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Bear Creek Fishery Section
- Commission Leaves Bear Creek Segment 1a on 2006 Monitoring & Evaluation List
-
Monitoring & Evaluation Issue Paper
version - IP10
-
Analyses Protocols
- 2006 Fish surveys at 7 locations completed segment 1a on September 25-27, 2006
- Macroinvertebrate Samples on September 5, 2006 (7 locations)
- Habitat Study on September 5, 2006 (7 locations)
- 2005-06 Off-Season Segment 1a Monitoring Plan
- 2006 Segment 1a Monitoring Plan
- 2005 Segment 1a Bear Creek Data Report
- 2007 Fish Data
- 2008 Fish Data (See Fishery Master)
- Flow Study Summary
- Special Stream Studies
Bear
Creek
Fishery
Management
and
Temperature
Investigations
2009
Fishery
Master
Spreadsheet Data
Fishery
Issues
Paper
IP10
Fishery
Analysis
Protocol
and Methods
V09
2008
Data Report Bear Creek Watershed
2008
Flow
Study
Summary
Macroinvertebrate data
Monitoring Sites
Bear
Creek
Segment
1a
Fishery
Problem
The
health
of
the
fishery
in
Bear
Creek
segment
1a
appears
affected
by
unknown
or
speculated
anthropogenic
causes
that
result
in
annual
variations
(erratic
increases
and
declines)
as
measured
at
fishery
trend
monitoring
sites
in
the
stream
reach.
Identify
factors
that
could
or
do
affect
fishery
and
could
or
do
result
in
fishery
declines
either
within
the
entire
stream
reach
or
at
specific
locations
along
the
stream
reach.


Regulatory
Issue Statement
-
In 2005, the Environmental Protection Agency listed a portion of the Bear Creek Segment 1a from the Evergreen Lake outfall to the Harriman Ditch in Morrison, Colorado as impaired by temperature resulting in an impact to the aquatic life, specifically the fishery.
-
EPA claims evaluated temperatures in the segment above a 20 degree Celsius mark stressed the fishery during lower flow periods and caused a decline in the biomass and size class at several upstream locations.
-
Segment 1a is not on the 2004 Colorado 303(d) list.
-
The Division has not proposed listing the segment on the 2006 303(d) list (Regulation #93). An evaluation of temperature data from 2002-2005 using a maximum weekly average temperature threshold of 20 degrees Celsius (MWAT 20) had no exceedances.
-
The Division has recommended retaining the segment on the 2006 Monitoring and Evaluation List (Regulation #94). The status of the fishery and recovery of the fishery from severe drought conditions remains questionable. Additionally, the Division believes more habitat, macroinvertebrate and fishery data correlated with river chemistry is needed to address the aquatic life concerns.
Association
Position
The
Bear
Creek
Watershed
Association
Board
takes
a
proactive
stance
and
has
begun
review
of
the
new
options
related
to
the
listing
through
a
technical
review
committee
(Bear
Creek
TRC).
The
positions,
issues,
concerns
and
comments
are
from
the
Bear
Creek
Association
Board,
WQCD
staff,
Colorado
Division
of
Wildlife,
and
Evergreen
Trout
Unlimited.
The
Bear
Creek
TRC
is
continuing
strategy
development
sessions
with
Board
members,
WQCD
staff,
TU,
DOW,
(Future
participants
include
EPA,
Denver
Parks
and
others
as
appropriate).
The
Association
will
maintain
a
detailed
temperature
and
ammonia
monitoring
program
on
segment
1a
for
three
years
(through
2008)
and
will
maintain
a
sampling
effort
until
the
temperature
issue
is
resolved.
The
Association
has
committed
funding
to
this
special
study
through
2008.
The
Association
will
use
a
five-year
data
set
of
temperature
readings
on
segment
1a
and
request
a
temperature
delisting
process
(EPA
List),
if
data
continues
to
confirm
no
MWAT
problem.
The
Association
Board
data
record
does
not
indicate
a
temperature
problem,
but
the
Board
does
acknowledge
fishery
concerns
related
to
low
flow
conditions.
The
Association
wants
an
open,
cooperative
and
coordinated
process
with
no
surprises
in
the
end.
All
Association
meetings
are
open
and
the
Board
will
address
any
and
all
related
issues
or
concerns.
New
Recommendations
or
Positions
From
Bear
Creek
TRC
-
Fishery survey sites added at Downtown Evergreen (across from Little Bear) and upstream of Evergreen Lake at Keys-On-The Green.
-
The Five traditional sites will have continued annual fish monitoring.
-
The DOW fishery data will be used to determine fishery health and no other surveys are necessary.
