Or. Admin. Code § 635-412-0035 - Fish Passage Criteria
(1)
General requirements for fish passage are:
(a)
Unless the owner or operator of an artificial obstruction chooses to provide
year-round fish passage for all native migratory fish and life history stages,
the Department shall determine:
(A) The native
migratory fish that are currently or were historically present at the site that
must be provided fish passage;
(B)
The life history stages the required fish passage must accommodate;
and
(C) The periods of the year and
any conditions relevant to when fish passage shall be provided for such life
history stages and native migratory fish.
(b) The person submitting the fish passage
plan to the Department for approval shall submit all information necessary for
the Department to efficiently evaluate whether the design will meet fish
passage criteria including a description of how climate change impacts have
been incorporated into the final design;
(c) If site-specific circumstances indicate
that the fish passage criteria are not adequate to provide fish passage at the
artificial obstruction, the Department may require in writing that additional
fish passage criteria be met;
(d)
If the Department determines that the existing or historically present native
migratory species or site-specific circumstances warrant an exception to any
specific fish passage criterion then the Department may approve such an
exception in writing as long as it finds that fish passage will likely still be
provided at the artificial obstruction;
(e) All fish passage structures shall be
designed considering their upstream and downstream connection and prevent
undesirable impacts to fish passage, including but not limited to scour and
headcuts;
(f) If federal approval
of a fish passage plan is required, the Department shall take into account
federal requirements during its review and determination;
(g) The Department may require monitoring and
reporting to determine if a fish passage structure meets applicable criteria
and is providing fish passage as intended and designed; and
(h) The owner or operator of an artificial
obstruction shall maintain the fish passage structure in such repair and
operation as to provide fish passage of native migratory fish at all times
required by the Department.
(2) Requirements for fish passage at dams and
other artificial obstructions which create a discontinuity between upstream and
downstream water surface or streambed elevations are:
(a) Fishways shall provide fish passage at
all flows within the design streamflow range and should be analyzed using
estimates for the projected life expectancy of the structure;
(b) The fishway entrance shall be located and
adequate attraction flow shall be provided at one or more points where fish can
easily locate and enter the fishway;
(c) Fishway water velocities shall:
(A) Range between 1 and 2 feet per second in
transport channels;
(B) Average no
greater than 5 feet per second in baffled-chute fishways, including but not
limited to Alaska steeppasses and denils; and
(C) Not exceed 8 feet per second in discrete
fishway transitions between the fishway entrance, pools, and exit through which
fish must swim to move upstream, including but not limited to slots, orifices,
or weir crests.
(d) At
any point entering, within, or exiting the fishway where fish are required to
jump to move upstream, the maximum difference between the upstream and
downstream water surface elevations shall be 6 inches, except it shall be 12
inches if only adult salmon or steelhead require fish passage;
(e) In fishway locations through which fish
must swim, water depths shall be a minimum of 6 inches where only juveniles
require passage and 12 inches where adults require passage, except:
(A) Baffled-chute fishways, including but not
limited to Alaska steeppasses and denils, shall have a minimum flow depth of 2
feet throughout the length of the fishway; and
(B) Water depths shall be a minimum of 2 feet
within jump pools which shall be located downstream of any point entering,
within, or exiting the fishway where fish are required to jump to move
upstream.
(f) All
fishway locations through which fish must swim shall be at least 12 inches
wide, except vertical slot weir width may be 6 inches where the Department has
determined the artificial obstruction is required to provide fish passage only
for juvenile native migratory fish;
(g) Fishway pools shall:
(A) Be sized according to the applicable
native migratory fish and life history stages and to avoid
over-crowding;
(B) Have V >=
wQH/4 at all flows within the design streamflow range, where:
(i) "V" is the water volume in cubic
feet;
(ii) "w" is 62.4, the unit
weight of water, in pounds per cubic foot;
(iii) "Q" is the fish ladder flow in cubic
feet per second;
(iv) "H" is the
energy head of pool-to-pool flow in feet; and
(v) 4 has a unit of foot-pounds per second
per cubic foot.
