Bruce Daniels
Bruce photo

Ph.D. Student

Earth and Planetary Sciences
University California Santa Cruz
1156 High St.
Santa Cruz, CA 95064
(831) 462-4303 [home]
(831) 459-3504 [work]

Affiliations:
° Paleoclimate and Climate Change Research Group

° Hydrogeology Research Group


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Resume

- Current Work

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Water Cycle diagram
The Hydrologic Cycle
Hydroclimatology
Research

"Knowing our Water Future"
water footprint
What's your water footprint?

water wave

I am engaged in research on hydroclimatology, the intersection of the science of climatology with hydrology and hydrogeology.  The goal is to develop a deep, fundamental understanding of the connections between climate and the terrestrial water cycle. An important result is the production of useful quantitative metrics of the impacts of climate change on water resources.

Motivation

What information do users and suppliers of water need to make wise decisions? What needs to be done to provide the information that they need? Water managers throughout the United States and the world are making decisions today about large investments in new water facilities for current and future needs that could take decades to complete. When completed these efforts must solve water shortages not just for a few years, but for many decades beyond.

Water supply projects are planned using assessments of future water conditions which have traditionally been estimated from past climate data. If an agency needed to know the future average yearly rainfall or how long the typical or worst drought might last, then they examined the historical records for the last hundred years and computed a value to use as a future estimate. However climate change research shows clearly that the future will not be like the past. In fact, today is already not much like the past. Therefore incorporating climate change projections into accurate forecasts of future available water supply and demands is critical so that projects are not immediately inadequate the moment they are completed.

Past Work

Most past work has been research on the impact of climate change on just winter mountain ice and snowpack. Since about a third of California's water comes from this source, snowpack is certainly important. However, parts of California and much of the world rely primarily or even exclusively on water supply from other sources like groundwater. These other sources are equally important and will become even more heavily used and critical as  snowpack dwindles as a readily available supply. Therefore, it is necessary for hydroclimatology research to investigate impacts on the full water cycle and these other water sources.

In addition to considering precipitation received in the form of snowfall, the amount of annual rainfall received is  essential to determine both surface water and groundwater resources. But even with constant precipitation, other climate aspects like predicted changes to precipitation patterns such as more intense rain storms, shorter rain season, etc could impact water resources. In addition, other aspects like warming temperatures might increase losses from evapotranspiration. So hydroclimatology research must also incorporate the changes caused by all the various aspects of climate.

Methodology

My research analyzes how each water supply resource and element of the hydrological cycle is impacted by a change of each climate aspect. This is much more complex than it might seem at first glance. Each climate aspect can have a different relationship with and effect on each element of the water cycle. It is necessary to rigorously evaluate and quantify each of these relationships and effects to better understand exactly how and why the water system responds to climate changes.
Water Cycle Element Partitioning
My research partitions climate impacts with a "follow the water" approach to assess effects on successive elements of the terrestrial water cycle, i.e. the path from precipitation, to surface features, to sub-surface soil, then deep underground.  Certainly the fundamental source of the water cycle is the precipitation deposited onto the surface as rain, sleet, hail, snow, or other water forms. As soon as the precipitation falls then it immediately starts to partition off into different flows and stores.

A significant fraction of precipitation may be subject to interception by the vegetation canopy or pooling at the ground surface and then to loss from evaporation or sublimation. The precipitation not diverted into surface capture is then subject to infiltration into the ground. Any infiltration excess water can then become storm runoff into surface water bodies.

Infiltrated water wets and is absorbed by the soil from which it can evaporate away into the air even from soil pores below the surface. [Evapotranspiration diagram]Water in the soil root zone is subject to uptake by vegetation and then to transpiration through its leaf surfaces into the air. Throughflow or interflow is the lateral movement of water in the vadose zone, i.e. below the soil surface and above the groundwater table. As the water moves downwards under gravity and the soil becomes more compact and less permeable with increasing depth, thus some water tends to move sideways. Percolation is the slower downward movement of the rest of the sub-surface water through the vadose zone.

Water that percolates downward eventually reaches the saturated water table and acts to recharge that ground water. [Vadose & baseflows]Shallow groundwater located near and above the levels of local streams, springs, wetlands, lakes, and other surface water features may exfiltrate (flow out of the ground) or discharge and contribute to surface water bodies. Since half of the water that percolates down to shallow ground water may contribute to long term baseflow of such streams, it can provide a possibly year round important source of surface water supply. Adequate baseflow is also vital as a supply for riparian vegetation, fish, amphibians and other water dependent life.

Groundwater in coastal areas can become submarine groundwater discharge (SGD) which is the net flow of fresh water through an aquifer out into the sea. The reverse flow called saltwater intrusion is seawater flowing inland into the freshwater aquifers. Finally, the extraction of groundwater from aquifers via the pumping of wells or flow from springs can provide an important source of groundwater supply. So my research performs a "follow the water" analysis of water flows and stores to quantify the impacts on these successive elements of the cycle.
Climate Aspect Characterization
As mentioned, precipitation aspects such as more intense rainfall events could induce impacts on water supply by channeling more water into stormwater runoff, leaving less for surface water base flow and for groundwater storage. In fact, there are a lot of potentially important ways to characterize precipitation that need to be considered [Thorp 1982], [Trenberth et al. 2003], [Hennessey et al. 1997], for example:
  • length of precipitation season (for regions with distinct seasonality)
  • number of identifiable storms in the season
  • length of storms [duration in hr]
  • delay time between storms [hr or days]
  • average intensity of storms [precipitation rate in mm/hr]
  • maximum intensity [mm/hr]
Other non-precipitation climate aspects like air temperature, humidity, wind speed, and radiation could help determine the rates of surface evapotranspiration. Higher temperatures might also be expected to change evapotranspiration by increasing the growing season length. The type and condition of vegetation is another factor in transpiration and might also be relevant. The sea level rise expected from climate change [Meehl 2005], [USGS 2000] might worsen the effects of saltwater intrusion and modify submarine groundwater discharge. Therefore, my analysis on the impacts to water cycle elements is performed separately afrom each of these climate aspects.

