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0.5 m depth at the center of ponds. sa=?.- -a--e filters: using GA-4, <br />0.8 pM Mi.lliporeg filters, extracted in 9.= gone, and aralyzed <br />spectrcphotaxtrically (Hac? spe - , at 665 na. <br />Quantitative estimates of chlorophyll a w- = obtained (no <br />correction for turbidity and phaeophytin z died); moults were <br />used only as an index of relative . <br />Surface water temperatures, aquatic mates, and fish were <br />sampled weekly between 1000 and 1400 and =nd 2400 hr. As alrec-& <br />noted, ponds were separated into three ha:_- =nes: "s,.allows" fro= <br />water's edge to the level bottoms; %Ott=e m=ined by height of a <br />device develcPed to sample between 8 to 3:-- = above bottans; and <br />"open water" from surface to 30.5 cm above ---ates. Plankton tows <br />were by a sled mounted (Pennak 1978) or plankton net (80 u <br />mesh) towed at constant speed the length -- mr-- pond. The shallow <br />zone was sampled by touring the sled a stw=?--: stance near shore at <br />cMparable speed. Samples were preserved ` k buffered formalin. <br />Invertebrate samples were agitated are :.Zm: aliquots removed by <br />Hensen-Stempel pipette to a Sedgewick-Rafe =ELI. Field or strip <br />ccxmts were made (APHA 1981) and data were -rsed as mmbers/L. <br />Organisms were identified to various tauo:== categories, but <br />combined to major groups (e.g., families s ^?*- categories) for <br />analysis• lengths and widths of inverteh.= ire measured by ocular <br />micr meter at appropriate magnification or- _ =qamd microscope, and <br />assigned geometric shapes to reconstruct v-;,=m (Edmondson and <br />WinbeYg 1971). Widths of invertebrates we- ----ad for estimating size-