(C)
Where the fishway changes direction 90 degrees or more, have turning pools with
a flowpath centerline double the length of non-turning pools; and
(D) Be placed at least every 25 feet of
horizontal distance in baffled-chute fishways, including but not limited to
Alaska steeppasses and denils;
(h) The fishway exit should be located to
minimize the risk of fish unintentionally falling downstream of the artificial
obstruction, or into a water diversion;
(i) Fishway trash racks shall:
(A) Allow for easy maintenance and debris
removal;
(B) Be maintained and
cleaned as necessary to provide fish passage;
(C) Have a minimum clear space between
vertical members of 10 inches, except at least 4 inches shall be provided if
only juveniles are present; and
(D)
Have a minimum clear space between horizontal members of 24 inches;
(j) The fishway shall:
(A) Have water temperatures which are within
1 degree Fahrenheit of the water entering the fishway;
(B) Be designed to assure that fish do not
leap out of the fishway;
(C) Have
all surfaces, edges and fasteners which fish may contact ground smooth or
chamfered;
(D) Not have protrusions
that extend into the flow path of the fishway;
(E) Not expose fish to any moving
parts;
(F) Be designed to avoid
turbulence and hydraulic transition flow conditions as much as
possible;
(G) Have as much ambient
lighting as possible and avoid lighting transitions;
(H) Have fishway components which are not
detailed in OAR 635-412-0035(2),
including but not limited to auxiliary water systems, designed considering the
most recent National Marine Fisheries Service or U.S. Fish and Wildlife Service
fish passage criteria and guidelines;
(I) Meet the species-specific requirements in
OAR 635-412-0035(7)
if any of those native migratory fish require fish passage;
(k) Requirements for specific
types of fishways include:
(A) Baffled-chute
fishways, including but not limited to Alaska steeppasses and denils, shall not
be used in areas where downstream passage will occur through the baffled-chute
fishway; and
(B) All fishways of a
specific type with accepted configurations shall comply with those
configurations.
(l)
Requirements for fishways which encompass the entire channel include:
(A) Roughened channels or nature-like fishway
designs shall:
(i) Meet the requirements of
OAR 635-412-0035(3)(a)(A) (ii), (iv),
(v) (II through VII), or OAR
635-412-0035(3)(b);
(ii) Not have a slope that exceeds 6 percent,
unless the average natural stream slope exceeds 6 percent; and
(iii) Contain partially buried over-sized
boulder or boulder clusters to provide structural integrity and localized areas
of lower water velocity.
(B) Stream channel-spanning weirs shall:
(i) Rise toward each bank from a low flow
section centered along the thalweg of the channel;
(ii) Have a downstream jump pool with a
minimum depth of 2 feet;
(iii) Have
a maximum difference in elevation of 6 inches between the lowest point on the
weir and the downstream pool's water surface control point;
(iv) Be sealed if fish passage during low
flows is required;
(v) Be spaced at
least 1.5 active channel widths apart if there are multiple weirs and recommend
consideration of wider spacing when appropriate; and
(vi) Extend into the streambank a sufficient
distance to protect against flanking;
(C) All fishway entrances or flow outlets
shall be designed to provide passage or be designed to only be used during a
period(s) defined by the Department.
(D) Fish passage plans for hybrid fishways
that may combine features of several established fishway types shall have
criteria established by the Department on a case-by-case basis and shall
clearly demonstrate how water depths, water velocities, water surface jump
height differentials or energy dissipation provides hydraulic conditions that
achieves fish passage;
(m) For downstream fish passage:
(A) Fish passage structures shall have an
open water surface, except a submerged or enclosed conduit or orifice may be
used if:
(i) Acceptable guidance or
collection mechanisms are used and kept free from debris;
(ii) Water depth is greater than 4 inches
during all flows;
(iii) Water
velocity is greater than 2 feet per second during all flows;
(iv) Water is not pumped;
(v) Conduits have smooth surfaces and avoid
rapid changes in direction to preclude fish impact and injury; and
(vi) Conduits are at least 10 inches
wide.
(B) Plunging flow
moving past an artificial obstruction via spillways, outlet pipes, or some
other means which may contain fish shall:
(i)
At all flows, fall into a receiving pool of sufficient depth, depending on
impact velocity and quantity of flow, to ensure that fish shall not impact the
stream bottom or other solid features; and
(ii) Have a maximum impact velocity into a
receiving pool, including vertical and horizontal velocity components, less
than 25 feet per second; and
(C) Water depth over spillways or other
artificial obstructions shall be greater than 4 inches during all
flows.
(D) Fish screening and
bypass devices installed to protect downstream migrating fish should be
constructed to Department specifications and must meet Department criteria when
installation is required.
