SOUTH THOMPSON RIVER Inventory, Mapping, and Aquatic Habitat Index
Prepared By: Ecoscape Environmental Consultants Ltd.
Prepared for: Fraser Basin Council on Behalf of
South Thompson-Nicola Regional District, City of Kamloops, Adams Lake Indian Band, and
TK’emlups te secwepemc
SOUTH THOMPSON RIVER Inventory, Mapping, and Aquatic Habitat Index
A Living Document – Version 1.0
Prepared For and In Partnership With:
FRASER BASIN COUNCIL ON BEHALF OF: SOUTH THOMPSON-NICOLA REGIONAL DISTRICT, CITY OF KAMLOOPS, ADAMS LAKE INDIAN BAND, AND TK’EMLUPS TE SECWEPEMC
Prepared By:
ECOSCAPE ENVIRONMENTAL CONSULTANTS LTD. # 102 - 450 Neave Court Kelowna, BC V1V 2M2
May 2016
Ecoscape File No. 15-1588
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ACKNOWLEDGEMENTS
This project would not have been realized without the assistance and contribution from the following individuals and organizations:
Department of Fisheries and Oceans Canada – for their support and expertise in development of the RIM methodology and Aquatic Habitat Index as it was first developed for the Lower Shuswap River project and carried forward to the South Thompson River project.
Salmon spawning information was contributed by Fisheries and Oceans Canada (2015)
Support for this project was provided by: Fraser Basin Council National Conservation Plan – Canada and South Thompson-Nicola Regional District
Field Inventory Crew: Kyle Hawes (Ecoscape) Bob Harding (Fisheries and Oceans Canada Tracy Thomas (Fraser Basin Council) Jennifer Pooley (Adams Lake Indian Band)
The following parties contributed to the development of the Aquatic Habitat Index: Kyle Hawes, Ecoscape Environmental Consultants Ltd Jason Schleppe, Ecoscape Environmental Consultants Ltd Bob Harding, Fisheries and Oceans Canada Bruce Runciman, Fisheries and Oceans Canada
The principle author of this report was: Kyle Hawes, R.P.Bio. (Ecoscape)
Geographical Information Systems (GIS) mapping and analysis was prepared by: Robert Wagner (Ecoscape) Rachel Plewes (Ecoscape)
Recommended Citation: Hawes, K. R. Wagner, R. Plewes and J. Schleppe. 2016. South Thompson River Inventory, Mapping, and Aquatic Habitat Index. Ecoscape Environmental Consultants Ltd. Project File: 15-1588. 63pp + appendices.
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INFORMATION DISCLAIMER
The results contained in this report are based upon data collected during a single season inventory. Biological systems respond differently both in space and time. For this reason, the assumptions contained within the text are based upon field results, previously published material on the subject, and airphoto interpretation. The material in this report attempts to account for some of the variability between years and in space by using safe assumptions and a conservative approach. Data in this assessment was not analyzed statistically and no inferences about statistical significance are made if the word significant is used. Use of or reliance upon biological conclusions made in this report is the responsibility of the party using the information. Neither Ecoscape Environmental Consultants Ltd., nor the authors of this report or Fraser Basin Council is liable for accidental mistakes, omissions, or errors made in preparation of this report because best attempts were made to verify the accuracy and completeness of data collected, analyzed, and presented.
This is intended as a “Living Document”. In so being, it may be continually edited and updated and may evolve and be expanded as needed, and serve a different purpose over time.
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EXECUTIVE SUMMARY
A comprehensive inventory was completed for the South Thompson River (STHM) in November 2015 from Little Shuswap Lake (Chase) downstream to Kamloops Lake and to subsequently complete an AHI. This Large River Inventory and Mapping approach (RIM) adapts the data collection methods and standards of Sensitive Habitat Inventory and Mapping (SHIM) (Mason and Knight, 2001) and Foreshore Inventory and Mapping. The ensuing Aquatic Habitat Index (AHI) uses many different criteria, such as biophysical, fisheries values, and anthropogenic characteristics to estimate the relative habitat value of river reaches and bank segments that were defined during the inventory. The Habitat Index classifies this information in a 5-Class system from Very High to Very Low.
The South Thompson River flows from Little Shuswap Lake to Kamloops Lake, a distance of approximately 70 km. The River was broken into a total of 21 reaches. The left bank (looking downstream) was divided into 64 Segments and the right bank was broken into 90 Segments.
The STHM forms a straight to mildly sinuous channel thorough glaciolacustrine sediments. This results in the predominance of benched to mildly sloping river banks that are composed primarily of silt. The hydraulic character is predominantly glide with fine-textured substrates (i.e. sand/silt) over lower reaches. There is a marked increase in channel complexity (moving upstream) and habitat quality beginning around the Campbell Creek fan (downstream of the Lafarge Bridge). Deep pools, important for cover and general living as well as holding areas for anadromous migrations, amount to about 84 ha (3%) of the river. Of this area, only about 10 ha have been identified by the Department of Fisheries and Oceans (2015) as key holding areas. In total, only about 4% of the STHM has documented salmon spawning use. Sockeye spawning in the STHM is only documented in the uppermost reach (21) just below Little Shuswap Lake, accounting for only about 0.1% of the river (by channel area). Moderate to Moderate–High Chinook spawning use areas occupy about 1.6% of the river. High and Very High Chinook spawning intensity is provided by about 1% and 0.5 of the river respectively.
Over 75% of the left bank and greater than 80% of the right bank of the STHM and THOM (downstream to Kamloops Lake) have been altered by human activities. Railway (infrastructure) is persistent along the left bank of the STHM, often with associated bank armouring. Rail encroachment and disturbance along the left bank amounts to over 31 km (38%) of the STHM.
Although the left bank was documented to have generally more intensive landuse activities (i.e. commercial/industrial and urbanization), the right bank of the river had a greater cumulative distance where impacts to the bank and riparian area exceeded 40% of the segment. Segments with a high level of impact (>40%) combined to over 41 km (50%) of the right bank. The combined length of highly impacted segments along the left bank totaled close to 26 km (31%) of the river from Chase to Kamloops Lake.
In total, there were 14 sanctioned and informal boat launches, 277 docks, and 106 water withdrawals (intakes) recorded. Livestock access was recorded to occur on over 5.3 km of the river bank with close to 73% of being along the right bank. Bank armouring (rip rap) and
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retaining walls were recorded on over 12.5 km (15%) of the left bank and 6.9 km (8%) of the right bank.
Bank instability along much of the river, is largely a function of the steep silt banks that have naturally eroded over time through the glaciolacustrine silts. However, this instability is exacerbated by riparian vegetation removal and encroachment associated with agriculture and industrial, commercial, urban, and rural developments. High to extreme severity bank erosion was documented on approximately 6.0 k m (7%) of the left bank and 4.6 km (6%) of the right bank.
The centerline AHI analysis resulted in about 6% of the river being ranked as Very High, 29% of the river being ranked as High, and 31% of the river ranked as Moderate. High scoring reaches included 4, 9, 10, 13, 18, and 19. Reach 21 received a Very High AHI score. Reach 4 represents the confluence with the North Thompson River. A slight increase in channel gradient within 2 km downstream of the Lafarge Bridge results in a greater prevalence of higher velocity runs and riffle-pool reaches especially prevalent around the Monte Creek confluence (Reaches 9 and 10) and then again upstream of Banana Island. Reach 21 is the uppermost reach just downstream of Little Shuswap Lake and provides high value riffle pool habitat with high documented use of both Chinook and Sockeye. In addition, the channel form, complexity, and substrates of Reach 21 have high suitability for resident fish spawning, and general living.
About 42% of the left bank of the STHM is ranked Very Low to Low according to Bank AHI scores. Similarly, about 40% of the right bank is ranked between Very Low and Low. Moderate AHI segments accounted for 39% of both the left and right banks of the STHM River. Approximately 18% and 20% of the left and right bank received High to Very High AHI scores respectively.
