered in the performance of transmission line maintenance and ROW vegetation maintenance projects to avoid accidental wetland impacts.
Since there could be wetlands present for which no map evidence or other data currently exists, maintenance crews remain alerted to such things as water on the surface of the ground, soil saturation, the type of vegetation growing in an area, and evidence of present, seasonal or temporary flooding.
In the absence of a ground survey by a wetlands specialist to determine wetland presence and location for ROW vegetation maintenance and transmission line maintenance projects, Best Management Practices, as described in Muncy (1999) are implemented to avoid and minimize potential impacts (see Tables 1
& 2).
These techniques would be implemented in all locations where NWI wetlands and potential wetland areas are indicated on the project maps submitted by the TVA Natural Heritage staff.
Site-specific recommendations for ROW vegetation maintenance and transmission line maintenance projects are provided when needed (see Tables 1 & 2).
In addition, certain activities that may occur during pole replacement in wetlands are regulated under Sections 404 and 401 of the Clean Water Act.
U.S. Army Corps of Engineers (USACE) Nationwide General Permit (NWP) #12 authorizes certain activities related to utility line construction and contains conditions to ensure that impacts to wetlands are minimal.
Section 401 gives states the authority to certify whether activities permitted under Section 404 are in accordance with state water quality standards (Strand, 1997).
A qualified TVA or TVA contract wetlands specialist would be required to delineate the wetland(s) and provide the wetland determination data forms which are required for inclusion in the permit application.
TVA also follows Executive Order 11990 which requires all federal agencies to minimize the destruction, loss, or degradation of wetlands, and to preserve and enhance the natural and beneficial values of wetlands, in carrying out the agency's responsibilities.
Potential impacts to wetlands resulting from ROW vegetation maintenance and transmission line maintenance activities include vegetation damage, soil compaction and erosion, sedimentation, and hydrologic alterations.
These impacts are avoided or minimized during TVA maintenance operations by following the recommendations of the guidelines presented above and implementing all relevant Best Management Practices.
In
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL addition, the appropriate permits are obtained if required for the specific activity.
Overview of Environmental Compliance Process for New Transmission Line Construction Prior to selection of potential routes for new transmission lines, PSO identifies the geographic "study area" that includes all potential routes.
Heritage database records of listed plants and animals, caves, natural areas, and NWI wetlands in this study area are provided to PSO at this stage in the planning process.
These and other data are used to support development of specific route alternatives for the new line.
Procedures for environmental review of proposed alternative routes developed with this preliminary information may include field surveys, depending on resource area (briefly discussed by resource) below.
Data obtained from field surveys for new construction projects are used to update the Heritage and wetlands databases so that it is available for future maintenance projects.
If potential construction impacts to plants or animals on the federal Endangered Species Act are identified, Heritage and PSO staffs will make every effort to avoid these impacts. If avoidance is not possible, Heritage specialists consult, as appropriate, with the U.S. F&WS.
(Managed Areas) - Managed Areas, Ecologically Significant Sites, and National Rivers Inventory review of New TVA Transmission Line Cons truc tion A desktop level review of the proposed route alternatives identifies MA, ESS, and/or NRI streams that could be impacted by new transmission line construction.
The TVA Natural Areas Coordinator might contact managers of any non-TVA areas that might be affected to confirm boundaries of the area and management objectives.
Natural Areas input to the NEPA docume:nt prepared for this new construction line project includes the commitment for any mitigation that might be appropriate to protect managed areas from any adverse impacts of construction activities. Field surveys are not usually required, but may be appropriate in some cases.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL (Botanry) -
State and Federal listed plant restrictions for Construction of New TVA Transmission Lines A desktop-level review of the proposed route alternatives is performed to identify state and federally listed plants known from within the counties included in the construction line route alternatives.
If this initial review indicates the project may impact a listed plant, field surveys are made of the proposed routes.
The PSO process for line construction normally allows for reroute negotiations to avoid potential impacts to listed plants.
These reroutes are worked out in cooperation between Heritage and PSO staffs, and are contingent upon environmental review results for other disciplines.
The botanical input to the NEPA document prepared for this new construction line project includes the commitment for any mitigation that might be appropriate to listed plants from any adverse impacts of construction activities, and also make recommendations about ROW maintenance activities specific to maintain populations of listed plants identified.
(Terrestrial Animals) - State and Federal Protected Animal reviews of new TVA Transmission Line construction A desktop-level review of the proposed route alternatives is performed to identify state and federally listed animals known to occur within the counties included in the construction line route alternatives.
If this initial review indicates the project may impact: a listed animal, field surveys are made of the proposed route:;.
The results of these field surveys are conservative, in that confirmation of the species presence is not required for EL determination that construction of the new line may affect the species.
The presence of appropriate habitat for the listed animals along the proposed route could result in route negotiations and/or specifically recommended mitigation. As mentioned above, the PSO process for line construction normally allows for reroute negotiations to avoid potential impacts to listed animals.
These reroutes are worked out in cooperation between Heritage and PSO staffs, and are contingent upon environmental review results for other disciplines.
The zoological input to the NEPA document prepared for this new construction line project includes the commitment for any mitigation that might be appropriate to protect listed animals or their habitats from any adverse impacts of construction activities, and also make recommendations about future ROW vegetation and transmission line maintenance activities specific to maintain populations of listed animals identified.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL (Aquatic Animals) - State and federal protected animal review of proposed new TVA transmission line construction A desktop-level review of the proposed route alternatives is performed to identify state and federally listed animals known to occur within the counties and watersheds included in the geographic areas potentially affected by construction line route alternatives.
Because topographic maps are not always accurate, and aquatic habitats can be more accurately described by seeing them, field surveys are required for all proposed routes.
Fie:!d surveys provide information to support recommendations for streanside management zones (Muncy 1999) appropriate for the streams encountered along the route.
These field surveys will be conservative, in that biological samples are not normally taken, and confirmation of the species presence is not required for a determination that the construction may affect the species.
The presence of appropriate aquatic habitat for the listed animals along the proposed route could result in route negotiations and/or specifically recommended mitigation.
As mentioned above, the PSO process for line construction normally allows for reroute negotiations to avoid potential impacts to listed animals.
These reroutes are worked out in cooperation between Heritage and PSO staffs, and are contingent upon environmental review results for other disciplines.
Streamside management zones for all waterbodies crossed by the proposed routes are flagged in the field and also documented with polygons designating the known or likely extent of that occurrence on an ArcMap electronic topographic map delineated using sub-meter accuracy GPS units.
The aquatic animal input to the NEPA document prepared for this new construction line project includes specification of streamside management zones for each stream crossed by the proposed routes, and also includes commitment for any mitigation that might be appropriate to protect listed animals or their habitats from any adverse impacts of construction activities.
Recommendations for future ROW vegetation and transmission line maintenance activities that would maintain populations of listed animals are also identified in the NEPA document.
(Wetlands) - Wetlands review of proposed new TVA transmission line construction A desktop-level review of the proposed route alternatives is performed to identify areas where 2/WI, soil survey maps and dat'a indicate wetlands present in the geographic areas potentially affected by construction line route alternatives.
Field surveys for wetlands are required for all proposed routes. Any wetlands
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL encountered are delineated with standard wetlands delineation techniques, and the ecological condition is also evaluated using a TVA-.developed wetland rapid assessment protocol.
Wetlands crossed by the proposed routes are flagged in the field, and also mapped using sub-meter accuracy GPS units.
The presence of wetlands along the proposed route could result in route negotiations and/or specifically recommended mitigation.
As mentioned above, the PSO process for line construction normally allows for reroute negotiations to avoid potential impacts to wetlands.
These reroutes are worked out in cooperation between Heritage and PSO staffs, and are contingent upon environmental review results for other disciplines and the practicability of the suggested reroutes.
The wetlands input to the NEPA document prepared for this new construction line project includes documentation (size and type of wetland, for example) for each wetland crossed by the proposed routes, and also includes commitment for any mitigation that might be appropriate to pr6tect these wetlands from adverse impacts of construction activxties.
Recommendations for future ROW vegetation and transmission line maintenance activities are also identified in the NEPA document.
Literature Cited Muncy, J.A. 1999.
A guide for environmental protection and best management practices for Tennessee Valley Authority transmission construction and maintenance activities (revised).
Technical note TVA/LR/NRM 92/1.
- TVA, Norris, TN.
(Chris Austin, Chris Brewster, Alicia Lewis, Kenton Smithson, Tina Broyles, Tom Wojtalik, editors).
Strand, M.N.
1997. Wetland Deskbook, 2nd edition.
The Environmental Law Reporter, Environmental Law Institute, Washington, D.C.
A ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL
- .NFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL F&WS Question No.6:
Indicate whether TVA is willing to select and use only low-toxic~ity surfactants and other adjuvants during herbicide treatments within stream buffer zones to protect listed aquatic species known or suspected of being present in the streams.
[Thiv may require addition of a BMP to existing plans.]
Surfactants should have LC50's of not less than 20 mg/L for daphnia, trout and [if data are available] mollusks.
TVA RESPONSE:
TVA'sE vegetation maintenance activities involving herbicide and adjuvant application are subject to environmental review procedures previously described in the response to Question #1.
Typically, limited maintenance activities are allowed within the Streamside Management Zones (SMZs).
Levels of protection for SMZs are identified in the environmental review based upon type of watercourse, primary use of water resource, topography, and identification and habitat suitability of threatened and endangered species.
TVA guidelines outlined in "A Guide for Environmental Protection and Best Management Practices for TVA Transmission Construction and Maintenance Activities" provide directions necessary to protect the stream channel or other water body and water quality, and alleviate any potential adverse impacts on threatened and endangered species.
TVA currently utilizes Activate Plus, as manufactured by Terra.,
as an adjuvant to herbicide to improve the performance of the spray mixture.
While the LCso toxicity of this particular surfactant is less than 20 mg/L and lower than recommended by U.S. F&WS, the surfactant contains isopropyl alcohol, which limits its propensity to migrate to water and thus, without direct application to water, limits any probable risks of toxic doses.
Additionally, because of the lack of published field data, it is difficult to determine true toxicity effects of surfactants on aquatic species.
However, TVA would agree to a trial period usage of side-by-side test plots over the next two years of low toxicity surfactants in the SMZs of area transmission lines.
Low toxicity surfactants could include LI700 as manufactured by Loveland Industries, Agri-Dex, as manufactured by Helena Chemicals, and Class Act Next Generation, as manufactured by Agrisolutions.
These particular products currently have some toxicity data available that demonstrate a toxicity range of greater than 20 mg/L.
A trial period usage
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL would allow TVA to determine efficacy of these particular surf.ctants in combination with currently used herbicides.
TVA could also adjust their evaluated surfactant use and respond as new products enter the market or LC50 toxicity data becomes available.
Some surfactants may work best with certain types of herbicides and not others due to their solubilities.
Differences in the herbicide's oil or water solubility influence absorption.
Additionally, surfactants perform differently based on the type of plant to be controlled due to differences in wax content and composition, leaf arrangement and architecture, and plant hairs.
TVA plans to engage expert assistance to evaluate the effectiveness of the spray mixtures for optimal vegetation control on the associated ROW SMZs.
Based on the surfactant evaluation, TVA would consider utilizing these products on an extended schedule in the BFNP SMZs, as well as wider scale use across the TVA region.
ENCLOSURE BROWNS FERRY NUCLEAR PLANT (BFN) UNITS 1, 2 AND 3 -
RESPONSE TO FISH & WILDLIFE SERVICES' (F&WS) REQUEST FOR ADDITIONAL INFORMATION (RAI) ON NRC'S BIOLOGICAL ASSESSMENT OF TVA'S APPLICATION FOR BFN LICENSE RENEWAL
==
Conclusion:==
TVA has provided responses to the six F&WS requests for additional information provided to TVA on August 12, 2005, regarding BFN license renewal environmental issues.
Based on the actions taken by TVA in response to these requests in concert with the discussions that took place between TVA and F&WS personnel on October 27, 2005, in Birmingham, Alabama, TVA believes that all issues have been resolved in support of TVA's BFN License Renewal Application.
ATTACHMENT 1 Listing of TVA & Contract Biologist Working on Transmission Line Projects
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Heritage Staff Qualifications Summoary (including contractors)
Name: John T. (Bo) Baxter, Jr.
Education: B.S. in Zoology; M.S. in Zoology Area of expertise: Fish and benthic macroinvertebrate taxonomy, threatened and endangered aquatic animals -
conservation and reintroduction efforts, NEPA reviews/endangered species consultation Years of professional experience: 15 TVA Position: Senior Aquatic Endangered Species Biologist Contact information: (865) 632-3360; jtbaxteretva.gov Years of TVA experience: 5 Professional licenses or memberships: Association of Southeastern Biologists, American Society of Ichthyolo;fists and Herpetologists, North American Benthological Society Other information: Board member Clinch River Environmental Studies Organization (CRESO). Peer reviewed taxonomic publications.
Name: Stephanie A. Chance Educaticn: B.S. in Fisheries Biology; M.S. in Environmental Biology Area of Expertise: Malacology, endangered species consultations Years of Professional Experience: 5 TVA Po! ition: Aquatic Endangered Species Biologist Contact Information: (865) 632-3403; sachanceetva.gov Years of Experience with TVA: 2 Professional licenses or memberships: Freshwater Mollusk Conservation Society Other in Formation: Peer-reviewed publications in scientific journals
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Joseph "Leo" Collins Education: B.S. in Biology; Ph.D in Plant Taxonomy Area of expertise: Plant taxonomy, threatened & endangered plants, uncommon plant communities of southeastern U.S., NIFPA reviews Years orprofessional experience: 30 TVA Pcsition: Botany Specialist Contact information: (865) 632-3416; jlcollinsetva.gov Years o r TVA experience: 27 Professional licenses or memberships: Tennessee Academy of Science, Southern Appalachian Botanical Society Other information: Nine years owning & operating a wholesale nursery; 20 years owning & operating a Chris mas tree farm; botanical field experience in Peru, Panama, and Costa Rica; ten years publishing a newsletter on landscaping with native plants; prepared scientific description of a new species of clover; peer-reviewed publications and several articles in conservation or nursery magazines.