-
The four fish species of interest are Brown Trout, Rainbow trout, Long-Nose Dace, and Long-Nose Sucker. Other “potential” species that could affect a temperature TMDL are Rainbow Trout, Long-nose dace and the Long-nose sucker.
-
Stocked Tiger Muskie in Evergreen Lake.
-
Brook Trout and Cut-throat Trout are not potential species in this segment.
-
The Brown Trout is a reproducing fishery.
-
Need to obtain life stages information for four target species.
-
Macroinvertebrate samples collected in the fall will be at fish survey sites, within limits of sample collection. The state collection method used and data will be incorporated in to both state and BEAR Creek data sets. The timed kick net method will be used. Several Bear Creek sample sites will be adjusted to coincide with fishery survey sites. The Association will target a five-year data set.
-
River chemistry data and future habitat surveys will also be linked with fish survey sites.
-
A model approach will be used to predict fishery recovery and maintenance.
-
The Association will develop a fact sheet on the temperature collection protocols for wide distribution.
-
A detailed flow study of segment with travel time, flow curves, gain-loss study and other needed hydrology.
|
Bear Creek Sement 1a Fishery Summary (DOW Data) |
|
|
Brown Trout - Number of Fish/ Acre |
|
|
Monitoring Site |
1988 |
1989 |
1990 |
1991 |
1992 |
1993 |
1994 |
1995 |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
2003 |
2004 |
2005 |
2006 |
2007 |
1998-06 Average |
SD |
|
Williams |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
716 |
|
|
|
Dedisse Park |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
886 |
805 |
640 |
846 |
57 |
|
Evergreen Downtown |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
855 |
1121 |
588 |
988 |
188 |
|
Davidson Lodge |
|
|
284 |
416 |
|
|
425 |
|
|
|
|
585 |
855 |
1098 |
528 |
390 |
474 |
562 |
902 |
644 |
593 |
252 |
|
O'Fallon Park |
103 |
260 |
|
320 |
|
|
180 |
|
|
356 |
|
201 |
554 |
368 |
66 |
113 |
92 |
538 |
638 |
491 |
291 |
192 |
|
Lair O' Bear |
71 |
88 |
|
143 |
|
|
98 |
|
|
244 |
|
96 |
325 |
309 |
463 |
333 |
943 |
1155 |
1449 |
841 |
440 |
452 |
|
Idledale |
20 |
4 |
|
55 |
|
|
83 |
|
|
245 |
|
82 |
|
|
640 |
535 |
662 |
1016 |
1229 |
520 |
416 |
431 |
|
Morrison Park |
2 |
12 |
9 |
65 |
|
|
43 |
|
|
|
|
72 |
|
|
224 |
359 |
702 |
1075 |
675 |
517 |
294 |
366 |
|
average |
49 |
91 |
147 |
200 |
|
|
166 |
|
|
282 |
|
207 |
578 |
592 |
384 |
346 |
575 |
870 |
974 |
620 |
345 |
244 |
|
Brown Trout - Estimated Pounds of Fish/ Acre |
|
|
Monitoring Site |
1988 |
1989 |
1990 |
1991 |
1992 |
1993 |
1994 |
1995 |
1996 |
1997 |
1998 |
1999 |
2000 |
2001 |
2002 |
2003 |
2004 |
2005 |
2006 |
2007 |
1998-06 Average |
SD |
|
Williams |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
87 |
|
|
|
Dedisse Park |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
101 |
71 |
65 |
86 |
21 |
|
Evergreen Downtown |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
177 |
233 |
171 |
205 |
40 |
|
Davidson Lodge |
|
|
48 |
75 |
|
|
74 |
|
|
|
|
159 |
277 |
268 |
61 |
86 |
101 |
83 |
136 |
115 |
124 |
80 |
|
O'Fallon Park |
11 |
23 |
|
42 |
|
|
33 |
|
|
64 |
|
55 |
147 |
108 |
15 |
39 |
12 |
38 |
108 |
89 |
53 |
43 |
|
Lair O' Bear |
7 |
11 |
|
17 |
|
|
34 |
|
|
64 |
|
4 |
74 |
132 |
151 |
122 |
85 |
137 |
226 |
148 |
82 |
68 |
|
Idledale |
4 |
1 |
|
12 |
|
|
20 |
|
|
40 |
|
35 |
|
|
296 |
116 |
92 |
130 |
147 |
89 |
81 |
89 |
|
Morrison Park |
1 |
3 |
2 |
3 |
|
|
5 |
|
|
|
|
34 |
|
|
23 |
54 |
47 |
142 |
69 |
76 |
35 |
43 |
|
Average |
6 |
10 |
25 |
30 |
|
|
33 |
|
|
56 |
|
57 |
166 |
169 |
109 |
83 |
67 |
115 |
141 |
105 |
95 |
56 |
|