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Science of Water : Concepts and Applications

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Environmental Biomonitoring, Sampling, <strong>and</strong> Testing 225<br />

Stream or river<br />

5. S<strong>and</strong> (<strong>and</strong> other fi ne sediment)—Usually the least productive macroinvertebrate habitat<br />

in streams, this habitat may be the most prevalent in some streams. Sample banks<br />

<strong>of</strong> unvegetated or s<strong>of</strong>t soil by bumping the net along the surface <strong>of</strong> the substrate rather<br />

than dragging the net through the s<strong>of</strong>t substrate; this reduces the amount <strong>of</strong> debris in<br />

the sample.<br />

In a biological sampling program (i.e., based on our experience), the most common sampling<br />

methods are the transect <strong>and</strong> the grid. Transect sampling involves taking samples along a straight<br />

line either at uniform or at r<strong>and</strong>om intervals (see Figure 8.1). The transect involves the cross section<br />

<strong>of</strong> a lake or stream or the longitudinal section <strong>of</strong> a river or stream. The transect sampling method<br />

allows for a more complete analysis by including variations in habitat.<br />

In grid sampling, an imaginary grid system is placed over the study area. The grids may<br />

be numbered, <strong>and</strong> r<strong>and</strong>om numbers are generated to determine which grids should be sampled<br />

(see Figure 8.2). This type <strong>of</strong> sampling method allows for quantitative analysis because the grids<br />

are all <strong>of</strong> a certain size. For example, to sample a stream for benthic macroinvertebrates, grids that<br />

are 0.25 m (squared) may be used. Then, the weight or number <strong>of</strong> benthic macroinvertebrates per<br />

square meter can be determined.<br />

R<strong>and</strong>om sampling requires that each possible sampling location have an equal chance <strong>of</strong> being<br />

selected. After numbering all sampling locations, a computer, calculator, or a r<strong>and</strong>om numbers table<br />

is used to collect a series <strong>of</strong> r<strong>and</strong>om numbers. An illustration <strong>of</strong> how to put the r<strong>and</strong>om numbers to<br />

work is provided in the following example. Given a pond that has 300 grid units, fi nd eight r<strong>and</strong>om<br />

sampling locations using the following sequence <strong>of</strong> r<strong>and</strong>om numbers taken from a st<strong>and</strong>ard r<strong>and</strong>om<br />

numbers table: 101, 209, 007, 018, 099, 100, 017, 069, 096, 033, 041, 011. The fi rst eight numbers <strong>of</strong><br />

the sequence for sample collection will depend on the type <strong>of</strong> sample.<br />

SAMPLE COLLECTION *<br />

Longitudinal transect<br />

FIGURE 8.1 Transect sampling.<br />

Cross-sectional transects<br />

After establishing the sampling methodology <strong>and</strong> the sampling locations, the frequency <strong>of</strong> sampling<br />

must be determined. The more samples collected, the more reliable the data will be. A frequency <strong>of</strong><br />

once a week or once a month will be adequate for most aquatic studies. Usually, the sampling period<br />

covers an entire year so that yearly variations may be included. The details <strong>of</strong> sample collection will<br />

∗ The following procedures are suggested by USEPA, 2000b.<br />

Lake or reservoir<br />

Cross-sectional transects

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