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III.5 - Transportation validation

A validation of transportation calibration was initiated by comparing model predicted measures of TBR to observed TBR values from transportation experiments conducted between 1968 and 1987. The analysis is preliminary at this time. Information was obtained by Fisher (1993).

Table 81 Estimated and Observed transport benefits ratios (TBR) for experiments conducted in the Snake River (Fisher 1993).
Year Species TBRestimated TBR observed
1968 spring 1.50 1.57
1969 spring 1.77 0.96
1969 steelhead 1.93 2.75
1972 spring 8.95 1.10
1973 spring 8.23 16.08
1975 spring 3.15 2.02
1975 steelhead 3.21 3.61
1976 spring 4.92 1.17
1976 steelhead 3.21 2.66
1977 spring 31.74 NA
1977 steelhead 7.04 NA
1978 fall 2.57 5.16
1978 spring 2.10 3.68
1978 steelhead 2.89 4.83
1979 fall 3.18 6.29
1979 spring(lgs) 1.72 3.42
1979 spring(mcn) 1.76 0.64
1979 steel(lgr) 1.59 1.78
1979 steel(mcn) 1.96 NA
1980 fall 2.73 3.63
1980 spring(mcn) 1.48 3.33
1980 steel(mcn) 1.41 NA
1980 spring(lgs) 1.88 NA
1980 steel(lgs) 2.38 1.71
1981 fall 2.24 3.63
1982 fall 2.84 0.99
1982 fall 2.54 4.88
1982 fall 2.25 1.30
1983 fall 2.53 2.10
1983 fall 2.94 2.60
1983 fall 3.07 5.95
1984 fall 2.81 NA
1984 fall 3.02 NA
1984 fall 2.98 NA
1985 fall 3.49 NA
1985 fall 3.13 NA
1985 fall 2.93 NA
1986 steelhead 2.09 1.99
1986 fall 3.45 2.05
1986 spring(mcn) 1.42 0.73
1986 spring(lgs) 1.86 1.58
1987 spring(mcn) 1.48 1.73
1987 fall 3.23 3.68
1988 spring(mcn) 1.47 NA
1988 fall 3.11 NA
1989 spring 1.75 2.46
1988 steelhead 2.03 2.19

For the comparison a measure of river passage effects on transportation was computed using the equation

(174)

where

The resulting correlation for all species and years between the observed TBR and the estimated TBR measure is illustrated in Fig. 83. A linear regression gives the relationship

(175)

Notice that the regression indicated that the estimated TBR underestimates observed TBR. Since the estimated TBR assumes a 100% transport survival factor the regression would suggest that actual fish survive better than predicted by the model. At the same time, note that the regression is very strongly affected by the outlier of 1973, where the observed TBR was over 16.

If we examine only the TBR below the mean of the estimated and observed TBR, both values are equal at 2.2. This additional information could be interpreted in one of several ways. The model could overestimate in-river survival in years with large TBRs or in years with large TBR the handling of the fish in the control groups produced additional mortality that was not represented in the model. In either scenario the fish transportation from model analysis and observations seems to produce survivals greater than could be obtained for in-river migration. Large TBR values are generally based on very small sample sizes and are therefore cannot be considered very robust. Fits for years with substantial recoveries are considerably better. Results of this analysis are preliminary and additional work will be conducted at a later date.

Fig. 83 Comparison of estimated and observed TBR for all species (chinook subyearling and yearling and steelhead) for years 1968 - 1987.

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Columbia River Salmon Passage Model CRiSP.1.5 Theory, Calibration & Validation Manual
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