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

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BIOLOGICAL METHODS<br />

pollution studies. These include St<strong>and</strong>ard<br />

Methods (2), Welch (57), Mackenthun (37),<br />

Kittrell (29), Hynes (26), <strong>and</strong> Buchanan <strong>and</strong><br />

Sommers (9).<br />

2.0 SELECTION OF SAMPLE SITES<br />

As discussed <strong>and</strong> defined more fully in <strong>the</strong><br />

section on biometrics, sample sites may be<br />

selected systematically or by various r<strong>and</strong>omization<br />

procedures.<br />

2.1 Systematic Sampling<br />

Unless <strong>the</strong> data are to be utilized <strong>for</strong> quantitative<br />

evaluations, some type <strong>of</strong> systematic<br />

sampling is generally employed <strong>for</strong> synoptic<br />

surveys <strong>and</strong> reconnaissance studies. Line<br />

transects established at discrete intervals across a<br />

river or stream <strong>and</strong> sampled at quarter points or<br />

more frequent intervals are a <strong>for</strong>m <strong>of</strong> systematic<br />

sampling <strong>and</strong> serve as an excellent means <strong>of</strong><br />

delimiting <strong>and</strong> mapping <strong>the</strong> habitat types. In<br />

lakes, reservoirs, <strong>and</strong> estuaries, transects may be<br />

established along <strong>the</strong> short or long axis or may<br />

radiate out from a pollution source. If a r<strong>and</strong>om<br />

start point is used <strong>for</strong> selecting sampling sites<br />

along <strong>the</strong> transects, <strong>the</strong> data may be amenable to<br />

quantitative evaluation (see Biometrics Section).<br />

As will be discussed, however, <strong>the</strong> confounding<br />

effects <strong>of</strong> changes in physical characteristics <strong>of</strong><br />

<strong>the</strong> environment along <strong>the</strong> transect must be fully<br />

recognized <strong>and</strong> accounted <strong>for</strong>.<br />

In ano<strong>the</strong>r <strong>for</strong>m <strong>of</strong> systematic sampling, <strong>the</strong><br />

investigator, using a variety <strong>of</strong> gear, consciously<br />

selects <strong>and</strong> intensively samples all recognizable<br />

habitat types. As previously mentioned, this<br />

<strong>for</strong>m <strong>of</strong> sample site selection is useful <strong>for</strong><br />

synoptic surveys <strong>and</strong> <strong>for</strong> comparative studies<br />

where qualitative comparisons are being made.<br />

2.2 R<strong>and</strong>om Sampling<br />

For conducting quantitative studies, where a<br />

measure <strong>of</strong> precision must be obtained, some<br />

type <strong>of</strong> r<strong>and</strong>omization procedure must be<br />

employed in selecting sampling sites. This selection<br />

may be carried out on <strong>the</strong> whole <strong>of</strong> <strong>the</strong> area<br />

under study (simple r<strong>and</strong>om sampling), or <strong>the</strong><br />

r<strong>and</strong>omization procedure may be conducted<br />

independently on selected strata (stratified<br />

r<strong>and</strong>om sampling). Because <strong>the</strong> characteristics <strong>of</strong><br />

2<br />

macroinvertebrate communities are so closely<br />

related to physical factors such as substrate<br />

type, current velocity, depth, <strong>and</strong> salinity, a<br />

design using simple r<strong>and</strong>om sampling is seldom<br />

meaningful. There<strong>for</strong>e, <strong>the</strong> investigator should<br />

stratify <strong>the</strong> habitat on <strong>the</strong> basis <strong>of</strong> known<br />

physical habitat differences <strong>and</strong> collect samples<br />

by <strong>the</strong> r<strong>and</strong>om grid technique within each<br />

habitat type.<br />

As alluded to above, <strong>and</strong> regardless <strong>of</strong> <strong>the</strong><br />

method <strong>of</strong> sample site selection, <strong>the</strong> biologist<br />

must consider <strong>and</strong> account <strong>for</strong> those natural<br />

environmental variations that may affect <strong>the</strong><br />

distribution <strong>of</strong> organisms. Among <strong>the</strong> more<br />

important natural environmental variables in<br />

fresh-water habitats are substrate type, current<br />

velocity, <strong>and</strong> depth. In estuaries, <strong>the</strong> salinity<br />

gradient is an additional variable that must be<br />

accounted <strong>for</strong>.<br />

2.3 Measurement <strong>of</strong> Abiotic Factors<br />

2.3.1 Substrate<br />

Substrate is one <strong>of</strong> <strong>the</strong> most important factors<br />

controlling <strong>the</strong> characteristics <strong>of</strong> <strong>the</strong> community<br />

<strong>of</strong> aquatic macroinvertebrates found at a given<br />

location in a body <strong>of</strong> water (49). Over a period<br />

<strong>of</strong> time, <strong>the</strong> natural substrates may be greatly<br />

altered by <strong>the</strong> discharge <strong>of</strong> particulate mineral or<br />

organic matter, <strong>and</strong> <strong>the</strong> location <strong>and</strong> expanse <strong>of</strong><br />

various substrate types (silt, s<strong>and</strong>, gravel, etc.)<br />

may change because <strong>of</strong> normal variations in<br />

hydrolic factors such as current velocity <strong>and</strong><br />

stream flow. The biologist, <strong>the</strong>re<strong>for</strong>e, must be<br />

cognizant <strong>of</strong> changes in <strong>the</strong> nature <strong>and</strong><br />

properties <strong>of</strong> <strong>the</strong> substrate which may provide<br />

clues on <strong>the</strong> <strong>quality</strong> <strong>and</strong> quantity <strong>of</strong> pollutants<br />

<strong>and</strong> consider factors which affect <strong>the</strong> normal<br />

distribution <strong>of</strong> <strong>the</strong> benthic fauna.<br />

Where <strong>the</strong> pollutant has a direct effect on <strong>the</strong><br />

characteristics <strong>of</strong> <strong>the</strong> substrate, <strong>the</strong> effects <strong>of</strong><br />

changes in water <strong>quality</strong> may be inseparable<br />

from <strong>the</strong> effects <strong>of</strong> changes in <strong>the</strong> substrate. In<br />

cases where substrate deterioration has occurred,<br />

faunal effects may be so obvious that extensive<br />

sampling may not be required, <strong>and</strong> special attention<br />

should be given to <strong>the</strong> physical <strong>and</strong>/or<br />

chemical characterization <strong>of</strong> <strong>the</strong> deposits.<br />

In conducting synoptic surveys or o<strong>the</strong>r types<br />

<strong>of</strong> qualitative studies <strong>and</strong> taking into account

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