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TABLE OF CONTENTS
ACKNOWLEDGEMENTS ...... I TABLE OF CONTENTS ...... V
1.0 INTRODUCTION ...... 1 1.1 Project Background ...... 2
2.0 RIVER INVENTORY MAPPING ...... 3
2.1 Pre-Field / Start-up ...... 4 2.2 RIM Adapted SHIM/FIM for Large River Systems ...... 4 2.2.1 Centerline Survey ...... 4 2.2.2 Left and Right Bank Mapping ...... 6 2.2.3 Feature Mapping ...... 8 2.2.4 Key Fisheries Zones ...... 8 2.3 Instream Morphology and Habitat Feature Polygonization ...... 8 2.4 Riparian Polygonization ...... 9 2.5 Data Processing and Quality Assurance and Control ...... 12 2.6 Photo Log ...... 13
3.0 SOUTH THOMPSON RIVER KEY FISH SPECIES ...... 13
3.1 Kokanee ...... 13 3.2 Sockeye Salmon ...... 15 3.3 Rainbow Trout ...... 16 3.5 Coho Salmon ...... 18 3.6 Chinook Salmon ...... 21 3.7 Pink Salmon ...... 22 3.8 Bull Trout ...... 23 3.9 Dolly Varden ...... 24
4.0 AQUATIC HABITAT INDEX ...... 25
4.1 Instream Polygon Scoring Matrix ...... 25 4.2 Riparian Polygon Scoring Matrix ...... 28 4.3 AHI Logic, Calibration, and Ranking ...... 30 4.3.1 Centerline – Instream Zone AHI Logic ...... 31 4.3.2 River Bank – Riparian Band AHI Logic ...... 32 4.4 Restoration and Segment Prioritization Analysis ...... 32
5.0 INVENTORY SUMMARY OF RESULTS ...... 34
5.1 Stream Primary Character ...... 34 5.1.1 Shore Type Relative Distribution ...... 34 5.1.2 Landuse Relative Distribution ...... 37 5.1.3 River Bank Level of Impact ...... 41 5.2 Stream Channel and Hydraulic Character ...... 42
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5.3 Fish Habitat ...... 43 5.4 Modifications ...... 46 5.5 Bank Stability and Erosion ...... 48 5.6 South Thompson River Condition Score ...... 51
6.0 AQUATIC HABITAT INDEX RESULTS ...... 52
6.1 The River ...... 52 6.2 Riverbanks ...... 53 6.3 Restoration Analysis and Priorities ...... 56
7.0 DISCUSSION ...... 58
8.0 CLOSURE ...... 60
REFERENCES ...... 61
LIST OF TABLES
Table 1. Overview of river centerline data fields collected using the Trimble data dictionary...... 5 Table 2. Level of Impact rating criteria for South Thompson River Inventory and Mapping...... 6 Table 3. Overview of data collected for right and left bank segments during the field inventory...... 7 Table 4. Overview of watercourse and habitat attributes that were collected using the Data Dictionary developed for this project (Adapted from Module 3, Mason and Knight, 2001). The complete data dictionary can be found in Appendix D...... 8 Table 5. Hydraulic and instream habitat feature classes assigned to South Thompson River and associated low flood and wetland polygons ...... 9 Table 6. Broad vegetation communities (Habitat Types) used for classification of stratified polygons occurring along the South Thompson River (100-m band) from Little Shuswap Lake to Kamloops Lake (Adapted from Mackenzie and Moran (2004) and Lloyd et al. (1990))...... 10 Table 7. Site qualifiers assigned to each polygon (Table 6) to reflect the estimated level of disturbance and habitat quality and condition...... 12 Table 8. Fisheries relative habitat values (RHV) and weighted scores for aquatic and riparian habitat features...... 26 Table 9. Weighted scores for mapped salmonid holding areas (DFO 2015)...... 26 Table 10. Relative value and weighted scores for mapped salmonid (Chinook, Sockeye) spawning areas and use intensity (DFO 2015). Assigned values are applied to the matrix based on the relative abundance spawning area polygons attribute to the total instream reach area...... 27 Table 11. Relative value and weighted scores for mapped instream substrate composition...... 27 Table 12. Ecological category: riparian habitat unit rating matrix (relative habitat value)...... 29 Table 13. The parameters and logic for the Centerline of the South Thompson River ...... 31 Table 14. The parameters and logic for the banks of the South Thompson River ...... 32 Table 15. Salmon aerial cover of spawning use (by density) in the South Thompson River...... 44 Table 16. Summary of anthropogenic features and modifications catalogued during the South Thompson River Inventory Mapping...... 47 Table 17. Summary of river bank integrity and erosion along the South Thompson River...... 49 Table 18. Summary of prominent erosion by bank and segment...... 50 Table 19. Level of impact rating / condition score for the South Thompson River...... 51 Table 20. Relative AHI rank distribution (by length) of the South Thompson River...... 52
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Table 21. Relative AHI rank distribution (by length) of the left and right bank (looking downstream) of the South Thompson and Thompson River (Little Shuswap Lake to Kamloops Lake)...... 53 Table 22. Summary of priority bank segments extracted from the AHI Restoration analysis. High priority sites are in bold...... 56
LIST OF FIGURES
Figure 1. Relative weighting of life history and habitat attributes for instream AHI scores...... 27 Figure 2. Relative distribution of shore types along the left and right bank of the South Thompson River. 35 Figure 3. Relative landuse distribution of along the left and right bank of the South Thompson River. The total length of the left (LB) and right river banks (RB) was 81 km and 83 km respectively...... 38 Figure 4. Level of impact category distribution on the left and right bank of the South Thompson River. . 41 Figure 5. South Thompson River hydraulic class distribution over the 83 km river length (centerline length)...... 42 Figure 6. Relative distribution of key habitat elements mapped during the South Thompson River inventory. Percentage values shown in the illustration represent the spatial coverage of respective key habitat features over the total instream area (~2785 ha)...... 44 Figure 7. Centerline/reach AHI scores and AHI Rank values (Low/Moderate/High/Very High)...... 52 Figure 8. Left bank segment AHI scores...... 54 Figure 9. Right bank segment AHI scores...... 55 Figure 10. Left bank potential AHI score differential (Potential bank AHI scores - Current AHI score) based on the results of the restoration analysis...... 57 Figure 11. Right bank potential AHI score differential (Potential bank AHI scores - Current AHI score) based on the results of the restoration analysis...... 57
MAPS
Map Set 1 ...... Riparian Habitat, Hydraulic, and Instream feature classification Map Set 2 ...... Inventoried Fish, Wildlife, and Habitat Attributes and Aquatic Habitat Index
APPENDICES
APPENDIX A. South Thompson River Reach Data (centerline survey) with AHI Scores APPENDIX B. River Bank (Left and Right) Segment Data Base with AHI Scores APPENDIX C. Centerline and Bank Aquatic Habitat Index Analysis Tables APPENDIX D. Data Dictionary for Large River System Inventory and Mapping
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1.0 INTRODUCTION
Mapping of waterbodies in the Okanagan and Shuswap and South Thompson-Nicola regions is being conducted following the current three step Lake Management process being standardized across British Columbia and described below:
1. Sensitive Habitat Inventory and Mapping (SHIM) and Foreshore Inventory and Mapping (FIM) are protocols used to collect baseline information regarding the current condition of watercourses (SHIM), shorelines (FIM), and associated riparian habitats. These inventories provide information on, channel character, shore/bank types and condition, substrates, land use, and habitat modifications. This information is combined where possible, with other mapping resources such as previous fisheries inventories, recent orthophotos, and other information. A protocol was subsequently developed for the Shuswap River to map large river habitat and character. This protocol, referred to as River Inventory and Mapping (RIM) was used in the current project to map the South Thompson River.
2. An Aquatic Habitat Index (AHI) is generated using the processed field data to determine the relative habitat value of the aquatic habitats and shoreline areas. This index follows similar methods that were developed for Okanagan Lake and Windermere Lake and is similar to other assessments used for Wasa, Moyie and Monroe Lakes. The Aquatic Habitat Index uses many different criteria, such as biophysical, fisheries values, and anthropogenic characteristics to estimate the habitat value of a shoreline segment. The Habitat Index classifies this information in a 5-Class system from Very High to Very Low. AHI is used for both FIM and RIM projects.
3. Shoreline Management Guidelines are prepared to identify the Shoreline Vulnerability or Sensitivity to changes in land use or habitat modification. Shoreline Vulnerability Zones are based upon the AHI described above. The Shoreline Vulnerability uses a risk-based approach to shoreline management, assessing the potential risks of different activities (e.g., construction of docks, groynes, marinas, etc.) in the different shore segments. The Shoreline Management Guidelines document is intended to provide background information to stakeholders, proponents, and governmental agencies when land use changes or activities are proposed that could alter the shoreline thereby affecting fish or wildlife habitat.
In 2015 Ecoscape Environmental Consultants Ltd. (Ecoscape) was contracted by the Fraser Basin Council to complete a comprehensive inventory of the South Thompson River (STHM) from Little Shuswap Lake (Chase) downstream to Kamloops Lake and to subsequently complete an AHI. The following technical report outlines the project approach and presents and analyzes the results of the both the Inventory and AHI phases of the project. This report is intended as a “Living Document”. In so being, it may be
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continually edited and updated and may evolve and be expanded as needed, and serve a different purpose over time.
1.1 Project Background
As resource development and human populations increase in British Columbia, pressures for all resources and services have accelerated. Rapid growth has often overwhelmed the ability of local planners to manage land and preserve sensitive habitats (Mason and Knight, 2001). This has resulted in the loss or degradation of aquatic and riparian habitats that are critical for fish and a diverse wildlife assemblage. More specifically, rapid population growth and development around our large interior lakes and rivers is one of many factors that is impacting our fish and wildlife resources. This tremendous growth rate has resulted in commercial and residential developments around these large lakes and rivers. This rapid increase in population and development presents a significant challenge to plan and/or manage future growth around our large interior lakes. Accordingly, there is an urgent need to develop stronger tools and better methods to conserve, protect and reclaim these habitats.
SHIM and FIM are recognized standards for fish and aquatic habitat mapping in urban and rural watersheds in British Columbia. These protocols attempts to ensure the collection and mapping of reliable, high quality, current, and spatially accurate information about local freshwater habitats, watercourses, and associated riparian communities.
