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Biological field and laboratory methods for measuring the quality of ...

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BIOLOGICAL METHODS<br />

fauna <strong>and</strong> hydrologic conditions. Place <strong>the</strong> top<br />

<strong>of</strong> <strong>the</strong> nets just below <strong>the</strong> surface <strong>of</strong> <strong>the</strong> water to<br />

permit calculation <strong>of</strong> <strong>the</strong> flow through <strong>the</strong> nets<br />

<strong>and</strong> to lessen <strong>the</strong> chance <strong>for</strong> collection <strong>of</strong><br />

floating terrestrial insects. Do not permit <strong>the</strong><br />

nets to touch bottom. In large rivers, maximum<br />

catches are obtained 0.3 to 0.6 meter above <strong>the</strong><br />

bottom in <strong>the</strong> shoreline zone at depths not<br />

exceeding 3 meters.<br />

Drift nets are useful <strong>for</strong> collecting macroinvertebrates<br />

that migrate or are dislodged from<br />

<strong>the</strong> substrate; <strong>the</strong>y are particularly well-suited<br />

<strong>for</strong> synoptic surveys because <strong>the</strong>y are lightweight<br />

<strong>and</strong> easily transported. Thous<strong>and</strong>s <strong>of</strong><br />

organisms - including larvae <strong>of</strong> stoneflies,<br />

mayflies, caddisflies, <strong>and</strong> midges <strong>and</strong> o<strong>the</strong>r<br />

Diptera, may be collected in a sampling period<br />

<strong>of</strong> only a few hours. Maximum drift intensity<br />

occurs between sunset <strong>and</strong> midnight (55). Elliot<br />

(14) presents an excellent synopsis <strong>of</strong> drift net<br />

methodology.<br />

3.3.6 Photography<br />

The use <strong>of</strong> photography is mainly limited to<br />

environments that have suitably clear water <strong>and</strong><br />

are inhabited by sessile animals <strong>and</strong> rooted<br />

plants. Many estuarine habitats, such as those<br />

containing corals, sponges, <strong>and</strong> attached algal<br />

<strong>for</strong>ms, fall in this category <strong>and</strong> can be photographed<br />

be<strong>for</strong>e, during, <strong>and</strong> after <strong>the</strong> introduction<br />

<strong>of</strong> stress. The technique has been used with<br />

success in south Florida to evaluate changes<br />

brought about by <strong>the</strong> introduction <strong>of</strong> heated<br />

effluents.<br />

The technique <strong>for</strong> horizontal underwater<br />

photos using scuba gear involves placing a photographically<br />

identifiable marker in <strong>the</strong> habitat to<br />

be photographed <strong>and</strong> an additional nearby<br />

marker on which <strong>the</strong> camera is placed each time<br />

a photograph is taken. By this means, identical<br />

areas can be photographed repeatedly over a<br />

period <strong>of</strong> time to evaluate on-site changes in<br />

sessile <strong>for</strong>ms at both affected <strong>and</strong> control<br />

stations. Vertical, overhead photos may also be<br />

taken under suitable conditions.<br />

3.3.7 Qualitative devices<br />

The investigator has an unlimited choice <strong>of</strong><br />

gear <strong>for</strong> collecting qualitative samples. Any <strong>of</strong><br />

12<br />

<strong>the</strong> qualitative devices discussed previously, plus<br />

h<strong>and</strong>-held screens, dip nets, rakes, tongs, post<br />

hole diggers, bare h<strong>and</strong>s, <strong>and</strong> <strong>for</strong>ceps can be<br />

used. For deep-water collecting, some <strong>of</strong> <strong>the</strong><br />

conventional grabs described earlier are normally<br />

required. In water less than 2 meters deep, a<br />

variety <strong>of</strong> gear may be used <strong>for</strong> sampling <strong>the</strong><br />

sediments including long-h<strong>and</strong>led dip nets <strong>and</strong><br />

post-hole diggers. Collections from vascular<br />

plants <strong>and</strong> filamentous algae may be made with<br />

a dip net, common garden rake, potato <strong>for</strong>k, or<br />

oyster tongs. Collections from floating debris<br />

<strong>and</strong> rocks may be made by h<strong>and</strong>, using <strong>for</strong>ceps<br />

to catch <strong>the</strong> smaller organisms.<br />

In shallow streams, short sections <strong>of</strong> common<br />

window screen may be fastened between two<br />

poles <strong>and</strong> held in place at right angles to <strong>the</strong><br />

water flow to collect organisms dislodged from<br />

upstream materials that have been agitated.<br />

4.0 SAMPLE PROCESSING<br />

4.1 Sieving<br />

Samples collected with grabs, tubular devices,<br />

<strong>and</strong> artificial substrates contain varying amounts<br />

<strong>of</strong> finely divided materials such as completely<br />

decomposed organic material, silts, clays, <strong>and</strong><br />

fine s<strong>and</strong>. To reduce sample volume <strong>and</strong><br />

expedite sample processing in <strong>the</strong> <strong>laboratory</strong>,<br />

<strong>the</strong>se fines should be removed by passing <strong>the</strong><br />

sample through a U. S. St<strong>and</strong>ard No. 30 sieve.<br />

Sieves may range from commercially constructed<br />

models to homemade sieves framed<br />

with wood or metal. Floating sieves with<br />

wooden frames reduce <strong>the</strong> danger <strong>of</strong> accidental<br />

loss <strong>of</strong> both sieve <strong>and</strong> sample when working over<br />

<strong>the</strong> side <strong>of</strong> a boat in deeper waters. A good sieve<br />

contains no cracks or crevices in which small<br />

organisms can become lodged.<br />

If at all possible, sieving should be done in <strong>the</strong><br />

<strong>field</strong> immediately after sample collection <strong>and</strong><br />

while <strong>the</strong> captured organisms are alive. Once<br />

preserved, many organisms become quite fragile<br />

<strong>and</strong> if subjected to sieving will be broken up <strong>and</strong><br />

lost or rendered unidentifiable.<br />

Sieving may be accomplished by one <strong>of</strong><br />

several techniques depending upon <strong>the</strong> reference<br />

<strong>of</strong> <strong>the</strong> individual biologist. In one technique, <strong>the</strong><br />

sample is placed directly into a sieve <strong>and</strong> <strong>the</strong>

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