Name: Patricia B. Cox Education: B.S. & M.S. in Biology; Ph.D Botany Area of expertise: Plant taxonomy & systematics; plant anatomy Years ol-professional experience: 30 TVA Position: Senior Botanist Contact information: (865) 632-3609; pbcox~tva.gov Years ol'TVA experience: I Professional licenses or memberships: Southern Appalachian Botanical Society, Membership secretary, Representative to the Smoky Mountain Wildflower Pilgrimage, chairman of the Bartholomew Award committee; Association of Southeastern Biologists, Co-meeting chair for ASB 2006, Meritorious teaching award committee; Discovei Life in America, Board of directors; American Fern Society; Great Smoky Mountain Wildflower Pilgrimage organizer.
Other information: Currently working on an All Taxa Biodiversity project in the Great Smoky Mountains Nat:onal Park. Project involves using the trails as transects to map the fern species present in the park. Over the past four summers, with the help of volunteers, over 165 miles of 47 trails have been mapped. Peer-reviewed taxonomic publications.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Travis Hill Henry Education: B.S. in Wildlife Science, M.S. in Zoology Area of expertise: Mammalogy, endangered species, cave biology, habitat analysis Years ol professional experience: 13 TVA Position: Terrestrial Zoology Specialist Contact information: (865) 632-6360; thhenry~tva.gov Years of TVA experience: 9 Professional licenses or memberships: The Wildlife Society, Society of Marnmalogists Other information: Board member, Tennessee Bat Working Group; Several peer-reviewed journal articles and accounts in a publication on imperiled wildlife in Alabama Name: Jason M. Mitchell Education: B.S. in Wildlife & Fisheries Science; M.P.A. in Environmental Policy Area of expertise: Natural resource management, emphasis on sensitive resources or ornithology Years of professional experience: 11 TVA Job title: Senior Natural Areas Biologist Years of TVA experience: 5 Professional licenses or memberships: Natural Areas Association, Association of Field Ornithologists Other information: Work history in resource management has emphasized project management, research &
monitonng, technical writing, public relations, and strategic planning; peer-reviewed & popular journal articles &
technical reports Name: Kim Pilarski Education: B.S. & M.S. in Geography, minor in Ecology Area of expertise: Wetland assessment & regulation; watershed assessment Years of professional experience: 11 TVA Position: Senior Wetlands Biologist Contact information: (865) 632-3405; kpilarski@tva.gov Years of TVA experience: II Profess onal licenses or memberships: Society of Wetland Scientists
ATTACHMENT I
[Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Scott, Edwin, M., Jr.
Education: B.S. in Zoology; M.S. in Fisheries Biology Area of expertise: Aquatic ecology, ichthyology Years of professional experience: 29 TVA Po ;ition: Aquatic Zoologist Contact information: (865) 632-3358; eniscottetva.gov Years of TVA experience: 29 Professional licenses or memberships: America Fisheries Society (President of Tennessee Chapter); Southern Division AFS Warmwater Streams committee Name: K. Brandon Chance Educations: B.A. Biology; M.S. Environmental Biology Areas of Expertise: Aquatic and Fisheries Biology and Herpetology Years of Professional Experience: Five TVA Pos;ition: Staff Augmentation Aquatic Ecology Contractor Contact information: (865) 632-2414; kbchanceetva.gov Experience with TVA: 2 years Name: Edward E.C. Clebsch Education: A.B., M.S., & Ph.D. in Botany Area of ixpertise: Botany Years of professional experience: 55 TVA Position: Staff augmentation contract Botany Specialist Contact information: (865) 632-3310; eeclebschetva.gov Years of TVA experience: 4 Professional licenses or memberships: Association of Southeastern Biologists, Southern Appalachian Botanical Society, American Arachnology Society, International Society of Arachnology, Ecological Society of America Other information: Staff augmentation contractor; Co-owvner Native Gardens, a native plant nursery; Proprieto;-,
Clebsh Ecology Consulting; interest and expertise of Pseudoscorpions; Many peer-reviewed journal articles
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Kelly Baxter Education: B.S. in Botany, M.S. in Plant Science & Landscape Systems Area of expertise: Plant taxonomy & ecology, botanical environmental reviews & NEPA compliance Years of professional experience: 3 TVA Position: Staff augmentation contract Botany Scientist Years of TVA experience: 2 Other in Formation: Staff augmentation contractor; experience managing a garden center - knowledgeable of cultivated plants Name: Paul C. Durr Education: M.S. in Botany Area of expertise: Wetland Science, Botany, Plant Ecology Years of professional experience: 25 TVA Po ition: Task Contract Botany & Wetlands Senior Scientist Contact information: (865) 9226-3608; ptrleseaol.com Years of TVA experience: 2 Professional licenses or memberships: Society of Wetland Scientists, Southern Appalachian Botanical Society Other information: Employed by PTRL Environmental Services Name: Larry D. Estes (Dwayne)
Education: B.S. in Plant Biology; currently, in the Ph.D program in Plant Systematics Area of Expertise: Vascular Flora of Tennessee, particularly Middle Tennessee; Floristics of limestone cedar glades; rhytogeographic patterns of southeastern flora of TN, AL, KY.
Years ol Professional Experience: 4 years of professional experience as a botanical consultant TVA Position: Staff augmentation Senior Botany contractor Contact information: (865) 974-2256; tnplantseyahoo.com Years o r TVA experience: 2.5 years
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Jo nny Fiedler Education: B.S. in Biology, M.S. in Wildlife Science Area of expertise: Bats & birds, wind turbine mortality of birds & bats Years of professional experience: 5 TVA Job title: Staff Augmentation Senior Terrestrial Zoologist contractor Years of TVA experience: 4 Professional licenses or memberships: The Wildlife Society Other inlormation: Extensive mist-netting experience (birds & bats), have taught bird monitoring & mist-netting skills to biologists in Mexico & Cuba, and continue to teach preparation of bird study-skins to students at the University of Tennessee Name: James P. Groton Education: M.S. in Forestry; B.S. in Natural Resources Area of Expertise: Wetlands Science, Geographic Information Systems and Analysis Years of Professional Experience: 26 TVA Position: Task Senior Wetlands Contractor Contact information: (865) 632-3148; jpgrotongtva.gov Years of Experience with TVA: 3 Professional licenses or memberships: Professional Wetland Scientist (PWS 558), Society of Wetlands Science, Association of State Wetland Managers, Soil and Water Conservation Society Other information: Employed by Science Applications Information Consultants. Conducts wetland delineations and assessment for TVA projects; conduct Sensitive Areas Reviews for TPS transmission line maintenance, reclearing, pole replacement, and lightning mitigation; provide input on Categorical Exclusion Checklists, Environmental Assessments, and Environmental Impact Statements; assisted with development of TVA wetland mitigation policy and TVA Rapid Assessment Method for evaluating wetland integrity.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Heather M. Hart Education: B.S. in Plant & Soil Science; M.S. Environmental Science & Soils (graduation May 2005)
Area of expertise: Interpreting the morphology & classification of soils and soil & water conservation Years of professional experience: 3 TVA Position: Staff augmentation Natural Areas biologist contractor Contact information: (865) 632-6417; hmhart@tva.gov Years of 'TVA experience: 2 Professional licenses or memberships: TDEC Fundamentals of Sedimentation & Erosion Control Certification; Associate Professional Soil Scientist American Society of Agronomy SSA/CPSC; USDA Regulatory Authority Application of Restricted Use Herbicides; member of Soil Science Society of America Name: David T. Nestor Educatio a: B.S. in Aquaculture, minor in Bioscience; M.S. in Botany Area of expertise: Botany Years of professional experience: I TVA Position: Staff augmentation Botany Scientist contractor Contact information: (865) 632-4209; dtnestoretva.gov Years of TVA experience: 1 Other information: Little River Association volunteer, Great Smoky Mountains National Park ATBI volunteer, plant nursery experience - perennial maintenance & propagation, musician Name: Lirry R. Pounds Education: M.A. & B.A. in Mathematics; Ph.D. in Ecology Area of Expertise: Endangered plants, plant communities, exotic pest plants Years of Professional Experience: 20 TVA Posi1tion: Staff augmentation Botany Specialist contractor Contact information: (865) 632-3302; lrpounds5@tva.gov Years of Experience with TVA: 8 Professional licenses or memberships: Ecological Society of America, Natural Areas Association, Southern Appalach:an Botanical Society.
Other information: Peer-reviewed publications in scientific journals
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Name: Jan Thomas Education: B.S. in Home Economics Education; M.S. in Human Ecology Area of expertise: Natural Areas Years ol professional experience: 10 TVA Position: Staff augmentation Natural Area Scientist contractor Contact information: (865) 632-6204; jkthomasetva.gov Years oITVA experience: 2 Other information: Several years experience in health & safety research, environmental restoration, technical writing, adult education/human services Name: Allan J. Trently Education: B.S. in Environmental Resource Management; M.S. in Biology Area of expertise: Ornithology Years of professional experience: 11 TVA Po:;ition: Staff augmentation Terrestrial Zoologist contractor Contact information: (865) 632-6356; ajtrentlyetva.gov Years of TVA experience: 5 Professional licenses or memberships: Tennessee Ornithological Society Other information: Several publications in bird watching and conservation journal
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects Examples of Proiect Impact Reviews involving Field Surveys A. Monkey-face orchid in the ROW for the Great Falls - Pikeville Transmission Line Demolition; Van Buren and Bledsoe Counties, TN ARC-ME p database records for the subject proposed transmission line project area were reviewed.
ReprodLced below is a section of the map showing green dots, which represent individual records of listed plants. When the TVA Heritage Project staff reviewer clicks on a green dot, it brings up the data for that record, including the name of the species, where it was collected, when it was first and last observed and by whom (including whether or not there is sufficient information to indicate the species is still present),
and dire :tions to get there. Each record has a reference (e.g., publication, letter, map sent by a botanist, herbarium specimen, etc.). On many records the database entry also states how many individuals were present at each observation. An example of the information that appears when a green dot is clicked is also reproduced below. ARC-Map also contains a ruler tool which can be used to measure the distance between the occurrence record and the project.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects as ~
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' SHAPE PoW OBJECTID SUS SCIENTIFICWAME RATANTHERAINTEGRILABLA COMMON-N.UE MONKEYFACE ORCHID
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<fo DIRECTIONS SCATTERED PLANTS BENEATH POWERUNE NEAR FIRE OWER ROAD. LOW. OPEN FIEWACCESS IS JUST SOUTH OF JUNCTION OF TN HI iEOHOATA PTHP.
2 1 t Ill PLANTS IN FLOWER. UNKNOWN NIUMBER OF VEGETTIVE PWITS. ALL PANTS WERE IN THE POWER UNE OPENI GENERAL-D ESCRIPTION LOW. OPEN FIELD WITH PLATANJTHERA OLLARIS AND WOODWARDLA AREOLATA [TNHPAl OPEN POWERUNIE RIOAW I
-COMMENTS 1TNPBESTSOURCESAREJ.ILJONES.N. PHIFIHART.C NOROkAI.AJO B BOWEN. TNHPOATADEDUCE.PIOV. S9I.1 SHAPE FID 535225 As stated above, the Heritage staff has specific guidelines for interpretation of the Arc-Map data when project reviews are performed. For example, if the Heritage database contains a plant record within 5 miles of the proposed project (in this case, within 5 miles of the ROW corridor), botanical personnel conside-it possible for that species to currently inhabit the project area. Other disciplines have different requirements; for example, the search radius for aquatic animals is 10 miles.
Also as described above, Transmission & Power Supply video flyovers are used to determine whether or not the habitat might be present for a given plant along the subject stretch of ROW. For example, a 5-mile search might pull up many possible plants from a reach of ROW, but if the video flyover shows row crops, the row crop area would probably not be marked for special ROW management techniques based on the rare plant record. However, if the video flyovers show anything similar to appropriate habitat, to be conservative the entire possible habitat area is marked With a polygon on the file that is sent to TPS, along with special instructions designed to protect the plant (for example, don't use chemicals; bush-hog instead).
Because of the record of the federally-listed Monkey-Face Orchid, Patricia Cox and Kelly Baxter visited the site before the plants were in flower. After being contacted by the State of Tennessee Heritage staff regarding the presence of the orchids in the ROW, Patricia Cox and Paul Durr revisited the area and found plants occurring in the ROW and growing in the nearby woods. Notes taken from the subsequent field visit are reproduced below:
Field Notes for Great Falls - Pikeville Transmission Line Demolition Project, 23 August 2004
- 1. UTM:16S 0642661/3939236 At the junction of the de-energized line and the "new" line there were eight flowering and many sterile plants oFPlatanthera integrilabia (federal candidate) as well as P. ciliaris growing in the ROWbetween the junction and structure 56. Platanthera integrilabia, Cyperpedium acaule, and Parnassia asarifolia were growing at the edge of the woods near a fire line.
- 2. UTM: 16S o642699/3939336 On the I)e-energized line...between structures 517 and 518 (closer to 517)...There were SIX Platanthera integrilabia plants flowering and many more sterile plants were found in the right of way (very grown up with red maple). These plants were marked with yellow tape.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects
- 3.
