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determine Td at the actual site under operational conditions at a previous time, with
the conditions similar to those for the operation under consideration. This
approach can be used only for existing sites.
Alternatively, the ratio Td/T = 1/HECF can be estimated from the equation:
T d = 0.9 1 - exp - 0.3 L
(B-5)
T
W
where L/W is the length-to-width ratio of the proposed basin.
The L/W ratio can be increased greatly by the use of internal spur dikes,
resulting in a higher hydraulic efficiency and a lower required total area. In the
absence of dye tracer data or values obtained from other theoretical approaches, a
value for HECF of 2.25 may be used based on field studies conducted at several
sites (Montgomery, Thackston, and Parker 1983).
Step 5 - Sample extraction. After the appropriate period of quiescent settling,
an interface will usually be evident between the supernatant water, with a low
concentration of suspended solids above, and the more concentrated settled
material below the interface. Samples of the supernatant water should be extracted
from the cylinder at a point midway between the water surface and interface using
syringe and tubing. Care should be taken not to resuspend the settled material.
Step 6 - Sample preservation and analyses. The sample should be analyzed
as soon as possible after extraction. If applicable water quality standards are in
terms of dissolved concentrations, the elutriate samples should be analysed for
dissolved concentrations of COC. If applicable water quality standards are in
terms of total or whole water concentrations, the elutriate samples should be split
and analysed for both dissolved and total concentrations of COC, and for total
suspended solids in milligrams per liter. This will allow the calculation of the
fraction of analytes in the total suspended solids in milligrams per kilogram SS.
Filtration using 0.45-um filters should be used to obtain subsamples for analysis of
dissolved concentrations. Samples to be analyzed for dissolved pesticides or
polychlorinated biphenyls (PCBs) must be free of particles but should not be
filtered because of the tendency for these materials to adsorb on the filter.
However, particulate matter can be removed before analysis by high-speed
centrifugation at 10,000 times gravity using Teflon, glass, or aluminum centrifuge
tubes (Fulk, Gruber, and Wullschleger 1975). The total suspended solids
concentration can also be determined by filtration (0.45 um).
B.2.3 Chemical analyses
Chemical analyses of the effluent elutriate samples should be performed
according to the guidance in Chapter 9 of the ITM (USEPA/USACE 1998).
B6
Appendix B Column Settling Test and Effluent Elutriate Procedures
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