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Background Information

Picture of old tree being sampled

Connie Woodhouse samples an old Douglas-fir near Dillon Reservoir.



Project history

In spring 2002, Connie Woodhouse and Robin Webb received funding from the NOAA Office of Global Programs for a multi-year project entitled Extended Hydroclimatic Records for the Upper Colorado River Basin, which proposed to use the new chronologies to develop reconstructions of hydrologic variables, principally streamflow, and to work with water resource managers to make these reconstructions more applicable to their operational and planning needs. The occurrence of a very severe drought event in 2002 spurred significant interest in the project, and by March 2003 a number of entities had become involved, including the Northern Colorado Water Conservancy District (NCWCD) and Denver Water. The scope of the project has expanded beyond the Upper Colorado basin to include Front Range watersheds, and future work will cover all major watersheds within Colorado.

In 2003 and again in 2004, additional funding was provided by NOAA/CIRES Western Water Assessment, a Regional Integrated Sciences and Assessment (RISA). Denver Water has also provided funding to update chronologies in western Colorado (2003) and the Front Range (2004).

This project has been supported by the work of past (Gary Bolton, Margot Kaye, Curtis Nepstad-Thornberry) and current (Henry Adams) assistants in the CU-INSTAAR Dendrochronology Lab. Mark Losleben (CU-INSTAAR Mountain Research Station) has also provided extensive field support.



Project objectives

  • Work with water resource managers to identify the gages and hydrologic metrics most useful in water resource planning and management, as candidates for reconstruction.
  • Develop reconstructions of annual streamflow, and associated products and analyses, for the gages of interest to water managers. Work with data users to ensure that the products and presentations are meaningful and useful.
  • Develop an online dendrohydrologic reference web page and database that will contain reconstructions and gage data, as well as information on reconstruction methods and assessment of reconstruction quality, and caveats for use.
  • Study the feasibility of developing reconstructions for other hydrologic metrics of interest (e.g., April 1 snow water equivalent, n-day low flow). Develop reconstructions of these as is possible.
  • Use the reconstructions to evaluate hydroclimatic events (droughts and wet periods) and characteristics (distribution of mean, extremes, and change in variability) over the past 300 to 800 years in comparison with 20th and 21st century events and characteristics.
  • Investigate linkages between drought in the upper Colorado and South Platte River basins and in other parts of the western U.S. to identify possible relationships between regional drought and atmospheric circulation.
  • Use the reconstructions to assess the ability of ensembles of climate model runs to simulate statistical characteristics of the reconstructions.


Project Partners

The following agencies and entities have become involved in the project. Their involvement includes providing gaged streamflow or instrumental climate records to be reconstructed, and /or collaboration in the development of reconstruction techniques and data products.



What is a tree-ring reconstruction?


A tree-ring reconstruction is a time series of tree ring-width data that have been calibrated with an instrumental or gaged record of a hydrologic or climatic variable (e.g. annual streamflow, precipitation, snow water equivalent, drought index). The reconstruction, based on a statistical model that describes the relationship between tree growth and the gage record, extends that record back hundreds of years into the past (see figure below).

Graph of reconstructed streamflow

Tree-ring reconstruction of annual streamflow for the Blue River at Green Mountain Reservoir, Colorado for the period 1540 to 1999. The green line shows annual values, and the black line is a 3-year running mean.



What is the physical basis for tree-ring reconstructions?

Tree growth is generally controlled by climate conditions during the year prior to and including the growing season. At lower elevations in Colorado, variations in tree growth closely reflect the amount of soil moisture at the onset of the growing season, which is controlled by variations in precipitation, and, to some degree, temperature, humidity, and wind. Since measures of streamflow, seasonal snowpack, and drought integrate both precipitation and temperature over the course of the previous seasons (similar to tree rings), they are often closely correlated with tree growth, and in fact, these correlations are usually closer than those between tree growth and precipitation alone.

Trees that provide the best information about hydroclimatic variability are those particularly sensitive to variations in moisture. These include species such as ponderosa pine, pinyon pine, and Douglas-fir, growing in open stands on dry and rocky sites where soil moisture storage is minimal. Trees growing in these types of sites are also less likely to be subject to non-climatic disturbances (such as fires and insect infestation) and the effects of competition from nearby trees. In addition, the oldest trees (up to 800 years old) of these species tend to be found on these sites.

Trees used in hydroclimatic reconstructions are not necessarily located in the same watershed as the instumental or gage records. The atmospheric flows of moisture which influence both tree growth and streamflow are regional, crossing watershed divides, so trees in one basin may capture a significant portion of the variability in streamflow in another basin. For example, reconstructions of streamflow for the Colorado Front Range are improved when tree-ring chronologies from the western slope are added to the pool of model predictors.


How are tree-ring reconstructions developed?


Tree-ring reconstructions of hydroclimatic variables are developed from tree-ring chronologies. A tree-ring chronology is a time-series of annual values derived from the ring-width measurements of 10 or more trees of the same species at a single site.