UTM: 16S o642689/3939302 Eighteen Flowering and many sterile plants were found in sphagnum at the edge of the woods adjacent to structure 517. The plants were within 1oo yards of the structure. The taxa associated with P.
integrilabia were: Acer rubrurm, Viburnum nudum, Alnus serrulata, Itea virginica, Osmunda cinnamomea, Osmunda regalis, Oxypolis rigidor, Cinna arundinacea, and Dicanthelium acuminatum.
Area w-s flagged with yellow tape.
- 4.
UTM: i6S o643007/3938942 Between structures 514 and 515 on the de-energized line, TWO flowering and many sterile plants of P.
integrilabia were found growing at the edge of the woods in sphagnum. They were growing in a large population of New York fern, Thelypteris novaboracensis. The Parnassia was also seen at this site.
Plants were flagged with yellow tape.
Platant;zera ciliaris and Bartonia virginica were found in abundance along this stretch of ROW between structures 514-515.
- 5. On the left side of the ROW, adjacent to the woods between the road and Structure 516 was one small tree of I'opulus grandidentata, a species of SPCO in TN.
B. Bald Eagle Nesting Sites in Proposed Transmission Line Corridors for Clay and Lowndes Counties, Mississippi In February 2005, a transmission line for the potential development of the Golden Triangle Industrial Park was proposed through Clay and Lowndes Counties, Mississippi.
The proposed transmission line routes were drawn into ArcMap (shown in yellow, orange, and red) and a 3-rnile buffer was added around the proposed routes (shown in purple). The Heritage database layer showed two terrestrial animal records (Black-knobbed Map Turtle and a Heronry) that fell within 3-miles of the proposed routes. Based on the proposed actions and the distances from those actions, there was no concern for either the turtle or the heronry. A Bald Eagle nest location was additionally noted 3.5 miles from the closest proposed route - the distance of this nest from the :proposed actions was also judged to be sufficient (based on U.S. Fish & Wildlife Service guidelines) for the construction activity not to affect any birds that may be present.
ATTACHMENT 1 [Continued]
Listing of TVA &
Working on Transm
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Contract Biologist ission Line Projects I 'a-:.
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Black-knobbed Map Turtle.
2.2 miles from the closest proposed route. :
i Bald Eagle nest location,.
3.5 miles from closest proposed route. Jo
< Heronry, 2.8 miles from the dosest proposed route.
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Wry; The information associated with the Bald Eagle record is shown below.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects
.. MALIAKoiW LIUCC
!oBJECTI 54I5D2 B
EO-ID 24X iSCIENTIFIC-NAME HALAETUS LUCOCEFWUJS COWONNAWE BALD EAGLE ISTATUS
}S-STATUS END tEO RANK C
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131 BESTrSOURCE BROOKS. TIN 1317 FIELD REPORTS FOR BALD EAGLES. OSPFREY.AND HERONS ALONG THE TENNESSEE.TOM3ISTEE WATERWAY IN 134 11%
DATASEUS (ok reTE A
CLASS I
,SP el
,;C 3I
'PREC
'DIRECTIONS NEAR A POND JUST EAST OF OFmCtRS LAKE ROAD AND SouTA OF SECTION LNE ROAD fEODATA BROOKS p(f7 REPORTED THAT AN ACTIVE NEST WAS OBSERVOD AT THIS LOCALITY IN 1N GENERAL.DESCRIPTION <a, COMMENTS SHAPE nIO 53552 Subsequently, however, a letter of concern from owners of the Young farm indicated probable locations of severa.l additional Bald Eagle nests.
A field visit by Hill Henry (Terrestrial Zoology Specialist for TVA Heritage) on February 16, 2005 confirmed two new locations of bald eagle nests. An adult bird was seen on the southern nest, while only a nest structure was found at the nor:hern location. However, the landowners said they had seen adult birds using the northern nest recently.
These two nest locations were plotted on the map, and using the buffer tools in ArcMap, buffers 0.5 mile (blue) and I mile (purple) in radius were created around the bald eagle locations of concern. We were than able to see where they occurred in relation to the different routes that were being proposed.
ATTACHMENT 1 [Continued)
Listing of TVA & Contract Biologist Working on Transmission Line Projects
+27:
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1<1 Initially, the right-of-ways of the first three alternative routes crossed the 0.5 mile buffer zone of at least one of the bald eagle nest locations. After a project meeting in Chattanooga, TN on February 28, 2005 a different route was chosen, (ia black), that avoided all the bald eagle nest locations by at least I mile.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects C. Colbert Fossil Plant Mooring Cell Replacement, Colbert County, AL In May 2005, a walkway and mooring cell at Colbert Fossil Plant were damaged by a barge. The Colbert Barge Unloading Facility is located in Wilson Tailwater/Pickwick Reservoir, where several state and federally-listed mussel species are known to occur. Using ARC-Map (pictured below), a ten mile buffer was drawn around the plant to determine what state and/or federally listed aquatic animal species were present. This resulted in a table including one crayfish, one shrimp, five fish, seven snails, and 44 mussels (ATTACHMENT 2). However, TVA biologists determined that several of these species would not be affected because they are found in caves or tributaries to the Tennessee River and not the river itself. The only species possibly affected by repairing the barge unloading facility would be the mussel and snail species, which could exist within the footprint of the damaged mooring cell. After informal consultation with the Daphne, Alabama office of the USFWS, it was decided that a mussel survey would be conducted to determine whether or not these listed species were present within the project area. The mollusk specialist in the Alabama Department of Conservation and Natural Resources, Division of Wildlife and Freshwater Fisheries (W&FF) was consulted to suggest the best person to conduct the mussel survey. A TVA aquatic biologist and U.S. Fish & Wildlife Service (F&WS) and W&FF personnel were on call during a weekend to hear whether or not there wvere endangered species in the area to remove. If listed species were present, they were to be relocated out of the project area to an area specified by FWS. However, the mussel survey performed by Paul Yokley, malacologist, Yokley Environmental Consulting Service, revealed that no state or federally-listed mussels were present within the barge unloading facility. Based on those findings we were able to say this project would have no effect on listed mussel or snail species and the mooring cell was repaired.
ATTACHMENT 1 [Continued]
Listing of TVA & Contract Biologist Working on Transmission Line Projects
ATTACHMENT 2 Colbert Steam Plant Species Listing
I I
I 1--
1 EO j
I State ScientificName
-ComName ame Feeral State Rank M
D Y
Rank Crustraceans Cambarusjonesi A Troglobitic Crayfish NOST E
S?
Cambarusjonesi A Troglobitic Crayfish NOST E
1 26 1976 S?
Palaemonias alabamae Alabama Blind Cave Shrimp END PROT E
2 23 2000 S?
Palaemonias alabamae Alabama Blind Cave Shrimp END PROT E
2 23 2000 S?
Procambarus pecki A Troglobitic Crayfish NOST E
1 21 1977 S?
Procambarus peckl A Troglobitic Crayfish NOST E
1 26 1976 S?
Fish :
Cyprinella monocha Spotfin Chub THR PROT X
10 27 1937 S?
Elassoma alabamae Spring Pygmy Sunfish PROT X
11 5
1937 S?
_Fthonncrnm= ftr,,-simhh:j To 00f1imh E
nI Dn c I 4tDI 4 nnc I co Etheostoma tuscumbia Tuscumbia Darter PROT X
11 5
1937 S?
Speoplatyrhinus poulsoni Alabama cavefish END PROT E
4 10 1996 S?
Typhlichthys subterraneus Southern Cavefish PROT E
10 6
1999 S?
Typhlichthys subterraneus Southern Cavefish PROT E
1 1996 S?
Typhlichthys subterraneus Southern Cavefish PROT E
2 23 2000 S?
Typhlichthys subterraneus Southern Cavefish PROT H
1 21 1977 S?
- Mussels, Actinonaias ligamentina Mucket NOST H
12 21 1937 S?
Actinonalas ligamentina Mucket NOST H
12 21 1937 S?
Cumberdandia monodonta Spetaclecase C
PROT E
8 11 2000 S?
fCumberlandia monodonta Spetaclecase
{ C lPROT E
8 15 2000 S?
Cumberlandia monodonta Spetaclecase C
PROT E
8 16 2000 S?
Cumberlandia monodonta Spetaclecase C
PROT E
1965 S?
Cyprogenlia stegeria Fanshell END PROT E
8 15 2000 S?
Cyprogenia stegaria Fanshell END PROT E
2001 S?
Cypro genie stegana Fanshell END PROT H
12 21 1937 S?
Cyprogenia stegaria Fanshell END PROT H
8 20 2003 S?
Cyprogenia stegaria Fanshell END PROT H
12 21 1937 S?
Dromus dromas Dromedary Pearlymussel END PROT H
12 21 1937 S?
Dromus dromas Dromedary Pearlymussel END PROT H
12 21 1937 S?
Dromus dromas Dromedary Pearlymussel END PROT X
8 125 2000 S?
Elliptio dilat s
ta Spike NOST H
12 21 1937 S?
Elliptio dilatata Spike NOST H
12 21 1937 S?
Epioblasma arcaeformis lSugarspoon EXT H
12 l 21 l 1937 S?
Epioblasma arcaeformis Sugarspoon EXT H
12 21 1937 S?
Epioblasma biemarginata Angled Riffleshell EXT H
12 21 1937 S?
Epioblasma biemarginata Angled Riffleshell EXT H
12 21 1937 S?
Epioblasma brevidens Cumberland Combshell END PROT H
12 21 1937 S?
Epioblasma brevidens Cumberland Combshell END PROT H
12 21 1937 S?
Epioblasma capsaeformis Oyster Mussel END PROT H
12 21 1937 S?
Epioblasma capsaeformis Oyster Mussel END PROT H
12 21 1937 S?
Epioblasma Flexuosa Leafshell EXT H
12 21 1937 S?
Epioblasma Flexuosa Leafshell EXT H
12 21 1937 S?
Epioblasma florentina florentina Yellow-blossom Pearlymussel END PROT X
8 24 1924 S?
Epioblasma florentina florentina Yellow-blossom Pearlymussel END PROT H
12 21 1937 S?
Epioblasma florentina florentina Yellow-blossom Pearlymussel END PROT H
12 21 1937 S?
Epioblasma haysiana Acornshell EXT H
12 121 1937 S?
Epioblasma haysiana Acornshell l
EXT H
12 _j21 __1937 S?
Epioblasma personata Round Combshell EXT H
12 21 1937 S?
Epioblasma propinqua Tennessee Riffleshell EXT H
12 21 1937 S?
Epioblasma propinqua Tennessee Riffleshell EXT H
12 21 1937 S?
Epioblasma stewardsonii Cumberland Leafshell EXT H
12 21 1937 S?
Epioblasma stewardsonfi Cumberland Leafshell EXT X
S?
Epioblasma stewardsondi Cumberland Leafshell EXT H
12 21 1937 S?
Epioblasma torulosa torulosa Tuberculed Blossom Pearlymussel END PROT X
8 15 2000 S?
Epioblasma torulosa torulosa Tuberculed Blossom Pearlymussel END PROT H
12 21 1937 S?
Epioblasma torulosa torulosa Tuberculed Blossom Pearlymussel END PROT H
12 21 1937 S?
Fusconaia bamesiana Tennessee Pigtoe NOST H
=
Fusconaia cor Shiny Pigtoe END PROT H
12 21 1937 S?
Fusconaia cor Shiny Pigtoe END PROT H
12 21 1937 S?
Fusconala cor Shiny Pigtoe END I PROTl X
S?
Fusconala cor Shiny Pigtoe END PROT X
8 15 2000 S?
Hemistena lata Cracking Pearlymussel END PROT H
0 0
1980 S?
Lampsilis abrupta Pink Mucket END PROT E
6 22 2000 S?
Lampsilis abrupta Pink Mucket END PROT E
8 9
2000 S?
Lampsilis abrupta Pink Mucket END PROT E
6 29 2000 S?
Lampsilis abrupta Pink Mucket END PROT E
8 19 1998 S?
Lampsilis abrupta Pink Mucket END PROT E
8 20 2003 S?
Lampsilis abrupta Pink Mucket END PROT E
8 2
2000 S?
Lampsilis abrupta Pink Mucket END PROT E
7 1
1998 S?
Lampsilis abrupta Pink Mucket END PROT E
6 30 1998 S?
e ampsieW brupta hnt Mnuckct END PROT' E
7 9
i999 Si Lampsilis abrupta Pink Mucket END PROT E
7 23 1997 S?
Lampsilis abrupta Pink Mucket END PROT E
8 11 2000 S?
Lampsilis abrupta Pink Mucket END PROT E
7 25 1997 S?
Lampsilis abrupta Pink Mucket END PROT E
8 31 1999 S?
Lampsilis abrupta Pink Mucket END PROT E
8 23 1999 S?
Lampsilis virescens Alabama Lampmussel END PROT X
S?
Lemiox rimosus Birdwing Pearlymussel END EXT H
12 21 1937 S?
Lemiox rimosus Birdwing Pearlyrmussel END EXT H
12 21 1937 S?
ILexingtonia dolabelloides Slabside Pearlymussel C
PROT H
J S?
Lexingtonia dolabe/loides Slabside Pearlymussel C
PROT H
12 21 1937 S?
Lexingtonia dolabelloides Slabside Pearlymussel C
PROT H
12 21 1937 S?
Ligumia recta Black Sandshell NOST E
8 18 2000 S?
Ligumia recta Black Sandshell NOST E
8 2
2000 S?
Ligumia recta Black Sandshe.l NOST E
6 22 2000 S?
