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Forecast of Adult Returns



Home
 •Forecast as of January 2012
 •2011 Annual Update
 •2011 Annual Report (pdf)
 •Adult Return Data
 •Past Reports
 
Large–scale Ocean and Atmospheric Indicators
 •Pacific Decadal Oscillation (PDO)
 •Oceanic Nino Index (ONI)
 
Local and Regional Physical Indicators
 •Sea surface temperature anomalies
 •Coastal upwelling
 •Physical spring transition
 •Deep–water temperature and salinity
 
Local Biological Indicators
 •Copepod biodiversity
 •Northern copepod anomalies
 •Copepod community structure
 •Biological spring transition
 •Winter Ichthyoplankton
 •June spring Chinook and September coho
 
Indicators Under Development
 
Ocean Sampling Methods
 •Hydrography, zooplankton, and ichthyoplankton
 •Juvenile salmon sampling
 
Introduction to Pacific Northwest Oceanography
 •Physical oceanographic considerations
 • Climate–scale physical variability
 
Acknowledgements
 
References
 
Glossary
 


Forecast of Adult Returns for coho and Chinook Salmon


2011 was characterized by the continuation of La Niña conditions that were initiated in July of 2010. Combined with persistently negative PDO values throughout the year and a high biomass of lipid-rich northern copepods supporting the base of the food-chain, 2011 had the potential to be a good year for supporting juvenile salmon entering the ocean. However, this positive bio-physical outlook is tempered by observations of low winter-time ichthyoplankton (larval stages of fish-prey for salmon) abundance and poor upwelling (both in terms of the total amount and duration) throughout the year. Considering the previous two years (2009 and 2010) were characterized by below-average ocean conditions, we suggest that 2011 was an intermediate year with the foundation to support a rich biological community if the ocean conditions remain positive in 2012.

As 2012 begins to unfold, all signs are that ocean conditions will be among the best observed in recent years. Our annual update of ecosystem indicators during 2011 is here, and our “stoplight” rankings and predictions are shown below in Table 1, Table 2, and Figure A.


Table 1.  Ocean ecosystem indicators of the Northern California Current. Colored squares indicate positive (green), neutral (yellow), or negative (red) conditions for salmon entering the ocean each year. In the two columns to the far right, colored dots indicate the forecast of adult returns based on ocean conditions in 2011.
 
 
    Forecast of
adult returns
 
2008

2009

2010

2011
  Coho
2012
Chinook
2013
 
Large–scale ocean and atmospheric indicators
PDO  
ONI (Jan-Jun)  
Local and regional physical indicators      
Sea surface temperature anomalies  
Coastal upwelling  
Physical spring transition  
Deep water temperature and salinity  
Local biological indicators     
Copepod biodiversity  
Northern copepod anomalies  
Biological spring transition  
June spring Chinook   ––
September Coho   ––
 
    Key good conditions for salmon    good returns expected
     intermediate conditions for salmon    no data
     poor conditions for salmon    poor returns expected


Table 2 shows rank scores for the color-coding in Table 1. Scores were assigned based on their effect on juvenile salmonids. We show variables that are correlated with returns of coho salmon after 1 year and of Chinook salmon after 2 years. For example, positive PDO values (and red colors) indicate poor ocean conditions in coastal waters off the northern California Current. Similarly, higher sea surface temperatures in summer are a negative indicator for salmon, but particularly so for resident coho. Table 3 shows the values of each variable shown by rank in Table 2.



Table 2.  Rank scores upon which color-coding of ocean ecosystem indicators is based. Lower numbers indicate better ocean ecosystem conditions, or "green lights" for salmon growth and survival, with ranks 1-4 green, 5-10 yellow, and 11-14 red. To arrive at these rank scores, 14 years of sampling data were compared across years (within each row), and each year received a rank between 1 and 14.
 
