MACHMELL WATERSHED
LEVEL I FISH HABITAT ASSESSMENT
VOLUME II - DATA APPENDICES
JULY, 1998
Prepared by
Judy E. Hillaby
under contract to
Western Forest Products Ltd.,
Mainland/Islands Regionm,
#118 - 1334 Island Highway,
Campbell River, B.C.
V9W 8C9
for submission to
Ministry of Environment, Lands and Parks,
680 Borland Street,
Williams Lake, B.C.
V2G 4T1
A program conducted through the auspices of Forest Renewal B.C.,
Contract # CCA - 855
TABLE OF CONTENTS
DOCUMENT ORGANIZATION
FISH DISTRIBUTION DATA FORM
Codes
Mainstem Machmell - Fish Distribution Criteria
Tributary Habitats - Fish Distribution Criteria
Fish Distribution Data Forms
HABITAT DIAGNOSIS SUMMARY FORM
Data Qualifications
Habitat Diagnosis Summary Forms
FISH CAPTURES
Capture Summary
Capture Operations
FIELD DATA
REPORT ORGANIZATION
This report contains appendix field data from the Machmell Watershed Level I Fish Habitat Assessment, FRBC Contract # CCA - 855. Deliverables from this contract include:
- Volume II (this document) - detailing field data for the project
- Photo library (archived separately)
- Forms 5 and 6 (contained in this document), which are linked to the GIS map product for each tributary with a watershed code
- Fish capture summary (contained in this document).
- Volume I (separate document) - summarizing field data and outlining proposed sites and strategies for fish habitat restoration
- GIS map product, outlining field sites visited, fish collection sites, proposed restoration sites and overall fish distribution (provided separately)
Field crews were requested to gather information in a number of formats, including photo records, quantitative Habitat Survey Data Form (Form 4), a field log of features and points of note, and sketch diagrams of the areas surveyed. This document has bundled the different data types together, so that the results from each team’s survey is contained together. Where data forms are lacking, or easily misinterpreted, the reader is referred to the subjective information for further explanation. Data is bundled by field code, which is then electronically mapped.
FISH DISTRIBUTION DATA FORM
Codes:
As per Technical Circular # 8, the following codes were used to describe fish distribution:
H = historically present
U = unknown whether or not this species exists here
K = presence known
N = not present
S = suspected presence
The following codes were used to describe the survey method for determining fish distribution:
VO = visual observation
MT - minnow traps
For the mainstem Machmell River, the data source was listed as:
DFO = DFO annual spawner surveys for salmon
CS = current study, where juvenile and adult fish were captured or seen, or carcasses found.
Mainstem Machmell - Fish Distribution Criteria:
- Sockeye are known to be present in the lower reaches and have access to anadromous stream area to Reach 4-2. Juveniles are listed as not present, as any found are present only briefly, as outmigrating fry.
- Coho are known to be present in the lower reaches and have access to anadromous stream area to Reach 4-2. Juveniles are also known to be present in pockets of suitable habitat within accessible stream areas.
- Chinook are known to be present in the lower reaches and have access to anadromous stream area to Reach 4-2. Juveniles are suspected to be present throughout these reaches; however, the length of stream residence is variable and they may have been absent during the October field survey.
- Steelhead are known to be present in the lower reaches and have access to anadromous stream area to Reach 4-2. Juveniles are also known to be present in pockets of suitable habitat within accessible stream areas.
- Chum are known to be present in the lower reaches but are not recorded beyond the lower bridge crossing at Reach 2-2. They are not normally found beyond the lower sections, and are not recorded further up in this case. They are listed as not present beyond Reach 2-2. The juveniles are listed as not present throughout the system, as any found are present only briefly, as outmigrating fry.
- Pinks are known to be present in the lower reaches but are not recorded beyond the lower bridge crossing at Reach 2-2. They are often found further upstream in large rivers; however, there is no suitable spawning habitat between Reach 2-2 and the anadromous barrier at Reach 4-2. They are not recorded further up in this case, and are listed as not present. The juveniles are listed as not present throughout the system, as any found are present only briefly, as outmigrating fry.
- Dolly Varden have been found in areas far upstream, and are assumed to be present (all life stages) in suitable habitats of all the accessible downstream areas. In selected low-gradient areas above barriers they are suspected to be present.