(3) Requirements for fish passage at
road-stream crossing structures such as bridges and culverts are:
(a) Stream Simulation Option (preferred
design alternative) where:
(A) Open-bottomed
and closed-bottom road-stream crossing structures shall have beds under or
within the structure that:
(i) Are equal to or
greater than the active channel width multiplied by 1.2 plus 2 feet, as
measured at sufficient locations outside the influence of any artificial or
unique channel constrictions or tributaries both upstream and downstream of the
site;
(ii) Are equal to the slope
of, and at elevations continuous with, the surrounding long-channel streambed
profile, unless the Department approves maintaining a pre-existing
road-impounded wetland;
(iii) Have,
for open-bottomed road-stream crossing structures, a minimum of 3 feet vertical
clearance from the active channel width elevation to the inside top of the
structure;
(iv) Maintain average
water depth and velocities that simulate those in the surrounding stream
channel; and
(v) Are composed of
material that:
(I) Assures the bed under or
within the road-stream crossing structure is maintained through time;
(II) Is either natural (similar size and
composition as the surrounding stream) or supplemented to address site-specific
needs including, but not limited to, bed retention and hydraulic
shadow;
(III) Contains
partially-buried, over-sized rock;
(IV) Is mechanically placed during structure
installation rather than allowed to naturally accumulate, unless the
surrounding streambed is primarily bedrock;
(V) Excluding partially-buried over-sized
rock, is, for closed-bottom road-stream crossing structures, at a minimum depth
of 20 percent of the structure height;
(VI) Considers bed scour and stability of the
bed material due to the confined flow through the crossing structure. Major
structural components within the crossing should be designed for structural
stability at the 100 year flood flow; and
(VII) Contains a low flow thalweg.
(B) Trash racks shall:
(i) Allow for easy maintenance and debris
removal;
(ii) Be maintained,
monitored, and cleaned as necessary to provide fish passage;
(iii) Not extend below the active channel
width elevation;
(iv) Have a
minimum of 10 inches clear spacing between vertical members; and
(v) Have a minimum clear space between
horizontal members of 12 inches.
(C) Beaver exclusion culvert protection
devices shall:
(i) Allow for easy maintenance
and debris removal;
(ii) Be
maintained, monitored, and cleaned as necessary to provide fish
passage;
(iii) Have a minimum clear
space between vertical and horizontal members of 6 inches when only resident
trout, Entosphenus and Lampetra species
(lamprey) species are present;
(iv)
Be approved on a case by case basis in areas with salmon, steelhead, bull
trout, or other large bodied species.
(D) Unvented and vented ford crossings shall
meet the requirements of OAR
635-412-0035(2)
and 635-412-0035(3)(b);
and
(i) Be located outside of all known or
suspected fish spawning areas such as pool tail-outs;
(ii) Be constructed perpendicular to the
stream flow;
(iii) Minimize the
width (perpendicular to streamflow);
(iv) Maintain similar water depths and flow
velocities as surrounding stream during the design stream flows; and
(v) Have a low flow channel constructed
within the crossing.
(E)
Unvented ford crossings shall meet design criteria in OAR
635-412-0035(3)(a)
and be constructed using materials approved
by the Department that shall:
(i) Not be
comprised of broken concrete, pavement or other debris;
(ii) Be comprised of clean washed gravel and
rock;
(iii) Be countersunk and
vertically align with the existing stream channel profile and
gradient;
(iv) Be designed to allow
natural bedload transportation;
(v)
Be designed to withstand overtopping flood events;
(vi) Be used during periods of no or low
stream flow; and
(vii) Be regularly
inspected and maintained to provide fish passage.
(F) The Department may authorize construction
of new fords in limited situations when it is the least impacting water
crossing option. The following are examples of situations where the Department
may authorize an unvented ford:
(i) The stream
has extreme seasonal flow variations and low flows during anticipated ford
use;
(ii) The channel has low bank
height and low gradient approaches;
(iii) The stream has dynamic flood plains,
such as alluvial fans; or
(iv) The
stream is subject to mass wasting events, debris transport, or extreme peak
flows.
(b)
Alternative Option: the Department may approve road-stream crossing structures
for which clear justification, based on fish performance, fish behavior data,
and proposed post treatment hydraulic conditions (e.g., water depths, water
velocities, and gate time open) is provided that demonstrates that the
alternative design provides fish passage.