Research Outline

It is not sufficient to consider each climate aspect and to determine just its qualitative relationship or even to rank its relative impact on each water cycle element or resource. To fully understand the system and produce useful information, the research must produce quantitative statements such as "a 20% reduction in precipitation produces a 70% reduction in groundwater recharge".

Here is a detailed list of the research tasks being performed:
  1. Select an appropriate combined surface water and groundwater model software to handle all elements and aspects of interest. Study surface water models and assemble a list of each package's capabilities and limitations. [DONE, choosing the GSFLOW model of USGS, click here for details]
  2. Document how the elements of the water path are impacted upon a simple increase or decrease of the total annual precipitation. This task requires a model, ideally through acquisition for some actual physical site. Drive this model with some real precipitation record and then again with the same record increased or decreased by some factor. [IN PROGRESS using the USGS Sagehen Creek model]
  3. Vary the amount of the simple increase or decrease of the precipitation in a linear progression, i.e. +1%, +2%, +3%, etc. Record the partitioning of the hydrological system impacts and establish each impact as a linear progression, quadratic, exponential, etc.
  4. Perform a stochastic Monte Carlo variation of important model parameters such as conductivity and specific storativity across some relevant range. Gather the ensemble results and compute a level of confidence for each statement of the amount of impact on some water element.
  5. Repeat the previous tasks for changes from other precipitation and climate aspects.
  6. Repeat the analysis above with models for other existing sites to show that these methodologies work in a variety of locations and to demonstrate how responses vary in different settings.
  7. Repeat the above tasks by driving the hydrological models with outputs from a climate model(s), hopefully of local regional scale.
  8. Derive mathematical procedures that can characterize precipitation outputs from climate models in terms of the precipitation aspects like intensity, season length, etc.
Note that some of task steps listed above could easily be reprioritized and swapped to change the order to be performed. For example, I could drive the system with climate model outputs before I investigate models for other sites.

The results from this research are numerical impacts on evapotranspiration, soil water content, runoff, stream flows, groundwater resource levels, etc. for numerical changes of precipitation, storm intensity, temperature, etc. These results are not only useful for water resource planning, but perhaps also for future assessments of crop growing conditions, forest and rangeland health, flood risks, sediment transport, water quality, and various other ecological and environmental conditions.

Finally, the other important topic not mentioned yet is climate impact on the demands for water. This includes the increased irrigation usage caused by higher temperatures and evapotranspiration, agriculture double cropping becoming triple cropping, etc. Such demand changes would be particularly complex to model and quantify since they often incorporate a large degree of human choice. Human decision making is notoriously non-linear or even unpredictable and so it is quite difficult to quantify and to model. I still would like to investigate such water demand impacts. But my plan is to first develop a rigorous solution and understanding of the impacts on water supply. Only after that is completed would I start to consider climate impacts on water demand.


Bibliography

Thorp, John M. and Bryan C. Scott, Preliminary calculations of average storm duration and seasonal precipitation rates for the northeast sector of the united states, Atmospheric Environment (1967), Volume 16, Issue 7, 1982, Pages 1763-1774.

Allison, G.B.; Gee, G.W.; Tyler, S.W. (1994). "Vadose-zone techniques for estimating groundwater recharge in arid and semiarid regions". Soil Science Society of America Journal 58: 6-14. OSTI:7113326.

Bond, W.J. (1998). Soil Physical Methods for Estimating Recharge. Melbourne: CSIRO Publishing.

Allison, G.B.; Hughes, M.W. (1978). "The use of environmental chloride and tritium to estimate total recharge to an unconfined aquifer". Australian Journal of Soil Research 16: 181–195. doi:10.1071/SR9780181.

Laury Miller and Bruce C. Douglas (2004). "Mass and volume contributions to twentieth-century global sea level rise". Nature 428: 406–409. doi:10.1038/nature02309.

Cazenave, A.; Nerem, R. S. (2004). "Present-day sea level change: Observations and causes". Rev. Geophys 42: RG3001. doi:10.1029/2003RG000139.

Hennessy, K.J., J.M. Gregory, and J. F.B. Mitchell. 1997. Changes in Daily Precipitation
under Enhanced Greenhouse Conditions. Climate Dyn., 13:667–680.

Trenberth, K.E., A. Dai, R.M. Rasmussen, and D.B. Parsons. 2003. The Changing
Character of Precipitation. Bulletin of the American Meteorological Society, 84(9):
1205–1217.

Meehl, G.A., W.M. Washington, W.D. Collins, J.M. Arblaster, A. Hu, L. E. Buja,
W.G. Strand, and H. Teng. 2005. How Much More Global Warming and Sea Level
Rise?  Science, 307:1769-1772.

U.S. Geological Survey. 2000. Sea Level and Climate, USGS Fact Sheet 002-00.
Available at: http://pubs.usgs.gov/factsheet/fs2-00/.