To create a tree-ring chronology, cores from the sampled trees at each site are cross-dated (i.e., patterns of narrow and wide rings are matched from tree to tree) to account for missing or false rings, so that every annual ring is absolutely dated to the correct year. Then all rings are measured to the nearest thousandth of a millimeter using a computer-assisted measuring device. After growth-related (i.e., unrelated to climate) trends are statistically removed, the ring-width values from all sampled trees for each year are averaged to create a time series of annual ring-width indices. The complete series of ring-width indices from a site is called a tree-ring chronology.

Graph of reconstructed and gaged streamflow

The Blue River at Dillon Reservoir reconstruction model (green) and the gaged record (blue) over their common time period (1916-2002).



How are tree-ring reconstructions used?


Water managers have long used instrumental records of climate and gaged records of streamflow to assess the natural variability of the system they are managing, determining the frequency of drought events of varying severity and establishing a drought of record to use as the worst-case scenario in contingency planning. However, instrumental and gaged records are usually only 30 to 100 years long and are unlikely to capture the full expression of potential natural variability. Tree-ring reconstructions, by providing a much longer window into the past (300-1000 years), more completely describe the potential natural variability of the system, including severe drought events. Many tree-ring reconstructions have indicated that droughts longer and more intense than those in the instrumental record have occurred in past centuries. This additional information on long-term hydroclimatic variability can guide water resource planning to better meet the challenges of potential future conditions. Water managers using tree-ring reconstructions will not be surprised by events, like the 2002 drought, that exceed the bounds of the operational experience of their system.



Uncertainty and limitations

In the reconstructions

Because the reconstruction models explain most (60-75%), but not all, of the variance in the gage record, there are uncertainties in the reconstructions. Estimates of uncertainty can be described by confidence intervals around the reconstruction. These confidence intervals describe the range of uncertainty (usually at a 95% level) that can be expected in the estimates. Narrow confidence intervals represent a stable reconstruction model. There are several way to estimate confidence intervals. Two of these are the use of bootstrapped series generated in the iterative model-fitting process of the linear neural network, and the use of the root mean squared error in the regression equation.

Other sources of uncertainty include the inevitable decline in tree sample size back in time, and extreme high and low values in the reconstruction which are extrapolated (i.e., the tree ring values are outside the range in the calibration period) rather than interpolated.

In the gaged records

Gaged and instrumental records are generally presumed to represent physical reality, and the tree-ring reconstructions on which they are based thus offer a close approximation of that reality. But it is worth noting that gaged and instrumental records do have some measurement error associated with them, and, more critically, may contain spurious trends and features caused by human manipulation of the watershed.

In Colorado, most streams have seen their natural flow regimes altered through water diversions and impoundments, as well as land-use changes in the watershed. As a result, the gaged streamflow record may not accurately represent the natural long-term trends and year-to-year variability in water supply in that watershed. Water management agencies have attempted to account for these alterations, using records of diversions and changes in watershed storage to correct the "raw" streamflow records. The resulting records are called "undepleted", "naturalized", "unimpaired", or "virgin" flow records to distinguish them from uncorrected gage records. Because they more accurately represent natural water supply variation than the raw gaged records, undepleted flow records, when they exist, are used as the basis for tree-ring streamflow reconstructions. The example below, from the Fraser River, demonstrates the typical discrepancies between the gaged (uncorrected) and undepleted (corrected) flow records in a highly manipulated watershed.

Graph of undepleted and gaged streamflow

The gaged USGS streamflow record (light blue) for the Fraser River near Winter Park is compared with the undepleted flow record (dark blue) derived by Denver Water from the gaged record to account for diversions, which began in earnest in 1936. The gaged record poorly represents the trends in streamflow on short and long time scales.

Additional caveats for using reconstructions

  • It is tempting to combine the reconstructed and gage records into a single record to which new gaged values (for 2003, 2004, etc.) could be easily appended. The problem with doing this is that the statistical properties of the reconstructed and gage streamflow series are not the same.Tree-ring chronologies do not explain all the variance in the gage record. Because of this, the estimates of flow produced by the reconstruction model do not represent the full range of values in the gage record, although dry extremes are typically more closely replicated than wet extremes. Consequently, the variance, standard deviation, range, and max/min values are different. Any attempt to blend the two records needs to acknowledge these important differences and the limitations they impose.
  • Although tree-ring reconstructions can be used to guide expectations for the future, they cannot be used to predict future droughts. Furthermore, the variability in past climate may not be an analog to future variability, given the human impacts on climate in the last century. Future conditions will be influenced by climate forcings, including changes in land use and elevated inputs of greenhouse gases, as well as by natural climate variability. Future climate will reflect natural climate variabilty, including the long-term range of variability described in the tree-ring reconstructions, but superimposed over this natural variability will be the anthropogenic impacts on climate.


 

NOAA Paleoclimatology Branch

Last Updated: 5 January 05