(4) Requirements for fish passage at
artificial obstructions in estuaries, and above which a stream is present, are:
(a) Fish passage shall be provided at all
current and historic channels;
(b)
Fish passage structures shall meet the criteria of OAR
635-412-0035(2) or
(3), except fish passage structures shall be
sized according to the cumulative flows or active channel widths, respectively,
of all streams entering the estuary above the artificial obstruction;
and
(c) Tide gates and associated
fish passage structures shall:
(A) Be a
minimum of 4 feet wide unless the natural channel conditions are less than 4
feet wide;
(B) Consist of an
aluminum tide gate door or other equivalent light weight material;
(C) Be a side hinged door
configuration;
(D) Meet the
requirements of OAR 635-412-0035(2)
or 635-412-0035(3)(b)
within the design streamflow range and for an average of at least 51 percent of
tidal cycles, excluding periods when the channel is not passable under natural
conditions;
(i) Design streamflow range shall
include tidal exchange, freshwater stream discharge and water storage volumes
draining to the tide gate:
(ii)
Design streamflow range should consider sub-surface flows if appropriate at the
project location;
(E)
Design invert elevation of tide gate and associated structure to be placed at 1
foot below Mean Lower Low Water elevation or as otherwise appropriate for the
site to prevent perched low flow fish passage conditions and allow proper tide
gate function;
(F) Consider the use
of pet doors, mitigators, self-managed and self-regulating tide gate devices to
maximize fish passage, time of tide gate door openness, water exchange, and
tidal inundation if the tide gate is associated with high priority restoration
habitat; and
(G) Submit a water
management plan for projects implementing self-managed or self-regulating
devices.
NOTE: Alternative self-regulating design features that meet the design criteria of this section will be considered for fish passage.
(5) Requirements for fish passage at
artificial obstructions in estuaries, floodplains, and wetlands, and above
which no stream is present, are:
(a)
Downstream Fish Passage shall be provided:
(A)
After any inflow which contains native migratory fish;
(B) Until water has drained from the estuary,
floodplain, or wetland, or through the period determined by the Department that
shall be based on one, or more of, the following:
(i) A specific date;
(ii) Water temperature, as measured at a
location or locations determined by the Department;
(iii) Ground surface elevation;
(iv) Water surface elevation; or
(v) Some other reasonable measure;
and
(C) Egress delays
may be approved by the Department based on expected inflow frequency and
suitable habitat exists and as long as passage is provided by the time the
conditions in OAR 635-412-0035(5)(a)(B)
occur;
(D) A minimum egress flow of
0.25 cubic feet per second (cfs) at one point of egress shall be
provided;
(E) Egress flow of 0.5
cfs per 10 surface acres, for at least the first 100 surface acres of impounded
water, shall be provided;
(F) All
plunging egress flows shall meet the requirements of OAR
635-412-0035(2)(l)(B);
(G) If egress flow is provided by a pump, it
shall be appropriately screened;
(H) The water depth and width through or
across the point of egress shall be at least 4 inches;
(I) The ground surface above the artificial
obstruction shall be sloped toward the point(s) of egress to eliminate isolated
pools and topographic conditions that may entrain native migratory fish;
and
(J) An uninterrupted, open
connection with a minimum water depth of 4 inches shall be present from the
point of egress to the downstream waters of this state, unless another
connection is provided as per OAR
635-412-0035(2)(l)(A).
(b) Upstream Fish Passage shall be
provided:
(A) If the Department determines
there is current or historic native migratory fish spawning or rearing habitat
within the estuary, floodplain, or wetland area impounded by the artificial
obstruction; and
(B) During the
period determined by the Department.
