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HomeMy WebLinkAboutLTN Appendix IV Appendix IV DWQ Water Quality Monitoring Programs in the Little Tennessee River Basin Appendices A-IV-1 DWQ Water Quality Monitoring Programs in the Little Tennessee River Basin Staff in the Environmental Sciences Section (ESS) and Regional Offices of DWQ collect a variety of biological, chemical and physical data. The following discussion contains a brief introduction to each program, followed by a summary of water quality data in Little Tennessee River basin for that program. For more detailed information on sampling and assessment of streams in this basin, refer to the Basinwide Assessment Report for the Little Tennessee River basin, available from the Environmental Sciences Branch website at http://www.esb.enr.state.nc.us/bar.html or by calling (919) 733-9960. DWQ monitoring programs for the Little Tennessee River Basin include: • Benthic Macroinvertebrates • Fish Assessments • Aquatic Toxicity Monitoring • Lake Assessment • Ambient Monitoring System Benthic Macroinvertebrate Monitoring Benthic macroinvertebrates, or benthos, are organisms that live in and on the bottom substrates of rivers and streams. These organisms are primarily aquatic insect larvae. The use of benthos data has proven to be a reliable monitoring tool, as benthic macroinvertebrates are sensitive to subtle changes in water quality. Since macroinvertebrates have life cycles of six months to over one year, the effects of short-term pollution (such as a spill) will generally not be overcome until the following generation appears. The benthic community also integrates the effects of a wide array of potential pollutant mixtures. Criteria have been developed to assign a bioclassification to each benthic sample based on the number of different species present in the pollution intolerant groups of Ephemeroptera (Mayflies), Plecoptera (Stoneflies) and Trichoptera (Caddisflies), commonly referred to as EPTs. A Biotic Index (BI) value gives an indication of overall community pollution tolerance. Different benthic macroinvertebrate criteria have been developed for different ecoregions (mountains, piedmont, coastal plain and swamp) within North Carolina and bioclassifications fall into five categories: Excellent, Good, Good-Fair, Fair and Poor. Overview of Benthic Macroinvertebrate Data Based on benthic macroinvertebrate data, water quality in the Little Tennessee River basin is Excellent to Good. Since 1999, 80 benthic macroinvertebrate basinwide samples have been collected with 48 (60%) receiving Excellent bioclassifications, 24 (30%) resulting in Good bioclassifications, five (6%) receiving Good-Fair bioclassifications, and three (4%) receiving Fair bioclassifications. Comparisons of benthos data from 1999 to 2004 between repeat sites show that three sites (Cowee Creek, Whiteoak Creek, and the Tuckasegee River) improved from Good to Excellent, one site (Little Tennessee River off SR 1629) improved from Fair to Good- Fair, one site improved from Good-Fair to Good (Little Tennessee River at SR 1651), and Middle Creek improved from Good-Fair to Excellent. However, nine sites (Cullasaja River at US64/SR 1688 and at SR 1678, Cartoogechaye Creek, Conley Creek, Noland Creek, Panther