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

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BIOLOGICAL METHODS<br />

As a rule <strong>of</strong> thumb, concentrate samples when<br />

phytoplankton densities are below 500 per ml;<br />

approximately 6 liters <strong>of</strong> sample are required at<br />

that cell concentration. Generally, 1 liter is an<br />

adequate routine sample volume.<br />

The following three <strong>methods</strong> may be used <strong>for</strong><br />

concentrating preserved phytoplankton, but<br />

sedimentation is preferred.<br />

3.1.1 Sedimentation<br />

Preserved phytoplankton samples can <strong>of</strong>ten be<br />

settled in <strong>the</strong> original storage containers. Settling<br />

time is directly related to <strong>the</strong> depth <strong>of</strong> <strong>the</strong><br />

sample in <strong>the</strong> bottle or settling tube. On <strong>the</strong><br />

average, allow 4 hours per 10 mm <strong>of</strong> depth.<br />

After settling, siphon <strong>of</strong>f <strong>the</strong> supernatant<br />

(Figure 1) or decant through a side drain. The<br />

use <strong>of</strong> a detergent aids in settling. Exercise<br />

caution because <strong>of</strong> <strong>the</strong> different sedimentation<br />

rates <strong>of</strong> <strong>the</strong> diverse sizes <strong>and</strong> shapes <strong>of</strong> phytoplankton.<br />

3.1.2 Cen trifugation<br />

During centrifugation, some <strong>of</strong> <strong>the</strong> more<br />

fragile <strong>for</strong>ms may be destroyed or flagella may<br />

become detached. In using plankton centrifuges,<br />

many <strong>of</strong> <strong>the</strong> cells may be lost; modern<br />

continuous-flow centrifuges avoid this.<br />

3.1.3 Filtration<br />

To concentrate samples by filtration, pass<br />

through a membrane filter. A special filter<br />

apparatus <strong>and</strong> a vacuum source are required.<br />

Samples containing large amounts <strong>of</strong> suspended<br />

rnaterial (o<strong>the</strong>r than phytoplankton) are<br />

difficult to enumerate by this method, because<br />

<strong>the</strong> suspended matter tends to crush <strong>the</strong> phytoplankters<br />

or obscure <strong>the</strong>m from view. The<br />

vacuum should not exceed 0.5 atmospheres.<br />

Concentration by filtration is particularly useful<br />

<strong>for</strong> samples low in plankton <strong>and</strong> silt content.<br />

3.2 Zooplankton<br />

The zooplankton in grab samples are concentrated<br />

prior to counting by allowing <strong>the</strong>m to<br />

settle <strong>for</strong> 24 hours in <strong>laboratory</strong> cylinders <strong>of</strong><br />

appropriate size or in specially constructed<br />

settling tubes (Figure 1).<br />

6<br />

50.8 eM<br />

Figure 1. Plexiglas plankton settling tube with<br />

side drain <strong>and</strong> detachable cup. Not<br />

drawn to scale.<br />

Take care to recover organisms (especially <strong>the</strong><br />

Oadocera) that cling to <strong>the</strong> surface <strong>of</strong> <strong>the</strong> water<br />

in <strong>the</strong> settling tube.<br />

4.0 SAMPLE ANALYSIS<br />

4.1 Phytoplankton<br />

4.1.1 Qualitative analysis <strong>of</strong>phytoplankton<br />

The optical equipment needed includes a good<br />

<strong>quality</strong> compound binocular microscope with a<br />

mechanical stage. For high magnification, a substage<br />

condenser is required. The ocular lens<br />

should be 8X to 12X. Binocular eyepieces are<br />

generally preferred over a monocular eyepiece<br />

because <strong>of</strong> reduced fatigue. Four turret-mounted<br />

objective lenses should be provided with magnifications<br />

<strong>of</strong> approximately 10, 20, 45, <strong>and</strong>

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