These protocols are designed as land-planning, computer-generated, interactive GIS tools that identify sensitive aquatic and terrestrial habitats. They are intended to provide community, stewardship groups, individuals, regional districts and municipalities with an effective, low-cost delivery system for information on these local habitats and associated current land uses.
SHIM and FIM have numerous applications and can:
Provide current information not previously available to urban planners, to allow more informed planning decisions and provide inventory information for integration into Official Community Plans. In addition, this information can be used to educate the public as to the natural resource values of these systems and the impacts our activities have on them;
Provide a catalogue of the current condition of the foreshore to aid with permit and compliance monitoring;
Assist in the design of stormwater/runoff management plans;
Monitor for changes in habitat resulting from known disturbance;
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Identify and map potential point sources of pollution;
Help guide management decisions and priorities with respect to habitat restoration and enhancement projects;
Assist in determining setbacks and fish/wildlife-sensitive zones;
Identify sensitive habitats for fish and wildlife along watercourses;
Provide a means of highlighting areas that may have problems with channel stability or water quality that require more detailed study;
Provide a baseline inventory of existing shoreline developments/modifications such as docks, retaining walls, groynes, stream mouths, and land use activities;
Provide baseline mapping data for future monitoring activities and development of a shoreline management plan; and
Map and identify the extent of riparian vegetation available and used by wildlife and fish.
2.0 RIVER INVENTORY MAPPING
Biophysical surveys of the STHM used the RIM methodology which adapted the data collection methods and standards of Sensitive Habitat Inventory and Mapping (SHIM) (Mason and Knight, 2001) and Foreshore Inventory and Mapping. Data was recorded using a Trimble Geo7x/Data Logger and entered into a digital data dictionary. Data collection fields for respective biophysical and anthropogenic attributes are listed in the following sub sections. Data collection methods and processing standards can be reviewed in full at:
http://www.shim.bc.ca/methods/SHIM_Methods.html
Entering data into the Trimble Geo 7x (Left) using the data dictionary developed specifically for RIM (Appendix D). Marking up large format field maps for subsequent incorporation into GIS mapping and integration into the final data deliverables (Right).
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2.1 Pre-Field / Start-up
Ecoscape reviewed all pertinent background information useful to the project and incorporated this data, where relevant, into respective watercourse features and their attributes.
Ecoscape obtained aerial imagery from South Thompson-Nicola Regional District, the City of Kamloops, and Department of Fisheries and Oceans Canada. Preliminary reach breaks (segments) were identified and right and left bank shoreline segments were determined. In addition, we identified adjacent natural features of interest (i.e., tributaries, side channels, islands, wetlands etc.) that otherwise may not be picked up during standard centerline surveys. Large format field maps were then produced, on which field staff transcribed various field data.
2.2 RIM Adapted SHIM/FIM for Large River Systems
The SHIM data collection, data processing, and data deliverables were based on the mapping standards for SHIM (Mason and Knight, 2001), with consideration that the STHOM is a middle sized river. The Data Dictionary (Version 1.1) is provided in Appendix D. This digital data collection format adapts both SHIM and FIM dictionaries into a common field data collection file, tailored to a spatial biophysical inventory on mid to large size river system like the South Thompson River. The intent of this approach is to utilize a specific mapping protocol that can be for mid to large sized river systems in British Columbia.
2.2.1 Centerline Survey
The centerline of the river channel was mapped along the center of the bankfull (not floodplain) width. While both banks and instream features were digitized using air photo interpretation. Comprehensive data for both the left and right river banks were collected independently of the stream centerline as unique “Right Bank” and “Left Bank” line features (reviewed below in Section 2.3.2).
The river was stratified into a series of successive reaches, each possessing and being characterized by different attributes or biophysical characteristics (i.e., hydraulic class, channel characteristics, substrates composition, and riparian class etc.) (Table 1).
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Table 1. Overview of river centerline data fields collected using the Trimble data dictionary. Reach Length Linear measure along centerline of channel (m) Primary Character: Modified; Natural; Other Channel width Bankfull level (m) Gradient % grade Salmonid Spawning Yes/No; Species Livestock Access Yes/No; Comment Hydraulic Character Cascade; Cascade-Pool; Falls; Pool; Run; Glide; Riffle; Riffle-Pool; Riffle- Run; Slough; Lake; Wetland; Other Channel Pattern Straight; Sinuous; Irregular; Irregular meandering; Regular meanders; Tortuous meanders Bars Side; Diagonal; Mid-channel; Spanning; Braided Islands Occasional; Split; Frequent – Irregular; Frequent – Regular; Anastomosing Substrate Composition % Organic; % Fines; % Gravel; % Cobble; % Boulder; % Bedrock Embeddedness/Compaction Degree of embeddeness of coarse substrates in fines (sand/silt) Boulder; Deep Pool; Instream Vegetation; Large Woody Debris; % Instream Cover Overstream Vegetation Reach Impact Rating See Table 2.
A Level of Impact rating was included in the data dictionary and applied to the centerline reach information (Appendix D). This rating system is intended to provide a more measurable parameter in evaluating river condition and monitoring and evaluating habitat changes on local watercourses and associated riparian and floodplain communities. Individual reach scores were assigned based on the criteria outlined in Table 2. Weighted scores for respective impact ratings were obtained by dividing the cumulative length of reaches receiving the same impact rating by the total river length being evaluated to obtain a fractional abundance (% of river length). This value was then multiplied by the respective Score (0-6) equaling the weighted score. The sum of weighted scores was then divided by the maximum attainable score (6)1 and transformed into a percentage value or river grade. This scoring system precedes the Aquatic Habitat Index and, on its own, is a field measure of river/bank condition.
1 A combined weighted score of 6 would be attained if all reaches were natural with no discernable human disturbance on either the right or left bank. In other words, the river is pristine.
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Table 2. Level of Impact rating criteria for South Thompson River Inventory and Mapping. River Bank Impact Criteria1 Combined River Reach Score Nil-Nil (Nil impacts on both banks) 6 Nil-Low 5 Nil-Mod 4 Nil-High 3 Low-Low 4 Low-Mod 3 Low-High 2 Mod-Mod 2 Mod-High 1 High-High (Impact on both banks is high) 0 1. Numeric Bank Impact Scores: Nil=3;Low=2; Mod=1; High=0
2.2.2 Left and Right Bank Mapping
Conventional SHIM methods describe the right and left bank character and condition within a single stream centerline feature for respective reaches. To better map and evaluate the larger scale represented in the STHOM, the SHIM approach was modified (Appendix D), which adapts the FIM field attributes into the data dictionary. Through this approach, left and right bank lines were logged in the field independently of one another (similar to FIM shoreline mapping) and data fields were populated separate from the Centerline. Individual segments were determined as relatively homogenous sections of shoreline based on vegetation structure, physical character, and general land use. Shoreline sections that displayed a consistent pattern or distribution of different biophysical units/features interspersed with anthropogenic units (e.g., clearings and fields) were also considered as a single segment. An example of this would be through rural areas; where remnant natural pockets along the river bank are interspersed with rural residences and small agricultural clearings. Shoreline segments were determined and assigned independently of river reaches. However, the adjacent river reach was identified in the data for each shoreline segment (e.g., Left Bank Segment 30, River Reach 9).
Large format laminated posters of the River were marked-up to illustrate river and riparian features, attribute lines (e.g., bank armouring) and points (e.g. docks). These features were then digitized in the office to supplement GPS field data. Table 3 summarizes the data fields that were collected for each bank segment.
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Table 3. Overview of data collected for right and left bank segments during the field inventory. Segment Number Reach Number Segment Length Representative Photo Category Menu/Data Fields Primary Shore Type Cliff/Bluff; Rocky Shore; Gravel; Sand; Confluence (alluvial fan); Wetland; Other; Flood Low Bench; Flood Mid Bench; Flood High Bench Shore Modifier Log Yard; Marina small (6-20); Marina large (20+); Railway; Road; None; Other Slope (general slope of shore landward) Bench; Low (0-5%); Moderate (5-20%); Steep (20-60%); Very Steep (60%+) Land Use (observed) Agriculture; Commercial; Conservation; Forestry; Industrial; Institution; Multi Family; Natural Area; Park; Recreation; Rural; Single Family; Urban Park Level of Impact None; Low (<10%); Medium (10-40%); High (>40%) Livestock Access Yes/No Relative Condition %Disturbed; %Natural % Shore Type Distribution %Cliff/Bluff; % Rocky; % Gravel; % Sand; % Confluence; % Wetland; % Other; % Flood Low Bench; % Flood Mid Bench; % Flood High Bench % Landuse Distribution Agriculture; Commercial; Conservation; Forestry; Industrial; Institution; Multi Family; Natural Area; Park; Recreation; Rural; Single Family; Urban Park Modifications % of segment retained/armoured by walls and rip rap Number of Boat launches per segment Docks per segment % of segment with railway influence Boat House per segment % of segment with a road influence Groins per segment Marinas per segment Bank Stability High; Medium; Low; Eroding % Eroding Bank Material Clay; Silt; Sand; Gravel; Cobble; Boulder; Bedrock Comments Provided with various categories listed above
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2.2.3 Feature Mapping
Morphological, habitat, and anthropogenic features were marked with both the GPS and described on field maps and later digitized as point and polygons into the modified STHOM data dictionary. These features, summarized in Table 4, provide a more quantitative measure of relative disturbance/modification, and aquatic habitat quality/complexity (e.g., aerial abundance of spawning substrates/coarse woody debris measure etc.).
