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<br />0050 <br /> <br />Table 2. Sampling-site locations and sampling dates at Lake Henry and Lake Meredith Reservoir <br /> <br />Location <br /> <br />Sampling data, <br />1987 <br /> <br />Sampling site <br /> <br />Latllude <br /> <br />Longitude <br /> <br />Lake Henry (fig. 2) <br /> <br />HEW2 <br />HNW <br />HSE <br />HEWI <br />HEW3 <br /> <br />38'15'43"' <br />38'I6'Il"" <br />38'15"34" <br />38'15'34" <br />38'15"51" <br /> <br />HNE <br />HSW <br />'HI <br />2HO <br /> <br />38'16'08" <br />38'15'37"" <br />38'15"58" <br />38'15' 14" <br /> <br />103'42'33" <br />103'42'36" <br />103'42'25" <br />103'42'14" <br />103'42'53" <br /> <br />5-1.6-29.8-19.10-6 <br />5-1.6-29.8-19 <br />5-1,6-29,8-19 <br />5-1.6-29,8-19 <br />5-1, 6-19, 8-19 <br /> <br />103'41'00" <br />103'43'05" <br />103'43'19" <br />103'43'14" <br /> <br />5-1,6-29,8-19 <br />5-1, 6-29, 8-19 <br />6-29,8-19 <br />5-1,6-29,8-19.10-6 <br /> <br />Lake Meredilh Reservoir (fig. 3) <br /> <br />M2B <br />MIB <br />M4B <br />MIA <br />MIC <br /> <br />38'11'40" <br />38'12'39" <br />38'10'18" <br />38'12'59" <br />38'11'58" <br /> <br />M2A <br />M2C <br />M3A <br />M3B <br />M4A <br />'Mil <br />'MI2 <br /> <br />38'12'11" <br />38'1 r 10" <br />38'11'37"" <br />38'1\"17"" <br />38'10'18" <br />38'13'46" <br />38'10'55" <br /> <br />103'41'3\"' <br />103'40'24" <br />103'43'45" <br />103'40'25" <br />103'40'24" <br /> <br />5-1, 6-30, 8-20. 10-6 <br />5-1, 6-30, 8-20 <br />5-1, 6-30, 8-21 <br />6-30. 8-20 <br />6-30, 8-20 <br /> <br />103'41'30" <br />103'41'31" <br />103'42'37"" <br />103'42'37"" <br />103'43'45" <br />103'41'01" <br />103'44'50" <br /> <br />6-30,8-20 <br />6-30, 8.20 <br />6-30.8-21 <br />6-30.8.21 <br />6-30. 8-21 <br />6-30.8-21 <br />6-30, 8-20. 10-6 <br /> <br />Jlnnow sampling-site location. <br />20utflow sampling-site localion. <br /> <br />Waler samples for phytoplankton analysis were <br />collected using the water-sampling bottle from a single <br />deplh near the lake surface. A l-L sample was pre- <br />served using a 37-percent fonnaldehyde solution. The <br />phyloplankton count was detennined by transferring a <br />known part of the sample to a settling chamber and was <br />examined using a 200 to 1.000 power inverted micro- <br />scope. The chlorophyll a samples were collected from <br />a single depth near the lake surface and from a single <br />depth near the lake bottom using the water-sampling <br />bottle. One to two liters of a sample were filtered <br />through a 0.45 Ilm, cellulose-acetate filter. The filter <br />then was placed in a petri dish, wrapped in aluminum <br />foil, and frozen using dry ice. The chlorophyll a <br /> <br />analysis was perfonned by placing the sample in a <br />90-percent-aqueous acetone solution. The mixture was <br />steeped in the dark for 24 hours at 40C then centrifuged <br />for 20 min. The supernatant was decanted into stop- <br />pered cuvettes and was analyzed with a spectropho- <br />tometer (Chadwick and Associates, Littleton, <br />Colorado, written commun.. 1985). The phytoplank- <br />ton and chlorophyll a analyses were done by a private <br />laboratory . <br />For this study, two trophic-classification systems <br />were used for comparison to assign a relative trophic <br />status to Lake Henry and Lake Meredith. The first sys- <br />tem used was the trophic-state index (TSl) developed <br />by Carlson (1977), which categorizes lakes using a <br /> <br />INTRODUCTION 7 <br />