Creek, Stecoah Creek, Tulula Creek, and Cheoah Creek) declined from Excellent to Good. Overall water quality in the Little Tennessee River is generally unchanged since 1999. A-IV-2 Several rare invertebrate taxa were collected in the Little Tennessee River basin in 2004 including the mayflies Serratella spiculosa (Turtle Pond Creek), Rhithrogena fuscifrons (Turtle Pond Creek, Bradley Fork, Hazel Creek), Rhithrogena exilis (Cullowhee Creek, Nantahala River, Whiteoak Creek, Deep Creek) Nixie, (Bradley Fork), the caddisflies Molanna tryphena, Agarodes (Iotla Creek), Mayatrichia ayama, Oecetis avara (Snowbird Creek), Rhyacophila amicis, Neotrichia (Hazel Creek), Micrasema rickeri (Cheoah River), and the stoneflies Agnetina flavescens (Oconaluftee River, Forney Creek, Hazel Creek, Deep Creek), and Beloneuria (Whiteoak Creek). Of particular interest, Caney Fork at SR 1740 set the second highest EPT diversity (54) and total species diversity (107) ever recorded in the Little Tennessee River basin. For detailed information regarding the samples collected during this assessment period, refer to the tables at the end of this appendix. Assessing Benthic Macroinvertebrate Communities in Small Streams The benthic macroinvertebrate community of small streams is naturally less diverse than the streams used to develop the current criteria for flowing freshwater streams. The benthic macroinvertebrate database is being evaluated and a study to systematically look at small reference streams in different ecoregions is being developed with the goal of finding a way to evaluate water quality conditions in such small streams. Presently, a designation of Not Impaired may be used for flowing waters that are too small to be assigned a bioclassification (less than 4 meters in width) but meet the criteria for a Good-Fair or higher bioclassification using the standard qualitative and EPT criteria. This designation will translate into a use support rating of Supporting. However, DWQ will use the monitoring information from small streams to identify potential impacts to small streams even in cases when a use support rating cannot be assigned. DWQ will use this monitoring information to identify potential impacts to these waters even though a use support rating is not assigned. DWQ will continue to develop criteria to assess water quality in small streams. Fish Assessments Twenty two sites were sampled from mid-May to early June 2004; 19 of the sites had not been previously sampled. Fish communities in the basin were last sampled in 1995. The most commonly collected species in 2004 was the mottled sculpin (collected at all sites); the central stoneroller and the northern hog sucker were collected at 21 of the 22 sites. The mottled sculpin was also the most abundant species, representing about one-third of all the fish collected. Seventeen of the 22 streams were evaluated using the North Carolina Index of Biotic Integrity (NCIBI). NCIBI ratings ranged from Fair to Excellent with the scores ranging from 38 to 58. The streams rated Fair and Excellent were the Little Tennessee River and Burningtown Creek, respectively. The remaining five streams were not evaluated using the NCIBI, were considered trout streams, and were not assigned a rating. However, Stecoah