Table 4. Overview of watercourse and habitat attributes that were collected using the Data Dictionary developed for this project (Adapted from Module 3, Mason and Knight, 2001). The complete data dictionary can be found in Appendix D. Main Attribute Detailed Feature Collected Type (retaining wall/water withdrawal/bridge/dock etc.) material; Modifications length; photo Culvert Attributes Type-Material; Condition; Barrier; Size; Baffles Obstruction Attributes Type-Material; Barrier; Size; Photo Stream Discharge Attributes Point of Discharge; Type-material; Size Erosion Feature Type of Erosion; severity; exposure; material Fish Habitat Attributes Type of Habitat (Spawning/rearing/cover); Size; Slope; Photo Enhancement Areas Type of Enhancement; Potential or existing enhancement Wildlife Observations Type of Observation; Wildlife species; Photo Wildlife Tree Attributes Type of Tree; Size; Location Near Waterbody Attributes Type of Waterbody (spring/side channel/pond etc.); Size Wetland Attributes (Polygon feature) Wetland Type-Class; Photo Representative Photograph Location Location; Direction
2.2.4 Key Fisheries Zones
Ecoscape incorporated detailed fish habitat use information, contributed by DFO (2015), regarding salmonid spawning locations, known rearing and nursery sites, and key holding areas. GIS shapefiles were digitized, outlining the spatial extents of respective fish habitat use information, and presented in Map Set 2 along with other observed or contributed wildlife information.
2.3 Instream Morphology and Habitat Feature Polygonization
The spatial extents of side channels, backwaters, and associated riverine wetland and floodplain communities were identified and mapped. Relative habitat scores were applied to each type to be used in analysis and habitat index calculations (Section 4.1). The river channel, extending to the outer limits of the mean annual high water level (to include low bench floodplain areas) was estimated using field inventory data and subsequent air photo interpretation. The spatial extents of the channel formed the basis for subsequent stratification of habitat units within (Map Series 1). Habitat units were
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classified based on complex hydraulic and instream habitat feature classes as one of the following in Table 5.
Table 5. Hydraulic and instream habitat feature classes assigned to South Thompson River and associated low flood and wetland polygons BW Backwater CA Cascade CO Confluence FL Low Flood Bench G Glide LK Lake LWD Large Woody Debris P Pool RF Riffle RM Riverine Marsh RN Run SC Side Channel
2.4 Riparian Polygonization
Broad vegetation communities/habitat types were stratified within a 100-m band along the right and left river banks (Map Series 1). Polygons were classified according to Table 6. In addition, site qualifiers (Table 7) were assigned to each polygon to reflect the estimated level of disturbance and habitat quality and condition.
The river channel boundary was established at the estimated mean annual floodplain level to include riparian marshes and low bench floodplain sites. Thus mid bench floodplain ecosystems (i.e., black cottonwood ecosystems) were included in the 100-m riparian band and not factored into the stream channel analysis (Section 4.2).
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Table 6. Broad vegetation communities (Habitat Types) used for classification of stratified polygons occurring along the South Thompson River (100-m band) from Little Shuswap Lake to Kamloops Lake (Adapted from Mackenzie and Moran (2004) and Lloyd et al. (1990)).
BGC Zone/ Site Map Code Description Association Site Series Name Assumed Situation/Comment Variant/ Phase Series Broadleaf At - Snowberry - Kentucky toe slope to depression; deep, medium- Upland broadleaf forest ecosystem above the active B IDFxh2 a95 AS Forest bluegrass textured soil; seepage floodplain predominated by trembling aspen FdPy - Pinegrass - gentle slope; deep, medium- textured 01 DP Feathermoss soils FdPy - Bluebunch significant slope, ; warm aspect; medium 02 WR wheatgrass - Rough fescue textured shallow soils over bedrock FdPy - Bluebunch significant slope, ; warm aspect; deep, IDFxh2 03 PB Upland Coniferous Forest ecosystem above the active Coniferous wheatgrass - Balsamroot medium- textured soils C floodplain. Including high bench site along the South Forest FdPy - Bluebunch gentle slope; deep medium - textured 04 DW Thompson River. wheatgrass - Pinegrass soil gentle slope; deep medium - textured 05 PP FdPy - Pinegrass soil FdPy - Snowberry - gentle lower receiving slope; deep, fine PPxh2 06 SS Saskatoon - textured soil Cultivated CF Cultivated fields (i.e., hayfields, row crops, orchards) Field GC Golf Course Golf Course Fescue - Bluebunch significant slope, cool aspect; deep, BGxh2;IDFxh2a 06;91 FW wheatgrass(Rough fescue) medium- textured soil Bluebunch wheatgrass - Natural grassland ecosystems generally not containing GN Grassland IDFxh2a 92 WN Needle-and-thread grass gentle slope; deep medium- textured shrub or tree strata Balsamroot - Kentucky soils IDFxh2a 94 BK bluegrass Low Flood Beaked sedge;Reed Wm01;RG Low bench ecosystems occur on sites that are flooded for moderate periods (< 40 days) of the growing Bench Canary Grass FL season, conditions that limit the canopy to tall shrubs, especially willows and alders. Annual erosion (G=graminoid; Fl06 Sandbar willow and deposition of sediment generally limit understorey and humus development. S=Shrub) Mid Flood BGxh2 07 Cottonwood – snowberry Middle bench ecosystems occur on sites briefly flooded (10–25 days) during freshet, allowing tree FM CD/Fm01 Bench – Rose - Dogwood growth but limiting tree species to only flood-tolerant broadleaf species such as black cottonwood. Upland Mixed stand Forest. High bench site along the gentle lower toe slope to level; deep, M Mixed Forest PPxh2 07 CW Act - Water birch South Thompson River. Tree canopy mix of cottonwood, medium - textured soils ponderosa pine, and interior Douglas-fir. Although similar to rural, these areas are more devoid of a fragmented tree canopy and are more PA Pasture modified/irrigated grassland ecosystems. Less modified than cultivated fields. BGxh2 03 PT Py - Red three-awn Py - Bluebunch BGxh2;PPxh2 04;03 PW PS Pine Savana wheatgrass Open ponderosa pine canopy grassland dominated ecosystem Py - Bluebunch PPxh2 01 PF wheatgrass - Fescue RL Railway Railway and associated fillslopes, armouring and other modifiers RI River Tributaries
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BGC Zone/ Site Map Code Description Association Site Series Name Assumed Situation/Comment Variant/ Phase Series RZ Road Surface Road Surface Rural areas containing houses, outbuildings, driveways, and landscaping. A native tree canopy may be present but it is perforated by development and the understory plant associations have been partly RU Rural removed. In higher disturbed sites the tree canopy is very limited to absence and natural plant associations sparse to absent. SB Silt bluff/bank Steep, sparsely vegetated silt bank. SH Shrub Persistently disturbed shrub sites that are not included within low flood bench Big sagebrush - Bluebunch BGxh2;PPxh2 01;05 SW;SF wheatgrass Big sage - Needle-and- SS Shrub-steppe BGxh2 05 SN Natural grassland/shrub-steppe ecosystems with >15% cover of big sagebrush thread grass Big sage - Kentucky IDFxh2a 93 SK bluegrass Wm01 Water sedge A marsh is a shallowly flooded mineral wetland dominated by emergent grass-like vegetation. A Wetland/Mars WN Wm02 Beaked Sedge fluctuating water table is typical, with early-season high water tables dropping through the growing h RG Reed canarygrass season. Exposure of the substrate in late season or during dry years is common.
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Table 7. Site qualifiers assigned to each polygon (Table 6) to reflect the estimated level of disturbance and habitat quality and condition. e early successional stage (Structural Stage 2-3) Highly disturbed, fragmented/broken canopy. Analogous to a partly treed rural site. Highly disturbed hd wetland and fragmented by land use and agricultural practices. The ecological function of this feature is severely impaired by human and associated activities. Moderately disturbed treed riparian area. The habitat community structure may be fragmented or md perforated by some land clearing and rural disturbances. Low disturbance, not recently disturbed. Containing natural tree canopy and understory vegetation ld associations. f Narrow riparian fringe generally less than 5-m wide but occasionally up to 10-m. i Island ls Persistent livestock access/disturbance n natural, undisturbed site pa Urban park/Recreational area Russian Olive disclimax riparian fringe – The spread of this invasive species has led to negative impacts on ro mid bench flood ecosystems along the South Thompson River.
