ID |
Site name |
Sample type |
Sample detail |
Date |
δ13C |
|
δ15N |
|
C/N atomic ratio |
Mean |
95%CI |
n |
Mean |
95%CI |
n |
low-N
n |
Mean |
95%CI |
n |
1-sf
n |
Late-Summer 1998 |
401 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, >80 μm |
– |
08-13-98 |
-35.03 |
0.11 |
6 |
|
9.34 |
0.33 |
6 |
0 |
|
5.39 |
0.38 |
6 |
0 |
402 |
Tualatin River at RM 5.5 (Stafford Road) |
Periphyton |
Species not identified |
08-13-98 |
-33.15 |
0.75 |
4 |
12.90 |
1.04 |
4 |
0 |
4.95 |
1.34 |
4 |
0 |
403 |
Tualatin River at RM 20.3 |
Periphyton |
Species not identified |
08-18-98 |
-18.42 |
0.22 |
3 |
5.80 |
0.44 |
3 |
0 |
11.68 |
1.12 |
3 |
0 |
404 |
Henry Hagg Lake |
Seston, >80 μm |
– |
08-11-98 |
-26.34 |
0.24 |
4 |
6.90 |
0.46 |
4 |
0 |
10.33 |
1.09 |
4 |
0 |
405 |
Tualatin River at RM 24.5 |
Duckweed |
Duckweed sorted from mat |
09-29-98 |
-29.44 |
0.12 |
4 |
6.82 |
0.34 |
4 |
0 |
11.85 |
0.94 |
4 |
0 |
406 |
Tualatin River at RM 5.5 (Stafford Road) |
Suspended sediment |
– |
09-17-98 |
-33.08 |
0.28 |
3 |
7.38 |
0.44 |
3 |
0 |
7.69 |
1.53 |
3 |
0 |
407 |
Tualatin River at RM 26.9 (Scholls) |
Suspended sediment |
– |
09-17-98 |
-27.95 |
0.21 |
4 |
4.93 |
0.50 |
4 |
0 |
11.40 |
1.45 |
4 |
0 |
408 |
Tualatin River at RM 5.5 (Stafford Road) |
Bed sediment |
– |
08-20-98 |
-28.03 |
0.36 |
9 |
4.32 |
0.67 |
9 |
2 |
16.22 |
2.43 |
9 |
4 |
409 |
Tualatin River at RM 26.9 (Scholls) |
Bed sediment |
– |
08-18-98 |
-27.52 |
0.29 |
9 |
3.79 |
1.02 |
9 |
0 |
17.52 |
3.29 |
9 |
4 |
410 |
Jackson Bottom (between Miller Swale and holding pond) |
Soil |
Chehalis soil |
10-06-98 |
-26.64 |
0.18 |
4 |
5.44 |
0.41 |
4 |
0 |
12.38 |
0.84 |
4 |
0 |
411 |
Zurcher Farm (Fernhill Road near Tualatin River) |
Soil |
Wapato soil |
10-06-98 |
-26.06 |
0.09 |
7 |
5.08 |
0.83 |
7 |
0 |
12.81 |
1.03 |
7 |
0 |
412 |
Oregon Graduate Institute (near Bronson Creek) |
Soil |
Woodburn soil |
10-06-98 |
-27.20 |
0.13 |
3 |
-0.87 |
0.93 |
3 |
0 |
24.60 |
1.63 |
3 |
0 |
413 |
Jackson Bottom (between Miller Swale and holding pond) |
Leaf litter |
Oregon Ash leaf litter |
10-06-98 |
-30.41 |
0.14 |
4 |
2.19 |
0.25 |
4 |
0 |
29.08 |
2.72 |
3 |
0 |
414 |
Tualatin River at RM 67.8 (Cherry Grove) |
Coniferous litter |
Western Red Cedar litter |
10-06-98 |
-26.80 |
0.39 |
3 |
-0.20 |
0.98 |
3 |
0 |
46.53 |
8.83 |
3 |
0 |
415 |
Tualatin River at RM 67.8 (Cherry Grove) |
Leaf litter |
Alder leaf litter |
10-06-98 |
-29.50 |
0.13 |
4 |
-1.64 |
0.10 |
4 |
0 |
32.93 |
2.29 |
4 |
0 |
416 |
Patton Valley Road (north side, 1 mi east of Cherry Grove) |
Coniferous litter |
Douglas Fir litter |
10-06-98 |
-27.41 |
0.14 |
4 |
-0.55 |
0.23 |
4 |
0 |
67.04 |
2.10 |
4 |
0 |
417 |
Patton Valley Road (north side,
1 mi east of Cherry Grove) |
Woody material |
Douglas Fir twigs |
10-06-98 |
-26.48 |
0.42 |
4 |
-2.87 |
0.14 |
4 |
1 |
77.75 |
27.70 |
4 |
0 |
418 |
Rock Creek Wastewater Treatment Facility |
WWTF effluent particulate |
– |
10-06-98 |
-26.64 |
0.16 |
4 |
11.61 |
1.03 |
4 |
0 |
5.47 |
1.77 |
4 |
0 |
419 |
Tualatin River at RM 5.5 (Stafford Road) |
Bryozoan |
– |
08-13-98 |
-35.36 |
0.32 |
4 |
16.13 |
1.34 |
4 |
0 |
4.24 |
1.34 |
4 |
0 |
Mid-Summer 1999 |
1 |
Henry Hagg Lake |
Seston, >80 μm |
– |
07-09-99 |
-29.06 |
0.38 |
4 |
7.04 |
0.48 |
4 |
0 |
5.41 |