Creek did show signs of being degraded. A-IV-3 For detailed information regarding the samples collected during this assessment period, refer to the tables at the end of this Appendix. Aquatic Toxicity Monitoring Acute and/or chronic toxicity tests are used to determine toxicity of discharges to sensitive aquatic species (usually fathead minnows or the water flea, Ceriodaphnia dubia). Results of these tests have been shown by several researchers to be predictive of discharge effects on receiving stream populations. Many facilities are required to monitor whole effluent toxicity (WET) by their NPDES permit or by administrative letter. Other facilities may also be tested by DWQ’s Aquatic Toxicology Unit (ATU). Per Section 106 of the Clean Water Act, the ATU is required to test at least 10 percent of the major discharging facilities over the course of the federal fiscal year (FFY). However, it is ATU’s target to test 20 percent of the major dischargers in the FFY. This means that each major facility would get evaluated over the course of their five-year permit. There are no requirements or targets for minor dischargers. The ATU maintains a compliance summary for all facilities required to perform tests and provides monthly updates of this information to regional offices and DWQ administration. Ambient toxicity tests can be used to evaluate stream water quality relative to other stream sites and/or a point source discharge. Three facility permits in the Little Tennessee River basin currently require whole effluent toxicity (WET) monitoring. All three facility permits have a WET limit. Across the state, the number of facilities required to perform WET has increased steadily since 1987, the first year that WET limits were written into permits in North Carolina. Consequently, compliance rates have also risen. Since 1996, the compliance rate has stabilized at approximately 90 percent. The following graph summaries WET monitoring compliance in the Little Tennessee River basin from 1987 to 2002. Facilities with toxicity problems during the most recent two-year review period are discussed in subbasin chapters. A-IV-4 0 1 2 3 4 19 8 7 19 8 8 19 8 9 19 9 0 19 9 1 19 9 2 19 9 3 19 9 4 19 9 5 19 9 6 19 9 7 19 9 8 19 9 9 20 0 0 20 0 1 20 0 2 20 0 3 20 0 4 Year Fa c i l i t i e s M o n i t o r i n g 0 10 20 30 40 50 60 70 80 90 100 Co m p l i a n c e ( % ) No. Facilities % Meeting Permit Limit Lakes Assessment Program Ten lakes were sampled in the Little Tennessee River Basin by DWQ in 2004. All of these lakes were sampled three times during the summer (June, July and August). Lake Sequoyah and Wolf Creek Reservoir were also sampled in September as part of an extended sampling period special study. Data collected during this sampling effort determined sedimentation concerns related to construction are a factor at several of the lakes. Local efforts need to be directed towards preventing sedimentation into the tributaries of these lakes. Lakes with noted water quality impacts are discussed in the appropriate subbasin chapter. Ambient Monitoring System The Ambient Monitoring System (AMS) is a network of stream, lake and estuarine stations strategically located for the collections of physical and chemical water quality data. North Carolina