2.5 Data Processing and Quality Assurance and Control
The Resource Inventory Committee and SHIM Methodology (Mason and Knight, 2001) provide specific requirements for quality assurance and quality control. These standards, such as GPS settings/precision, logging intervals, and data management and deliverables were followed throughout the field inventory stages of the project.
GPS settings and use were in accordance with Resource Inventory Committee Standards to ensure the collection of spatially accurate data. The coordinate system used was UTM Zone 10 and 11 North, North American Datum 83.
Field data was differentially corrected using base data provided by the Oroville Airport (RKD1), Washington (ITRF00(1997)-DSTHOMed from IGS08 (NEW)) Position: 48°57'51.66889"N, 119°24'46.89431"W, 313.27 m.
Data dictionary tools designed for ARC View 3.x were employed to process the data and to export the data into ESRI shapefiles. Subsequent processing and mapping was completed using ArcGIS 10.x. Processed GPS data (shapefiles) were then converted into geodatabases.
To ensure Quality Assurance and Control the following tasks were followed during completion of this project:
Field data collected was backed up daily onto the local server and field computer at the end of each field day.
All field data collected during the field inventories was post processed by the field inventory biologist, and data manager, Kyle Hawes, R.P.Bio.
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We reviewed each attribute collected during the field survey as part of a quality control / assurance process. The final database will be provided to Fraser Basin Council and project partners at the completion of the project. Corrections and adjustments to the database will be made as necessary.
We integrated this assessment with additional GIS information provided by other parties.
2.6 Photo Log
SHIM/FIM standards require that a detailed photo log accompany and be incorporated into the database. All photos were entered into a log for location and subject reference. In addition, coordinate locations (UTM Zone 11 North (upper STHOM) and 10 North (lower STHOM and THOM to Kamloops Lake), North American datum 83 Canada) were included in the photo data to enable spatial referencing on the ground.
3.0 SOUTH THOMPSON RIVER KEY FISH SPECIES
The South Thompson River flows from Little Shuswap Lake to Kamloops Lake, a distance of approximately 70 km. It supports populations of five of the seven species of Pacific salmon (for spawning and/or migration); pink (Oncorhynchus gorbuscha), Coho (O. kisutch), Sockeye (O. nerka), and Chinook (O. tshawytscha), as well as the non- anadromous forms (freshwater only) Kokanee (O. nerka) and Rainbow Trout (O. mykiss). Other salmonid fish species include the, Rocky Mountain whitefish (Prosopium williamsoni), Bull Trout (Salvelinus confluentus) and Dolly Varden (Salvelinus malma). Non-salmonid fish include suckers (Catastomus spp.), Peamouth Chub (mylocheilus caurinus), sculpins (Cottus spp.), carp (Cyprinus carpio), prickly sculpin (Cottus asper), redside shiner (Richardsonius balteatus), slimy sculpin (Cottus cognatus) and longnose dace (Rhinichthys cataractae). Because of their importance to commercial, recreational and ceremonial purposes the following were selected as key species for matrix development in this study: Kokanee, Sockeye Salmon, Rainbow Trout, Coho Salmon, Chinook Salmon, Pink Salmon, Bull Trout, and Dolly Varden.
3.1 Kokanee
LIFE HISTORY
Kokanee (Oncorhynchus nerka) are considered a keystone species in many large British Columbia lakes. They are most often the major source of forage for other predators such as burbot, Rainbow Trout, lake trout and Bull Trout. Provincially they are third only to Rainbow and cutthroat trout in sport fish catch (Ministry of Water, Land and Air Protection 2003).
Kokanee are a non-migratory form of Sockeye Salmon. They have very similar traits to Sockeye with the one major exception that they spend their entire life in freshwater.
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Both species will normally spend their first year of juvenile rearing in a freshwater lake, in this case Shuswap Lake, but while Sockeye will out-migrate to the ocean after one year, Kokanee remain for 2 or 3 years in the lake before returning to spawn. In British Columbia Kokanee typically reach maturity at the end of their third (age 2+) or fourth (age 3+) summer (McPhail 2007). Kokanee management in the system, and in general in B.C., is the responsibility of the provincial Ministry of Forests, Lands and Natural Resource Operations, Fish and Wildlife Branch (formerly B.C. Ministry of Environment).
In 2001, a four year investigation into the status of Kokanee populations in the South Thompson-Shuswap watersheds was initiated by the Ministry of Water, Land and Air protection and completed by Redfish Consulting. The results of this study were particularly helpful in the preparation of this species account.
Traditionally most fishery managers believed that Kokanee were quite abundant, requiring little attention. Today, however, that perception has changed and the prevailing view is that this important species appears to be in trouble in many interior lakes. Reasons for this decline are believed to be habitat related and are focused on spawning habitat deficiencies (Redfish Consulting 2005).
Kokanee populations in most of the Shuswap Lake system, are not well understood. There appears to be a critical absence of information on habitat use, angler harvest and escapement numbers over time (Ministry of Forests, Lands and Natural Resource Operations files 2011).
REPRODUCTION
Fisheries personnel use various methods to enumerate these spawning runs including helicopter and drift boat surveys. Frequencies of counts and survey dates have varied considerably over the years which have likely contributed in some part to large variations in annual counts.
AGE GROWTH AND MATURITY
Upon emergence, Kokanee usually migrate to a nursery lake before starting to feed. This downstream migration occurs at night with peak migration between dusk and midnight (Lorz and Northcote 1965; Webster, J. 2007). The fry are negatively phototactic (avoid light) and, if the migration takes more than one night, they shelter during the day under rocks and organic debris (McPhail 2007).
On lake entry the, fry of some Kokanee populations immediately move offshore and begin vertical migrations in search of zooplankters, their preferred feed. Other populations, however, remain inshore and forage in the littoral zone for variable amounts of time. These differences in fry behavior probably are related to food availability, temperature and predation risk (McPhail 2007).
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HABITAT INDEX MATRIX
The Habitat Index Matrices developed for this study accordingly rates Kokanee adult stages as high for spawning gravel requirements but low in requirements for cover and rearing. During the spawning process they show little concern about hiding and cover as they go about the task of building redds and laying and fertilizing eggs. Gravel conditions and flows are very important during the egg to fry incubation stage. The emergent fry may have some limited requirements for cover or habitat complexity as they attempt to swim downstream under cover of darkness as quickly as possible. As McPhail (2007) explains, if the journey takes more than one night they will seek cover of organic debris or boulders along the way then resume their swim after dark.
3.2 Sockeye Salmon
LIFE HISTORY
Sockeye Salmon (Oncorhynchus nerka) are the third most abundant of seven species of Pacific salmon (Groot and Margolis1991). In British Columbia Sockeye tend to have similar life history traits as Kokanee with a few major exceptions. As with Kokanee, Sockeye fry normally will spend their first year in a freshwater lake – in this case Shuswap Lake – then will begin the long journey to the Pacific Ocean. This anadromous tendency allows them to become much larger than Kokanee as there is more abundance of feed in the north Pacific than in interior lakes. Sockeye spend from one to four years in the ocean before returning to fresh water to spawn. Sockeye management in the province is the responsibility of the Federal Department of Fisheries and Oceans.
REPRODUCTION
Sockeye spawn in the fall, usually when water temperatures drop below 120C. Historically there have been both early (spawning in early to mid-September) and late Sockeye runs (late October) in the South Thompson River (DFO 1997). As with Kokanee, Sockeye will form dense aggregations on spawning grounds. They will normally choose larger spawning substrates than Kokanee which tends to cause separation in spawning locations. Like other Pacific salmon Sockeye will defend their redds until too weak to maintain position and die after spawning.
Even in larger rivers, Sockeye tend to spawn in shallow riffle areas (Groot and Margolis 1991). There are exceptions, however, and it is clear that they have the ability to detect and utilize groundwater upwelling areas. Fecundity varies from about 2,000 to 4,000 eggs related to female size (Harris 1986 as discussed in Groot and Margolis 1991). Incubation times vary related to water temperatures. Fry typically emerge from late March to late May with peak emergence occurring in early May (Stewart et al. 1989 and Whelan et al. 1982 in DFO 1997). It is known, however, that these fry need to move downstream quickly to lakes where they begin feeding or they will not survive. They move downstream under cover of darkness to avoid predators. Fry generally rear and overwinter in the lake environment and outmigrate in June and early July. Large numbers of yearlings have been observed in the lower Fraser in September which
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suggest that South Thompson Shuswap Sockeye smolts enter the Strait of Georgia later than other Fraser stocks (Healy 1980 in DFO 1997).
Sockeye cycle on a four year rotation and can vary considerably in numbers from year to year.
Sockeye tend to spawn in areas above nursery lakes or in some cases just below (McPhail 2007).
AGE, GROWTH AND MATURITY
As with Kokanee, Sockeye fry once emerged from the gravel normally will migrate downstream under cover of darkness to their nursery lake for a period of rearing, usually lasting one year. J. D. McPhail (2005) suggests that the migrating fry will look for cover areas in organic debris or boulder substrate if the migration cannot occur in one night. They will then resume their downstream travel once darkness returns.