0.86 |
4 |
0 |
2 |
Henry Hagg Lake |
Seston, 80–202 μm |
– |
07-09-99 |
-28.91 |
0.34 |
3 |
6.33 |
0.53 |
3 |
0 |
5.83 |
0.18 |
3 |
0 |
3 |
Tualatin River at RM 20.3 |
Seston, >80 μm |
– |
07-14-99 |
-30.46 |
0.16 |
3 |
7.77 |
0.63 |
3 |
0 |
11.35 |
1.07 |
3 |
0 |
4 |
Tualatin River at RM 20.3 |
Seston, 80–202 μm |
– |
07-14-99 |
-30.70 |
0.15 |
4 |
7.75 |
0.93 |
4 |
0 |
10.19 |
1.02 |
4 |
0 |
5 |
Tualatin River at RM 20.3 |
Duckweed |
Duckweed sorted from mat |
07-14-99 |
-28.65 |
0.14 |
3 |
10.48 |
0.81 |
3 |
0 |
14.61 |
1.00 |
3 |
0 |
6 |
Tualatin River at RM 20.3 |
Woody material |
Twigs sorted from duckweed mat |
07-14-99 |
-29.03 |
0.78 |
3 |
2.65 |
0.48 |
3 |
0 |
31.62 |
5.83 |
3 |
0 |
7 |
Tualatin River at RM 20.3 |
Suspended sediment |
– |
07-14-99 |
-32.24 |
0.31 |
4 |
8.99 |
0.52 |
4 |
0 |
7.61 |
1.16 |
4 |
0 |
8 |
Tualatin River at RM 20.3 |
Bed sediment |
– |
07-14-99 |
-27.46 |
0.12 |
3 |
5.63 |
3.01 |
2 |
0 |
14.67 |
1.74 |
3 |
2 |
10 |
Tualatin River at RM 20.3 |
Coniferous litter |
Cones sorted from duckweed mat |
07-14-99 |
-27.25 |
0.35 |
3 |
0.16 |
3.34 |
3 |
3 |
110.57 |
25.40 |
3 |
0 |
12 |
Tualatin River at RM 20.3 |
Leaf litter |
Oregon Ash seed pods from river surface |
07-14-99 |
-25.55 |
0.31 |
4 |
1.51 |
0.75 |
4 |
1 |
64.88 |
15.43 |
4 |
0 |
13 |
Tualatin River at RM 20.3 |
Leaf litter |
Oregon Ash leaves from river surface |
07-14-99 |
-27.06 |
0.40 |
3 |
0.88 |
0.75 |
3 |
0 |
30.96 |
3.81 |
3 |
0 |
14 |
Tualatin River at RM 26.9 (Scholls) |
Seston, >80 μm |
– |
07-14-99 |
-28.51 |
0.13 |
3 |
6.67 |
0.60 |
3 |
0 |
16.55 |
2.43 |
3 |
0 |
15 |
Tualatin River at RM 26.9 (Scholls) |
Seston, 80–202 μm |
– |
07-14-99 |
-28.27 |
0.18 |
3 |
6.24 |
0.57 |
3 |
2 |
17.23 |
0.99 |
3 |
0 |
16 |
Tualatin River at RM 26.9 (Scholls) |
Suspended sediment |
– |
07-14-99 |
-28.55 |
0.28 |
4 |
6.81 |
0.91 |
4 |
2 |
9.47 |
1.33 |
4 |
0 |
17 |
Tualatin River at RM 26.9 (Scholls) |
Bed sediment |
– |
07-14-99 |
-27.51 |
0.38 |
3 |
5.89 |
0.70 |
3 |
0 |
14.73 |
2.24 |
3 |
0 |
18 |
Tualatin River at RM 26.9 (Scholls) |
Duckweed |
Duckweed sorted from mat |
07-14-99 |
-28.48 |
na |
1 |
9.32 |
na |
1 |
0 |
12.00 |
na |
1 |
0 |
19 |
Tualatin River at RM 26.9 (Scholls) |
Woody material |
Twigs sorted from duckweed mat |
07-14-99 |
-26.45 |
0.84 |
3 |
5.36 |
0.81 |
3 |
0 |
28.31 |
2.00 |
3 |
0 |
20 |
Tualatin River at RM 38.4
(Rood Bridge) |
Suspended sediment |
– |
07-14-99 |
-28.14 |
0.11 |
4 |
6.41 |
0.35 |
4 |
0 |
10.49 |
0.92 |
4 |
0 |
21 |
Tualatin River at RM 38.4
(Rood Bridge) |
Bed sediment |
– |
07-14-99 |
-26.74 |
0.46 |
3 |
4.81 |
0.61 |
3 |
0 |
13.66 |
1.20 |
3 |
3 |
22 |
Gales Creek at Old Highway 47 |
Suspended sediment |
– |
07-16-99 |
-26.39 |
0.14 |
3 |
4.60 |
0.48 |
3 |
0 |
8.60 |
1.30 |
3 |
0 |
23 |
Gales Creek at Old Highway 47 |
Bed sediment |
– |
07-16-99 |
-27.15 |
0.15 |
4 |
2.62 |
0.63 |
4 |
4 |
14.61 |
4.16 |
4 |
4 |
24 |
Dairy Creek at Highway 8 |
Suspended sediment |
– |
07-16-99 |
-29.59 |
0.18 |
3 |
6.17 |
0.36 |
3 |
0 |
8.91 |
1.32 |
3 |
0 |
25 |
Dairy Creek at Highway 8 |
Bed sediment |
– |
07-16-99 |
-26.92 |
0.46 |
3 |
4.30 |
0.51 |
2 |
1 |
16.50 |
2.52 |
3 |
2 |
26 |
Tualatin River at RM 58.8 (Dilley) |
Suspended sediment |
– |
07-16-99 |
-27.63 |
0.53 |
3 |
4.10 |
