Surface Water - Alabama Department of Environmental Management

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Upper Black Warrior River (0316-0112) Assessment stations located within the sub-watershed. Descriptions are provided in Appendix E-1. Station Assessment Type Date Location Area (mi 2 ) BW6U6-54 Habitat, Chemical 2002 Barbee Cr. approx. ½ mi S of Tuscaloosa CR 40 BERT-4 Habitat, Biological, Chemical Classification 4 F&W 2002 Bear Cr. at Oregonia Rd 12 F&W BW5U6-45 Habitat, Chemical 2002 Binion Cr. approx. ¼ mi ds of unnamed CR BINT-31f Tuscaloosa5 Habitat, Biological, Chemical Biological, Chemical 8 F&W 2002 Binion Cr. at unnamed Tuscaloosa CR 61 F&W Binion Cr. immediately us of US Hwy 43 72 F&W NRRT-1 Chemical 2002 North R. at Tuscaloosa CR 38 223 F&W Tuscaloosa2 TUS2 Tuscaloosa4 Tuscaloosa3 Tuscaloosa1 TUS1 Biological, Chemical Biological, Chemical Biological, Chemical Biological, Chemical North R. directly ds of confluence with Binion Cr. North R. immediately us of Bull Slough crossing 360 F&W 362 F&W North R. 1 mi ds of AL Hwy 69 372 F&W North R. at dam forebay of Lake Tuscaloosa 423 F&W Binion Creek: Located in the Shale Hills (68f) subecoregion, Binion Creek at BINT-31f was a sandy-bottomed, glide pool stream (Appendix J). Habitat quality was impaired by sediment deposition and unstable banks. The macroinvertebrate and fish communities were assessed as fair and good, respectively (Appendix K). One time water quality sampling conducted in June of 2002 did not indicate a cause of the impairment (Appendix M). Intensive water quality data were collected monthly from the Binion Creek embayment at Tuscaloosa5 to determine the sediment and nutrient loading to Tuscaloosa Reservoir (ADEM 2004b). The site is located within the Fall Line Hills (65i) subecoregion (Appendix E). Concentrations of total nitrogen, total phosphorus, chlorophyll a and total suspended solids were among the lowest of the Black Warrior tributaries (ADEM 2004b). Binion Creek at BW5U6-45 was evaluated during ADEM’s 2002 ALAMAP Program (Appendix E). At BW5U6-45, Binion Creek was a small, shaded, bedrock-bottom stream located within the Fall Line Hills (65i) subecoregion (Appendix T-1). The reach was characterized by poor instream habitat and riffle quality. Dissolved oxygen was measured at 0.5 mg/L during a one-time water quality sampling event in August of 2002 (Appendix T-2). Bear Creek: Bear Creek at BERT-4 has been intensively monitored in conjunction with ADEM’s EcoregionalReference Reach Program (Appendix E). Located in the Shale Hills (68f) subecoregion, Bear Creek at BERT-4 is characterized by cobble/gravel riffles 166
Upper Black Warrior River (0316-0112) (Appendix O-1). In June of 2002, 7 EPT families were collected, indicating a fair macroinvertebrate community (Appendix O-2). Intensive water quality sampling conducted from March through November of 2002 did not indicate a cause of the impairment (O-3). North River: North River at NRRT-1 is located in the Fall Line Hills (65i) subecoregion (Appendix E). Intensive water quality sampling was collected on the North River at NRRT-1 from January through August of 2002 (Appendix P-3). Results showed fecal coliform concentrations >2,000 colonies/100 mL during the May sampling event. Nutrient concentrations and conductivity were periodically elevated. Intensive water quality samples were collected monthly during April through October, 2002 in the upper- (Tuscaloosa2 and Tuscaloosa4), mid- (Tuscaloosa3), and lower- (Tuscaloosa1) reservoir to evaluate nutrient and sediment loading as a source of water quality impairment to Tuscaloosa Reservoir (ADEM 2004b). Mean concentrations of total nitrogen and total phosphorus were among the lowest on the Black Warrior River during the 2002 sampling season (ADEM 2004b). However, total phosphorus concentrations have nearly doubled since 1998. Total suspended solids have also increased throughout the reservoir since 1998. Barbee Creek: At BW6U6-54, Barbee Creek was a moderate gradient, bedrock-bottomed stream located in the Fall Line Hills (65i) subecoregion (Appendix T-1). Results of water quality sampling conducted during August of 2002 are located in Appendix T-2. Sub-watershed status: Macroinvertebrate assessments conducted during 2002 indicated impaired macroinvertebrate communities at locations on Bear and Binion Creek. Sedimentation was observed at both sites. Roadside surveys conducted in 1997, upstream of each assessment site, indicated cattle production, silviculture, and roadside erosion to be prevalent throughout the sub-watershed. A 38.0 mile segment of the North River is on ADEM’s 2002 CWA §303(d) list of impaired waterbodiesfor nutrient enrichment, siltation, and other habitat alteration caused by runoff from abandoned surface mines. Total phosphorus concentrations and total suspended solids have increased throughout the Tuscaloosa Reservoir since 1998. However, monitoring within the Binion Creek and the Tuscaloosa Reservoir has indicated the potential for nutrient and sediment loading from these sources to be relatively low. 167
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SURFACE WATER QUALITY SCREENING ASS
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Table of Contents TABLE OF CONTENTS
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List of Figures LIST OF FIGURES 1 C
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List of Abbreviations LIST OF ABBRE
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Introduction INTRODUCTION Backgroun
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Introduction document includes a de
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Introduction Table 1, cont. List of
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Methodology Table 7. Sub-watersheds
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Methodology Fig. 1. Cataloging unit
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Methodology Fig. 2. Level IV Ecoreg
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Methodology The southern section of
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Methodology The Southern Table Plat
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Methodology Table 8. Current conver
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Methodology SITE SELECTION Alabama
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Methodology Process samples in the
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Methodology Water quality samples a
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Summary: BWC River Basins Summary:
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Summary: BWC River Basins Fig. 3. C
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Summary: BWC River Basins Fig. 4. E
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Summary: BWC River Basins Fig. 10.