HABITAT INDEX MATRIX
The Habitat Index Matrices developed for this study tend to be very similar for Sockeye as they are for Kokanee. Spawning gravel attributes score very high for adult spawning and juvenile incubation while rearing and cover attributes score low due to their tendency to spend most of their juvenile stage rearing in Shuswap Lake and then the remainder of their adult life rearing in the Pacific Ocean.
3.3 Rainbow Trout
LIFE HISTORY
Rainbow Trout (Oncorhynchus mykiss) are an important game fish that reside in the South Thompson River. They are considered the number one target for anglers in the British Columbia interior. It is apparent that there are two forms of trout in the system; a resident population that lives its entire life cycle in the river and adjoining tributaries, and an adfluvial form that spends the majority of its life in large lakes but migrates to rivers and streams to spawn or feed (Ministry of Environment files, Okanagan Region). There are many similarities between these two groups as far as spawning requirements, early rearing and adult life forms and accordingly these life forms will be grouped in this discussion.
Rainbow Trout management in B.C. is the responsibility of the provincial Ministry of Forests, Lands and Natural Resource Operations, Fish and Wildlife Branch. In British Columbia, Rainbow Trout occur both as freshwater resident and anadromous (Steelhead) populations.
Rainbow Trout in the system, both in lake forms and resident river populations are heavily sought after by anglers and tend to be easily overfished. For this reason, conservative, ‘catch and release’ angling regulations were introduced by MOE fisheries
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managers in the mid to late 1990’s (Jantz, memo to file, MOE). According to local opinions these measures appear to have been successful in conserving adult trout in the system and increasing angler catch success (pers. comm. Neil Brooks, Kingfisher Community Hatchery).
REPRODUCTION
Rainbow Trout are spring spawners and migrations into spawning streams are triggered by rising water temps (above 50C.) and rising water levels (Hartman 1966 in McPhail 2007). The South Thompson River is normally in freshet at this time with high flows and turbid waters. These conditions present a challenge for fisheries managers to monitor their activities and population strengths.
A search of the Ministry of Environment Habitat Wizard reveals that Rainbow Trout have been found in many of the tributary streams of the South Thompson River (along with Coho, Chinook and Sockeye). These streams are critically important for the nursery phase of Rainbow Trout juvenile rearing. Maturing adults will migrate into these streams during freshet flows (April and May) and will spawn on the receding flows following. Unlike Pacific salmon, Rainbow Trout adults can survive spawning and it has been determined that about 10% will live on to spawn a second time (McPhail 2007).
Rainbow Trout juveniles rearing in small streams tend to be highly connected with riffles, runs and large woody debris. These areas provide the best habitat for cover and feed consisting of small aquatic insects. They need to select streams that provide suitable habitat to survive summer and winter extremes for up to three years. Low summer flows, caused by agricultural irrigation diversions can have significant impact on smaller streams. Rainbow Trout juveniles can also be displaced by other fish, such as Coho, which tend to compete heavily for prime feeding areas as they have similar diets (Griffith 1986).
It is believed that many of these developing juveniles will eventually move from nursery tributary streams down to the South Thompson River or Shuswap Lake. In rivers, Rainbow Trout will normally establish territories in shallow water along stream margins (Slaney and Northcote 1974). During their adult phase in streams and rivers they occupy riffles, runs, glides and pools and tend to occur in deeper and faster water than juveniles (McPhail 2007). As they grow, terrestrial insects are added to their diet and so riparian areas along river margins become increasingly important to them (McPhail 2007).
AGE, GROWTH AND MATURITY
Some Rainbow Trout will live their entire life cycle in small streams or rivers (resident) while others are of an adfluvial nature and will move down to large lakes. Information is limited on downstream migration traits but it is believed that they travel in the freshet and utilize cover habitats along the way to escape their predators (McPhail 2007). Adfluvial trout can live up to 8 years before maturing with the norm being 5 or
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6 (MOE Okanagan Region files). Their biggest obstacle in lakes is anglers who target them extensively. Rainbows can tolerate temperatures up to 270C but anything higher can be lethal (Lee and Rinne 1980 in McPhail 2007). In adfluvial populations, Rainbow Trout rely heavily on Kokanee and Sockeye forage once they move to large lake habits.
HABITAT INDEX MATRIX
The Habitat Index Matrices developed for this study indicate that Rainbow Trout depend heavily on pools, runs, riffles, boulder areas and cover afforded by riparian vegetation or in-stream woody debris. Log jams associated with pools are also used extensively for feeding and hiding. Tributary stream confluences are important as are small, stable streams which provide rearing habitat for juveniles and resident populations. Of the five species of fish, discussed in these accounts for the Lower South Thompson River, Rainbow Trout are likely the most sensitive to habitat changes because they spend so much of their life cycle in these zones.
3.4 Coho Salmon
LIFE HISTORY
Coho Salmon (Onchorynchus kisutch) are an important species and range through hundreds of coastal and interior streams in British Columbia. Interior Fraser River Coho Salmon are genetically unique and can be distinguished from lower Fraser River Coho. Studies of the genetic structure of Interior Fraser Coho indicate that there are five distinct populations. Three are within the South Thompson (North South Thompson, South Thompson, and Lower South Thompson regions) and two are within the Fraser (the area between the Fraser Canyon and the South Thompson-Fraser confluence and the Fraser River and tributaries above the South Thompson-Fraser confluence) (Interior Fraser Coho Recovery Team 2006). South Thompson populations are further divided into sub-populations which are comprised of: the Adams River; Shuswap Lake and tributaries; and the Middle and Lower Shuswap River. Coho in the province is managed federally by Fisheries and Oceans Canada.
Coho populations in the interior of British Columbia face many threats and challenges. So much so that in 2002 the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) listed them as endangered. COSEWIC was concerned that if Interior Fraser Coho distribution became too fragmented, genetic exchange within the populations may be insufficient to ensure long-term survival (COSEWIC 2002).
Over the period of record (1975-2003) the 3-year average escapement for Interior Fraser Coho peaked in the mid-1980’s at over 70,000 fish, and declined to a running average of less than 18,000 individuals in the late 1990’s. Similar trends are observed in total abundance (i.e. catch plus escapement), which declined from over 200,000 in the late 1970’s and 1980’s to less than 30,000 in recent years (Interior Fraser Coho Recovery Team. 2006).
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On average, North and South Thompson Coho Salmon declined in numbers by approximately 60% during the 10-year period from 1990-2000. There were four years (1991, 1995, 1997, and 1998) when productivity was so low that some of the populations may not have been able to maintain replacement spawner numbers, even with a zero exploitation rate (Irvine et al 1999).
Natural spawning is responsible for producing most of the Coho Salmon escaping to the Interior Fraser River, except for the Lower South Thompson population where hatchery fish outnumber those produced from fish spawning in natural stream areas. There is no evidence that the overall distribution of Coho Salmon within the Interior Fraser River watershed has changed, although spawners were observed in fewer streams as spawning abundance declined.
The South Thompson River is considered a major Coho producer (DFO 1997). A decline in Coho escapement rates in the South Thompson Shuswap Habitat Management Area has been attributed to excessive exploitation rates, low marine survival and degradation of freshwater habitat. Historically Coho stocks in the South Thompson River were supplemented by a hatchery which was closed in 1994.
Population trends from 1975 to 2003 for the South Thompson Unit peaked at 25209 with the lowest escapement at 1799 for years 1988 and 1996 respectively.
Interior Fraser Coho require adequate freshwater and marine habitats to survive and reproduce. These fish spawn in freshwater and the juveniles normally spend one full year in freshwater before migrating to the sea as smolts. The distribution of spawning habitat for Coho Salmon is usually clumped within watersheds, often at the heads of riffles in small streams and in side-channels of larger streams. However, Interior Fraser Coho are commonly observed spawning in mainstems of larger rivers during periods of low flow, presumably when tributary and side-channel habitats are less accessible.
The outlook for Interior Fraser Coho is highly uncertain and depends on the magnitude of negative impacts due to fishing, habitat perturbations, and climate related changes in survival. A return to higher survivals, combined with continued low exploitation rates, conservation of existing habitat, and habitat restoration, could produce increases in escapements and subsequently population recovery. However, if survival rates are at low levels, such as those recorded in 1998, spawner numbers will continue to decrease, possibly resulting in the eventual extinction of Interior Fraser Coho. Since there is no predictor of future survival rates, a cautious approach to harvest and habitat management will be required to ensure the long-term viability of Interior Fraser Coho (Interior Fraser Coho Recovery Team. 2006).
Between 1971 and 1995 the South Thompson River had the highest Coho escapements of any of the rivers in the South Thompson Shuswap Habitat Management area where enumeration was completed. Coho escapements between 1989 and 1995 declined in the South Thompson River. Declines are attributed to poor marine survival, exploitation rates and impacts to freshwater habitat (DFO 1997).
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REPRODUCTION
The timing of river entry and spawning varies with latitude and distance from the ocean. South Thompson Coho stocks return at age 3 to the lower Fraser between late August and October and spawning occurs from mid-October to December. Spawning Coho are the most secretive of Pacific salmon and most reproduction behavior occurs at night.
