Climate Change in the Fraser River Watershed: Flow and Temperature

Climate Change in the Fraser River Watershed: Flow and Temperature

Journal of Hydrology 263 52002) 230±244 www.elsevier.com/locate/jhydrol Climate change in the Fraser River watershed: ¯ow and temperature projections John Morrisona,*, Michael C. Quickb, Michael G.G. Foremanc aVynx Design Inc., Sidney, BC, Canada bDepartment of Civil Engineering, University of British Columbia, Vancouver, BC, Canada cInstitute of Ocean Sciences, Department of Fisheries and Oceans, Sidney, BC, Canada Received 1 October 2001; revised 19 February 2002; accepted 22 March 2002 Abstract An analysis of the historic ¯ows and water temperatures of the Fraser River system has detected trends in both the annual ¯ow pro®le and the summer temperatures. This study was undertaken to determine if these trends are likely to continue under the conditions predicted by various global circulation models. To do this, existing ¯ow and temperature models were run with weather data that were derived from actual weather observations, but modi®ed using changes predicted by the global circulation models. The validity of the ¯ow model results is supported by very close agreement with the historical record. The differences between model output and the historical record for mean ¯ow, mean peak ¯ow, mean minimum ¯ow and peak ¯ow day were not statistically signi®cant; furthermore, there was only a 3±4 day shift in the occurrence of cumulative ¯ow milestones. The temperature model's mean water temperature was only 0.2 8C higher than the historical record. For the period 2070±2099, the ¯ow model predicted a modest 5% 5150 m3/s) average ¯ow increase but a decrease in the average peak ¯ow of about 18% 51600 m3/s). These peaks would occur, on average, 24 days earlier in the year even though for 13% of the years the peak ¯ow occurred much later as a result of summer or fall rain, instead of the currently normal spring freshet. In the same period, the summer mean water temperature is predicted to increase by 1.9 8C. The potential exposure of salmon to water temperatures above 20 8C, which may degrade their spawning success, is predicted to increase by a factor of 10. Trends in both ¯ow and temperature in this study closely match the trends in the historical record, 1961±1990, which suggests that the historical trends may already be related to climate change. While the mean ¯ow of 2726 m3/s does not show a statistically signi®cant trend, the hydrological pro®le has been changing. q 2002 Elsevier Science B.V. All rights reserved. Keywords: Climate change; Fraser River; Runoff; Temperature; Fish 1. Introduction Draining a watershed of approximately 217,000 km2, the Fraser River is the largest Canadian * Corresponding author. Address: Institute of Ocean Sciences, river that ¯ows to the Paci®c Ocean. With headwaters Fisheries and Oceans Canada, P.O. Box 6000, 9860 West Saanich near Jasper, Alta in the Rocky Mountains, the Fraser Road, BC V8L 4B2, Sidney, Canada. ¯ows for 1370 km before it discharges into the Strait E-mail addresses: [email protected] 5J. Morrison), [email protected] 5M.C. Quick), of Georgia near Vancouver 5Thompson, 1981). [email protected] 5M.G.G. Foreman). The Fraser River watershed is a major spawning 0022-1694/02/$ - see front matter q 2002 Elsevier Science B.V. All rights reserved. PII: S0022-1694502)00065-3 J. Morrison et al. / Journal of Hydrology 263 -2002) 230±244 231 Fig. 1. Fraser River watershed. ground for Sockeye and Chinook salmon, accounting between pre-spawning mortality and high river for the majority of the Canadian stocks 5DFO, temperature 5Gilhousen, 1990; Rand and Hinch, 1999a,b). Sockeye salmon begin their lives in spawn- 1998; Williams, 2000). Temperatures between 22 ing beds distributed throughout the watershed. Eggs and 24 8C over a period of several days can be fatal laid in these beds hatch in the following spring. After for salmon 5Servizi and Jansen, 1977) and tempera- spending the next year in fresh water, they move into tures over 24 8C can cause death within a few hours the ocean for a period of 2±3 years after which time 5Bouke et al., 1975). Even water temperatures as low they return to their original natal streams where they as 20 8C can have an adverse affect on spawning spawn and then die. On the migration back to the success rates 5Gilhousen, 1990). spawning beds the salmon are sensitive to the river Daily ¯ow records recorded at Hope since 1912 water temperatures and there is a strong correlation indicate that the Fraser River has been changing. 