Ligumia recta Black Sandshell NOST E
8 10 2000 S?
Ligumia recta Black Sandshcll NOST E
8 15 2000 S?
Ligumia recta Black Sandshell NOST E
8 16 2000 S?
Ligumia recta Black Sandshell NOST E
8 11 2000 S?
Ligumia recta Black Sandshell NOST E
6 10 2000 S?
Obovaria olivaria Hickorynut EXT H
8 0
1963 S?
Obovaria retusa Ring Pink END PROT H
12 21 1937 S?
I I
I _
_ I
_ I
_ I _
_ I
_ 1 I_
I
lObovaria retusa lRing Pink END lPROT{
E 11 0
l1992l S?
Obovaria retusa Ring Pink END PROT H
12 21 1937 S?
Obovaria retusa Ring Pink END PROT H
8 20 2003 S?
Obovaria subrotunda Round Hickorynut NOST H
12 21 1937 S?
Obovaria subrotunda Round Hickorynut NOST H
7 8
1999 S?
Obovaria subrotunda Round Hickorynut NOST H
12 21 1937 S?
Plethobasus cicatricosus White Wartyback END PROT H
12 21 1937 S?
Plethobasus cicatricosus White Wartyback END PROT E
8 20 2003 S?
Plethobasus cicatricosus White Wartyback END PROT E
8 23 1999 S?
Plethobasus cooperianus Orange-foot Pimpleback END PROT H
0 0
1900 S?
Plethobasus cyphyus Sheepnose C
PROT H
12 21 1937 S?
Plethobasus cyphyus Sheepnose C
PROT E
8 15 2000 S?
1Pkiiifuudsus cypnyus Sneepnose I
PROT E
7 1
1998 S?
Plethobasus cyphyus Sheepnose C
PROT E
7 24 1997 S?
Plethobasus cyphyus Sheepnose C
PROT E
8 20 2003 S?
Plethobasus cyphyus Sheepnose C
PROT E
8 11 1999 S?
Pleurobema clava Clubshell END PROT H
S?
Pleurobema clava Clubshell END PROT H
12 21 1937 S?
Pleurobema clava Clubshell END PROT H
12 21 1937 S?
Pleurobema clava Clubshell END PROT X
8 15 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST H
12 21 1937 S?
Pleurobema cordatum Ohio Pigtoe NOST E
6 22 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
8 15 2000 S?
lPleurobema cordatum lOhio Pigtoe NOST {
E 8
16 12000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
8 10 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST H
3 30 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
8 2
2000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
6 10 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
6 10 2000 S?
Pleurobema cordatum Ohio Pigtoe NOST E
8 11 2000 S?
Pleurobema oviforme Tennessee Clubshell NOST H
12 21 1937 S?
Pleurobema oviforme Tennessee Clubshell NOST H
S?
Pleurobema plenum Rough Pigtoe END PROT H
12 21 1937 S?
Pleurobema plenum Rough Pigtoe END PROT H
9 22 1998 S?
Pleurobema plenum Rough Pigtoe END PROT E
7 1999 S?
Pleurobema plenum Rough Pigtoe END PROT E
6 22 2000 S?
Pleurobema plenum Rough Pigtoe END PROT E { 7 j 7
1999 S?
Pleurobema plenum Rough Pigtoe END PROT H
12 21 1937 S?
Pleurobema rubrum Pyramid Pigtoe PROT E
6 10 2000 S?
Pleurobema rubrum Pyramid Pigtoe PROT H
12 21 1937 S?
Pleurobema rubrum Pyramid Pigtoe PROT E
8 10 2000 S?
Pleurobema rubrum Pyramid Pigtoe PROT E
6 22 2000 S?
Pleurobema rubrum.
Pyramid Pigtoe PROT H
12 21 1937 S?
Pleurobema rubrum Pyramid Pigtoe PROT E
6 27 2000 S?
Pleurobema rubrum Pyramid Pigtoe PROT E
8 15 2000 S?
Potamilus ohiensis Pink Papershell NOST E
9 21 2000 S?
Potamilus ohiensis Pink Papershell NOST E
5 25 2000 S?
Potamilus ohiensis Pink Papershell NOST E
7 27 2000 S?
Ptychobranchus fasciolaris Kidneyshell NOST H
12 21 1937 S?
Ptychobranchus fasciolaris Kidneyshell NOST E
8 16 2000 S?
lPtychobranchus fasciolaris lKidneyshell l
l NOSTI E
8 10 1 20001 S?
Ptychobranchus fasciolaris Kidneyshell NOST E
7 9
1999 S?
Ptychobranchus fasciolaris Kidneyshell NOST H
12 21 1937 S?
Ptychobranchus fasciolaris Kidneyshell NOST E
8 2
2000 S?
Ptychobranchus subtentum Fluted Kidneyshell C
EXT H
12 21 1937 S?
Quadrula cylindrica cylindrica Rabbitsfoot PROT H
8 1 5 2000 S?
Quadrula cylindrica cylindrica Rabbitsfoot PROT H
12 21 1937 S?
Quadrula intermedia Cumberland Monkeyface END PROT H
12 21 1937 S?
Quadrula intermedia Cumberland Monkeyface END PROT H
12 21 1937 S?
Quadrula intermedia Cumberland Monkeyface END PROT X
0 0
1900 S?
Toxolasma cylindrellus Pale Lilliput END PROT H
12 21 1937 S?
Toxolasma cylindrellus Pale Lilliput END PROT H
12 21 1937 S?
Toxolasma lividus Purple Lilliput NOST E
8 9
2000
Toxolasma lividus PurDle LilliDut MCST a
t I
SS I
Toxolasma lividus Purple Lilliput NOST E
7 9
1999 S?
Toxolasma lividus Purple Lilliput NOST E
7 8
1999 S?
Toxolasma lividus Purple Lilliput NOST E
8 15 2000 S?
Toxolasma lividus Purple Lilliput NOST E
8 16 2000 S?
Toxolasma lividus Purple Lilliput NOST E
8 2
2000 S?
Toxolasma lividus Purple Lilliput NOST E
8 17 1999 S?
Toxolasma lividus Purple Lilliput NOST E
9 22 1998 S?
Toxolasma lividus Purple Lilliput NOST E
8 24 1999 S?
Toxolasma lividus Purple Lilliput NOST E
6 30 1998 S?
Toxolasma lividus Purple Lilliput NOST E
8 10 2000 S?
Toxolasma lividus Purple Lilliput NOST E
6 10 2000 S?
Truncilla truncata jDeertoe NOST El 7 1 7 1rgg S I Truncilla truncata Deertoe NOST E
7 8
1999 S?
Truncilla truncata Deertoe NOST E
6 22 2000 S?
Truncilla truncata Deertoe NOST E
8 1
2000 S?
Truncilla truncata Deertoe NOST E
8 9
2000 S?
Villosa taeniata Painted Creekshell NOST H
12 21 1937 S?
Villosa taeniata Painted Creekshell NOST H
12 21 1937 S?
Snails.
Athearnia anthonyi Anthony's River Snail END PROT H
12 21 1937 S?
Athearnia anthonyi Anthony's River Snail END PROT H
12 21 1937 S?
Lithasia geniculata Ornate Rocksnail NOST E
S?
Lithasia lima Warty Rocksnail NOST H
S?
Lithasia salebrosa Muddy Rocksnail NOST E
S?
Lithasia salebrosa Muddy Rocksnail NOST H
12 21 1937 S?
Lithasia salebrosa Muddy Rocksnail NOST H
12 21 1937 S?
_ I
_ I _
_ I _
_ I _
lLithasia verrucosa lVaricose Rocksnail NOST [ H { 12 21 1937 S?
Llnhasia verrucosa Varicose Rocksnail NOST H
12 21 1937 S?
Lithasia verrucosa Varicose Rocksnail NOST E
0 0
1978 S?
Lithasia verrucosa Varicose Rocksnail NOST E
5 0
1977 S?
Pleurocera alveare Rugged Hornsnail NOST H
12 21 1937 S?
Somatogyrus humerosus Atlas Pebblesnail HIST H
12 21 1937 S?
I
r T
[Directions EO Data MCKINNEY PIT CAVE (GCAVEAL033.015).
HOBBS, HOBBS, AND DANIEL (1977) REPORTED THE MC..
SPECIES IN THIS CAVE; THE DATE WAS NOT GIVEN.
KEY AVE(GCAEAL77.03).COOPER (PERS. COMM.) REPORTED THIS SPECIES FROM KEY CAVE (GCAVEALO77.003).
THIS LOCALITY ON JANUARY 26. 1976.
KUHAJDA (PERS. COMM. 1999) REPORTED COLLECTING SHRIMP SPECIMENS FROM THIS LOCALITY SUMMER 1999.
MCKINNEY PIT (GCAVEAL033-003-TV) CAVE.
SPECIMENS ARE UNDER INVESTIGATION BY JOHN COOPER (NC) AND HORTON HOBBS III (OHIO) FOR CORRECT TAXONOMIC IDENTIFICATION. ALSO, KUHAJDA AND MAYDEN (2000) REPORTE KUHAJDA (PERS. COMM. 1999) REPORTED COLLECTING SHRIMP SPECIMENS FROM THIS LOCALITY SUMMER 1999.
ELBOW CAVE (GCAVEAL033-037-TV).
SPECIMENS ARE UNDER INVESTIGATION BY JOHN L.
COOPER (NC) AND HORTON HOBBS III (OHIO) FOR CORRECT TAXONOMIC IDENTIFICATION. ALSO, KUHAJDA AND MAYDEN (2000) REPORTE MCKINNEY PIT. (GCAVEAL033.015). THIS IS TYPE COOPER (PERS. COMM.) REPORTED THE SPECIES FROM LOCALITY FOR THIS SPECIES.
THIS LOCALITY. BOSCHUNG (1976) ALSO REPORTED THIS LOCAITYFOR HISSPECES.SPECIES AT THIS LOCALITY.
COOPER (PERS. COMM.) REPORTED THE SPECIES FROM KEY CAVE (GCAVEAL077*003*TV), LAUDERDALE CO. AL.
THIS LOCALITY. BOSCHUNG (1976) ALSO REPORTED THIS SPECIES FROM THIS LOCALITY.
LITTLE BEAR CREEK, 5.6 AIR KM SOUTHWEST OF ONE SPECIMEN, UMMZ CATALOG NO. 132502 TUSCUMBIA SIX SPECIMENS WERE COLLECTED AT THIS LOCALITY ON CAVE SPRING NOVEMBER 5, 1937 AND ARE STORED IN THE UNIVERSITY OF MICHIGAN MUSEUM OF ZOOLOGY (CAT. NOS. 132689-132690);(PREIMPOUNDMENT COLLECTION).
GILBERT (1887 AND 1891) COMMENTED THAT THE SPECIES WAS EXCEEDINGLY ABUNDANT IN THIS LOCALITY IN 1884 TI IRSC. IMRIA SPRING. Im N
nW TfWNn TUSCUMRIA.
AND 1889 COLLECTIONS. FURTHER COLLECTIONS W. -T -W.REPORTED BY ARMSTRONG (1 971) SEPTEMBER 1962, JULY 1964, APRIL 1965 AND MARCH 1967. ALSO, KUHAJDA AND MAYDEN (199 TWO SPECIMENS COLLECTED THIS LOCALITY ON CAVE SPRING, NEAR SMITHSONIA.
NOVEMBER 5, 1937 AND ARE STORED IN THE UNIVERSITY OF MICHIGAN MUSEUM OF ZOOLOGY (CAT. NO. 132686).
KUHAJDA AND MAYDEN (1996) REPORTED RESULTS OF KEY CAVE, 1.14 AIR MILES NE OF TENNESSEE RIVER 1995-1996 SURVEYS AS TOTAL OF 30-33 INDIVIDUALS MILE248 CAE N. A99 I ALCAV SUVEYOBSERVED DURING FOUR SAMPLING TRIPS (FOR MEAN MILE 248; CAVE NO. AL99 IN AL CAVE SURVEY OF 7.5-8.3 INDIVIDUALS PER TRIP). HOWEVER, THEY INDICATE THAT SOME INDIVIDUALS MAY HAVE BEEN OBSERVED ON MORE THAN ELBOW CAVE (GCAVEAL033-037-TV).
KUHAJDA AND MAYDEN (2000) OBSERVED 1 SPECIMEN ON ELBO CAE (GAVELO3337*V).OCT.
- 6. 1999, DURING SURVEY OF ELBOW CAVE.
KUHAJDA AND MAYDEN (1996) REPORTED 1 (60 MM SL)SPECIMEN COLLECTED, FIN CLIPPED. AND RELEASED KEY CAVE. 1.14 AIR MILES NE TENNESSEE RIVER MILE FROM THIS LOCALITY IN 1996 SURVEY. GODWIN (1996) 248; AL CAVE #99 IN AL CAVE SURVEY.
ALSO REPORTED THIS OBSERVATION. KUHAJDA AND MAYDEN (1996) ALSO REPORTED THAT (PRESUMABLY)
THE SAME INDIVIDUAL HAS COOPER (PERS. COMM.) REPORTED THE SPECIES FROM THIS LOCALITY IN 1977. ALSO, KUHAJDA AND MAYDEN MCKINNEY PIT (GCAVEAL033.015).
(2000) OBSERVED 1 SPECIMEN ON JULY 7,1999: 10 SPECIMENS ON SEPT. 22. 1999; 1 SPECIMEN ON NOV. 9.