Coho have similar tendencies to Rainbow Trout in their selection of rearing habitat (Griffith 1986). They prefer sites with sub-gravel flow as is found in tail-outs of pools immediately above riffles or upwelling sites. They prefer smaller tributary and headwater streams often not much more than 1m in width. Eggs incubate over winter and hatch in the spring. Incubation timing is dependent on water temperatures as with all other salmonids in the Shuswap system.
Fry emerge from late March through late May and early June (DFO 1997). Several of the tributaries of the South Thompson River, including the Perry River, Crazy Creek and South Pass Creek have obstructions to upstream migration and only low numbers of Coho spawn in their lower reaches (DFO 1990 in DFO 1997). Rearing in Shuswap Lake occurs adjacent to spawning streams like the South Thompson River and along migration routes (Russell et al. 1980 in DFO 1997). Juveniles spend one year in freshwater, rearing initially in their natal streams and subsequently moving downstream to rear and overwinter in rivers and lakes (DFO 1997). Overwintering also occurs in the South Thompson River mainstem. Juvenile Coho move offshore in mid-July and rear in the pelagic zone of Shuswap Lake until migration the following spring. Migration likely occurs between mid-April and early May.
AGE, GROWTH AND MATURITY
In British Columbia, Coho fry usually reach 80-90mm in their first year (Sandercock 1991 in McPhail 2007). Coho fry in interior streams normally spend 1 to 2 years in nursery streams before out-migrating to the Pacific Ocean. They are primarily drift- feeders and take the drifting stages of aquatic insects from the water column or terrestrial insects from the surface. Coho prefer pools and backwater areas. They will aggregate in backwaters, side-channels and quiet embayments along stream margins. They will eventually emigrate to larger rivers and will search out off-channel overwintering areas such as beaver ponds and flooded wetlands (Peterson 1982 in McPhail 1997). In winter they will seek cover under woody debris, undercut banks, cobbles and move deeply into root wads.
HABITAT INDEX MATRIX
The Habitat Index Matrices indicate that Coho adults require cascade areas, confluence areas, pools, riffles, runs, cover and access to small streams in upper watersheds. They will hide under cut banks and root wads and will search for suitable gravel in upwelling areas and tail-outs of pools.
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Coho juveniles depend heavily on pools, backwaters, in-stream vegetation areas, low and middle flood benches, marsh areas, side channels, cobble areas and large woody debris. Tributary stream confluences are important as are small, stable streams which provide rearing habitat. These streams will support Coho through their incubation period and their first year of rearing. Adequate year-round flows and cool temperatures afforded by well-developed riparian zones are important. Some fry will move to the main rivers where they will seek back-waters, flood benches and beaver dams.
Coho in south central B.C. will usually rear for 1 year in freshwater and then begin their migration to the ocean. They will spend 18 months at sea before returning as adults to spawn. As with other Pacific salmon (except for Steelhead and coastal cutthroat) they die after spawning.
3.5 Chinook Salmon
In British Columbia Chinook salmon spawn in over 250 rivers and streams (McPhail 2007). Within the Fraser River system, there are seven genetically recognizable geographic groupings: an upper, middle, and lower Fraser group; a northern, southern and lower South Thompson group; and the Birkenhead River population (Beacham et al. in McPhail 2007). Chinook are the largest of seven species of Pacific salmon and have the widest distribution. They have sustained First Nations for thousands of years, provide important recreational and commercial harvesting opportunities, and were an important part of the colonization of British Columbia.
Chinook stocks exhibit both ocean type and stream type life history patterns. Ocean type Chinook rear in freshwater for several months and migrate to the ocean in the first fall while stream type Chinook rear in freshwater for one year before migrating to the ocean (Fraser et al. 1982 in DFO 1997). South Thompson River Chinook are predominantly stream type.
REPRODUCTION
South Thompson River Chinook runs typically return to the lower Fraser by mid-July with peak spawning occurring from late August to November. Since South Thompson River Chinook are spring run, peak spawning typically occurs earlier during this period, around mid-September (DFO 1997). Chinook in the South Thompson River spawn below Griffin Lake.
Chinook females choose the spawning site and appear to prefer sites with subgravel flow (eg. In the tail-outs of pools immediately above riffles or in upwelling sites) (McPhail 2007). Chinook eggs are the largest of the species of Pacific salmon and require higher rates of flow and oxygen than other species. As with most other species of Pacific salmon, adults will die after spawning.
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AGE, GROWTH AND MATURITY
Chinook eggs incubate through the winter period and fry emerge in the early spring. As with the other species discussed earlier, their incubation period varies with water temperatures. Once emerged the diet of fry includes adult chironomids as well as chironomid larvae and pupae, terrestrial insects taken from the surface, and nymphs of larvae of aquatic insects (McPhail 2007). Upon emergence, Chinook fry are often moved downstream by flows from areas where they incubated (Groot and Margolis 1991). Their habitat range is often keyed to flow velocities rather than habitat types. They range widely in habitat use but generally will occupy bouldery areas in faster waters.
Downstream timing appears to be correlated strongly with size (Groot and Margolis 1991).They will eventually move out to the Pacific and return 5 years later to spawn as adults.
Juvenile rearing is not well understood but both natal streams and lakes are utilized. Lakes and larger natal streams provide overwintering habitat for stream type Chinook (DFO 1997). Ocean type Chinook likely realize a greater benefit from the productivity of larger lakes; as opposed to stream type Chinook which typically overwinter in freshwater to be able to reach a sufficient size to allow for salt water adaptation (DFO 1997).
HABITAT INDEX MATRIX
Chinook adults are heavily dependent on deep pools where they may hold for up to 8 weeks before moving out to spawning grounds. Their spawning areas must have larger diameter clean gravels which will afford adequate percolation of flows and oxygen to meet incubation requirements. They are particularly sensitive to movements of silt or reductions in flow during the incubation period.
3.6 Pink Salmon
LIFE HISTORY
Pink Salmon are not as adept as other pacific salmon at negotiating barriers and typically spawn closer to the ocean than these other species (McPhail 2007). Pinks mature at two years and southern populations of Pink Salmon (Oncorhynchus gorbuscha) typically spawn September to October. A three year life cycle is rare. The population of Pink Salmon that would use the South Thompson River is likely limited, although redds were documented during the 2015 inventory in less turbid South Thompson waters proximal to the confluence with the North Thompson River.
REPRODUCTION
Spawning typically occurs in September and October. In the Fraser system the spawning run has early and late segments (McPhail 2007). Female Pink Salmon prefer sites with clean coarse gravel and subgravel flow. Sites are typically shallow riffles or
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channels 20 – 100 cm deep with current. Some streams have both early and late spawning runs (McPhail 2007) and some stocks appear to be adapted to different temperature regimes.
AGE, GROWTH AND MATURITY
Eggs incubate in gravel over winter, hatch in about 1.5 to 3 months and emerge from gravel about 3 to 5 months after hatching. Once they begin swimming, fry quickly migrate downstream (McPhail 2007). Fry migrate to the ocean as soon as they fill their swimbladders (McPhail 2007).
HABITAT INDEX MATRIX
Medium sized gravel areas with sub-gravel flow are the areas that are important to Pink Salmon for spawning.
3.7 Bull Trout
LIFE HISTORY
Bull Trout (Salvelinus confluentus) have a highly variable life history. There are three life history forms in BC: fluvial, adfluvial and resident. The fluvial form spends its entire life in flowing water but often makes extensive migrations within large river systems (McPhail 2007).
REPRODUCTION
Timing of spawning migrations depends on a number of factors such as water temperature, habitat, genetic stock and possibly amount of daylight (MWLAP 2004). They spawn between mid-August and late October (MWLAP 2004) with resident populations tending to migrate shorter distances to spawning grounds. Migratory or adfluvial populations can have a much larger home range and migratory Bull Trout may travel up to or over 250 km (MWLAP 2004). The temperature below which Bull Trout begin spawning activity appears to be 9⁰C (MWLAP 2004). Bull Trout spawn in flowing water in habitat similar to other salmonids, often in runs or glides in larger river or in pockets of suitable gravel in smaller streams (McPhail 2007). They show a preference for gravel and cobble sections ins smaller, lower order rivers and streams (MWLAP 2004). Size of the redd and size of gravel at the spawning site depends on female size (i.e. larger females spawn in larger gravel).
AGE, GROWTH AND MATURITY
Bull Trout fry tend to stay near the substrate to avoid being swept downstream (Ford et al. 1995 in MWLAP 2004). Juvenile trout feed on aquatic insects. Adfluvial trout are typically piscivorous and typically tend to grow larger than fluvial populations (MWLAP 2004). Bull Trout reach maturity most often at 5 to 7 years but the range is 3
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to 8 years. Juvenile fish (fly to 3+) move from streams to lakes or reservoirs throughout the summer months (McPhail and Murray 1979 in MWLAP 2004).