0.74 |
3 |
3 |
11.08 |
3.22 |
3 |
3 |
27 |
Tualatin River at RM 58.8 (Dilley) |
Bed sediment |
– |
07-16-99 |
-27.06 |
0.33 |
3 |
2.71 |
0.69 |
3 |
3 |
15.35 |
2.75 |
3 |
3 |
28 |
Rock Creek at Highway 8 |
Suspended sediment |
– |
07-16-99 |
-29.21 |
0.31 |
3 |
5.22 |
1.69 |
3 |
1 |
10.31 |
1.66 |
3 |
0 |
29 |
Rock Creek at Highway 8 |
Bed sediment |
– |
07-16-99 |
-27.98 |
0.13 |
3 |
5.81 |
0.69 |
3 |
0 |
15.31 |
1.05 |
3 |
0 |
30 |
Tualatin River at RM 5.5 (Stafford Road) |
Suspended sediment |
– |
07-16-99 |
-35.41 |
0.18 |
3 |
9.11 |
0.73 |
3 |
0 |
5.78 |
1.41 |
3 |
0 |
31 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, >80 μm |
– |
07-19-99 |
-37.46 |
0.23 |
3 |
9.01 |
0.63 |
3 |
0 |
5.87 |
1.39 |
3 |
0 |
32 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, 80–202 μm |
– |
07-19-99 |
-37.64 |
0.05 |
4 |
9.22 |
0.57 |
4 |
0 |
5.92 |
0.44 |
4 |
0 |
33 |
Tualatin River at RM 5.5 (Stafford Road) |
Bed sediment |
– |
07-19-99 |
-27.41 |
0.72 |
4 |
5.74 |
1.17 |
3 |
0 |
12.35 |
1.96 |
4 |
0 |
34 |
Tualatin River at RM 5.5 (Stafford Road) |
Periphyton |
Spirogyra |
07-19-99 |
-17.36 |
0.22 |
3 |
6.87 |
0.55 |
3 |
0 |
10.64 |
1.03 |
3 |
0 |
35 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, >80 μm |
– |
07-19-99 |
-35.05 |
0.20 |
3 |
8.25 |
0.54 |
3 |
0 |
7.29 |
1.33 |
3 |
0 |
36 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, 80–202 μm |
– |
07-19-99 |
-34.99 |
0.33 |
3 |
9.10 |
1.01 |
3 |
3 |
6.92 |
1.41 |
3 |
0 |
37 |
Tualatin River at RM 9.9
(Cook Park) |
Suspended sediment |
– |
07-19-99 |
-34.98 |
0.12 |
4 |
7.29 |
0.82 |
3 |
0 |
6.86 |
0.78 |
5 |
0 |
38 |
Tualatin River at RM 9.9
(Cook Park) |
Bed sediment |
– |
07-19-99 |
-28.16 |
0.22 |
6 |
5.48 |
0.29 |
6 |
6 |
13.97 |
1.54 |
6 |
6 |
39 |
Tualatin River at RM 9.9
(Cook Park) |
Duckweed |
Unsorted duckweed mat |
07-19-99 |
-28.50 |
0.33 |
4 |
3.20 |
0.33 |
4 |
0 |
27.21 |
1.32 |
4 |
0 |
40 |
Tualatin River at RM 9.9
(Cook Park) |
Duckweed |
Duckweed sorted from mat |
07-19-99 |
-29.85 |
0.06 |
3 |
6.90 |
0.39 |
3 |
0 |
11.25 |
1.00 |
3 |
0 |
41 |
Tualatin River at RM 9.9
(Cook Park) |
Woody material |
Twigs sorted from duckweed mat |
07-19-99 |
-27.82 |
1.11 |
6 |
2.30 |
0.15 |
6 |
0 |
29.96 |
0.41 |
6 |
0 |
42 |
Tualatin River at RM 9.9
(Cook Park) |
Coniferous litter |
Cones sorted from duckweed mat |
07-19-99 |
-26.55 |
0.05 |
3 |
0.72 |
1.03 |
3 |
3 |
90.52 |
16.79 |
3 |
0 |
43 |
Tualatin River at RM 9.9
(Cook Park) |
Soil |
A-horizon from bank with slump |
07-19-99 |
-26.10 |
0.22 |
3 |
1.38 |
1.12 |
3 |
0 |
29.92 |
3.08 |
3 |
0 |
44 |
Tualatin River at RM 9.9
(Cook Park) |
Soil |
Bottom of slump at water edge |
07-19-99 |
-27.12 |
0.28 |
3 |
5.29 |
1.71 |
4 |
4 |
14.29 |
3.14 |
4 |
4 |
45 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Seston, >80 μm |
– |
07-19-99 |
-34.88 |
0.21 |
3 |
10.58 |
0.99 |
3 |
0 |
7.61 |
1.24 |
3 |
0 |
46 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Seston, 80–202 μm |
– |
07-19-99 |
-34.83 |
0.26 |
3 |
10.88 |
1.15 |
3 |
3 |
7.65 |
1.45 |
3 |
0 |
47 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Suspended sediment |
– |
07-19-99 |
-35.82 |
0.13 |
4 |
12.19 |
1.11 |
4 |
0 |
6.96 |
1.16 |
4 |
0 |
48 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Bed sediment |