 
 

Year of Samples

Ecosystem Indicators 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
 
PDO (December-March) 13 5 2 9 6 14 8 12 10 7 4 1 11 3
PDO (May-September) 8 3 5 4 9 13 12 14 10 11 1 7 6 2
ONI Jan-June 14 1 1 5 10 11 9 12 6 8 3 7 13 4
 
SST at 46050 (May-Sept) 12 8 3 4 1 7 14 11 5 13 2 9 6 10
SST at NH 05 (May-Sept) 8 4 1 6 2 5 14 11 7 13 3 12 10 9
SST winter before (Nov-Mar) 14 11 3 5 7 10 12 9 8 2 1 4 13 5
Physical Spring Trans (UI Based) 3 6 13 12 4 9 11 14 9 1 5 2 7 8
Upwelling Anomaly (Apr-May) 7 1 12 3 6 10 9 14 7 2 4 5 11 12
Length of upwelling season (UI Based) 6 2 13 9 1 10 8 14 5 3 7 3 11 12
Deep Temperature at NH 05 14 4 7 3 1 10 11 12 13 5 2 9 8 6
Deep Salinity at NH05 14 3 6 2 5 12 13 9 7 1 4 10 11 8
 
Copepod Richness Anomaly 14 2 1 5 4 10 9 13 11 8 6 7 12 3
N.Copepod Anomaly 13 9 5 6 3 12 11 14 10 8 2 7 4 1
Biological Transition 13 9 6 5 7 12 8 14 11 2 1 4 10 3
Copepod Community structure 14 4 3 6 1 10 11 13 12 8 2 5 9 7
Winter Ichthyoplankton 14 6 2 4 5 13 12 8 11 10 1 7 3 9
 
Catches of salmon in surveys
June-Chinook Catches 13 2 3 11 7 9 12 14 8 6 1 4 5 10
Sept-Coho Catches 10 2 1 4 3 6 11 13 8 9 7 14 12 5
 
Mean of Ranks 11.3 4.6 4.8 5.7 4.6 10.2 10.8 12.3 8.8 6.5 3.1 6.5 9.0 6.5
RANK of the mean rank 13 2 4 5 2 11 12 14 9 6 1 6 10 6


  


Table 3.  Data for rank scores of ocean ecosystem indicators.                                 
 
  1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
 
PDO (Sum Dec-March) 5.07 -1.75 -4.17 1.86 -1.73 7.45 1.85 2.44 1.94 -0.17 -3.06 -5.41 2.17 -3.65
PDO (Sum May-Sep) -0.37 -5.13 -3.58 -4.22 -0.26 3.42 2.96 3.48 0.28 0.91 -7.63 -1.11 -3.53 -6.45
ONI Jan-June (Average) 1.20 -0.98 -0.98 -0.32 0.35 0.45 0.32 0.47 -0.25 0.17 -0.95 -0.22 0.88 -0.70
 
SST 46050 deg C 13.66 13.00 12.54 12.56 12.30 12.92 14.59 13.56 12.77 13.87 12.39 13.02 12.92 13.06
SST NH 05 Summer deg C 11.26 10.79 10.64 11.08 10.73 10.91 13.11 12.00 11.11 12.08 10.74 12.00 11.50 11.27
SST NH 05 Winter Before (Nov-Mar) deg C 12.00 10.80 9.96 10.04 10.11 10.78 11.02 10.74 10.47 9.84 9.36 10.03 11.28 10.04
Physical Spring Trans UI Based Day of Year 83 88 134 120 84 109 113 142 109 70 87 82 95 105
Upwelling Anom (April-May) -14 19 -36 2 -12 -34 -27 -55 -14 9 0 -5 -35 -36
Length of upwelling season (UI Based) days 191 205 151 173 218 168 177 129 195 201 179 201 161 153
NH 05 Deep T (May-Sept) deg C 8.58 7.51 7.64 7.50 7.38 7.75 7.88 7.91 7.92 7.55 7.46 7.70 7.67 7.57
NH 05 Deep S (May-Sept) 33.51 33.87 33.83 33.87 33.86 33.70 33.66 33.79 33.82 33.88 33.87 33.73 33.71 33.8
Copepod richness anomaly no. of species 4.81 -2.92 -3.61 -1.17 -1.45 1.58 0.98 3.94 2.68 -0.82 -1.04 -0.92 2.93 -2.41
Northern Copepod Biomass log biomass -0.58 0.10 0.19 0.15 0.28 -0.07 0.06 -0.77 0.10 0.14 0.31 0.14 0.26 0.43
Biological Transition Day of Year 209 134 102 93 120 156 132 230 150 81 64 83 135 82
Copepod Community structure X-axis ordination 0.76 -0.84 -0.84 -0.78 -0.99 -0.18 -0.13 0.57 0.03 -0.67 -0.94 -0.79 -0.20 -0.70
Winter Ichthyoplankton log biomass * 10^3 0.12 0.90 1.80 1.25 1.05 0.53 0.58 0.83 0.59 0.60 1.84 0.89 1.65 0.61
 