1999; AND ALSO 5 SPECIMENS ON FEB. 23, 2000. THREE SPECIMENS W COOPER (PERS. COMM.) REPORTED THE SPECIES FROM THOMASON CAVE (GCAVEALO33.012).
THIS LOCALITY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER MILE 251.3, SEVENMILE ISLAND, SECONDARY CHANNEL.
GARNER (2000) REPORTED 2 LIVE SPECIMENS AT THIS LOCALITY DURING A MUSSEL SURVEY, AUG 11, 2000.
TENNESSEE RIVER MILE 247.0 AND 247.3; SEVENMILE lnJi.wIN Et nuA Ir2rJUI XI Au I VV25i $iifL.IvL' L/Lr"M ISLAD ARA OFWILON DM TALWATRS.SPECIMEN AT TRM 247.0, AUG. 25. 1999. DURING IDSLLAND ARE OFt WILSi ON DAM v Al TA PLWATD E{nf I MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED TENNESSEE RIVER bt: I WEEN BUCK ISLAND AND SEVEN WEATHERED DEAD SHELLS FROM THIS LOCALITY DURING MILE ISLAND. PLOTTED LAT/LONG COORDINATES FRESHWATER MUSSEL SURVEY, JULY 1, 1998. ALSO.
ACCORDING TO DIRECTIONS GIVEN. ALSO, TRM 249.3 GARNER (1999) REPORTED 1 RELIC SPECIMEN AT TRM PLOTS HERE.
249.3, AUG. 2, 1999, DURING FRESHWATER MUSSEL SURVEY. GARNER (2000)
SEVENMILE ISLAND AREA, MUSCLE SHOALS, WILSON DAM TAILWATER OF PICKWICK RESERVOIR, TENNESSEE RIVER MILES 247-253. PLOTTED IN BUCK STANSBERRY (1964) AND ISOM (1969) REPORTED THE ISLAND CHUTE ON SOUTH SIDE OF SEVEN MILE ISLAND. SPECIES FROM THIS LOCALITY.
CA. RIVER MILE 248.9.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND.
GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY. AUG 15, 2000.
TENNSSE RIER ILE249., UPERENDOF UCK GARNER (2001) REPORTED ONE LIVE SPECIMEN (L=49, TENNESSEE RIVER MILE 249.7, UPPER END OF BUCK H46, W=37 MM) AT THIS LOCALITY DURING A SUMMER ISLAD CHTE.2001 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER AT WILSON DAM TAILWATERS. TRM GARNER (2003) REPORTED RELICT SPECIMENS AT THIS 245.1.
LOCATION.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 15, 2000.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
__l SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
CYPRESS CREEK AT FLORENCE. PLOTTED AT CREEK ORTMANN (1925) REPORTED THE SPECIES FROM THIS MILE 4.2 AT UNNUMBERED COUNTY ROAD CROSSING LOCALITY.
(WATERLOO RD). EXACT LOCALITY UNKNOWN.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN ISMITHSONIA, APPROXIMATE RIVER MILE 242.0 ISURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
kHFL L MO'N! LOC.ATED.AT SM THSC:LAND;NG. vNvvEAt AND UtJAHNETTE (1 942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SPECIMENS IN OHIO STATE UNIVERSITY MUSEUM (CAT.
TENNESSEE RIVER AT TUSCUMBIA, ALABAMA. PLOTTED NOS. 10371.2 AND 10371.4) FROM HENRY MOORE'S JUST DOWNSTREAM FROM MOUTH OF SPRING CREEK COLLECTION FROM THIS LOCALITY. SPECIMENS WERE AT RIVER MILE 251.9. EXACT LOCALITY UNKNOWN.
TAKEN IN 1800S, BUT MORE SPECIFIC COLLECTION DATE UNKNOWN.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 15, 2000.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SPRING CREEK AT TUSCUMBIA. EXACT LOCALITY ORTMANN (1925) REPORTED SPECIMENS FROM THIS UNKNOWN.
LOCALITY. DATE OF COLLECTION UNKNOWN.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
ORTMANN (1925) REORTED THE SPECIES COLLECTED BY CYPRESS CREEK AT FLORENCE WALKER FROM THIS LOCALITY. SPEC. EXAMINED BY ORTMANN. COLLECTING DATE UNKNOWN.
TENNESSEE RlVtK MILE 4Y.3, SEVENMILE ISLAND, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 15, 2000.
SPECIMEN FROM MUSCLE SHOALS IN WALKER COLL..
EXAMINED BY ORTMANN; ALSO, DEAD SHELL FOUND BY TENNESSEE RIVER AT HEAD OF SEVEN-MILE ISLAND.
ORTMANN AT FLORENCE: ALSO, DR. PAUL YOKLEY, JR.
MUSCLE SHOALS.
(PERS. COMM.) INDICATED THAT HE HAD COLLECTED SPECIMENS (LIVE OR RELICT??) FROM THIS LOCALITY IN THE 1980'S.
TENNESSEE RIVER MILE 248.0, LOWER END OF GARNER (2000) REPORCTA LITY DURING A SURVEY. JUNE 22.
SEVENMILE ISLAND, SECONDARY CHANNEL.
2000.
TENNESSEE RIVER MILE 253.3, WILSON DAM GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS TAILWATERS.
LOCALITY DURING A MUSSEL SURVEY, AUG 9, 2000.
ERIVER MILE 247.4, SEVENMILE ISLAND, GARNER (2000) REPORTED A LIVE SPECIMEN (3 YEARS SECONDARY N
SHANNELS(MID-CHANNEL)
OLD) AT THIS LOCALITY DURING A MUSSEL SURVEY, JUNE SECODAR CHNNE (MD-CANNL).29.
2000.
KOCH (PERS. COMM.) REPORTED TWO MALES AND ONE FEMALE COLLECTED AND RETURNED ALIVE BY TVA DIVERS AT RIVER MILE 255.8. ISOM (1978) AND GOOCH ET TENNESSE RIVER MI. 252.8-255.8. PLOTTED AT RM 252.8. DVR AT RIEPRMED 2
ISOM (178 A OCHETY AL. (1979) REPORTED 4 SPECIMENS FROM', THIS LOCALITY.
ALSO, GARNER (1998, FIELD NOTES) REPORTED 2 LIVE SPECIMENS AT TENNESSEE RIVER AT WILSON DAM TAILWATERS. TRM GARNER (2003) REPORTED 1 SPECIMEN AT THIS 245.1.
LOCATION.
RICHARDSON (1993) REPORTED AVERAGE DENSITY OF TENNESSEE RIVER MILE 255.5-256.2, 'MCFARLAND PARK 0.11M2 AT MCFARLAND SITE LOCALITY. DIVERS SAMPLED BED') I (RMI255.5)OND'CPES C199 REEKRT SITE ATTRM 0.25 SQUARE METER QUADRAT. TOTAL OF 19 INDIVIDUALS 254.7) IN RICHARDSONFS (N1993)E CREP. DT5 AT TRM OBSERVED: 18 IN LINE TRANSECT AT CYPRESS CREEK 255. THE CENTRUM OF TN RIVER MILES 251-256 ALSO SITE (TRM 254.7) AND ONE AT MCFARLAND SITE (TRM H.
255.5). ALSO, TENNESSEE RIVER AT LOWER END OF BUCK ISLAND, MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED LIVE TRM 249. PLOTTED LAT/LONG COORDINATES SPECIMENS FROM THIS LOCALITY DURING FRESHWATER ACCORDING TO DIRECTIONS GIVEN.
MUSSEL SURVEY, JULY 1. 1998.
TENNESSEE RIVER SECONDARY CHANNEL, ABOVE MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED A PIPPIN TOWHEAD. PLOTTED LAT/LONG COORDINATES WEATHERED DEAD SHELL FROM THIS LOCALITY DURING ACCORDING TO DIRECTIONS GIVEN.
FRESHWATER MUSSEL SURVEY, JUNE 30. 1998.
GARNER (1999) REPORTED 1 RELIC SPECIMEN AT THIS TENNESSEE RIVER MILE 252.0, SEVENMILE ISLAND LOCALITY, JULY 9, 1999, DURING FRESHWATER MUSSEL SURVEY. ALSO, GARNER (1998, FIELD NOTES) REPORTED SECONDARY CHANNEL. TENNESSEE RIVER MILE 252.4 Ii RFI IC lrP~rC!MEM AT TDI 252. A A
A -WSUL.
O S.
FRESHWATER MUSSEL SURVEYS CONDUCTED AUG 17, 1998.
TENNESSEE RIVER, TRM 245.7; T4S, R12W, SECTION 6; GARNER (1997, EMAIL) REPORTED 1 SPECIMEN NEAR HEAD OF BUCK ISLAND. PLOTTED AT ABOVE COLLECTED ON JULY 23, 1997, AT THIS LOCALITY DURING LAT/LONG.
MUSSEL SURVEY.
ISOM (1978) AND GOOCH ET AL. (1979) REPORTED 1 SPECIMEN FROM THIS LOCALITY IN 1978. ALSO, GARNER TENNESSEE RIVER Mi. 251.0 (TRM 251.3 ALSO PLOTS (1999) REPORTED 1 LIVE SPECIMEN FROM THIS LOCALITY, HERE); SEVENMILE ISLAND SECONDARY CHANNEL.
AUG. 23, 1999, DURING A FRESHWATER MUSSEL SURVEY.
ALSO, GARNER (2000) REPORTED ONE LIVE SPECIMEN (AGE 7-8 KOCH REPORTED THIRTEEN INDIVIDUALS OBSERVED IN TENNSSE RIER.PICWICKRESRVOR, LABMA.SHELL PILES HARVESTED BY MUSSEL FISHERMEN.
IN SHELL PILES HARVESTEDCKROESERVOIR, ALABAMA SPECIMENS OLD AND SOMEWHAT ERODED. LAYZER (1999)
SEVENMILE ISLAND. PLOTTED AT RM. 250.0.
REPORTED 2 LIVE SPECIMENS COLLECTED BY JEFF GARNER ON 7/25/97. (ONE WAS FOUND DEAD, 11112/98, AT NORMANDY HATCHERY.
SEVENMILE ISLAND AREA OF WILSON DAM MCGREGOR (PERS. COMM. WITH U.S. FISH & WILDLIFE TAILWATERS, TENNESSEE RIVER MILES 247 TO 253. DOT SERVICE 1998) REPORTED 1 MALE AND 2 GRAVID AT CENTRUM, APPROX. RIVER MILE 249.7. ALSO, A FEMALES FROM STATIONS SPECIFIED BY LAT/LONG IN LOCALITY IN THE MAIN CHANNEL (LAT/LONG 1997. MCGREGOR & GARNER (1997) ALSO REPORTED THIS 344428N/0874543W) AND ONE IN THE SECONDARY RECORD. STANSBERY (1964) REPORTED THE SPECIES CHANNEL (LAT/LONG 344427N/
PRESENT AT THIS LOCAL TENNSSE RIVR MLE 20.7 SEVNMIE ISAND GARNER (1999) REPORTED 1 LIVE SPECIMEN AT TRM SECONDARY CHANNEL.
250.7, AUG. 23.1999, DURING FRESHWATER MUSSEL SECODARYCHANEL.SURVEY.
MILE3.5ATSPRING CREEKAT UUMBAPLOTTED AT CREEK ORTMANN (1925) REPORTED SPECIMENS COLLECTED BY ML35ATSPRING CREEK ATGUOUM FA PLOTTSED.TCRE CALL PRIOR TO 1885. EXACT COLLECTING DATE G.
UNKNOWN.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
SEVENMILE ISLAND AREA. MUSCLE SHOALS. WILSON ISOM (1969). STANSBERY (1964) AND ORTMANN (1924)
DAM DAILWATER, TENNESSEE RIVER MILES REPORTED THE SPECIES FROM THIS LOCALITY. NO (APPROXIMATELY) 247-253.PLOTTED IN BUCK ISLAND SPECIFIC COLLECTION DATES GIVEN.
CHUTE. TFNNFRF:F PIVF:R MIlE 29.5.PCFI OLCTO AESGVN SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER, KOGERS ISLAND, PLOTTED AT TRM GARNER (2000) REPORTED 1 RELIC SPECIMEN AT THIS 239.0.
LOCALITY DURING A MUSSEL SURVEY, AUG 18, 2000.
TENNSSE RIVR MLE 25.3 ACRSS ROMGARNER (2000) REPORTED 1 RELIC SPECIMEN AND 1 LIVE TENNESSEE RIVER MILE 255.3. ACROSS FROM SPECIMEN AT THIS LOCALITY DURING A MUSSEL SURVEY, MCFARAND ARK.AUG
- 2. 2000.
TENNESSEE RIVER MILE 242.2, JUST UPSTREAM OF GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS MULBERRY CREEK.
LOCALITY DURING A MUSSEL SURVEY, JUNE 22, 2000.
TENNESSEE RIVER MILE 253.3. WILSON DAM GARNER (2000) REPORTED 2 LIVE SPECIMENS AT THIS TAILWATERS.
LOCALITY DURING MUSSEL SURVEYS. AUG 9 & 10, 2000.
GARNER (2000) REPORTED 3 LIVE SPECIMENS (2 TENNESSEE RIVER MILES 247.0, 247.2, AND 247.3, FEMALES, 1 MALE) AT TRM 247.0, 1 LIVE SPECIMEN LOWER END OF SEVENMILE ISLAND, PRIMARY AND (FEMALE) AT TRM 247.2, AND 1 LIVE SPECIMEN (L=88MM.
SECONDARY CHANNELS.
AGE 3-4 YRS) AT TRM 247.3 DURING MUSSELS SURVEYS ON JUNE 10 AND AUG 15. 2000.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED 2 LIVE SPECIMENS AT THIS SECONDARY CHANNEL.