– |
07-19-99 |
-27.84 |
1.00 |
4 |
5.57 |
1.59 |
4 |
4 |
13.77 |
2.12 |
4 |
4 |
49 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Suspended sediment |
Fraction that settled after 24 hours |
07-21-99 |
-29.79 |
0.68 |
4 |
5.55 |
1.31 |
3 |
0 |
9.06 |
0.87 |
4 |
0 |
50 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, >80 μm |
Aphanizomenon floating on sample |
07-21-99 |
-34.42 |
0.32 |
3 |
7.58 |
0.64 |
3 |
0 |
4.37 |
1.63 |
3 |
0 |
51 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, >80 μm |
– |
07-21-99 |
-29.36 |
0.39 |
7 |
na |
na |
0 |
0 |
12.35 |
0.53 |
7 |
0 |
52 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, 80–202 μm |
– |
07-21-99 |
-30.45 |
0.49 |
3 |
5.98 |
0.94 |
3 |
3 |
10.07 |
1.27 |
3 |
0 |
53 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Bed sediment |
– |
07-21-99 |
-27.18 |
0.87 |
3 |
5.20 |
0.62 |
3 |
1 |
17.02 |
4.70 |
3 |
3 |
54 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Woody material |
Twigs removed from bed sediment |
07-21-99 |
-27.01 |
0.62 |
4 |
4.56 |
0.47 |
4 |
4 |
91.83 |
12.02 |
2 |
0 |
55 |
Fanno Creek at Durham
City Park |
Suspended sediment |
Fraction that settled after 24 hours |
07-21-99 |
-29.01 |
0.54 |
4 |
4.82 |
1.42 |
4 |
0 |
13.52 |
0.54 |
4 |
0 |
56 |
Fanno Creek at Durham
City Park |
Seston, >80 μm |
– |
07-21-99 |
-28.74 |
0.64 |
6 |
6.26 |
1.00 |
6 |
6 |
13.06 |
1.29 |
6 |
0 |
57 |
Fanno Creek at Durham
City Park |
Seston, 80–202 μm |
– |
07-21-99 |
-28.41 |
0.47 |
3 |
5.37 |
0.45 |
3 |
3 |
14.43 |
1.02 |
3 |
0 |
58 |
Fanno Creek at Durham
City Park |
Bed sediment |
– |
07-21-99 |
-28.01 |
0.18 |
4 |
3.57 |
0.78 |
4 |
4 |
14.58 |
4.04 |
4 |
4 |
59 |
Fanno Creek at Durham
City Park |
Bed sediment |
Top 10 cm, both oxic and anoxic fractions |
07-21-99 |
-27.99 |
0.30 |
3 |
3.56 |
0.88 |
3 |
0 |
17.42 |
4.00 |
3 |
0 |
60 |
Fanno Creek at Durham
City Park |
Leaf litter |
Redtwig dogwood leaves in stream |
07-21-99 |
-29.60 |
0.17 |
3 |
4.46 |
0.53 |
3 |
0 |
33.94 |
2.90 |
3 |
0 |
61 |
Fanno Creek at Durham
City Park |
Leaf litter |
Oregon Ash leaves in stream |
07-21-99 |
-26.80 |
0.10 |
3 |
3.17 |
0.54 |
3 |
0 |
51.42 |
9.59 |
3 |
0 |
62 |
Fanno Creek at Durham
City Park |
Decomposed terrestrial detritus |
Decomposed leaves & twigs in stream |
07-21-99 |
-27.85 |
0.43 |
3 |
4.92 |
0.74 |
3 |
0 |
22.21 |
4.13 |
3 |
0 |
63 |
Fanno Creek at Durham
City Park |
Leaf litter |
Oregon Ash leaves from trail |
07-21-99 |
-27.29 |
0.91 |
3 |
0.88 |
0.37 |
4 |
0 |
19.95 |
5.21 |
2 |
0 |
64 |
Fanno Creek at Durham
City Park |
Leaf litter |
Oregon Ash seed pods from trail |
07-21-99 |
-26.80 |
0.95 |
5 |
0.80 |
0.44 |
5 |
0 |
46.79 |
4.19 |
5 |
0 |
65 |
Fanno Creek at Durham
City Park |
Periphyton |
Cladophera |
07-21-99 |
-39.69 |
0.11 |
3 |
4.56 |
0.31 |
3 |
0 |
8.00 |
1.21 |
3 |
0 |
67 |
Tualatin River at RM 9.4
(Basalt sill) |
Periphyton |
Cladophera |
07-19-99 |
-34.14 |
0.15 |
3 |
5.50 |
0.39 |
3 |
0 |
11.02 |
1.10 |
3 |
0 |
68 |
Onion Flat (Cipole Road
and Highway 99W) |
Soil |
Agricultural field, tilled, not planted |
07-21-99 |
-27.87 |
0.13 |
2 |
4.81 |
1.02 |
3 |
0 |
17.40 |
1.58 |
3 |
0 |
69 |
Jackson Bottom (between Miller Swale and holding pond) |
Soil |
Chehalis soil |
08-04-99 |
-27.21 |
0.31 |
3 |
6.12 |
0.90 |
