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C.3.2 Sediment characterization
The following sediment characterization test should be performed in
replicates of three on the dredged material in the lysimeter prior to each rainfall
simulation run (wet and dry).
Sediment Moisture. Three replicate samples (1 to 2 g) of wet sediment are
placed in preweighed aluminum pans and oven-dried at 95 EC for 48 hr. The
pans are then removed and reweighed to determine percent water on a dry weight
basis using the formula ((wet weight dry weight) /dry weight) H 100).
C.3.3 RSLS procedure
Up to eleven 208-L (45-gal) drums or 2,290 L of sediment are required to
conduct the RSLS test. The sediment is loaded into the lysimeter one drum at a
time, mixing as the sediment is dumped. Polyethylene shovels or large spatulas
are used to mix the material as effectively as possible. Final depth of the
sediment in the lysimeter is approximately 33.0 cm. The interstitial water is
allowed to evaporate and a series of rainfall simulations are conducted while the
sediment is still anaerobic. Three 30-min storm events at 5.08 cm/hr (2 in./hr) are
applied on successive days (Skogerboe et al. 1987). Runoff rates are measured
every minute, and 4-L runoff samples are collected at 5, 15, and 25 min after
runoff begins to occur. Additional samples are collected in 250-ml polyethylene
bottles for pH, electrical conductivity and suspended solids determinations every
minute through 15 min and then every 5 min thereafter to 30 min. The 4-L
samples are combined at the end of the each day's test representing one replicate
of three successive test runs. After the three test runs are complete the lysimeter
is moved outside and covered with a ventilated, transparent top, and the sediment
is allowed to dry and oxidize over a 6-month period. After 6 months of drying,
the lysimeter is moved back into the rainfall simulation bay and the three
consecutive storm events are repeated on the now dry and oxidized sediment.
The sampling protocol is the same as for the wet sediment.
C.3.4 Characterization of runoff samples and preparation for
analysis
The 250-mL samples collected are subjected to the determination of
suspended solids, pH and electrical conductivity as described below. The
composite runoff samples are split and half are placed into appropriate
containers for contaminants of concern for analysis of total contaminants. The
other half of the samples are prefiltered, if necessary, through a 2.7-um filter and
then filtered through a 0.45-um membrane filter for metals or a 0.7-um glass
fiber filter for organics to represent the soluble fraction of contaminants.
Preservation of filtered samples should be done according to specific
requirements for each contaminant according to USEPA (1986).
The samples should be analyzed as soon as possible after extraction.
Dissolved and, if required, total concentrations of desired analytes should be
C8
Appendix C Test Procedures for Surface Runoff Discharges

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