has more than 378 water chemistry monitoring stations statewide, including 7 stations in the Little Tennessee River basin, although 2 of those stations were discontinued in 2000. Between 23 and 32 parameters are collected monthly at each station. The locations of these stations are listed in the following table and shown on individual subbasin maps. Notable ambient water quality parameters are discussed in the subbasin chapters. Refer to 2005 Little Tennessee Basinwide Assessment Report at http://www.esb.enr.state.nc.us/bar.html for more detailed analysis of ambient water quality monitoring data. A-IV-5 Locations of Ambient Monitoring Stations in the Roanoke River Basin by Subbasin Subbasin/ Station ID Location Class Lat. Long. County Map ID 01 Little Tennessee River, Cullasaja River, and Cartoogechaye Creek G0035000 Little Tennessee River at SR 1651 near Prentiss C 35.1221 -83.3743 Macon A1 G01300001 Cartoogechaye Creek at SR 1152 near Franklin B Tr 35.1580 -83.3920 Macon A2 G2000000 Little Tennessee River at NC 28 at Iotla B 35.2349 -83.3958 Macon A3 02 Oconaluftee River, Tuckasegee River, Hazel Creek, and Deep Creek G85500002 Oconaluftee River at SR 1359 at Birdtown C Tr 35.4610 -83.3540 Jackson A4 G8600000 Tuckasegee River at SR 1364 at Bryson City B 35.4284 -83.4460 Swain A5 03 Nantahala River G3500000 Nantahala River at US 64 near Rainbow Springs B Tr ORW 35.0942 -83.5599 Macon A6 04 Cheoah River G9550000 Cheoah River at SR 1138 at Robbinsville C Tr 35.3291 -83.8098 Graham A7 1Station G0130000 ceased sample collection on 5/25/2000. 2Station G8550000 ceased sample collection on 5/23/2000. Benthic Macroinvertebrate Data Collected in the Little Tennessee River Basin, 1999 – 2004 (Current basinwide sampling sites are in bold print.) Sub/Waterbody Location County Index No. Date ST EPT BI EPTBI BioClass 040401 L Tennessee R SR 1629 Macon 2-(1) 7/21/2004 70 22 5.59 3.81 Good-Fair 9/11/2000 67 15 6.29 3.99 Fair 8/12/1999 60 14 6.23 4.75 Fair L Tennessee R SR 1651 Macon 2-(1) 7/22/2004 93 37 5.46 3.95 Good 10/20/1999 62 29 4.42 3.49 Good-Fair L Tennessee R NC 28 Macon 2-(1) 7/22/2004 70 32 5.3 4.28 Good-Fair 8/24/1999 86 32 5.3 3.75 Good-Fair Middle Cr SR 1635 Macon 2-(8) 7/22/2004 --- 43 --- 2.93 Excellent 8/24/1999 --- 25 --- 4.15 Good-Fair Tessentee Cr SR 1684 Macon 2- 9 7/22/2004 --- 47 --- 3.02 Excellent Coweeta Cr SR 1114 Macon 2-10 7/22/2004 --- 45 --- 2.62 Excellent 8/21/1999 --- 39 --- 3.01 Excellent Cartoogechaye Cr SR 1146 Macon 2-19-(1) 7/21/2004 --- 31 --- 3.70 Good 8/24/1999 --- 41 --- 3.05 Excellent Jones Cr SR 1303 Macon 2-19-2 7/21/2004 --- 38 --- 3.07 Excellent Cullasaja R US 64 Macon 2-21-(0.5) 7/21/2004 58 14 5.74 4.67 Fair 7/25/2001 41 10 6.55 5.93 Fair 8/28/2000 65 18 6.34 5.13 Fair 6/23/1999 47 14 5.70 4.97 Fair Cullasaja River River Court Macon 2-21 (0.5) 7/26/2001 56 16 5.77 4.64 Not Rated 5/16/2000 61 25 4.85 3.71 Not Impaired Cullasaja River US 64, ab Dry Falls Macon 2-21 (0.5) 8/11/2000 20 20 4.17 4.17 Good-Fair UT Cullasaja River US 64 Macon 7/25/2001 46 23 3.32 2.39 Not Impaired Salt Rock Branch Highlands Falls Macon 2- 21 1 7/26/2001 43 5 6.54 5.52 Not Rated Ammons Branch Spruce Lane Macon 2-21 2 7/25/2001 47 20 2.94 1.15 Not Impaired Mill Creek 5th Street Macon 2-21 3 8/29/2000 41 11 6.14 5.36 Not