3 |
0 |
11.14 |
1.41 |
3 |
0 |
70 |
Jackson Bottom (between Miller Swale and holding pond) |
Leaf litter |
Oregon Ash leaves |
08-04-99 |
-25.06 |
0.48 |
3 |
2.02 |
0.98 |
3 |
0 |
66.10 |
7.82 |
3 |
0 |
71 |
Tualatin Nature Park |
Coniferous litter |
Mixed Western Red Cedar litter |
08-04-99 |
-24.91 |
0.29 |
3 |
-2.53 |
1.09 |
3 |
0 |
37.02 |
3.89 |
3 |
0 |
72 |
Tualatin Nature Park |
Coniferous litter |
Mixed Douglas Fir litter |
08-04-99 |
-27.83 |
0.29 |
3 |
-2.62 |
1.12 |
3 |
0 |
31.90 |
2.20 |
3 |
0 |
73 |
Rock Creek Wastewater Treatment Facility |
WWTF effluent particulate |
– |
07-14-99 |
-24.77 |
1.13 |
6 |
10.46 |
0.84 |
6 |
0 |
6.14 |
0.90 |
6 |
0 |
74 |
Durham Wastewater Treatment Facility |
WWTF effluent particulate |
– |
07-14-99 |
-26.01 |
0.10 |
3 |
9.26 |
0.71 |
3 |
3 |
5.31 |
1.47 |
3 |
3 |
76 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Suspended sediment |
Fraction remaining suspended after 24 hours |
07-21-99 |
-33.86 |
0.09 |
3 |
6.60 |
0.38 |
3 |
0 |
5.57 |
1.42 |
3 |
0 |
77 |
Fanno Creek at Durham
City Park |
Suspended sediment |
Fraction remaining suspended after 24 hours |
07-21-99 |
-28.41 |
0.17 |
3 |
5.06 |
0.38 |
3 |
1 |
10.14 |
1.25 |
3 |
3 |
Late-Summer 1999 |
101 |
Henry Hagg Lake |
Seston, >80 μm |
– |
09-10-99 |
-30.18 |
0.16 |
3 |
8.46 |
0.79 |
3 |
0 |
4.47 |
1.54 |
3 |
0 |
102 |
Henry Hagg Lake |
Seston, 80–202 μm |
– |
09-10-99 |
-31.22 |
0.16 |
3 |
6.58 |
0.50 |
3 |
0 |
6.16 |
1.37 |
3 |
0 |
103 |
Tualatin River at RM 38.4
(Rood Bridge) |
Suspended sediment |
– |
09-10-99 |
-31.08 |
0.28 |
3 |
4.12 |
0.43 |
3 |
0 |
13.92 |
0.90 |
3 |
2 |
104 |
Tualatin River at RM 38.4
(Rood Bridge) |
Bed sediment |
– |
09-10-99 |
-27.88 |
0.46 |
8 |
3.95 |
0.10 |
8 |
0 |
16.13 |
1.03 |
8 |
1 |
105 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, >80 μm |
– |
09-11-99 |
-33.19 |
0.62 |
3 |
8.05 |
0.59 |
3 |
0 |
8.24 |
1.23 |
3 |
0 |
106 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, 80–202 μm |
– |
09-11-99 |
-33.00 |
0.36 |
3 |
7.59 |
0.60 |
3 |
0 |
8.85 |
1.23 |
3 |
0 |
107 |
Tualatin River at RM 9.9
(Cook Park) |
Suspended sediment |
– |
09-11-99 |
-34.06 |
0.14 |
4 |
7.35 |
0.41 |
4 |
0 |
8.71 |
1.04 |
4 |
0 |
108 |
Tualatin River at RM 9.9
(Cook Park) |
Bed sediment |
– |
09-11-99 |
-30.58 |
0.74 |
4 |
5.16 |
1.48 |
4 |
4 |
17.26 |
1.51 |
3 |
4 |
109 |
Tualatin River at RM 9.4
(Basalt sill) |
Periphyton |
Cladophera |
09-11-99 |
-35.50 |
0.13 |
3 |
4.28 |
0.59 |
3 |
0 |
10.03 |
1.13 |
3 |
0 |
110 |
Tualatin River at RM 20.3 |
Seston, >80 μm |
– |
09-13-99 |
-29.53 |
0.39 |
4 |
4.17 |
0.30 |
4 |
0 |
12.63 |
1.62 |
4 |
0 |
111 |
Tualatin River at RM 20.3 |
Seston, 80–202 μm |
– |
09-13-99 |
-30.86 |
0.41 |
3 |
5.88 |
0.93 |
3 |
0 |
11.91 |
2.31 |
3 |
0 |
112 |
Tualatin River at RM 20.3 |
Suspended sediment |
– |
09-13-99 |
-30.80 |
1.35 |
3 |
6.73 |
0.77 |
3 |
0 |
14.84 |
2.21 |
3 |
0 |
113 |
Tualatin River at RM 20.3 |
Bed sediment |
– |
09-13-99 |
-29.30 |
0.35 |
5 |
5.49 |
0.44 |
4 |
0 |
15.86 |
1.38 |
5 |
0 |
114 |
Tualatin River at RM 20.3 |
Bed sediment |
Anoxic blue-gray fraction |
09-13-99 |
-28.72 |
0.27 |
4 |
5.37 |
0.77 |
4 |
4 |
14.75 |
1.17 |
4 |
4 |
115 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Suspended sediment |
– |
09-13-99 |