June-Chinook Catches fish per km 0.26 1.27 1.04 0.44 0.85 0.63 0.42 0.13 0.69 0.86 2.56 0.97 0.89 0.46
Sept-Coho Catches fish per km 0.11 1.12 1.27 0.47 0.98 0.29 0.07 0.03 0.16 0.15 0.27 0.01 0.03 0.30
 



  

Figure A shows correlations between adult Chinook and coho salmon counts at the Bonneville Dam and coho salmon smolt to adult survival versus a simple composite integrative indicator — the mean rank of all indicators (the second line from the bottom) in Table 2. This index explains about 50% of the variance in adult returns. A weakness of this simple non-parametric approach is that each indicator is given equal weight, an assumption that may not be true, thus Brian Burke (NWFSC/FE) has begun to explore a more quantitative analysis of the ocean indicators shown in Table 3, using principal component analysis (PCA). PCA was run on the indicator data, a procedure which reduces the number of variables in a dataset as much as possible, while retaining the bulk of information contained in the data (a sort of weighted averaging of the indicators). Another important feature of PCA is that the principal components (PCs), which are the new, rotated data, are uncorrelated. This eliminates one of the original problems with the indicator data set (i.e., multi co-linearity). We used the PCs obtained from the PCA as new predictor variables in a linear regression analysis of adult salmon returns (this process is termed principal component regression, or PCR) and results are shown below in Figure B.

Scatter plot showing relationships between ocean indicators and counts of adult salmon at Bonneville Dam.
 
Figure A.  Salmon returns versus the mean rank of ecosystem indicators. Arrows show the forecasted returns of Chinook salmon in 2012 and 2013 (upper four panels) and Coho salmon in 2012 (lower left two panels). With a mean rank of the ecosystem indicators of 8.1 in 2010, the spring and fall Chinook salmon forecast for 2012 (top left two panels) is 160,000 and 325,000 adults returning to the Bonneville dam respectively. With a more favorable mean rank (6.5) of the ecosystems indicators in 2011, the forecasted adult returns of spring and fall Chinook are expected to be slightly higher at 177,000 and 400,000 adult fish returning to the Bonneville dam in 2013 (upper right two panels). Coho adult returns to the Bonneville Dam in 2012 are expected to be approximately 119,000 fish and the smolt to adult survival of coho to Oregon coastal streams is expected to be approximately 2.9% in 2012 (lower left two panels).
Results of principal components regression
 
Figure B. 

Comparison between adult salmon returns to Bonneville Dam and the smolt to adult survival rate (OPIH, blue circles) of coho and the predicted returns calculated from a principal components regression analysis (yellow diamonds). The x-axis indicates the out-migration year that corresponds to the year we characterize with ecosystem indicators (e.g. mean rank of ecosystem indicators). Predicted returns (purple diamonds) for spring Chinook in 2012 and 2013 are 150,000 and 233,000 (top panel) and the predicted returns for fall Chinook in 2012 and 2013 are 364,000 and 302,000. The predicted smolt to adult survival rate (OPIH) of coho salmon to Oregon coastal streams in 2011 is 2.58%, and for 2012 it is 3.31%. Results are from work done by Brian Burke (NWFSC/FE).

In summary, we have received mixed signals from ocean ecosystem indicators over the past three years and the variable ocean conditions in 2011 made our forecasts less certain for returns of coho salmon in 2012 and Chinook salmon in 2013. Our best guess is to expect average to above-average returns of coho in 2012 and Chinook in 2013. Based on a simple comparison to adult counts at Bonneville (Figure A), this translates to 177,000 spring Chinook, 400,000 fall Chinook, and 119,000 coho. Perhaps the most positive sign is that the ocean became very cold (and the PDO signal strongly negative) in summer 2010 and has remained so to date. If the cold conditions continue to persist into 2012, we may be seeing some of the better ocean conditions among the past 15 years.









last modified 03/02/2012
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