LEWIS SMITH LAKE - Auburn University

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List ofTables (Continued) Table 10-25. Orthophosphate and total phosphorus concentrations measured at each Smith Lake sampling station during the winter (January) of 1986 and 1995. Photic zone composite samples were analyzed. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 90 Table 10-26. Mean (range) orthophosphate and total phosphorus concentrations measured at each Smith Lake sampling station during the spring (April and May) of 1986 and 1995. Photic zone composite samples were analyzed . . . . . . . . . . . . . . . . . . . . . . . . . .. 91 Table 10-27. Mean (range) orthophosphate and total phosphorus concentrations measured at each Smith Lake sampling station during the summer (June, July and August) of 1986 and 1995. Photic zone composite samples were analyzed 92 Table 10-28. Mean (range) orthophosphate and total phosphorus concentrations measured at each Smith Lake sampling station during the fall (September and October) of 1986 and 1995. Photic zone composite samples were analyzed 93 Table 10-29. Summer mean total nitrogen Cf;g!L TN), total phosphorus (/-lgIL TP) and the TN:TP ratio at all mainstem and tributary embayment stations in Smith Lake, 1995 95 Table 10-30. Chloride, total organic carbon and phaeophytincorrected chlorophyll", concentration measured at each Smith Lake sampling station during the winter (January) of 1995 96 Table 10-31. Mean (range) chloride, total organic carbon and phaeophytin-corrected chlorophyll", concentration measured at each Smith Lake sampling station during the spring (April and May) of 1995 97 Table 10-32. Mean (range) chloride, total organic carbon and phaeophytin-corrected chlorophyll", concentration measured at each Smith Lake sampling station during the summer (June - August) of 1995 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 98 Table 10-33. Mean (range) chloride, total organic carbon and phaeophytin-corrected chlorophyll", concentration measured at each Smith Lake sampling station during the fall (September - October) of 1995 99 Table 10-34. Analytical methods used in measuring carbon and microbiological variables in Smith Lake during the diagnostic study, 1995 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 102 Table 10-35. Mean (range) phytoplankton density and uncorrected chlorophyll", concentration at each Smith Lake sampling station during the winter (January) of 1986 and 1995 104 xx
List ofTables (Continued) Table 10-36. Mean (range) phytoplankton density and uncorrected chlorophyll!! concentration at each Smith Lake sampling station during the spring (April and May) of 1986 and 1995 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . • . . . . . . . . . . . . . . . . . . . .. 105 Table 10-37. Mean (range) phytoplankton density and uncorrected chlorophyll!! concentration at each Smith Lake sampling station during the summer (June. August) of!986 and 1995 . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 106 Table 10-38. Mean (range) phytoplankton density and uncorrected chlorophyll!! concentration at each Smith Lake sampling station during the fall (September and October) of 1986 and 1995 107 Table 10-39. Phytoplankton taxa by major group indicating occurrence at selected stations in Smith Lake during the 1995 diagnostic study 112 Table 10-40. Dominant algal taxa collected at sampling stations on Smith Lake during the diagnostic study, 1995 116 Table 10-41. Mean (range) phytoplankton primary productivity measured at select sampling stations in Smith Lake during the growing seasons of 1986 and 1995. Productivity reported on a volumetric (mgC m" hr'l) and areal (mgC m" day") basis. . . . . . . . . . . . . . . . . . . . . . . . . . • . . . . . . . . . . . . . . . .. 122 Table 10-42. Mean maximum dry weight (mg/l) ofSelenastrurn capricomutum cultured in Smith Lake waters in 1995. The growing season mean weight for each station is also presented 124 Table 10-43. Temporal and spatial variation in nutrient limitation based on results ofAlgal Growth Potential Tests conducted during the 1995 growing season at Smith Lake 126 Table II-I. Total number, catch per unit effort (CPE) and percent ofsample of target species collected by electrofishing in Smith Lake, 1993 130 Table 11-2. Number ofspecies collected by gear type from Smith Lake, 1993 13 I Table 11-3. Ranking by quality indicators for all reservoirs with five or more tournament reports in the 1994 B.A.LT. program . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 132 Table 11-4. Ranking by quality indicators for all reservoirs with five or more tournament reports in the 1995 RA.LT. program. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 133 Table 11-5. Checklist offish species collected from Smith Lake and the surrounding watershed ... . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .. 134 Table 11-6. Fish stockings in Lewis Smith Reservoir, 1980-1993 137 XXI
Page 1 and 2: LEWIS SMITH LAKE Phase I Diagnostic
Page 3 and 4: EXECUTIVE SUMMARY
Page 5 and 6: January 1986 (Bayne et al. 1987). T
Page 7 and 8: Total alkalinity, the concentration
Page 9: found at concentrations ranging fro
Page 16 and 17: etween 10 and 15 mgIL as CaCO, but
Page 19 and 20: Table 1-1. Table 1-2. Table 2-1. Ta
Page 21: List ofTables (Continued) Table 10-
Page 25 and 26: LIST OF FIGURES Figure 8-I. Locatio
Page 27 and 28: PARTI. DIAGNOSTIC STIJDY 1
Page 29 and 30: Table I-I. Morphometric characteris
Page 31 and 32: 2.0 BASIN GEOLOGY AND DRAINAGE Smit
Page 33 and 34: Table 2-1 (Cont'd) Suitability/Limi
Page 35 and 36: 4.0 SIZE AND ECONOMIC STRUCTIJRE OF
Page 37 and 38: - U. II Table 4-2. Number ofbusines
Page 39 and 40: I, Table 4-4. Agricultural producti
Page 42 and 43: 7.0 LAKE USE COMPARISON WIlli NEARB
Page 44 and 45: 00 Table 8-1. Actual point source l
Page 46 and 47: N 0 Table 8-1 (Continued) Actual To
Page 48 and 49: N N Table 8-1 (Continued) Actual To
Page 50 and 51: 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
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V> tv Table 10-1. Schedule of activ
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..,. en IN o 2 4 i Miles Figure 10-
Page 82 and 83:
sample were poured into Nalgene"' c
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flows encountered in 1995,428 days.
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Table 10-6. Mean (range) temperatur
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Table 10-8. Mean (range) temperatur
Page 94 and 95:
Examination oftemperature, DO and s
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Table 10-10. Mean (range) turbidity
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Table 10-12. Mean (range) turbidity
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Table 10-14. Mean (range) Secchi di
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Table 10-16. Mean (range) Secchi di
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a low of 7 mgIL to a high of67 mgIL
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Table 10-18. Mean (range) pH, total
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Table 10-20. Mean (range) pH, total
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Table 10·21. Ammonia, nitrite, nit
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Table 10-23. Mean (range) ammonia,
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in concert with changes in algal bi
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Table 10-25. Orthophosphate and tot
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Table 10-27. Mean (range) orthophos
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stratification (Fig. 10-2). During
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Table 10-30. Chloride, total organi
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Table 10-33. Mean (range) chloride,
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In August 1986, iron and manganese
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1971). Productivity measured during
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Table 10-36. Mean (range) phytoplan
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Page 139:
Table 10-39. Phytoplankton taxa by
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(station 2) in the winter to a high
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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
Page 171 and 172:
Page 174:
Page 177 and 178:
Page 179 and 180:
Page 181 and 182:
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
Page 189 and 190:
13. Are there additional feasible a
Page 191 and 192:
Bayne, D. R., W. C. Seesock, P. P.
Page 193:
Taylor, W.D., S.c. Hem, L.R. Willia
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LEWIS SMITH LAKE - Auburn University

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