Why Has Redmond Updated its
Stream Classification?
The Washington
State Growth Management Act (GMA) requires that all County and Municipal
Government Critical Areas Ordinances (CAO) be updated based on “Best Available
Science,” preferably before January 2005.
This includes updating local stream classification systems and their associated
protective riparian stream buffer requirements.
The most widely used stream classification system in Washington
is the “water typing” system developed and
implemented by the Washington Department of Natural Resources (WDNR). This system was recently updated (January
2005) and Redmond has adopted the
concepts behind these classification changes.
The fundamental change in WDNR’s water typing system is the
development of more accurate maps of fish habitat. These maps are based upon a multiparameter,
geographic information system logistic regression model. The distribution of fish habitat is predicted
using geomorphic parameters such as basin size, gradient, and elevation, and
can be verified by on the ground surveys.
In producing these improved maps, WDNR has acknowledged the need for a
better understanding of fish distribution statewide. The City of Redmond
similarly recognizes that responsible protection and restoration of our
critical areas depend directly on knowing exactly where fish and supporting
habitat occur.
It is important to note that the new water typing system
retains key concepts from its predecessor:
- In the
absence of fish, a water body can still be designated “fish-bearing” if
the associated habitat has “the
potential to support fish.”
This fish-bearing potential is determined by specific physical attributes of the stream habitat,
including channel width and gradient.
- Downstream
man-made barriers to fish passage are not sufficient reason to classify
upstream habitat as incapable of supporting fish, since upstream fish
access may be regained in the future upon removal of such barriers.
Redmond has
adopted both of these existing concepts.
Prior to 2004, Redmond’s
knowledge of the species composition and distribution of fish populations
within City streams was very basic.
Observations were generally limited to third-party records (Salmon
Watchers volunteer program; King County
staff; Dept. of Fish and Wildlife staff) of adult salmonids moving through the Sammamish
River and Bear and Evans Creeks to
spawn.
To remedy this situation, in Spring 2004, and again in
Spring 2005, the City of Redmond contracted with Washington Trout—a respected,
local, science-based non-profit organization—to perform systematic sampling of
the fish in most of our smaller City streams (all tributaries to Lake
Sammamish, the Sammamish River, or Bear and Evans Creeks), and to assess the
adequacy of our City stream habitats to support fish. Most of the fish they documented—and there
were plenty of them—were juvenile trout and salmon that we did not know were
using our streams.
King County
has also chosen to adopt the updated WDNR water typing/stream classification
system, thus Redmond’s use of a
similar classification allows comparisons with other streams across the region
to be made more easily.
How Has Redmond Natural
Resources Chosen to Use Washington Trout’s
Data?
Natural Resources chose Washington Trout to survey City
stream habitats and fish populations based on its integrity, objectivity, and
extensive prior experience working with both municipal and regulatory
jurisdictions to accurately classify streams using the WDNR water typing
protocol. Their acknowledged advocacy on
behalf of protecting streams and fish also provides the City with stronger
safeguards to protect our natural heritage for future generations.
After careful review of all of the materials provided by
Washington Trout to the City, and following extensive joint discussions, Natural
Resources chose to adopt their complete study results.
There are several special circumstances that the City of Redmond
must address, however, that require some modification and additional
interpretation of Washington Trout’s study results. These special circumstances are outlined
below:
(1) The Growth Management Act
requires that affected jurisdictions “…provide special protections for
anadromous fish” (e.g., salmonids). The best available science indicates that
salmonids are among the most widely distributed of all local fish and are
likely to move further upstream than any other species.
The WDNR water typing system
provides equal protection to all
species of fish and their habitats (under WDNR Type F, fish-bearing or with the
potential to be fish-bearing) but in order to meet the spirit of the GMA,
Redmond has chosen to emphasize special
protection for salmonids and their habitats, defining these as Class II Streams,
which have wider protective buffers.
(2) Redmond
has a special class of small, perennial and seasonal valley wall streams. These streams typically rise along the crest
of the Sammamish River
valley wall, gather flow from springs and seeps as they flow down the valley
walls, and then infiltrate into the ground when they reach the valley
floor. Most never reach larger streams
or the Sammamish River.
Several of these streams contain
populations of native sticklebacks and thus warrant protection as fish-bearing
streams (WDNR Type F), but since they lack connections to river tributaries
they are unlikely to contain salmonids. Redmond
has chosen to define these as Class III Streams that support non-salmonid fish use, or have the
potential to support non-salmonid
fish. This Class has narrower protective
buffers than our salmon-bearing streams.
Also included under Redmond’s
Class III are streams without fish and
without any potential to support fish that are connected downstream to
either Class I or Class II salmonid-bearing streams. While these streams don’t contain fish
themselves, they can be critical “headwater
streams,” providing cold, clean water to the salmon-bearing streams into
which they flow, further downstream.
(3) Redmond’s
Class IV Streams combine both WDNR category Np and Ns streams—perennial and
seasonal streams that neither support, nor have any potential to support, any
fish.
(4) In addition to natural or
modified natural streams, Redmond
has some “Intentionally Created Streams,” man-made ditches and swales, generally
created for irrigation or drainage purposes.
If fish are found within such
streams, then they are subject to the same protective buffer requirements of
natural fish-bearing streams.
This category specifically excludes
man-made streams that are created as part of stream habitat restoration efforts
or in response to mitigation requirements—such intentionally created streams
are regulated the same as other Redmond
streams.