-32.27 |
0.98 |
3 |
7.08 |
2.60 |
2 |
0 |
11.86 |
1.22 |
3 |
0 |
116 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, >80 μm |
– |
09-13-99 |
-31.07 |
0.51 |
3 |
5.96 |
0.37 |
3 |
1 |
10.05 |
1.17 |
3 |
0 |
117 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, 80–202 μm |
– |
09-13-99 |
-31.41 |
0.53 |
4 |
6.69 |
0.40 |
4 |
4 |
10.75 |
1.24 |
4 |
0 |
118 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Bed sediment |
– |
09-13-99 |
-28.72 |
0.08 |
3 |
6.05 |
0.36 |
3 |
0 |
16.45 |
0.99 |
3 |
0 |
119 |
Tualatin River at RM 26.9 (Scholls) |
Seston, >80 μm |
– |
09-15-99 |
-28.93 |
0.17 |
3 |
6.38 |
0.52 |
3 |
2 |
14.03 |
0.90 |
3 |
0 |
120 |
Tualatin River at RM 26.9 (Scholls) |
Seston, 80–202 μm |
– |
09-15-99 |
-29.00 |
0.13 |
4 |
5.75 |
0.32 |
4 |
0 |
14.47 |
0.89 |
4 |
0 |
121 |
Tualatin River at RM 26.9 (Scholls) |
Suspended sediment |
– |
09-15-99 |
-28.47 |
1.23 |
4 |
7.12 |
1.07 |
3 |
0 |
14.47 |
0.84 |
4 |
0 |
122 |
Tualatin River at RM 26.9 (Scholls) |
Bed sediment |
– |
09-15-99 |
-29.55 |
0.14 |
7 |
5.66 |
0.21 |
5 |
1 |
17.45 |
1.50 |
7 |
4 |
123 |
Tualatin River at RM 5.5 (Stafford Road) |
Suspended sediment |
– |
09-15-99 |
-33.68 |
0.30 |
3 |
12.79 |
1.29 |
3 |
0 |
9.54 |
1.18 |
3 |
0 |
124 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, >80 μm |
– |
09-15-99 |
-37.66 |
0.08 |
4 |
16.71 |
1.39 |
4 |
0 |
5.69 |
1.23 |
4 |
0 |
125 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, 80–202 μm |
– |
09-15-99 |
-38.23 |
0.50 |
3 |
17.36 |
2.39 |
2 |
0 |
5.31 |
1.46 |
3 |
0 |
126 |
Tualatin River at RM 5.5 (Stafford Road) |
Bed sediment |
– |
09-15-99 |
-29.42 |
0.08 |
3 |
6.29 |
0.57 |
3 |
0 |
13.05 |
1.21 |
3 |
0 |
Winter 2000 |
201 |
Tualatin River at RM 38.4
(Rood Bridge) |
Suspended sediment |
– |
02-08-00 |
-30.71 |
0.85 |
3 |
4.89 |
1.38 |
3 |
0 |
12.12 |
2.46 |
3 |
3 |
202 |
Tualatin River at RM 5.5 (Stafford Road) |
Suspended sediment |
– |
02-04-00 |
-32.01 |
0.46 |
5 |
4.05 |
1.06 |
5 |
5 |
16.19 |
1.51 |
5 |
5 |
203 |
Tualatin River at RM 26.9 (Scholls) |
Suspended sediment |
– |
02-04-00 |
-31.01 |
0.35 |
5 |
4.29 |
0.51 |
3 |
3 |
17.83 |
1.76 |
5 |
3 |
204 |
Tualatin River at RM 26.9 (Scholls) |
Bed sediment |
Woody debris removed |
02-04-00 |
-27.64 |
0.18 |
6 |
4.83 |
0.67 |
6 |
3 |
32.43 |
2.39 |
6 |
0 |
206 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Suspended sediment |
– |
02-04-00 |
-30.96 |
0.42 |
3 |
3.86 |
1.70 |
3 |
2 |
15.36 |
2.55 |
3 |
3 |
207 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Bed sediment |
– |
02-04-00 |
-28.55 |
0.31 |
4 |
4.07 |
0.42 |
4 |
4 |
27.11 |
2.24 |
4 |
4 |
208 |
Gales Creek at Old Highway 47 |
Suspended sediment |
– |
02-07-00 |
-28.88 |
1.91 |
3 |
3.60 |
0.80 |
2 |
2 |
33.00 |
5.73 |
3 |
2 |
209 |
Dairy Creek at Highway 8 |
Suspended sediment |
– |
02-07-00 |
-31.57 |
0.64 |
5 |
3.87 |
0.40 |
4 |
4 |
15.19 |
1.27 |
5 |
4 |
210 |
Tualatin River at RM 58.8 (Dilley) |
Suspended sediment |
– |
02-07-00 |
-29.55 |
0.72 |
6 |
3.61 |
0.69 |
6 |
4 |
16.51 |
1.44 |
6 |
6 |
211 |
Rock Creek at Highway 8 |
Suspended sediment |
– |
02-07-00 |
-32.51 |
0.79 |
4 |
4.59 |
0.44 |
4 |
4 |
17.58 |
2.33 |
4 |
4 |
212 |
Fanno Creek at Durham Road |
Suspended sediment |
– |
02-07-00 |
-31.66 |
0.71 |
6 |
4.34 |
0.53 |
