Groundwater Under the Pacific Northwest
Stevenson, Washington
November 2-3, 2005
Pre-Conference Workshop: Groundwater Essentials
The Pre-Conference Workshop on November 1 covered the topics of basic
groundwater hydrology, regional groundwater quantity issues, state policies
on surface water-groundwater interactions, groundwater issues in rural
residential and urbanizing areas, public drinking water issues, and source
water protection planning.
Michael Barber (State of Washington Water Research Center) covered groundwater
essentials and introduced the concept of Aquifer Storage and Recovery
(ASR). In ASR, water not being used is pumped into an aquifer and stored
until needed. Although ASR avoids most of the environmental impacts associated
with above-ground storage, it is a relatively new tool. Potential issues
include the cost of the required pilot phase of a project, mitigation
plans, and groundwater quality regulations.
Robert Mahler (University of Idaho) discussed the complicated administration
of water use, a complication at least partly due to the fact that surface
water and groundwater often interact. Pumping groundwater may eventually
impact surface water, but the definition of eventually is
variable. The challenge for the states is balancing the need to administer
an understandable policy with the fact that science needs to fit into
the equation somewhere. In Idaho, water quantity is regulated by the Idaho
Department of Water Resources, while quality is regulated by the Idaho
Department of Environmental Quality. The law, however, is not well developed.
Both agencies have rules that indicate the state recognizes the connection
between groundwater and surface water, but groundwater mining is a problem
in southern Idaho.
Gail Andrews (Oregon State University) said that in Oregon, First
in time, first in right is the basic rule for water quantity. Oregons
Groundwater Act allows groundwater use if reasonable levels are maintained,
but individual basins also have rules. Surface water-groundwater interference
is regulated largely by the distance separating well and surface water
(i.e., by geometry).
Barber said that in Washington, senior water rights are protected from
all junior rights. Currently, water right applications are evaluated in
the context of water availability in the watershed. The widely debated
one molecule standard is used--if no further surface water
diversions can be permitted, no matter how small, then the same holds
for groundwater withdrawals. In summary, Barber said that the differences
in water laws makes management of interstate watersheds like the Columbia
Plateau area extremely complicated. What may seem like a good solution
in one state may, in fact, be illegal in another.
Andrews said that one quarter to one third of the population of Oregon
has a well, a septic system, or both. Yet there is no census of them,
and no regulations with respect to testing wells or pumping septic tanks
and maintaining drain fields. Regulations for the placing of both are
again geometric, and not all sites are suitable for septic systems or
wells. One interesting aspect of septic design is that groundwater dilution
actually is the final treatment--by design.
Mahler presented the results of a Pacific Northwest survey on drinking
water, and outlined the standards that protect central water supplies
serving 25 or more residences. Individual, exempt wells, however, are
not regulated. The primary national standards, which are those that are
enforced, include organic chemicals, inorganic chemicals, microorganisms,
turbidity and radionuclides. Elevated nitrates, common in agricultural
areas, may also indicate that other contaminants are present.
Barber concluded the workshop by discussing source water protection in
watershed management, the use of zoning or policy to keep high-risk activities
away from the drinking water supply, and monitoring to insure existing
operations do not negatively impact supply. Land uses allowed vary according
to travel time considerations. Management focuses largely on shallow aquifers,
which may be deemed nonsensitive or sensitive. The latter classification
requires a determination of wellhead protection areas, which can be produced
using the wellhead analytic element model WhAEM2000. It is important,
however, not to overlook the importance of routine monitoring and public
participation in the process.
Summary by Mary Aegerter, Technical Writer, Washington State University