232 J. Morrison et al. / Journal of Hydrology 263 -2002) 230±244 1948 during a period of extensive ¯ooding of the lower Fraser River. Summer water temperatures have been recorded manually at Hells Gate since the early 1940s. Typi- cally these recordings were made from July 1 to September 15 but unfortunately in the early years there was much missing data. In this paper, the river temperature comparisons are based on the manual data collected at Hells Gate between 1961 and 1990. Recently this activity was supplemented by the instal- lation of an automatic data recorder at Qualark, a few kilometres downstream from Hells Gate. Of all of the summer river temperatures recorded at these loca- tions, the highest was 21.2 8C occurring on August 3, 1998, and the lowest was 11.0 8C recorded on July 1, 1955. Restricting the analysis to the time span when records are almost contiguous 5i.e. 1953± Fig. 2. Days of the year by which one-third and one-half the inte- grated yearly Hope discharge has occurred. Trend analyses suggest 1998), it was found that the summer mean tempera- earlier progressions at the rates of 0.11 and 0.09 days per year, ture, which ranges from 15 to 19 8C, was increasing at respectively, with the statistical signi®cance .95% in both cases. a rate of 0.022 8C per year with a signi®cance of 98%. Fig. 3 shows the latest available summer mean The Julian day numbers by which one-third and one- temperatures with their linear trend line. This line half of the integrated yearly discharge occurred have has a slope of 0.018 8C per year with a signi®cance been transpiring earlier 5Fig. 2) in the year and the of 95%. summer water temperatures have been increasing The purpose of this paper is to extend the preceding 5Fig. 3; Foreman et al., 2001). The river ¯ows are analyses of historical data, and those described by highly seasonal with winter lows at Hope often Foreman et al. 52001), into the future through the below 1000 m3/s and peak ¯ows typically occurring use of global climate change models. These models, in mid-June in the range of 9000 m/s. These ¯ows are which predict possible climate changes under various primarily generated from seasonal snowmelt. The scenarios of increasing greenhouse gases and aero- lowest ¯ow recorded between 1913 and 2000 was sols, will allow us to assess the possible impact of 340 m3/s on January 8, 1916, while the highest changing climate conditions on river ¯ow and recorded level of 15,200 m3/s occurred on May 31, temperature. Because of the sensitivity of salmon to water temperature, it is critical to determine if the historical trends are likely to continue to the point where the survival of the Fraser River salmon stocks are threatened. This manuscript is organised as follows. In Section 2, we describe the methods used in this study with an emphasis on downscaling global climate data and our ¯ow and temperature models. The climate experiment is described in Section 3. The statistical methodology, model validation, and projected changes in river ¯ows and temperatures are presented in Section 4. Implications of some of these changes are discussed in Section 5 and Fig. 3. Mean summer temperatures and their trend for the period the paper concludes with recommendations for 1953±2000. future work in Section 6. J. Morrison et al. / Journal of Hydrology 263 -2002) 230±244 233 2. Method the Hadley Centre for Climate Prediction and Research model HadCM2 5Johns et al., 1997). As an extension of the analysis of historic river conditions, this study was designed to determine the types of changes that could be expected under a chan- 2.2. Downscaling ging climate. To do this, the same models that were used to hindcast river conditions from historical GCM model output is available on large grid scales weather data were run using weather data derived 53.758 £ 3.758 for CCGM1 and 2.58 £ 3.758 for from climate change models. HadCM2) that do not lend themselves to assessing Model output from coupled global circulation the impact of climate change at local levels. Regional models was downscaled to sites in the Fraser River climate models are being developed that will have watershed that had reliable historic weather records. scales more suitable to local impact assessment, but The downscaled predicted changes were added to the the output from these models is not yet generally historic data and then used to drive the ¯ow and available. Various techniques for mapping the large temperature models. Using the IPCC guidelines GCM grids to local levels have been developed 5IPCC-TGCIA, 1999), a baseline was established 5Wilby and Wigley, 1997; Giorgi and Mearns, 1991) using the years 1961±1990. The modelled ¯ow and and this process is referred to as downscaling. The temperatures were compared with the historical hydrologic ¯ow and temperature models used in this record in order to establish the validity of the models. study were developed to use actual weather data from The climate change impacts were then assessed by multiple sites located throughout the Fraser comparing the baseline values to future 30-year peri- watershed.

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