6 |
6 |
16.11 |
1.19 |
6 |
6 |
Early-Summer 2000 |
301 |
Henry Hagg Lake |
Seston, >80 μm |
– |
06-03-00 |
-26.37 |
0.17 |
4 |
3.38 |
0.24 |
4 |
0 |
11.49 |
0.43 |
4 |
0 |
302 |
Henry Hagg Lake |
Seston, 80–202 μm |
– |
06-03-00 |
-26.34 |
0.80 |
4 |
3.03 |
0.14 |
4 |
1 |
10.07 |
0.56 |
4 |
0 |
303 |
Tualatin River at RM 38.4
(Rood Bridge) |
Suspended sediment |
– |
06-05-00 |
-31.14 |
0.13 |
4 |
5.39 |
0.18 |
4 |
0 |
11.56 |
0.55 |
4 |
0 |
304 |
Tualatin River at RM 38.4
(Rood Bridge) |
Bed sediment |
– |
06-05-00 |
-28.12 |
0.12 |
3 |
4.06 |
0.49 |
3 |
0 |
15.81 |
1.23 |
3 |
0 |
305 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, >80 μm |
– |
06-03-00 |
-32.55 |
0.20 |
3 |
9.02 |
0.49 |
3 |
0 |
8.87 |
0.22 |
3 |
0 |
306 |
Tualatin River at RM 9.9
(Cook Park) |
Seston, 80–202 μm |
– |
06-03-00 |
-32.56 |
0.15 |
4 |
8.68 |
0.48 |
4 |
0 |
8.95 |
0.22 |
4 |
0 |
307 |
Tualatin River at RM 9.9
(Cook Park) |
Suspended sediment |
– |
06-03-00 |
-35.07 |
0.17 |
3 |
9.50 |
0.08 |
3 |
0 |
7.82 |
0.35 |
3 |
0 |
308 |
Tualatin River at RM 9.9
(Cook Park) |
Bed sediment |
– |
06-03-00 |
-28.67 |
0.40 |
3 |
5.27 |
0.62 |
3 |
3 |
15.79 |
0.74 |
3 |
3 |
309 |
Tualatin River at RM 9.9
(Cook Park) |
Duckweed |
Decomposed duckweed |
06-03-00 |
-28.73 |
0.88 |
4 |
7.08 |
1.63 |
3 |
0 |
12.73 |
0.54 |
4 |
0 |
310 |
Tualatin River at RM 9.4
(Basalt sill) |
Periphyton |
Cladophera |
06-03-00 |
-36.21 |
0.04 |
4 |
6.81 |
0.27 |
4 |
0 |
9.66 |
0.32 |
4 |
0 |
311 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Seston, >80 μm |
– |
06-03-00 |
-32.61 |
0.18 |
3 |
9.99 |
0.13 |
3 |
0 |
9.56 |
0.20 |
3 |
0 |
312 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Seston, 80–202 μm |
– |
06-03-00 |
-32.64 |
0.06 |
3 |
9.15 |
0.64 |
3 |
0 |
10.17 |
0.27 |
3 |
0 |
313 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Suspended sediment |
– |
06-03-00 |
-35.22 |
0.97 |
3 |
11.46 |
1.08 |
3 |
3 |
7.70 |
0.10 |
3 |
0 |
314 |
Tualatin River at RM 8.7
(Boones Ferry Bridge) |
Bed sediment |
– |
06-03-00 |
-28.81 |
0.16 |
3 |
5.92 |
0.34 |
3 |
3 |
15.49 |
0.94 |
3 |
3 |
315 |
Tualatin River at RM 20.3 |
Seston, >80 μm |
– |
06-05-00 |
-29.61 |
0.29 |
3 |
8.04 |
0.93 |
3 |
0 |
15.27 |
1.37 |
3 |
0 |
316 |
Tualatin River at RM 20.3 |
Seston, 80–202 μm |
– |
06-05-00 |
-29.77 |
0.02 |
4 |
7.63 |
0.69 |
4 |
0 |
15.43 |
0.40 |
4 |
0 |
317 |
Tualatin River at RM 20.3 |
Suspended sediment |
– |
06-05-00 |
-32.55 |
0.32 |
3 |
8.77 |
0.12 |
3 |
0 |
10.20 |
0.18 |
3 |
0 |
318 |
Tualatin River at RM 20.3 |
Bed sediment |
– |
06-05-00 |
-28.29 |
0.20 |
3 |
5.47 |
0.29 |
3 |
0 |
15.09 |
0.49 |
3 |
0 |
319 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Suspended sediment |
– |
06-02-00 |
-30.24 |
0.48 |
3 |
10.63 |
1.35 |
3 |
0 |
12.93 |
0.56 |
3 |
0 |
320 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, >80 μm |
– |
06-02-00 |
-29.21 |
0.34 |
3 |
10.25 |
0.25 |
3 |
0 |
12.99 |
1.08 |
3 |
0 |
321 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Seston, 80–202 μm |
– |
06-02-00 |
-31.62 |
0.18 |
3 |
10.37 |
0.77 |
3 |
2 |
10.99 |
0.15 |
3 |
0 |
322 |
Tualatin River at RM 16.2 (Elsner Bridge) |
Bed sediment |
– |
06-02-00 |
-27.93 |
0.44 |
3 |
5.22 |
0.13 |
3 |
0 |
15.17 |
1.27 |
3 |
0 |
323 |
Tualatin River at RM 26.9 (Scholls) |