(6) Requirements for fish passage by trap
collection and transport include:
(a) A permit
issued by the Department is required to take fish when operating
traps;
(b) Traps shall be
constructed and operated to prevent physical or physiological injury to native
migratory fish;
(c) Traps shall
meet all requirements of OAR
635-412-0035(2)(g);
(d) Traps located within a fishway (i.e.,
"in-ladder" traps) shall not inhibit native migratory fish from entering the
fishway or trap and shall be removed if the Department determines that fish are
not entering the trap;
(e) Traps
should be constructed and operated so native migratory fish proceed through
traps with minimal delay and are removed from traps as frequently as necessary
to avoid over-crowding;
(f) All
native migratory fish, excluding those which have approved take authorization
from the Department and that do not require fish passage as per OAR
635-412-0035(1)(a),
shall be returned to the stream by one of the following methods:
(A) Movement from the trap to
immediately-adjacent water which has fish passage; or
(B) Transport within a watered container,
including but not limited to lifts, hoppers, locks, and trucks, from the trap
to a location approved by the Department; and
(g) Traps shall be utilized where the
feasibility of other fish passage structures or other site-specific
considerations warrant use of trap collection and transport, or otherwise, the
Department determines, using its professional judgment, trap collection and
transport will result in an effective means of ensuring access to habitat above
or below the artificial obstruction by native migratory species.
(7) Additional requirements for
specific native migratory fish are:
(a)
Acipenser species (sturgeon):
(A) The fish passage structure shall not
require fish to jump when entering, within, or exiting the structure;
(B) The fish passage structure, including
trash racks, shall be sized to accommodate the largest individual expected to
require fish passage;
(C)
Non-volitional transport within a watered container may only be allowed with
Department approval; and
(D)
Turning pools within the fish passage structure must be designed to allow for
fish passage of a native migratory species at least 2 body lengths of the
largest individual native migratory species currently or historically in the
waters affected by the artificial obstruction.
(b)
Catostomus,
Chasmistes, and Deltistes species (suckers):
(A) The fish passage structure shall not
require fish to jump when entering, within, or exiting the structure;
(B) Fishways shall:
(i) Have a maximum water velocity of 4 feet
per second;
(ii) Have a minimum
water depth of 12 inches;
(iii)
Maximize downstream flow between pools to avoid back eddies;
(iv) Have curved walls within turning pools;
and
(v) Have a slope less than 4
percent.
(c)
Entosphenus and Lampetra species (lamprey):
(A) Fishways and associated structures (e.g.,
dams and spillways) shall have 4 to 6 inch smooth rounded radii edge surfaces
(floors, aprons, walls, and weir crests) over which
Entosphenus and Lampetra species may
pass;
(B) Fishways shall not have
water surface to water surface jumps or overhanging surfaces unless fishway
surfaces have a 4 to 6 inch smooth rounded radii (floors, walls and weir
crests) over which Entosphenus and Lampetra
species may pass;
(C) Fishways
shall, in locations with water velocities greater than 2 feet per second, have
a passage route that:
(i) Has a smooth,
continuous, impermeable, uninterrupted surface or a simulated
streambed;
(ii) Has water
velocities over the structure's surface less than 8 feet per second;
and
(iii) Is wetted;
(D) Denil fishways shall not be
used unless an alternative passage route is provided;
(E) Traps, picketed leads, picket weirs,
auxiliary water supply grating or any other fishway grating shall have a
spacing of less than 0.7 inches to preclude lamprey passage, or greater than
1.0 inch to allow lamprey to pass through;
(F) Fishway wall diffusers for auxiliary
water supply shall be located at least 6 inches above finish floor of fishway
pool;
(G) Auxiliary water floor
diffusers shall be avoided if possible, but if necessary shall be located to
provide at least 12 inches width of continuous smooth floor passage route along
fishway floor;
(H) Fishway designs
shall consider orifice flow if Entosphenus or
Lampetra species are present.
(I) Orifices shall be positioned flush with
the fishway floor and flush along one fishway wall; and
(J) Lamprey Passage Structures (Lamprey
Ramps) shall be considered when retrofitting existing artificial obstructions
to improve conditions for upstream migration of Entosphenus
and Lampetra species.
(d)
Oncorhynchus species
(trout and salmon): fish passage structures for Oncorhynchus
keta (chum) shall not require fish to jump when entering, within, or
exiting the structure.
(e)
Ptychocheilus species (pikeminnow): fish passage structures
shall meet the requirements of OAR
635-412-0035(7)(a).
(f) If more than one native migratory fish
species requires passage at a site and the requirements for the different
species are mutually exclusive, the Department shall determine the required
passage criteria.
(8)
Requirements for artificial obstruction removal are:
(a) Artificial obstruction removals shall
follow the requirements of OAR
635-412-0035(10);
(b) If not completely removed, no parts of
the remaining artificial obstruction shall:
(A) Constrict the stream channel;
or
(B) Cause low flow depths less
than the surrounding stream channel.