Rated 5/17/2000 37 13 5.54 4.51 Not Rated Mill Creek Brookside Lane Macon 2-21 3 8/28/2000 47 17 5.48 4.51 Not Rated Big Creek SR1538 Macon 2-21 5 1 (0.5) 7/25/2001 49 29 2.86 2.22 Good 8/29/2000 103 41 3.52 2.44 Excellent Big Creek SR 1548, Ab WTP Macon 2-21 5 1(0.5) 9/11/2000 30 30 2.92 2.92 Good Houston Branch Simon Speed Rd Macon 2-21 5 1 3 (2) 8/29/2000 47 25 2.65 1.95 Not Impaired Cullasaja R Off US 64, Jackson H Macon 2-21 (5.5) 8/5/2004 77 36 4.21 3.44 Good 6/22/1999 49 2.70 2.86 Excellent Cullasaja R US 64/SR 1668 Macon 2-21 (5.5) 8/5/2004 86 42 4.68 3.84 Good 8/10/1999 99 51 3.94 3.32 Excellent N Skitty Creek N Cliffside Rec Area Macon 2-21 6 1 8/29/2000 45 28 2.35 1.62 Not Impaired Turtle Pond Cr SR 1620 Macon 2-21 8 7/23/2004 --- 49 --- 2.10 Excellent A-IV-6 6/22/1999 --- 42 --- 1.90 Excellent Walnut Cr SR 1533 Macon 2-21 17 8/6/2004 68 38 2.94 2.16 Excellent 6/21/1999 34 34 2.04 2.04 Good Iotla Cr SR 1372 Macon 2-27 7/22/2004 73 32 4.8 3.94 Good 8/10/1999 --- 35 --- 3.84 Good Iotla Cr SR 1485 Macon 2-27 7/22/2004 48 35 3.9 3.53 Good Cowee Cr NC 28 Macon 2-29 7/22/2004 --- 38 --- 3.24 Excellent 8/10/1999 --- 35 --- 3.06 Good Burningtown Cr SR 1371 Macon 2-38 8/3/2004 --- 43 --- 3.12 Excellent 8/10/1999 --- 39 --- 3.20 Excellent Burningtown Cr SR 1392 Macon 2 38 8/3/2004 68 34 3.18 2.51 Good Tellico Cr SR 1367 Macon 2 40 8/3/2004 93 44 3.62 2.68 Excellent 8/9/1999 108 54 3.57 2.62 Excellent 040402 L Tennessee R off SR 1113 Swain 2-(1) 8/5/2004 95 42 4.33 3.35 Good 8/9/1999 75 31 4.74 3.67 Good Alarka Cr SR 1185 Swain 2-69-(2.5) 8/2/2004 101 46 3.80 2.67 Excellent 8/9/1999 86 51 3.66 3.11 Excellent Tuckasegee R SR 1140 Jackson 2-79-(0.5) 8/2/2004 36 36 1.83 1.83 Excellent 7/19/1999 46 46 1.96 1.96 Excellent Sub/Waterbody Location County Index No. Date ST EPT BI EPTBI BioClass Caney Fk SR 1740 Jackson 2-79-28-(2.5) 8/2/2004 107 54 3.63 2.68 Excellent 7/20/1999 97 53 3.68 3.03 Excellent Moses Cr SR 1739 Jackson 2-79-28-8 8/2/2004 46 46 1.71 1.71 Excellent 7/20/1999 37 37 1.91 1.91 Excellent Cullowhee Cr SR 1001 Jackson 2-79-31 8/4/2004 --- 47 --- 2.61 Excellent 7/20/1999 43 43 2.96 2.96 Excellent Savannah Cr SR 1367 Jackson 2-79-36 8/4/2004 91 40 4.15 3.11 Good 7/21/1999 53 32 3.80 3.48 Good Tuckasegee R off SR 1378 Jackson 2-79-(38) 8/4/2004 84 44 4.27 3.44 Excellent 7/21/1999 75 40 4.39 3.82 Good Scott Cr SR 1556 Jackson 2-79-39 8/4/2004 74 35 4.07 3.23 Good 7/21/1999 70 36 4.14 3.22 Good Conley Cr off SR 1177 Swain 2-79-39 8/3/2004 34 34 2.82 2.82 Good 7/21/1999 --- 44 --- 3.17 Excellent Bradley Fk off US 441 Swain 2-79-55-12-(11) 8/3/2004 79 47 2.59 2.02 Excellent 7/22/1999 67 39 2.67 1.87 Excellent Oconaluftee R SR 1359 Swain 2-79-55-(16.5) 8/5/2004 106 51 3.96 2.97 Excellent 7/22/1999 104 53 3.93 3.20 Excellent Deep Cr AB Campground Swain 2-79-63-(16) 8/2/2004 --- 43 --- 2.13 Excellent 8/9/1999 --- 47 --- 2.67 Excellent Deep Cr SR 1340 Swain 2-79-63-(21) 8/2/2004 --- 38 --- 2.18 Excellent 8/9/1999 --- 45 --- 2.95 Excellent Noland Cr near mouth Swain 2 90 8/3/2004 --- 35 --- 1.92 Good 8/11/1999 --- 40 --- 1.98 Excellent Forney Cr near mouth Swain 2 97 8/3/2004 78 44 2.58 1.80 Excellent 8/11/1999 81 46 2.66 1.68 Excellent Panther Cr SR 1233 Graham 2 115 8/4/2004 --- 35 --- 2.07 Good 8/10/1999 --- 39 --- 2.24 