LOCALITY DURING MUSSEL SURVEYS, AUG 15 & 16, 2000.
GARNER (2000) REPORTED 2 LIVE SPECIMENS (MALE AND SECONDARY CHANNEL.
FEMALE) AT THIS LOCALITY DURING A MUSSEL SURVEY, SECODARYCHANEL.AUG 11. 2000.
GARNER (2000) REPORTED 3 LIVE SPECIMENS (2 MALES. 1 TENNESSEE RIVER MILE 249.1, BUCK ISLAND CHUTE.
FEMALE) AT THIS LOCALITY DURING A MUSSEL SURVEY, JUNE 10, 2000.
TENNESSEE RIVER. SEVENMILE ISLAND AREA, MUSCLE SHOALS. WILSON DAM TAILWATER OF PICKWICK STNBR 16)ADIO(99 EPTDTH RESERVOIR, APPROXIMATE RIVER MILES 247-253 S
SFROM THIS LOCISOMY1969) REPORTED THE PLOTTED AT RIVER MILE 248.8, 0.8 MILE NORTHWEST OF MOUTH OF LITTLE BEAR CREEK.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATP PEI FARIA!LE 2A.1.B SRVEY.
KROGERS ISLAND AREA OF TENNESSEE RIVER.
TERRY RICHARDSON (PERS. COMM.) REPORTED PLOTTED AT HEAD OF ISLAND.
OBSERVATION OF THIS SPECIES AT THIS LOCALITY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHFI I MinnFl SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER AT WILSON DAM TAILWATERS. TRM GARNER (2003) REPORTED RELICT SPECIMENS AT THIS 245.1.
LOCATION.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
GARNER (1999) REPORTED 1 RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
SEVENMILE ISLAND LOCALITY, JULY 8, 1999, DURING FRESHWATER MUSSEL SECODARYCHANEL.SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER AT WILSON DAM TAILWATERS. TRM GARNER (2003) REPORTED 2 SPECIMENS AT THIS 245.1.
LOCATION.
TENNESSEE RIVER, VICINITY OF SEVENMILE ISLAND, GARNER (E-MAIL TO STUART MCGREGOR) REPORTED PICKWICK RESERVOIR: ONE STATION IN MAIN CHANNEL ONE SPECIMEN IN THE VICINITY OF SEVENMILE ISLAND (344350N/874635W) ONE IN SECONDARY CHANNEL JULY 1999 (COLLECTORS WERE:GARNER. DICK BIGGINS.
(344426N/87461 5W). DOT AT CENTRUM. ALSO, DON HUBBS, & ALAN JONES). ALSO, GARNER (PERS.
TENNESSEE RIVER MILES 248.9. 249.1, 249.6 AND 250.5 COMM.) REPORTED THE FOLLOWING: 1 LIVE ON 8-6-97 (IN PLOT WITH CAPTIVITY WITH SEVENMILE ISLAND AREA. MUSCLE SHOALS, WILSON ISOM (1969) REPORTED SPECIMENS FROM THIS SITE. SEE DAM TAILWATER OF PICKWICK RESERVOIR, APPROX.
ALSO STANSBERY. D. (1964).
TENN. RIV. MI 247-253.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER MILES 249.3-249.8 SEVENMILE GARNER (E-MAIL TO STUART MCGREGOR) REPORTED ISLAND AREA, MUSCLE SHOALS ALSO PLOTS HERE.
ONE SPECIMEN IN THE VICINITY OF SEVENMILE ISLAND PLOTTED AT APPROX. RIVER MILE 250.5. ALSO, PLOTS JULY 1999 (COLLECTORS WERE GARNER, DICK BIGGINS, AT TENNESSEE RIVER AT LEE SIDE OF BUCK ISLAND, DON HUBBS, & ALAN JONES). ALSO, ISOM (1969) AND LOWER END; PLOTTED LATtLONG COORDINATES STANSBERY (1964) REPORTED SPECIMENS FROM THIS ACCORDING TO DIR LOCALITY. DATE OF C
a' MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED LIVE TENNESSEE RIVER AT LOWER END OF BUCK ISLAND, SPECIMENS FROM THIS LOCALITY DURING FRESHWATER TRM 249. PLOTTED LAT/LONG COORDINATES MUSSEL SURVEY. JULY 1. 1998. ALSO, GARNER (1998, ACCORDING TO DIRECTIONS GIVEN. ALSO PLOTS AT FIELD NOTES) CONFIRMED THE ABOVE COt I FrCTInq (AT TRM 249.1.
TRM 249.1: 1 LIVE SPECIMEN; AT TRM 249: 3 LIVE SPECIMENS).
TENNESSEE RIVER, TRM 249.6, NEAR HEAD OF BUCK GARNER (1997, EMAIL) REPORTED 1 SPECIMEN ISLAND.
COLLECTED ON JULY 24. 1997. FROM TRM 249.6 DURING MUSSEL SURVEY.
TENNESSEE RIVER AT WILSON DAM TAILWATERS. TRM GARNER (2003) REPORTED 1 SPECIMEN AT THIS 245.1.
LOCATION.
MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED LIVE TENNESSEE RIVER AT TRM 248.9, DOWNSTREAM OF SPECIMENS FROM THIS LOCALITY DURING FRESHWATER BUCK ISLAND. PLOTTED LAT/LONG COORDINATES MUSSEL SURVEY, JULY 1, 1998. ALSO. GARNER (1999)
ACCORDING TO DIRECTIONS GIVEN.
REPORTED I LIVE SPECIMEN AT TRM 248.9, AUG. 11. 1999, DURING FRESHWATER MUSSEL SURVEY.
TENNSSE RIER T TSCLI~fA EXCT OCAITY ORTMANN (1919) REPORTED SPECIMENS COLLECTED BY TENNESSEE RIVELROAT T ATU RIVER MILE 252.0L H. H. SMITH AT THIS LOCALITY. COLLECTION DATE NOT UNKN WNPLO TEDAT RVER MIL 25.0.GIVEN.
SPECIMENS AT CARNEGIE MUSEUM.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER MILE 249.3. SEVENMILE ISLAND, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 15, 2000.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 248.0, LOWER END OF GARNER (2000) REPORTED TWO LIVE SPECIMENS AT THIS SEVENMILE ISLAND, SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, JUNE 22, 2000.
GARNER (2000) REPORTED ONE LIVE SPECIMEN AT TRM LOWER END OF SEVERMILES2472. 247.3, AND 247.4; 247.2, ONE LIVE SPECIMEN AT TRM 247.3. AND FOUR LIVE SECONDARY CHANNELS.
SPECIMENS AT TRM 247.4. DURING MUSSEL SURVEYS:
SECO DARYCHAN ELS.JUNE
- 10. JUNE 27, JUNE 29, AND AUG 15, 2000.
I TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND.
ONE RELIC SPECIMEN AT THISOLITY DURIS AND SEC YCHNNE.
SURVEYS, AUG 15 AND 16,2000.
TENNESSEE RIVER Mll F 9.A.
Wit SIN DAl GARNER (2000) REPORTED THREE LIVEY PFrIMEN9 AT
_A THIS LOCALITY DURING MUSSEL SURVEYS. AUG 9 AND 10.
TAILWATERS.
12000.
SPRING CREEK AT TUSCUMBIA, LATILONG: 344343N, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS 0874233W. PLOTTED AT CREEK MILE 3.0.
LOCALITY DURING MUSSEL SURVEY. MARCH 30. 2000.
TENNESSEE RIVER MILE 255.3, ACROSS FROM AND AT GARNER (2000) REPORTED SIX LIVE SPECIMENS AT THIS MCFARLAND PARK.
LOCALITY DURING A MUSSEL SURVEY, AUG 2,2000.
TENNESSEE RIVER MILE 247.0, LOWER END OF GARNER (2000) REPORTED TWO LIVE SPECIMENS AT THIS SEVENMILE ISLAND, PRIMARY CHANNEL.
LOCALITY DURING MUSSEL SURVEY, JUNE 10. 2000.
TENNSSE RIER MLE 49.. BCK ILAN CHTE.
GARNER (2000) REPORTED FIVE LIVE SPECIMENS AT THIS TENNESSEE RIVER MILE 249.1. BUCK ISLAND CHUTE.
LOCALITY DURING A MUSSEL SURVEY. JUNE 10. 2000.
TENNSSE RIER ILE251.. SVENILEISLND, GARNER (2000) REPORTED FOUR LIVE SPECIMENS AT SECONDARY CHANNEL.
THIS LOCALITY DURING MUSSEL SURVEYS. AUG 10 AND SECODARYCHANEL.11.2000.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
WILSON DAM TAILWATER OF PICKWICK RESERVOIR, SEVENMILE ISLAND AREA, TENNESSEE RIVER MILE 247-ISOM (1969) REPORTED THE SPECIES FROM THIS 253. PLOTTED AT APPROXIMATE RIVER MILE 249.5 AT LOCALITY. COLLECTION DATE UNKNOWN.
BUCK ISLAND CHUTE.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER AT TRM 241.4 NEAR SMITHSONIA MCGREGOR. O'NEIL, AND GARNER (1998) COLLECTED A BEACON. PLOTTED ACCORDING TO LAT/LONG WEATHERED DEAD SHELL FROM THIS LOCALITY DURING COORDINATES GIVEN IN DIRECTIONS.
FRESHWATER MUSSEL SURVEY, SEPT. 22, 1998.
JEFF GARNER, IN E-MAIL TO STUART MCGREGOR, TENNESSEE RIVER MILE 249.1. ALSO, TENNESSEE REPORTED ONE SPECIMEN IN VICINITY OF SEVENMILE RIVER, UPPER PICKWICK RESERVOIR NEAR SEVEN-MILE ISLAND JULY 1999 (GARNER, R. BIGGINS, DON HUBBS &
ISLAND PLOTS HERE. ALSO, TENNESSEE RIVER MILE ALAN JONES COLLECTORS). ALSO, JEFF GARNER (PERS.
249. AT LOWER END OF BUCK ISLAND PLOTS HERE.
COMM.)REPORTED ONE LIVE FOUND BY HIMSELF & BOB BUTLER AT RIVER MIL SEVNENS RIVER MILE 2~o4N8.0, LOWER END OF GARNER (2000) REPORTED A LIVE SPECIMEN (L=52, H =57.
TENNESSE RIVERND MIEC248.0, LOWNERLNDO W=34 MM) AT THIS LOCALITY DURING A SURVEY. JUNE 22.
SEVEMIL ISLND.SECODAR CHANEL2000.
GARNER (1999) REPORTED 1 LIVE SPECIMEN AT TRM TENNESSEE RIVER MILE 249.9.
249.9. JULY 7, 1999, DURING FRESHWATER MUSSEL SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (19421 FOUND WFATHFRFl DEAf THE TENNESSEE RiVER BANK JUS I SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 247.0, LOWER END OF GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS SEVENMILE ISLAND, PRIMARY CHANNEL.
LOCALITY DURING MUSSEL SURVEY, JUNE 10, 2000.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 251.3, SEVENMILE ISLAND, GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 10, 2000.
TENNESSEE RIVER MILE 248.0, LOWER END OF GARNER (2000) REPORTED ONE LIVE SPECIMEN AND TWO SEVENMILE ISLAND, SECONDARY CHANNEL.
FRESH DEAD SHELLS AT THIS LOCALITY DURING A MUSSEL SURVEY, JUNE 22, 2000.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER MILE 247.4, LOWER END OF GARNER (2000) REPORTED TWO LIVE SPECIMENS AT THIS SEVENMILE ISLAND. SECONDARY CHANNEL.
LOCALITY DURING MUSSEL SURVEY, JUNE 27, 2000.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED ONE RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY CURING A MUSSEL SURVEY. AUG 15 2000.
TENNESSEE RIVER AT COLBERT FERRY BOAT RAMP.
GARNER (2000) REPORTED FOUR FRESH DEAD PLOTTED AT LAT/LONG: 345019N, 0875640W, NEAR SPECIMENS AT THIS LOCALITY DURING MUSSEL SURVEY, RIVER MILE 236.5.
SEPT 21, 2000.
TENNESSEE RIVER 238.9, KOGERS ISLAND, SECONDARY GARNER (2000) REPORTED TWO WEATHERED DEAD CHANNEL.
SPECIMENS AT THIS LOCALITY DURING A MUSSEL SURVEY, MAY 25, 2000.
GARNER (2000) REPORTED ONE WEATHERED DEAD TENNESSEE RIVER MILE 238.4, KOGERS ISLAND.
SPECIMEN. TWO LIVE SPECIMENS, AND ONE FRESH DEAD SECONDARY CHANNEL.
SPECIMEN AT THIS LOCALITY DURING MUSSEL SURVEYS, MARCH 21, APRIL 18, AND JULY 27,2000.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED ONE LIVE SPECIMEN (L=92, TECNNESSE RIVNERMLE 4.3SENMLILAD H=52. W=30 MM, AGE LESS THAN 10 YEARS) AT THIS SECODARYCHANEL.LOCALITY DURING A MUSSEL SURVEY, AUG 16. 2000.
TENNESSEE RIVER MILE 251.3, SEVENMILE ISLAND, GARNER (2000) REPAE D34 YEARS) AT THIS LOCALITY FSECONDARY CHANNEL.
DURING A MUSSEL SURVEY, AUG 10. 2000.