(c) After an artificial obstruction is
removed the stream channel shall be restored; and
(d) The stream channel restoration shall
address impacts to stream habitat caused by the artificial obstruction while in
place and by its removal, including but not limited to upstream and downstream
channel degradation, and provisions shall be made to address unexpected fish
passage issues resulting from removal.
(9) Requirements for exclusion barriers are:
(a) When fish passage is not required or is
provided by other means, exclusion barriers shall only be placed in the
following situations:
(A) To guide fish to an
approved fish passage structure or trap;
(B) To prevent fish from leaving waters of
this state and entering human-made water supply conduits;
(C) To prevent fish from entering waters of
this state associated with operations of another artificial obstruction that
could lead to fish injury; or
(D)
To achieve other fish management objectives approved in writing by the
Department; and
(b)
Exclusion barriers shall comply with National Marine Fisheries Service or U.S.
Fish and Wildlife Service criteria.
(10) Requirements for fish passage during
construction of fish passage structures and periods when temporary artificial
obstructions are in place are:
(a) All fish
passage structures shall be constructed and temporary artificial obstructions
shall be in place only during the Department approved site-specific in-water
work period;
(b) At times indicated
by the Department as per OAR
635-412-0035(1)(a),
downstream fish passage shall be provided and:
(A) The outfall of a stream flow bypass
system shall be placed to provide safe reentry of fish into the stream channel;
and
(B) If downstream fish passage
during construction is not required and stream flow is pumped around the site,
the site shall meet Department screening or bypass requirements.
(c) At times indicated by the
Department as per OAR
635-412-0035(1)(a),
upstream fish passage shall be provided and shall be based on the wetted-width
or flows of the stream during the period of construction or temporary
obstruction;
(d) In-stream
construction sites shall be isolated from stream flow and fish;
(e) Prior to in-stream construction
activities, all fish shall be safely collected, removed from the construction
site or de-watered reach, and placed in the flowing stream outside of the areas
of project impacts by an authorized person with an ODFW Fish Rescue Salvage
Authorization issued by and following the guidance of the Department;
and
(f) After construction, the
construction site shall be re-watered slowly and in a controlled manner to
prevent loss of downstream surface water as the construction site's streambed
absorbs water.
(11)
Requirements for experimental fish passage structures are:
(a) Experimental fish passage structures
shall only be allowed in waters of this state after:
(A) Laboratory testing with native migratory
fish or similar species indicates that the structure provides fish
passage;
(B) Field testing with a
prototype structure, at a location where existing fish passage will not be
compromised and where fish passage does not need to be addressed under OAR
635-412-0020(2) and
(3), indicates that the structure will
provide fish passage; and
(C) In
addition to information needed to evaluate the structure's design for the
specific location, the following are submitted to and approved by the
Department:
(i) A written summary of the
laboratory and field testing and how the results indicate that fish passage
shall be provided;
(ii) A
monitoring and reporting plan to determine if the installed experimental fish
passage structure meets applicable design objectives and is providing fish
passage; and
(iii) A modification
plan for the experimental fish passage structure if monitoring indicates that
fish passage is not being provided, including standard thresholds that once met
will require owner or operator to initiate these modifications.
(b) If at any time an
experimental fish passage structure is deemed by the Department in writing to
not provide fish passage, the owner or operator, in consultation with the
Department, shall make such modifications to the structure or operation as are
necessary to provide fish passage, and, after a reasonable period, if
modifications are deemed by the Department in writing to not provide fish
passage, a fish passage structure that meets the standard criteria of OAR
635-412-0035 shall be installed
as soon as practicable but no later than the end of the next complete in-water
work period after notification by the Department, unless the Department
determines additional time is necessary;
(c) The owner or operator of an experimental
fish passage structure shall allow the Department to inspect experimental fish
passage structures at reasonable times;
(d) Five years after the experimental fish
passage structure is installed and fish are present to attempt passage a final
monitoring report shall be submitted to the Department and the Department shall
determine if the experimental fish passage structure provides fish passage;
and
(e) The Department may consider
a fish passage structure to no longer constitute an experimental fish passage
structure after the Department finds three such structures of the same design
concept placed in waters of this state effectively provide fish
passage.
Notes
Statutory/Other Authority: ORS 496.138 & ORS 509.585
Statutes/Other Implemented: ORS 496.012 & ORS 509.585
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