LEWIS SMITH LAKE - Auburn University

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Table 10-16. Mean (range) Secchi disk visibility and 1% incident light depth at each Smith Lake sampling station during the fall (September and October) of 1986 and 1995. Mainstem Station Secchi Visibility (cm) 1986 1995 I% Incident Light (cm) 1986 1995 421 290 897 (416-425) (272-307) (879-915) 5 373 322 770 (370-375) (307-336) (770-770) 7 322 302 628 (310-334) (290-314) (612-644) Embayment Stations 2 539 280 867 (490-588) (266-293) (831-903) 3 430 300 816 (420-440) (293-307) (704-927) 4 340 251 739 (330-350) (232-270) (736-742) 6 260 200 445 (200-319) (175-224) (445-445) 8 266 643 (234-297) (627-658) 9 288 617 (251-324) (609-624) 76
Figure 10-6. Seasonal mean Secchi disk visibility at stations 1-7 during the spring, summer and fall of 1986 and 1995. 77
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LEWIS SMITH LAKE Phase I Diagnostic
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EXECUTIVE SUMMARY
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January 1986 (Bayne et al. 1987). T
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Total alkalinity, the concentration
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found at concentrations ranging fro
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etween 10 and 15 mgIL as CaCO, but
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Table 1-1. Table 1-2. Table 2-1. Ta
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List ofTables (Continued) Table 10-
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List ofTables (Continued) Table 10-
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LIST OF FIGURES Figure 8-I. Locatio
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PARTI. DIAGNOSTIC STIJDY 1
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Table I-I. Morphometric characteris
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2.0 BASIN GEOLOGY AND DRAINAGE Smit
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Table 2-1 (Cont'd) Suitability/Limi
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4.0 SIZE AND ECONOMIC STRUCTIJRE OF
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- U. II Table 4-2. Number ofbusines
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I, Table 4-4. Agricultural producti
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7.0 LAKE USE COMPARISON WIlli NEARB
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00 Table 8-1. Actual point source l
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N 0 Table 8-1 (Continued) Actual To
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N N Table 8-1 (Continued) Actual To
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Table 8-1 (Continued) Actual Total
Page 52 and 53: tv 0- Table 8-2 (Continued) Permitt
Page 54 and 55: Annual point source total suspended
Page 56 and 57: Table 9-1. Location oftributary sam
Page 58: nitrogen, nitrite-nitrogen, total a
Page 68: highly positively correlated (p < 0
Page 71 and 72: (31.4% and 30.5%, respectively). Ro
Page 73: In 1985, the paucity ofinfonnation
Page 76 and 77: population of 1.15 million. In addi
Page 78 and 79: V> tv Table 10-1. Schedule of activ
Page 80 and 81: ..,. en IN o 2 4 i Miles Figure 10-
Page 82 and 83: sample were poured into Nalgene"' c
Page 84: flows encountered in 1995,428 days.
Page 87 and 88: Table 10-6. Mean (range) temperatur
Page 89: Table 10-8. Mean (range) temperatur
Page 94 and 95: Examination oftemperature, DO and s
Page 96 and 97: Table 10-10. Mean (range) turbidity
Page 98 and 99: Table 10-12. Mean (range) turbidity
Page 100 and 101: Table 10-14. Mean (range) Secchi di
Page 105 and 106: a low of 7 mgIL to a high of67 mgIL
Page 107 and 108: Table 10-18. Mean (range) pH, total
Page 109 and 110: Table 10-20. Mean (range) pH, total
Page 111 and 112: Table 10·21. Ammonia, nitrite, nit
Page 113 and 114: Table 10-23. Mean (range) ammonia,
Page 115 and 116: in concert with changes in algal bi
Page 117 and 118: Table 10-25. Orthophosphate and tot
Page 119 and 120: Table 10-27. Mean (range) orthophos
Page 121 and 122: stratification (Fig. 10-2). During
Page 123: Table 10-30. Chloride, total organi
Page 126 and 127: Table 10-33. Mean (range) chloride,
Page 128 and 129: In August 1986, iron and manganese
Page 130 and 131: 1971). Productivity measured during
Page 132 and 133: Table 10-36. Mean (range) phytoplan
Page 134: Table 10-38. Mean (range) phytoplan
Page 139: Table 10-39. Phytoplankton taxa by
Page 145: (station 2) in the winter to a high
Page 149 and 150: Table 10-41. Mean (range) phytoplan
Page 151 and 152: Table 10-42. Mean maximum dry weigh
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Table 10-43. Temporal and spatial v
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11.0 BIOLOGICAL RESOURCES 11.1 Fish
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Table 11-1. Total number, catch per
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Table \\-3. Ranking by quality indi
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Table 11-5. Checklist of fish speci
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Table 11-5 (Continued) Scientific N
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11.2 WILDLIFE A checklist ofbirds,
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Table 11-7 (Continued) Family Scien
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PART II. FEASffiILITY STUDY 154
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from Atlanta, Georgia received an a
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An additional source ofnutrients to
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Indirectly, low pH can result in hi
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13. Are there additional feasible a
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Bayne, D. R., W. C. Seesock, P. P.
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Taylor, W.D., S.c. Hem, L.R. Willia
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