Seston, >80 μm |
– |
06-02-00 |
-28.93 |
0.13 |
4 |
6.23 |
0.57 |
4 |
2 |
17.79 |
0.30 |
4 |
0 |
324 |
Tualatin River at RM 26.9 (Scholls) |
Seston, 80–202 μm |
– |
06-02-00 |
-29.11 |
0.07 |
3 |
5.55 |
1.47 |
3 |
3 |
17.81 |
0.25 |
3 |
0 |
325 |
Tualatin River at RM 26.9 (Scholls) |
Suspended sediment |
– |
06-02-00 |
-31.13 |
0.66 |
3 |
7.05 |
0.08 |
3 |
0 |
6.94 |
0.69 |
3 |
0 |
326 |
Tualatin River at RM 26.9 (Scholls) |
Bed sediment |
– |
06-02-00 |
-27.80 |
0.55 |
4 |
5.26 |
0.27 |
4 |
0 |
9.48 |
1.32 |
4 |
0 |
327 |
Tualatin River at RM 5.5 (Stafford Road) |
Suspended sediment |
– |
06-02-00 |
-33.51 |
0.44 |
3 |
12.10 |
0.29 |
3 |
0 |
10.63 |
0.44 |
3 |
0 |
328 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, >80 μm |
– |
06-02-00 |
-37.81 |
0.23 |
3 |
13.58 |
0.22 |
3 |
0 |
7.51 |
0.02 |
3 |
0 |
329 |
Tualatin River at RM 5.5 (Stafford Road) |
Seston, 80–202 μm |
– |
06-02-00 |
-37.99 |
0.20 |
3 |
13.74 |
0.10 |
3 |
0 |
7.14 |
0.13 |
3 |
0 |
330 |
Tualatin River at RM 5.5 (Stafford Road) |
Bed sediment |
– |
06-02-00 |
-28.15 |
0.16 |
4 |
5.77 |
0.23 |
4 |
0 |
9.22 |
0.57 |
3 |
0 |
331 |
Gales Creek at Old Highway 47 |
Suspended sediment |
– |
05-31-00 |
-29.72 |
0.10 |
3 |
3.02 |
0.44 |
3 |
0 |
9.68 |
1.20 |
3 |
0 |
332 |
Gales Creek at Old Highway 47 |
Bed sediment |
– |
05-31-00 |
-27.61 |
0.23 |
3 |
1.72 |
0.29 |
3 |
0 |
12.64 |
3.63 |
3 |
0 |
333 |
Tualatin River at RM 58.8 (Dilley) |
Suspended sediment |
– |
05-31-00 |
-30.62 |
0.59 |
4 |
4.64 |
0.20 |
4 |
0 |
10.50 |
0.39 |
4 |
0 |
334 |
Tualatin River at RM 58.8 (Dilley) |
Bed sediment |
– |
05-31-00 |
-27.77 |
0.17 |
3 |
2.48 |
0.21 |
3 |
0 |
13.10 |
3.56 |
3 |
0 |
335 |
Dairy Creek at Highway 8 |
Suspended sediment |
– |
05-31-00 |
-31.34 |
0.14 |
3 |
3.71 |
0.02 |
3 |
0 |
8.94 |
3.36 |
3 |
0 |
336 |
Dairy Creek at Highway 8 |
Bed sediment |
– |
05-31-00 |
-27.77 |
0.11 |
4 |
3.69 |
0.26 |
4 |
0 |
18.09 |
2.05 |
4 |
0 |
337 |
Dairy Creek at Highway 8 |
Grass |
Grass growing in stream |
05-31-00 |
-31.09 |
0.13 |
3 |
4.64 |
0.15 |
3 |
0 |
16.92 |
1.35 |
3 |
0 |
338 |
Rock Creek at Highway 8 |
Suspended sediment |
– |
05-31-00 |
-32.01 |
0.15 |
3 |
5.61 |
0.14 |
3 |
0 |
7.71 |
1.27 |
3 |
0 |
339 |
Rock Creek at Highway 8 |
Bed sediment |
– |
05-31-00 |
-28.79 |
0.29 |
3 |
5.56 |
0.03 |
3 |
0 |
17.31 |
1.47 |
3 |
0 |
340 |
Rock Creek at Highway 8 |
Periphyton |
Species not identified |
05-31-00 |
-42.84 |
0.22 |
4 |
3.54 |
0.03 |
4 |
0 |
8.08 |
0.08 |
4 |
0 |
341 |
Rock Creek at Highway 8 |
Decomposed terrestrial detritus |
Decomposed non-woody plant material in stream |
05-31-00 |
-28.92 |
1.24 |
3 |
5.00 |
0.07 |
3 |
0 |
23.13 |
2.41 |
3 |
0 |
342 |
Fanno Creek at Durham
City Park |
Suspended sediment |
– |
05-31-00 |
-31.82 |
0.18 |
3 |
4.43 |
0.46 |
3 |
0 |
8.86 |
0.68 |
3 |
0 |
343 |
Fanno Creek at Durham
City Park |
Bed sediment |
– |
05-31-00 |
-28.58 |
0.49 |
4 |
4.13 |
0.19 |
4 |
0 |
13.00 |
1.40 |
4 |
0 |
344 |
Rock Creek Wastewater Treatment Facility |
WWTF effluent particulate |
– |
06-01-00 |
-27.41 |
0.77 |
3 |
10.14 |
0.21 |
3 |
2 |
8.04 |
2.83 |
3 |
2 |
345 |
Durham Wastewater Treatment Facility |
WWTF effluent particulate |
– |
06-01-00 |
-27.94 |
1.18 |
3 |
7.15 |
0.60 |
3 |
0 |
7.44 |
0.89 |
3 |
2 |