- Cutthroat trout are recorded in some areas of the lower Machmell, but were not found throughout the survey. Anadromous cutthroat populations are known in Oweekeno Lake tributaries and they are listed as known to the anadromous barrier, even though suitable in-stream habitat is very limited. Isolated resident populations above barriers have not been found; however, these are listed in this case as unknown for all life stages.
- Rainbow trout are not recorded in this system; however, given the presence of steelhead, there may be species identification problems, or residual populations. They are listed throughout as unknown, rather than as clearly not present.
Tributary Habitats - Fish Distribution Criteria:
* If the tributary habitat was too steep to provide fish habitat, all species were
considered to be NOT PRESENT.
* In areas that were above anadromous fish access, if fish were found in a stream
section, then they were KNOWN to be present in all accessible downstream
locations.
* If the tributary habitat was accessible to anadromous fish but did not provide suitable
habitat for a particular species and that species was not observed, the presence of that
species was considered as UNKNOWN.
* If the tributary habitat was accessible to anadromous fish but did provide suitable
habitat for a particular species and that species was not observed, the presence of that
species was considered as SUSPECTED PRESENT.
Fish Distribution Data Forms:
HABITAT DIAGNOSIS SUMMARY FORM
Data Qualifications:
- Tech. Circular #8 does not provide habitat evaluation standards for streams with 50 - 100m channel widths, as the Machmell is. Field studies indicated that fish (both adults and rearing juveniles) were concentrated in complex habitats near stable banks. Accordingly, professional judgements were based on Technical Circular #8 and applied to the stream margin areas only. The quality and quantity of juvenile rearing, substrate type and condition, LWD presence and in-stream cover does not apply to mid-channel habitat.
- A field was added to correlate the data with left or right stream bank (facing downstream) for the lower reaches of the mainstem.
- Adult salmon were seen holding in the mainstem. These may have been recorded as "glide" habitats in the notes; but the presence of the spawners were an indication that holding areas were not limiting, at least for larger fish. Accordingly, the condition of adult holding pool habitats refers generally to the mainstem, and secondarily to marginal habitats, where these exist.
- The water level in this system rose and fell significantly during the study, according to rainfall patterns (see Hydrology section). The effect of this during the study is that pool habitat was sometimes obscured in high water, as pools and glides merged together. Pool habitats were sometimes judged to be non-limiting in cases where glide habitats may be very similar to pools.
- Smaller tributaries were also affected by high water. where appropriate, some glide habitats were included in pool habitats for diagnostic purposes.
- Dominant substrate varied considerably across the inside channel width. In marginal areas in the lower reaches, it was often fine material, indicating degraded spawning habitat and gravel compaction and would be judged "poor". In fact, a large amount of gravel was located in mid-channel; however, it was still judged to be "poor" as the fine material in the margins (where fish congregated) was also an indicator of bank and channel instability.
- LWD data is subject to great interpretation by individual reviewers, especially so in rivers where large fluctuations in flow cause LWD to be high up on the bankfull area, or in large jams, so that its functionality and stability is questionable. In this case, the lower reaches had plenty of LWD, but it was not providing good cover in pools. To arrive at the habitat condition judgements in this case, photo records were used extensively.
- The fish habitat condition of stream sections in reaches 2-5 to 5 were judged from very limited field data, as the stream channel is at the bottom of a 100m canyon and was only marginally accessible, even with aircraft.
- The reader is reminded that judgements are in general categories, rather than precise calculations from individual data sets. Several forms of data were used to arrive at these judgements, including field data measurements, subjective field notes and sketches, as well as ground and aerial photos. Refer to the field data section for further details on specific areas.
Habitat Diagnosis Summary Forms:
FISH CAPTURES
FIELD DATA
BR - 1
BR - 2
BR - 3
BR - 4
BR - 5
BR - 6
BR - 7
BR - 8
BR - 9
BR - 10
BR - 11
GB - 1
BR - 12
GB - 2
GB - 3
GB - 5
GB - 6
HP - 1
HP - 2
HP - 3
HP - 4
M - 1
M - 2
0C - 3
0C - 4
0C - 5
0C - 6
0C - 7
0C - 8
0C - 9
0C - 10
0C - 11
OC - 1
OC - 2
M - 3
M - 4