GARNER (E-MAII TO STUART IAPR Cf-1%
R lT'D A I
FAIRLY FRESH DEAD SPECIMEN FROM VICINITY OF TENNESSEE RIVER MILE 252.0. SEVENMILE ISLAND SEVENMILE ISLAND AREA 1999 (COLLECTORS WERE:
AREA, MUSCLE SHOALS, WILSON DAM TAILWATER.
GARNER, DICK BIGGINS, DON HUBBS, & ALAN JONES).
ALSO, STANSBERY (1964) AND ISOM (1969) REPORTED THE SPECIES FROM THIS LO SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 255.3. ACROSS FROM AND AT GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS MCFARLAND PARK.
LOCALITY DURING A MUSSEL SURVEY, AUG 2,2000.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND.
GARNER (2000) REPORTED A RELIC SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY. AUG 15. 2000.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNESSEE RIVER AT TUSCUMBIA CITED FROM HINKLEY, A. 1906. NAUT. 20(3):34-36, (4):40-44, TENNSSEERIVE AT USCUBIA(5):52-55 SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
GARNER (1999) REPORTED 1 LIVE SPECIMEN AT TRM TENNESSEE RIVER MILE 253.5 (AND 253.3 ALSO PLOTS 253.5. JULY 6, 1999, DURING FRESHWATER MUSSEL HERE). WILSON DAM TAILWATERS NEAR SEVENMILE SURVEY. ALSO, GARNER (2000) REPORTED 4 LIVE ISLAND. JUST DOWNSTREAM OF SHEFFIELD BOAT SPECIMENS AT TRM 253.3 DURING MUSSEL SURVEYS.
RAMP.
AUG 2, 3 AND 9. 2000.
SEVENMILE ISLAND AREA OF WILSON DAM GARNER (1999) REPORTED 3 FRESH DEAD AT TRM 251.0, TAILWATERS; TENNESSEE RIVER MILES 247-253. DOT AT ON AUG. 23, 1999; 1 WEATHERED DEAD SPECIMEN AT TRM
- CENTUM, PPRX.
TM 24.7.ALSOINCLDES 250.0, JULY 7, 1999; 2 LIVE SPECIMENS AT TRM 249.8. JULY TENNESSE ARIVERMILES 2497. ALSOALSOL7 i99; 1 FRESH UDAD AT TRM 249.1. JULY 8, 1999; AND TENNESSEE RIVER MILES 251-256.
ALSO I FRESH DEAD AT TRM 249.4, AUG. 2,199 TENNESSEE RIVER MILES 252.03 AND 247.4SLOAND FGARNER (1999) REPORTED 2 WEATHERED DEAD TNESEERMILE 252.0,SECONDARY CHANNEL.
SPECIMENS AT TRM 252.0, JULY 9.1999, DURING SECONDARY CHANNEL.
GFRESHWATER MUSSEL SURVEY.
TENNESSEE RIVER MILE 254.9, ACROUTH OFCYPRESS A
GARNER (1999) REPORTED S LIVE SPECIMENS AT TRM TREESE RE 254.9, JULY 8, 1999. DURING FRESHWATER MUSSEL CREEK.SURVEY.
GARNER (2000) REPORTED NINE LIVE SPECIMENS, 23 TENNESSEE RIVER MILES 247.3 AND 247.4; LOWER END FRESH DEAD SPECIMENS, AND 23 WEATHERED DEAD OF SEVENMILE ISLAND, SECONDARY CHANNEL.
SPECIMENS AT THIS LOCALITY DURING MUSSEL SURVEYS: JUNE 27, JUNE 29, AND AUG 15,2000.
TENNESSEE RIVER MILE 249.3, SEVENMILE ISLAND, GARNER (2000) REPORTED TWO LIVE SPECIMENS AT THIS SECONDARYG CHNEC S GLOCALITY DURING MUSSEL SURVEYS, AUG 15 AND 16, SECODARYCHANEL.2000.
TENNESSEE RIVER MILE 255.3, ACROSS FROM AND AT GARNER (2000) REPORTED SIX LIVE SPECIMENS AT THIS MCFARLAND PARK.
LOCALITY DURING MUSSEL SURVEYS, AUG 1 AND 2,2000.
TENNESSEE RIVER MILE 237.0, LOWERS ISLAND GARNER (1999) REPORTED 1 LIVE SPECIMEN AT TRM ENNESEPRIMARY CHANNEL.
S239.0 AUG. 17,1999, DURING FRESHWATER MUSSEL PRIMAY CHANEL.SURVEY.
TENNESSEE RIVER AT TRM 241.4 NEAR SMITHSONIA MCGREGOR, O-NEIL, AND GARNER (1998) COLLECTED LIVE BEACON. PLOTTED ACCORDING TO LATILONG SPECIMENS FROM THIS LOCALITY DURING FRESHWATER COORDINATES GIVEN IN DIRECTIONS.
MUSSEL SURVEY, SEPT. 22, 1998.
TENNSSE RIER ILE 2560 AD 26.1 ACOSS GARNER ('1999) REPORTED 1 FRESH DEAD SPECIMEN AT TENNSS FLRIERN IES260CNE261.ARS TRM 256.0, AUG. 24,1999, DURING FRESHWATER MUSSEL FROMFLORNCE.SURVEY.
TENNESSEE RIVER SECONDARY CHANNEL, ABOVE MCGREGOR, O'NEIL, AND GARNER (1998) COLLECTED LIVE PIPPIN TOWHEAD. PLOTTED LATIL.ONG COORDINATES SPECIMENS FROM THIS LOCALITY DURING FRESHWATER ACCORDING TO DIRECTIONS GIVEN.
MUSSEL SURVEY, JUNE 30, 1998.
TENNESSEE RIVER MILE 251.3, SEVENMILE ISLAND, GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS SECONDARY CHANNEL.
LOCALITY DURING A MUSSEL SURVEY, AUG 10, 2000.
TENNESSEE RIVER MILE 247.0, LOWER END OF GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS SEVENMILE ISLAND, PRIMARY CHANNEL.
LOCALITY DURING MUSSEL SURVEY, JUNE 10, 2000.
GARNER (1999) REPORTED 1 LIVE SPECIMEN AT TRM 249.9. JULY 7, 1999, DURING FRESHWATER MUSSEL SEVENMILE ISLAND AREA OF WILSON DAM SURVEY. ALSO. GARNER (1998, FIELD NOTES) REPORTED TAILWATERS; TENNESSEE RIVER MILE 249.9.
1 FRESH DEAD SPECIMEN FROM TRM 249.3. AND 1 WEATHERED DEAD SPECIMEN AT TRM 255.7 AS RESULT OF FRESHWATER MUSSEL S SECONDARIERY MNEL 2GARNER (1999) REPORTED 1 FRESH DEAD SPECIMEN AT TENNESSEE RIVER MILE 252.0, SEVNOLNSLAN TRM 252.0, JULY 8,1999, DURING FRESHWATER MUSSEL SECODARYCHANEL.SURVEY.
TENNESSEE RIVER MILE 238.1, JUSDOWNSTFREM O GARNER (2000) REPORTED ONE FRESH DEAD SPECIMEN TCENRS IULAND.
AT THIS LOCALITY DURING A MUSSEL SURVEY. JUNE 22, KOGES ISAND.2000.
TENNESSEE RIVER MILE 255.3, ACROSS FROM GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS MCFARLAND PARK.
LOCALITY DURING A MUSSEL SURVEY, AUG 1. 2000.
TENNESSEE RIVER MILE 253.3. WILSON DAM GARNER (2000) REPORTED ONE LIVE SPECIMEN AT THIS TAILWATERS.
LOCALITY DURING A MUSSEL SURVEY. AUG 9,2000.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (.942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK. ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETYE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA. APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
TENNSSEERIVR MIE 24.8.ISOM (1978) REPORTED 5 SPECIMENS FROM THIS TENNESSEE RIVER MILE 249.8.
LOCALITY. DATE OF COLLECTION UNKNOWN.
TENNESSEE RIVER. TUSCUMBIA. PLOTTED AT APPROX. UNIVERSITY OF MICHIGAN MUSEUM OF ZOOLOGY RIVER MILE 251.9.
CATALOG NO. 43519. COLLECTION DATE UNKNOWN.
TENNESSEE RIVER AT TUSCUMBIA. PLOTTED AT RIVER UNIVERSITY OF MICHIGAN MUSEUM OF ZOOLOGY MILE 252.0.
CATALOG NO. 132453. DATE OF COLLECTION UNKNOWN.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON THE TENNESSEE RIVER BANK JUST SOUTH OF SMITHSONIA, APPROXIMATE RIVER MILE 242.0 WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNErTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD ITHF TENNESSEE R!ER 2NK J SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
GOOCH (1979) REPORTED 12 SPECIMENS FROM THIS TENNESSEE RIVER MILE 252.9.
LOCALITY. GOODRICH (1940) ALSO REPORTED SPECIMENS FROM THIS SITE.
TENNESSEE RIVER AT FLORENCE. ALONG SOUTH ISOM, ET. AL. (1979) REPORTED SPECIMENS FROM THIS SHORE BELOW US HWY 72 BRIDGE.
LOCALITY.
SHELL MOUND LOCATED AT SMITHSONIA LANDING. ON WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD THE TENNESSEE RIVER BANK JUST SOUTH OF SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN SMITHSONIA, APPROXIMATE RIVER MILE 242.0 SURVEY.
SHELL MIDDEN LOCATED ON THE SOUTH SIDE OF THE WEBB AND DEJARNETTE (1942) FOUND WEATHERED DEAD TENNESSEE RIVER AT THE MOUTH OF MULBERRY SHELLS DURING AN ARCHEOLOGICAL SHELL MIDDEN CREEK, ALABAMA. APPROXIMATE RIVER MILE 241.8 SURVEY.
Comments SPEOPLATYRHINUS POULSONI (LE), MYOTIS GRIESCENS (LE) AND PROCAMBARUS (REMOTICAMBARUS) PECK! (AL SPCO) ARE ALSO PRESENT AT THIS LOCALITY.
APPARENTLY THESE SPECIMENS MAY REPRESENT AN ENTIRELY NEW, UNDESCRIBED SPECIES IF NOT ALABAMA CAVE SHRIMP.
APPARENTLY THESE SPECIMENS MAY REPRESENT AN ENTIRELY NEW, UNDESCRIBED SPECIES IF NOT ALABAMA CAVE SHRIMP.
COOPER ALSO REPORTED GYRINOPHILUS PALLEUCUS AND TYPHLICHTHYS SUBTERRANEUS ALSO PRESENT AT THIS LOCALITY.
COOPER ALSO REPORTED MYOTIS GRIESCENS, SPEOPLATYRHINUS POULSONI AND CAMBARUS (AVITICAMBARUS) JONESI PRESENT AT THIS LOCALITY.
JENKINS AND BURKHEAD (1984) MENTION THAT LOCALITY HAS APPARENTLY NOT BEEN RECOLLECTED. ONLY CHANGE AFFECTING STREAM SINCE 1937 IS IMPOUNDMENT AT MOUTH IN 1938. THEY SPECULATE ON POSSIBILITY OF HYPOTHETICAL PARENT POPULATION IN MUSCLE SHOALS
UNSURE # OF VOUCHER SPECIMENS IN EACH OF KUHAJDA AND MAYDEN'S COLLECTIONS, PRESUMABLY FEWER NUMBERS OF VOUCHER SPECIMENS KEPT AND REMAINDFR OF ClI LOT!IN R A~fl THIS IS ONLY KNOWN LOCALITY FOR SPECIES. MAYDEN ET AL. ALSO OBSERVED A SOUTHERN CAVEFISH, TYPHLICHTHYES SUBTERRANEOUS (EOR # 088)IN FEB.
1995. THIS IS FIRST KNOWN OCCURRENCE OF THIS SPECIES AT THIS LOCALITY.
KUHAJDA AND MAYDEN (1996) REPORT THE SPECIES IS SYMPATRIC WITH ALABAMA CAVEFISH (FEDERALLY ENDANGERED), SPEOPLATYRINUS POULSONI (EOR #001) IN KEY CAVE.
COOPER REPORTED GYRINOPHILUS PALLEUCUS AND PROCAMBRUS PECKI ALSO PRESENT.
COOPER REPORTED THAT WESTERN MOST POPULATION OF GYRINOPHILUS PALLEUCUS ALSO OCCURS IN THIS CAVE.
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
4.
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTES SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTES SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 ICORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONuS WiT-i W6it ANU UUJARNE I I E'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 WILLIAMS ET AL. (1993) LISTED THE SPECIES AS ENDANGERED, POSSIBLY EXTINCT. PARMALEE & BOGAN (1998) ALSO NOTED THAT 'THE CUMBERLAND LEAFSHELL HAS NOT BEEN COLLECTED IN OVER 70 YEARS AND IS PRESUMED EXTINCT.'
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 A USFWS FINAL RULE (2001) DESIGNATED E. TORULOSA TORULOSA AS A NONESSENTIAL EXPERIMENTAL POPULATION (NEP) ON JUNE 14, 2001; TO BE REINTRODUCED IN THE REMAINING FREE-FLOWING REACH (-12 MILES) OF THE TN RIVER BETWEEN WILSON DAM AND BACKWATERS CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
EXACT LOCALITY OF EARLIER RECORDS UNKNOWN.
EXACT DATE OF RICHARDSON'S SURVEYS UNSPECIFIED, BUT HIS STUDY BEGAN OCTOBER 1992 AND IS CONTINUING TO PRESENT (OCTOBER 1993).
RICHARDSON (1993) ALSO REPORTED ZEBRA MUSSELS FROM HERE (ATTACHED TO NATIVE MUSSELS).
