Water, suspended particulate materials (SPM), and biota were sampled b
etween June 14 and 22, 1992 at forty-five mid-channel sites along a do
wnstream gradient in the lower 350 km of the Columbia River drainage,
at four mid-channel sites in the lower 27 km of the Willamette drainag
e and at the mouths of nine smaller tributaries to the Columbia. Water
samples were analyzed for nutrient (ammonium, nitrate, phosphate, sil
icate), dissolved organic carbon (DOC) and SPM concentrations, bacteri
al cell density and activity, and zooplankton composition and density.
The SPM samples were analyzed for particulate organic carbon (POC), p
lant pigment (chlorophyll and pheopigment) and major metal (Al, Mn, Ti
, V) content as well as stable isotopic (delta(1) 3C) composition of t
he POC. Willamette waters displayed significantly higher nutrient and
DOC concentrations than those in the mainstem Columbia or any of the s
maller tributaries. Elevated nutrient and DOC concentrations are attri
buted to runoff from the extensive agricultural lands found throughout
the Willamette Valley. Regardless of collection site, total Al conten
t of all riverborne particles was high (5.8 +/- 0.5% by weight), indic
ating total SPM mass was predominantly (similar to 70%) detrital miner
al. Nonetheless, the majority of riverborne organic matter was not all
ochthonous but rather derived from healthy phytoplankton as indicated
by high chlorophyll a to POC (Chl:POC) values. Chlorophyll a concentra
tion increased by almost 100% downstream in the mainstem Columbia betw
een Bonneville Dam and the estuary. This apparent increase in phytopla
nkton biomass was not accompanied by a parallel decrease in any nutrie
nt concentration probably because non-point source additions occurred
all along the drainage and compensated for nutrient loss due to phytop
lankton growth. Despite nutrient concentrations near eutrophic levels,
phytoplankton biomass in the Willamette was significantly lower than
that in the mainstem Columbia. This particular contrast between the Wi
llamette and the mainstem Columbia is likely due to light limitation i
mposed on the phytoplankton by specific differences in the mixing dyna
mics of the two flow regimes. POC in Willamette waters displayed a 50%
reduced chlorophyll content and 2-2.5% C-13-depletion relative to tha
t present in waters from the mainstem Columbia. These compositional di
ssimilarities may simply reflect physiological difference between the
diatom communities that comprised the bulk of phytoplankton in these t
wo systems at the time of sampling. Alternatively, they may be caused
by greater contribution of POC from non-phytoplankton sources in the W
illamette. An argument is advanced suggesting that methanotrophy has c
ontributed up to 5% of the POC that was measured in the Willamette Riv
er at the time of our study.