Excellent Stecoah Cr SR 1237 Graham 2 130 8/4/2004 --- 30 --- 2.94 Good 8/11/1999 --- 39 --- 3.02 Excellent Hazel Cr near mouth Swain 2-146-(19) 8/3/2004 96 46 3.26 2.17 Excellent 8/11/1999 106 56 2.95 1.97 Excellent Twenty Mile Cr NC 28 Swain 2-178-(4) 8/4/2004 --- 29 --- 2.15 Good 040403 Nantahala R FSR 437 Macon 2-57-(0.5) 7/21/2004 92 49 3.2 1.93 Excellent 8/24/1999 100 49 3.4 2.45 Excellent Nantahala R US 19/74 Swain 2-57-(22.5) 7/20/2004 83 35 4.2 2.26 Good 8/23/1999 --- 35 --- 2.29 Good Dicks Cr off SR 1401 Macon 2-57-42 7/21/2004 --- 27 --- 1.59 Good-Fair 8/13/1999 --- 34 --- 1.93 Good Whiteoak Cr SR 1397 Macon 2-57-45 7/21/2004 63 26 4.3 2.33 Good-Fair Whiteoak Cr off SR 1310 Macon 7/20/2004 78 34 3.5 1.68 Excellent 8/13/1999 --- 31 --- 2.14 Good 040404 A-IV-7 Tulula Cr SR 1275 Graham 2-190-2-(0.5) 7/19/2004 61 31 4.0 3.24 Good Cheoah R off SR 1138 Graham 2-190-(3.5) 7/19/2004 84 38 4.0 3.14 Good 8/12/1999 89 48 3.5 2.84 Excellent Snowbird Cr SR 1120 Graham 2-190-9-(15.5) 7/20/2004 --- 48 --- 2.06 Excellent 8/12/1999 --- 52 --- 2.56 Excellent L Santeetlah Cr Ab Footbridge Graham 2-190-19-7 7/20/2004 59 32 2.9 1.65 Good Cheoah R SR 1147 Graham 2-190-(22) 7/4/2005 54 19 5.7 3.92 Fair Cheoah R At gauge Graham 2-190-(22) 08/04/2004 --- 42 --- 3.00 Excellent Fish Community Structure Data Collected in the Little Tennessee Basin, 1993 – 2003 (Current basinwide sampling sites are in bold print.) Subbasin/Waterbody Location County Index No. Date NCIBI Score NCIBI Rating 040401 Little Tennessee R off SR 1683 Macon 2-(1) 05/17/04 38 Fair Middle Cr SR 1635 - 2nd bridge Macon 2-8 05/17/04 56 Good Middle Cr SR 1635 - 1st bridge Macon 2-8 05/03/95 46 Good-Fair Tessentee Cr SR 1636 Macon 2-9 05/18/04 52 Good 05/03/95 56 Good Coweeta Cr SR 1119 Macon 2-10 05/20/04 56 Good Coweeta Cr US 23/441 Macon 2-10 05/01/95 44 Good-Fair Cartoogechaye Cr SR 1146 Macon 2-19-(1) 05/18/04 56 Good Cartoogechaye Cr SR 1168 Macon 2-19-(10.5) 05/02/95 56 Good Cullasaja R SR 1677 Macon 2-21-(5.5) 10/19/99 50 Good 10/15/96 52 Good Cullasaja R SR 1653 Macon 2-21-(5.5) 10/20/99 46 Good-Fair 10/16/96 34 Fair Walnut Cr SR 1533 Macon 2-21-17 05/18/04 --- Not Rated Ellijay Cr SR 1524 Macon 2-21-23 05/20/04 56 Good Rabbit Cr SR 1504 Macon 2-23 05/20/04 44 Good-Fair Iotla Cr SR 1372 Macon 2-27 05/03/95 22 Poor Iotla Cr off SR 1378 Macon 2-27 05/19/04 44 Good-Fair Cowee Cr SR 1340 Macon 2-29 05/19/04 56 Good Burningtown Cr SR 1364 Macon 2-38 05/21/04 58 Excellent Tellico Cr SR 1367 Macon 2-40 05/21/04 50 Good 040402 Brush Cr off SR 1129 Swain 2-46 05/19/04 50 Good Alarka Cr SR 1185 Swain 2-69-(2.5) 06/03/04 46 Good-Fair Caney Fk SR 1738 Jackson 2-79-28-(2.5) 06/01/04 56 Good Cullowhee Cr SR 1545 Jackson 2-79-31 06/02/04 46 Good-Fair Savannah Cr NC 116 Jackson 2-79-36 06/02/04 50 Good Scott Cr SR 1527 Jackson 2-79-39 06/01/04 --- Not Rated Conley Cr SR 1183 Swain 2-79-52 06/02/04 --- Not Rated Panther Cr SR 1233 Graham 2-115 06/03/04 --- Not Rated Stecoah Cr SR 1237 Graham 2-130 06/03/04 --- Not Rated 040403 Nantahala R SR 1401 Macon 2-57-(22.5) 11/15/93 --- Not Rated Whiteoak Cr SR 1310/1404 Macon 2-57-45 11/15/93 --- Not Rated Silvermine Cr SR 1103 Swain 2-57-55 11/16/93 --- Not Rated 040404 Tulula Cr SR 1260 Graham 2-190-2-(0.5) 06/04/04 46 Good-Fair A-IV-8 A-IV-9