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Summary: BWC River Basins Results o
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Summary: BWC River Basins Impaired
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Summary: BWC River Basins Table 5,
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Cahaba River (0315-0202) Cahaba Riv
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Cahaba River (0315-0202) Types of a
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Cahaba River (0315-0202) Fig. 15. I
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Cahaba River (0315-0202) Sub-Waters
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Cahaba River (0315-0202) suspended
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Cahaba River (0315-0202) indicating
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Cahaba River (0315-0202) assessed a
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Cahaba River (0315-0202) Assessment
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Mulberry Fork (0316-0109) Program (
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Mulberry Fork (0316-0109) Fig. 16.
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Mulberry Fork (0316-0109) List of i
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Mulberry Fork (0316-0109) Assessmen
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Mulberry Fork (0316-0109) greater t
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Mulberry Fork (0316-0109) Eightmile
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Mulberry Fork (0316-0109) Broglen R
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Mulberry Fork (0316-0109) Sub-Water
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Mulberry Fork (0316-0109) Bunkum Cr
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Mulberry Fork (0316-0110) Sipsey Fo
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Mulberry Fork (0316-0110) waters. A
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Page 127 and 128: Sipsey Fork (0316-0110) and GSA (Ap
Page 129 and 130: Sipsey Fork (0316-0110) Assessment
Page 139 and 140: Sipsey Fork (0316-0110) unstable ba
Page 141 and 142: Sipsey Fork (0316-0110) conditions
Page 143 and 144: Locust Fork (0316-0111) Historical
Page 145 and 146: Locust Fork (0316-0111) Fig. 18. 20
Page 147 and 148: Locust Fork (0316-0111) Upper Locus
Page 149 and 150: Locust Fork (0316-0111) ADEM 1999a)
Page 151 and 152: Locust Fork (0316-0111) and fair/po
Page 153 and 154: Locust Fork (0316-0111) bottom subs
Page 155 and 156: Locust Fork (0316-0111) Assessment
Page 157 and 158: Locust Fork (0316-0111) oxygen. ADE
Page 159 and 160: Locust Fork (0316-0111) Longs Branc
Page 161 and 162: Upper Black Warrior River (0316-011
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Page 179 and 180: Lower Black Warrior River (0316-011
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Page 199 and 200: References ACES. 1997. Soil areas o
Page 201 and 202: References ADEM. 2002b. Nonpoint so
Page 203 and 204: References APHA, AWWA, and WEF. 199
Page 205 and 206: References Omernik, J.M. 1996. Leve
Page 207 and 208: APPENDICES
Page 209 and 210: Appendix A, cont. Land use percenta
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Page 215 and 216: Appendix C-2. List of waterbodies w
Page 217 and 218: Appendix C-2, cont. List of waterbo
Page 219 and 220: Appendix D, cont. Estimates of (H)i
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Page 223 and 224: Appendix E. Stations assessed in th
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Appendix E. Stations assessed in th
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Appendix F--Page 2 of 2 Appendix F,
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Appendix G, cont. Summary of assess
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Appendix H, cont. Estimates of anim
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Appendix I. Sedimentation estimates
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Appendix I, cont. Sedimentation est
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Appendix J, cont. Physical characte
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Appendix K. Bioassessment results f
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Appendix L-2. ADEM Glide/Pool habit
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ADEM — FIELD OPERATIONS DIVISION
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Appendix M--Page 2 of 3 Appendix M.
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Appendix N. Concentration of metals
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Appendix O-1. Physical characterist
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Appendix O-3. Physical/chemical dat
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Appendix O-3--Page 3 of 4 Appendix
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Appendix P. §303(d) Waterbody Moni
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Appendix P-1. Physical characterist
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Appendix P-2. Bioassessment results
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Appendix P-3. Physical/chemical dat
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Appendix Q. Periphyton Bioassessmen
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Appendix Q--Page 2 of 2 Appendix Q.
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Appendix R--Page 1 of 5 Appendix R.
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Appendix S--Page 1 of 9 Appendix S.
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Appendix S. Physical/chemical data
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Appendix T-1. Results of habitat as
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Appendix T-1. Results of habitat as
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Appendix T-2--Page 1 of 1 Appendix
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