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 NO COLLECTION DATE ON RECORD CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 A USFWS FINAL RULE (2001) DESIGNATING P. CLAVA A NONESSENTIAL EXPERIMENTAL POPULATION (NEP) WAS ANNOUNCED JUNE 14, 2001: SPECIES WILL BE REINTRODUCED IN THE REMAINING FREE-FLOWING REACH (-12 MILES)
OF THE TN RIVER BETWEEN WILSON DAM AND THE CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 SPECIMEN FOUND IN 1998 AND REPORTED BY GARNER WAS PHOTOGRAPHED, AND IS AWAITING CONFIRMATION.
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMB9ER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 EXTIRPATED FROM MAINSTREAM OF TENNESSEE RIVER CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
1
-1 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTES SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5
CW-CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 5 CORRESPONDS WITH WEBB AND DEJARNETTE'S SITE NUMBER 27
ATTACHMENT 3 Wheeler Reservoir Profiles Taken 1990 -
2005 At Locations: TRM 277.0 (Wheeler Dam Forebay) &
TRM 295.9 (Transition Zone)
Station ID Reservoir River Mile Sample Name Location WEHFB Wheeler TRM 277 ForebaY WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay WEHFB Wheeler TRM 277 Forebay Date Time (C) Temp degC pH SpCond DO %Sat DO mg/l Depth uS/cm meters 01/30/1990 11:55:00 01/30/1990 11:57:00 01/30/1990 11:59:00 01/30/1990 12:01:00 01/30/1990 12:03:00 01/30/1990 12:05:00 01/30/1990 12:07:00 01/30/1990 12:09:00 04/24/1990 12:10:00 04/2411990 12:11:00 04/24/1990 12:12:00 04/24/1990 12:15:00 04/24/1990 12:17:00 04/24/1990 12:19:00 04/24/1990 12:21:00 04/24/1990 12:23:00 05/22/1990 10:35:00 05/22/1990 10:38:00 05/22/1990 10:39:00 05/22/1990 10:42:00 05/22/1990 10:44:00 05/22/1990 10:46:00 05/22/1990 10:48:00 05/22/1990 10:50:00 06/27/1990 10:50:00 06/27/1990 10:53:00 06/27/1990 10:54:00 06/27/1990 10:57:00 06127/1990 10:58:00 06/27/1990 10:59:00 06/27/1990 11:00:00 06/27/1990 11:02:00 06/27/1990 11:04:00 06/27/1990 11:06:00 07/25/1990 10:52:00 9.1 9.1 9
9 9
9 9
9 21.2 19.3 17.8 16.8 16.5 16.4 16.1 15.8 21.8 21.8 21.8 21.8 21.8 21.8 21.9 21.9 28.3 27.9 27.6 27.3 27.2 27.2 27.2 27.1 27.1 27.1 28.5 7.6 7.5 7.5 7.5 7.5 7.5 7.5 7.5 8.9 8.8 8.6 8.5 8.4 8.4 8.3 8
7.8 7.8 7.8 7.8 7.8 7.7 7.7 7.7 8.7 8.8 8.4 7.8 7.6 7.5 7.5 7.5 7.4 7.4 8.7 151 151 150 151 152 152 151 154 148 143 160 158 161 159 157 154 160 160 160 161 161 161 162 162 151 150 148 150 150 150 149 149 145 143 166 11 7 11.5 11.3 11.3 11.3 11.3 11.2 11.3 12.1 11.5 10.3 9.5 8.9 8.8 8.5 8.4 7.6 7.5 7.5 7.5 7.4 7.4 7.4 7.3 10.4 10.7 8.4 6.3 6
5.7 5.7 5.7 5.6
- 5. 6 10.1 n.3 1.5 4
6 8
10 12 13 0.3 1.5 4
6 8
10 12 13 0.3 1.5 4
6 8
10 12 13 0.3 1.5 4
5 6
7 8
9 10 11.8 0.3
WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM
-'vFnBF WhVVeeier TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEH..FB Ea i
vVileeler T RMVI 277 Forebay 277 Forebay 277 Forebay I I Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 277 Forebay 07/25/1990 10:55:00 07/25/1990 10:56:00 07/25/1990 10:57:00 07/25/1990 10:58:00 07/25/1990 11:01:00 07/25/1990 11:03:00 07/25/1990 11:05:00 07/25/1990 11:07:00 08/29/1990 08/2911990 08/29/1990 08/29/1990 08129/1990 08/29/1990 08/29/1990 08/29/1990 08/29/1990 09/26/1990 09/26/1990 09/26/1990 09/26/1990 09/26/1990 09/26/1990 09/26/1990 01/29/1991 01/29/1991 01/29/1991 01/29/1991 01/29/1991 01/29/1991 01/29/1991 03/13/1991 03/13/1991 03/13/1991 03/13/1991 03/13/1991 03/13/1991 9:05:00 9:07:00 9:08:00 9:09:00 9:11:00 9:12:00 9:13:00 9:14:00 9:16:00 8:45:00 8:47:00 8:48:00 8:50:00 8:52:00 8:54:00 8:56:00 8:35:00 8:37:00 8:38:00 8:41:00 8:42:00 8:44:00 8:46:00 8:30:00 8:32:00 8:34:00 8:37:00 8:40:00 8:42:00 28.4 28.3 28.1 28 27.8 27.8 27.7 27.7 29.8 29.8 29.7 29.4 28.7 28.7 28.5 28.5 28.4 23.9 24 24 24.1 24.1 24.1 24.1 7
7 7
7 7
7 7
10.4 10.4 10.4 10.4 10.4 10.4 8.7 8.6 8.4 8.3 8
7.8 7.7 7.4 8.3 8.3 8.2 7.6 7.2 7.3 7.1 7
6.9 7.8 7.8 7.8 7.8 7.8 7.8 7.8 7.6 7.7 7.7 7.7 7.8 7.8 7.8 7.74 7.69 7.65 7.63 7.61 7.6 165 162 162 160 159 158 154 150 165 164 162 163 163 162 161 160 158 185 183 182 180 176 174 173 188 186 185 181 179 173 173 148 146 143 140 140 138 10.1 9.8 R8R 8.4 7.6 7.3 6.9 6.7 9.4 9.3 8.9 7.5 5.2 5.1 4.8 4.6 4.3 6.9 6.8 6.8 6.8 6.8 6.8 6.8 10.8 10.7 10.6 10.6 10.6 10.6 10.5 10.7 10.7 10.7 10.7 10.7 10.7 1.5 2
I 4
6 8
10 11 0.3 1.5 3.5 4
5 6
8 10 12 0.3 1.5 4
6 8
10 10.4 0.3 1.5 4
6 8
10 10.8 0.3 1.5 4
6 8
10
WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM WEHFB Wheeler TRM 277 Forebay 03/13/1991 277 Forebay 03/27/1991 277 Forebay 03/27/1991 277 Fnrehny nvsI7I1O00O 277 Forebay 03/27/1991 277 Forebay 03/27/1991 277 Forebay 03/27/1991 277 Forebay 03/27/1991 277 Forebay 04109/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/09/1991 277 Forebay 04/18/1991 277 Forebay 04/18/1991 277 Forebay 04/18/1991 277 Forebay 04/18/1991 277 Forebay 04/18/1991 277 Forebay 04(18/1991 277 Forebay 04/18/1991 277 Forebay 04118/1991 277 Forebay 04/24/1991 277 Forebay 04124/1991 277 Forebay 04/24/1991 277 Forebay 04/24/1991 277 Forebay 04/24/1991 277 Forebay 04/24/1991 277 Forebay 04/24/1991 277 Forebay 04/24/1991 277 Forebay 05/08/1991 277 Forebay 05/08/1991 277 Forebay 05/08/1991 277 Forebay 05/08/1991 277 Forebay 05108/19N1 8:44:00 7:50:00 7:52:00 7-ZA *nr 7:56:00 7:58:00 8:00:00 8:02:00 8:30:00 8:32:00 8:34:00 8:36:00 8:38:00 8:40:00 8:42:00 8:44:00 8:00:00 8:02:00 8:04:00 8:06:00 8:08:00 8:10:00 8:12:00 8:14:00 8:10:00 8:12:00 8:14:00 8:16:00 8:18:00 8:20:00 8:22:00 8:24:00 8:00:00 8:02:00 8:04:00 8:06:00 8R:08:0 10.3 16 15.9 40 f%
evv 15.9 15.6 15.4 15.3 17.4 17.3 17.1 16.5 16.1 15.4 15.3 15.2 19 18.9 18.7 18.5 18.3 18.3 18.3 18.2 18.3 18.3 18.3 18.3 17.9 17.8 17.8 17.8 20.2 20.2 20.2 20 20 7.59 7.81 7.81
~7 7 1.1 1 7.77 7.77 7.75 7.74 7.98 7.96 7.83 7.7 7.62 7.54 7.52 7.51 7.49 7.46 7.43 7.42 7.41 7.41 7.4 7.39 7.65 7.64 7.63 7.61 7.63 7.61 7.6 7.6 7.59 7.59 7.58 7.56 7 Z)
I.._
133 145 144 Iiqi 139 139 138 135 151 151 153 154 162 149 152 154 147 148 148 152 150 149 149 147 152 152 153 155 164 167 168 169 145 145 146 147 4 A7 1'.7 10.6 10 9.6 9.6 9.6 9.7 9.8 9.8 11.2 11.1 10.7 10.3 10.2 9.6 9.8 9.6 7.9 7.6 7.5 7.5 7.4 7.4 7.4 7.3 7.9 7.9 7.9 7.9 7.8 7.9 7.8 7.8 7.8 7.8 7.8 7.6
,.5 12 0.3 1.5 4
6 8
10 12 0.5 1.5 4
6 8
10 12 13.2 0.5 1.5 4
6 8
10 12 13.7 0.5 1.5 4
6 8
10 12 13.3 0.5 1.5 4
6 8
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- Flow 10,000 cfs
- Upstream ambient temperature 870F E BFN
- Three units in service and operating at extended power uprate (120 percent of original licensed thermal power)
- Six cooling towers - four Ecodyne 16 cell towers, one Balcke-Durr 16 cell tower, and one Balcke-Durr 20 cell tower
- All cooling towers in service
- Intake flow 4490 cfs
- Diffuser flow (all three units combined) 4410 cfs
- Diffuser effluent temperature 97.4'F
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ATTACHMENT 7 Table 1.
Class Definitions for Transmission ROW's vegetation management of TVA Table 2.
Class Definitions and Associated Polygon Colors of Sensitive Areas for line or pole maintenance on TVA transmission
/
I I
Table 1. Class Definitions for vegetation management of TVA Transmission ROW's Terrestriai Piants (A), Terrestrial Animals (D). and Aquatic Animals (E)
I Class Restriction if Sensitive area in ROW Restriction for Sensitive Areas Polygon Color Potentially Affected I
No broadcast spraying. Use one of the three following alternatives: 1)
Not Applicable Yellow Hand or mechanical clearing, 2) Request field surveys by TVA Heritage staff to determine if suitable habitat for these species exists in the subject area, 3) Selective spraying of herbicides to shrubs or tree saplings less than 12 feet in height.
2 HIand-clearing only. Vehicles and equipment restricted from area unless Vehicles and equipment restricted from Red confined to existing access road.
area unless confined to existing access road.
3 Special circumstance (specified by documentation accompanying that ROW review).
Orange Botany: listed plant recorded from within ROW. Please contact Heritage botanist prior to entering or conducting maintenance activities in subject area.
Terrestrial Animals: if project occurs during the breeding season (March to mid-July), a Heritage terrestrial zoologist must be contacted prior to conducting the work. If outside this time period, no restrictions are necessary.
Wetlands* C)
Wetlands obtained from National Wetland Inventory data. Refer to "Wetlands ROW and Pole Replacement Blue Outline Guidelines" for restrictions.
I Potential wetlands identified by Natural Heritage wetland biologists based on interpretation of topographic Pink Outline features, water bodies, soil surveys and proximity to NWI features. Wetlands biologists will make recommendations specific to the situation Natural Arcas (B Class Call*
Definition Color I
No Same as Class I definition above.
Yellow 2
No Same as Class 2 definition above.
Red I
Yes Same as Class I definition above, and must contact area manager prior to Yellow hatching 2
Yes Same as Class 2 definition above, and must contact area manager prior to entering or conducting Red hatching maintenance in subject area.
3 Yes Must contact area manager prior to entering or conducting maintenance in subject area.
Neon Green 4
Special circumstance (specified by documentation accompanying that ROW review).
Green
-f.^ -
ds
-taP.I*L url.euude iii ihlis p ckaLe.
- The "Call" column on the accompanying datasleets is used by Natural Area specialists only.
A blank in the column indicates.no call is necessary.
hle 2. Class Definitions and Associated Polygon Colors of Sensitive Areas for line or pole maintenance on TVA transmission lines.
All Resources Areas (Plants. Natural Areas. Wetlands. Terrestrial Animals. and Aauatic Animals)
Class Restri tion Color I
Botany: Sensitive Botanical resources are known from the area. Details of proposed Pink activities should be submitted to TVA Heritage staff to determine if the proposed activities require restrictions.
Natural Areas: Refer to table accompanying project for restrictions.
Wetlands: Potential wetlands identified by Natural Heritage wetland biologists based on interpretation of topographic features, water bodies, soil surveys and proximity to NWI features. Refer to wetlands ROW and pole replacement guidelines (below) for restrictions.
Terrestrial Animals: Refer to table accompanying project for restrictions.
Aquatic Animals: Refer to table accompanying project for restrictions.
Wetlands lWetlands obtained from National Wetland Inventory data. Wetlands biologists will Blue Outline l make recommendations specific to the situation I