Tl. Wade et al., TIDAL RIVER SEDIMENTS IN THE WASHINGTON, DC AREA .2. DISTRIBUTION ANDSOURCES OF ORGANIC CONTAMINANTS, Estuaries, 17(2), 1994, pp. 321-333
Concentrations of aliphatic, aromatic, and chlorinated hydrocarbons we
re determined from 33 surface-sediment samples taken from the Tidal Ba
sin, Washington Ship Channel, and the Anacostia and Potomac rivers in
Washington, D.C. In conjunction with these samples, selected storm sew
ers and outfalls also were sampled to help elucidate general sources o
f contamination to the area. All of the sediments contained detectable
concentrations of aliphatic and aromatic hydrocarbons, DDT (total dic
hlorodiphenyltrichloroethane), DDE (dichlorodiphenytdichloroethene), D
DD (dichlorodiphenyldichloroethane), PCBs (total polychlorinated biphe
nyls) and total chlordanes (oxy-, alpha-, and gamma-chlordane and cis
+ trans-nonachlor). Sediment concentrations of most contaminants were
highest in the Anacostia River just downstream of the Washington Navy
Yard, except for total chlordane, which appeared to have upstream sour
ces in addition to storm and combined sewer runoff. This area has the
highest number of storm and combined sewer outfalls in the river. Poto
mac River stations had lower concentrations than other stations. Total
hydrocarbons (THC), normalized to the fine-grain fraction (clay + sil
t, <63 mu m), ranged from 120 mu g g(-1) to 1,900 mu g g(-1) fine-grai
n sediment. The hydrocarbons were dominated by the unresolved complex
mixture (UCM), with total polycyclic aromatic hydrocarbons (PAHs) conc
entrations ranging from 4 mu g. g(-1) to 33 mu g g(-1) fine-grain sedi
ment. Alkyl-substituted compounds (e.g., C1 to C4 methyl groups) of na
phthalene, fluorene, phenanthrene + anthracene, and chrysene series do
minated the polycyclic aromatic hydrocarbons (PAHs). Polycyclic aromat
ic hydrocarbons, saturated hydrocarbons, and the unresolved complex mi
xture (UCM) distributions reflect mixtures of combustion products (i.e
., pyrogenic sources) and direct discharges of petroleum products. Tot
al PCB concentrations ranged from 0.075 mu g g(-1) to 2.6 mu g g(-1) f
ine-grain sediment, with highest concentrations in the Anacostia River
. Four to six C1-substituted biphenyls were the most-prevalent PCBs. V
ariability in the PCB distribution was observed in different sampling
areas, reflecting differing proportion of Arochlor inputs and degradat
ion The concentration of all contaminants was generally higher in sedi
ments closer to known sewer outfalls, with concentrations of total hyd
rocarbon, PAHs, and PCBs as high as 6,900 mu g g(-1), 620 mu g g(-1) a
nd 20 mu g g(-1) fine-grain sediment, respectively. Highest PCB concen
trations were found in two outfalls that drain into the Tidal Basin. C
oncentrations of organic contaminants from sewers draining to the Wash
ington Ship Channel and Anacostia River had higher concentrations than
sediments of the mid-channel or river. Sources of PCBs appear to be r
elated to specific outfalls, while hydrocarbon inputs, especially PAHs
, are diffuse, and may be related to street runoff. Whereas most point
-source contaminant inputs have been regulated, the importance of nonp
oint source inputs must be assessed for their potential addition of co
ntaminants to aquatic ecosystems. This study indicates that in large u
rban areas, nonpoint sources deliver substantial amounts of contaminan
ts to ecosystems through storm and combined sewer systems, and control
of these inputs must be addressed.