Gales Creek Large Woody Debris Inventory Report
Results |
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All of the surveyed reaches contained
pieces of LWD within the stream’s
bankfull width and in the recruitment zone
(Table 2). The 200-ft segments averaged
15 pieces of LWD instream and in the recruitment
zone, combined (n = 26; 8 pieces LWD per
100 ft). All segments averaged 2 pieces
of instream LWD (n= 26; 1 pieces LWD per
100 ft) and 14 pieces of recruitment zone
LWD (n= 26; 7 pieces LWD per 100 ft). Recall
that the recruitment zone for this study
was defined as 50 ft from the stream’s
bankfull mark. Instream numbers reflect
wood counted within the stream’s bankfull
mark. There were no live, qualifying, coniferous
trees observed within the survey.
Reach GL05 contained the highest total
number of instream and recruitment zone
LWD. The greatest number of perched or dead
trees within the recruitment zone occurred
in reach GL08 (Table
2). The majority of
LWD within all reaches (82.5 %) fell into
the 1-2 ft diameter class (Table 3). Debris
jams were found infrequently throughout
the surveys, with a total of five found
throughout the 5,000 ft of stream sampled.
When these debris jams did occur, 40% demarcated
a break in habitat types, from pool to riffle
or glide (Table 4). This may be viewed as
the ability of LWD jams to create habitat
heterogeny in Gales Creek.
Habitats encountered within the reaches
were glides, pools and riffles. Stream temperatures
ranged from 10 to 15 °C throughout the
surveys; air temperatures ranged from 6 to
18 °C. Land use in the surveyed portion
of Gales Creek is primarily agricultural
with some forested and rural residential
lands. A synopsis of the LWD survey in each
reach follows.
GL02
Reach GL02 begins at the confluence
of Gales and Kelly Creeks and extends
upstream approximately 3,100 ft (Figure
2). Habitat types in GL02 include riffles,
glides and pools with a mean gradient of
1% (Figure 3).
The air temperature and water temperature
at GL02 were 8 °C and 10 °C, respectively.
On average, GL02 had 16.0 pieces LWD per
200-ft reach. A total of 80 pieces of qualifying
wood were observed within the survey, with
one piece observed within the stream. The
remaining 79 pieces were observed within
the recruitment zone of the creek. Within
the recruitment zone, 11 pieces were dead
or perched for recruitment while 68 were
live trees (Table
2). The majority (87.5%)
of the LWD surveyed within the reach fell
within the 1-2 ft diameter class (Table
3). No large debris jams or notable wood
features were observed within the surveyed
reach segments on GL02.
GL05
Reach GL05 begins where Roderick Road
crosses Gales Creek and extends upstream
approximately 1000 ft (Figure 4). Habitat
types within GL05 include riffles, glides
and pools with a mean gradient of 2% (Figure
5).
The air temperature and water temperature
in GL05 were 9 °C and 11 °C, respectively.
On average, GL05 had 25.4 pieces LWD per
200-ft reach. One hundred twenty-seven pieces
of qualifying wood were observed within
the survey area, with 13 pieces observed
within the bankfull width of the Gales Creek.
The remaining 114 pieces were observed within
the recruitment zone. Of these pieces for
potential introduction, eight were dead
or perched for recruitment; 106 were live
trees (Table 2). The majority (89.8%) of
the LWD surveyed within the reach fell into
the 1-2 ft diameter class (Table
3). Two
large debris jams were observed within the
survey segments (Figures 4 and 6). The jams
contained five and four pieces of qualifying
wood and distinguished no habitat changes
(Table 4).
GL06
Reach GL06 begins 900 ft downstream of
the Roderick Road crossing of Gales Creek
and extends upstream, ending at this crossing
(Figure 4). Habitat types encountered included
glides and pools with a mean gradient of
1% (Figure 7).
The air temperature and water temperature
were 5.5 °C and 11 °C, respectively.
On average, GL06 had 16.0 pieces LWD per
200-ft reach. A total of 72 pieces of qualifying
wood were observed during the survey, with
five pieces observed within bankfull width
of the stream. The remaining 67 pieces were
observed within the recruitment zone outside
of either bankfull of the creek. Of these
pieces for potential introduction, nine
were dead or perched for recruitment while
the remaining 58 were live trees (Table
2). The majority (59.7%) of the LWD surveyed
within the reach sized within the 1-2 ft
diameter class (Table
3). One large debris
jam was observed within the survey segments
(Figures 4 and 8). This debris jam contained
three pieces of qualifying wood and marked
a change in habitat type from pool above
the jam to riffle below (Table
4).
GL08
Reach GL08 begins approximately 2,500
ft above the Springtown Road crossing and
extends upstream 1,600 ft (Figure 9). Habitat
types in GL08 include riffles, glides and
pools with a mean gradient of 1% (Figure
10).
The air temperature and water temperature
were 18 °C and 15 °C, respectively.
On average, GL08 had 12.4 pieces LWD per
200-ft reach. Sixty-two pieces of qualifying
wood were observed within the survey;
four of these pieces were lying within the
stream’s
bankfull width. The remaining 58 pieces
were observed within the recruitment zone
on either bank. Within the recruitment
zone, twelve pieces of LWD were dead or
perched for recruitment. Forty-six trees
were live (Table
2). The majority (85.5%) of the LWD
surveyed within the reach sized within
the 1-2 ft diameter class (Table
3). One large
debris jam, containing four pieces of
qualifying wood, and two beaver dams were
observed within the survey segments (Figures 9 and
11). The beaver dams contained no qualifying
wood pieces, but marked changes from pool
to riffle habitat types (Figure
11).
GL09
Reach GL09 begins approximately 930 ft
above the Springtown Road crossing of Gales
Creek and extends upstream 1,700 ft (Figure
9). Habitat types in GL09 include riffles,
glides and pools with a mean gradient of
1% (Figure 12).
On the survey date, the air temperature
and water temperature at GL09 were 18 °C
and 15 °C, respectively. On average,
GL09 had 9.8 pieces LWD per 200 ft reach.
Of the fifty-four pieces of qualifying wood
observed within GL09, 11 pieces were within
the stream’s bankfull width. The remaining
43 pieces were observed within the recruitment
zone on either side of the creek. Six pieces
within the recruitment zone were dead or
perched for recruitment, while 37 pieces
were live (Table 2). The majority (83.3%)
of the LWD surveyed within the reach sized
within the 1-2 ft diameter class (Table
3).
One large debris jam was observed within
the survey segments (Figures 9 and 13). This
jam contained five pieces of qualifying wood,
and marked no change in habitat type (Table
4).
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