HABITAT INDEX MATRIX
Mature forest capable of producing large woody debris is typically more important to Bull Trout than younger structural stages. These forests typically trap and store more sediment and provide more nutrients and fish habitat structure than younger forests (MWLAP 2004). Bull Trout are dependent upon cover, usually in the form of deep pools, woody debris jams and undercut banks (MWLAP 2004). Factors that are often associated with Bull Trout distribution and abundance include channel and hydraulic stability, substrate, cover, temperature and the presence of migration corridors (MWLAP 2004). The influence and importance of these factors varies bases on life history (resident, adfluvial or anadromous) and life history stage (MWLAP 2004).
3.8 Dolly Varden
Life History
Dolly Varden (Salvelinus malma) are primarily a coastal species, however, there have reportedly been transferred historically from coastal drainages into the upper Fraser (McPhail 2007). There are three forms of Dolly Varden in BC (stream resident, anadromous and adfluvial [lake dweller that spawns in streams]) and the population in the South Thompson River is likely resident.
Reproduction
Dolly Varden spawn in the fall and stream residents usually spawn locally (McPhail 2007). The female typically digs a redd in gravel; the size of gravel and the associated redd depends upon the size of the female. Females in headwater populations typically spawn at a smaller size.
AGE, GROWTH AND MATURITY
Dolly Varden eggs overwinter in gravel and hatch in about 3 months (McPhail 2007). Fry in other headwater systems emerge in early June. Most Dolly Varden reach maturity at the end of their fifth growing season. Stream residents feed on the nymphs and larvae of aquatic insects; as a result feeding during the day occurs close to the bottom of the channel (McPhail 2007).
HABITAT INDEX MATRIX
Dolly Varden utilize gravel for spawning similar to other salmonids. There is some evidence that in areas of contact between Bull Trout and Dolly Varden, the latter are more likely to use small stream habitat (McPhail 2007). Adult Dolly Varden often use similar habitat as juvenile Bull Trout including main and side channel pools and riffles (McPhail 2007). Juveniles are associated with shallow (<0.5 m deep), slow (<0.10 m/s)
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runs and pools as well as side channels. For cover they utilize large rocks, woody debris, root wads and undercut banks (McPhail 2007). They overwinter in streams associated with cover (MWLAP 2004). Young-of-the-year are denser than water and are primarily associated with shallow areas and are found around coarse gravel and cobble interspersed with boulders. They seek shelter under rocks, logs and undercut banks. Fry will shift to deeper water as they grow (Dolloff and Reeves 1990 in McPhail 2007) and in winter in river systems subject to freezing. Adults will often carry out extensive downstream migration to overwintering habitat (MWLAP 2004).
4.0 AQUATIC HABITAT INDEX
AHI scores for each reach of the river channel and left and right bank segments are analogous to the current productivity, which is defined as the sum of relative habitat values for all subareas occurring within a defined area (i.e., river channel extents of a respective reach) (Minns 1997). The AHI is a categorical scale of relative habitat value that ranks the river channel and bank segments in a range between Very High and Very Low. Our approach to development of the index incorporated the following components:
1. Utilization of all existing data that occurs in a spatial GIS format to develop the index.
2. Species Accounts (Section 3), developed to inform life history scores for discrete instream habitat units/features for key species of the South Thompson River.
3. The AHI was developed and calibrated using professional opinion similar to other habitat indices that have been developed for lake systems. Criteria were reviewed for relevancy and weighted appropriately (i.e., representative of the contribution to overall habitat sensitivity), and the index was developed in such a way that new data layers may be added in the future.
The data previously collected for this project involved numerous spatial data layers and is substantially more complicated to develop than an AHI developed for a lake ecosystem. The dynamic nature of riverine ecosystems required that four separate layers of data be collected as part of the inventory phase. One layer of data was attributed to the primary character of the river, one layer was used to describe the right bank, one layer was used to describe the left bank, and one layer was used to describe the mapped extent of salmonid spawning utilization.
4.1 Instream Polygon Scoring Matrix
Habitat unit classes (Section 3.1) were assigned a relative habitat value for each key fish life history stage/habitat quality categories. The relative productivity value was defined for each habitat unit as the sum of all production scores accrued by each of the fish species during the time they spend any part of their life history in that area (e.g.,
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for spawning, rearing, and feeding) or accrued elsewhere as a result of a strict habitat requirement to use that area of habitat (e.g., for staging, migration, or cover).
Habitat unit: Fish life history and habitat requirement matrices were developed to determine the relative habitat value for each habitat unit. Life history stages considered were:
Spawning Rearing General Living/Feeding
Habitat Requirement categories included:
Substrate composition Cover (habitat complexity)
Life history accounts informed the relative values assigned each habitat unit for each species and life history stage. The relative habitat unit values are presented in the following matrices (Tables 6-9). A 3-class score was assigned to each matrix cell; where 1 = low value, 2 = moderate value, and 3 = High value. The sum of species scores for each habitat unit were then transformed to a relative habitat value, which was calculated as the habitat unit score / maximum habitat unit score.
Table 8. Fisheries relative habitat values (RHV) and weighted scores for aquatic and riparian habitat features.
Rearing General Living Cover Habitat Variable Code RHV Wt. Score RHV Wt. Score RHV Wt. Score Backwater BW 1.00 28.75 0.23 1.31 0.20 3.45 Confluence CO 0.72 20.76 0.91 5.23 0.83 14.38 Low Flood Bench (graminoid) FL 0.57 16.25 0.11 0.65 0.08 1.44 Low Flood Bench (shrub-willow) FL 0.35 10.00 0.11 0.65 0.08 1.44 Mid Flood Bench FM 0.11 3.19 0.07 0.39 0.05 0.86 Glide G 0.44 12.78 0.36 2.09 0.27 4.60 Lake LK 0.44 12.78 0.68 3.92 0.72 12.36 Large Woody Debris LWD 1.00 28.75 0.91 5.23 0.98 16.96 Mixed Forest M 0.11 3.19 0.07 0.39 0.07 1.15 Pool P 1.00 28.75 1.00 5.75 1.00 17.25 Riffle RF 0.72 20.76 0.82 4.70 0.67 11.50 Riverine Marsh RM 1.00 28.75 0.16 0.91 0.15 2.59 Run RN 0.72 20.76 0.80 4.57 0.57 9.78 Side Channel SC 0.89 25.56 0.84 4.84 0.70 12.08
Table 9. Weighted scores for mapped salmonid holding areas (DFO 2015). Species Weighted Score Chinook 11.5
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Table 10. Relative value and weighted scores for mapped salmonid (Chinook, Sockeye) spawning areas and use intensity (DFO 2015). Assigned values are applied to the matrix based on the relative abundance spawning area polygons attribute to the total instream reach area. Spawning and intensity Weighted Score Relative Value Very High 11.5 1 High 9.2 0.8 Moderate - High 8.05 0.7 Moderate 5.75 0.5 Low - Moderate 3.45 0.3 Low 2.3 0.2 Unknown 1.15 0.1
Table 11. Relative value and weighted scores for mapped instream substrate composition. Substrate Class Relative Value Weighted Score Organic 0.3 5.175 Fines (silt/sand) 0.2 3.45 Gravel 1 17.25 Cobble 0.75 12.9375 Boulder 0.5 8.625 Bedrock 0.1 1.725
Figure 1. Relative weighting of life history and habitat attributes for instream AHI scores.
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4.2 Riparian Polygon Scoring Matrix
Relative habitat values were assigned to riparian polygons (delineated within the 100- m riparian band) based the sum of values of four categories: Wildlife habitat rating; biodiversity rating; nutrient value/leaf and litter fall; and large woody debris recruitment (Table 12). The sum of relative habitat unit scores were then added to the other parameters of the bank AHI system relating to the current level of impact, degree of bank modifications, and current severity of erosion (caused by human activities).
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Table 12. Ecological category: riparian habitat unit rating matrix (relative habitat value). Habitat Type Code Qualifier Wildlife Rating LWD Biodiversity Rating Nutrients ld 0.7 0.4 0.7 0.8 Broadleaf Forest B md 0.6 0.4 0.5 0.6 n 0.8 1 0.8 0.9 Backwater BW 0.7 0 0.5 0 i 0.6 0.8 0.6 0.6 ld 0.5 0.8 0.5 0.6 Coniferous Forest C md 0.5 0.6 0.4 0.5 n 0.7 0.8 0.6 0.6 Cultivated Field CF 0.1 0 0.1 0.1 Golf Course GC 0.1 0 0.1 0.1 hd 0.1 0 0 0 ld 0.6 0 0.4 0.2 Grassland GN md 0.5 0 0.3 0.1 n 0.6 0 0.4 0.2 ld 0.7 0 0.7 0.3 Low Flood Bench FL n 0.9 0 0.9 0.4 hd 0.4 0.4 0.5 0.4 ld 0.8 1 0.8 0.9 Mid Flood Bench FM md 0.6 0.8 0.6 0.7 n 1 1 1 1 Flood Bench – Russian Olive ro 0.4 0.1 0.2 0.3 e 0.3 0 0.2 0.2 f 0.3 0.6 0.4 0.4 hd 0.3 0.4 0.3 0.4 Mixed Forest M ld 0.7 0.8 0.8 0.4 md 0.6 0.7 0.6 0.6 n 0.9 1 1 0.4 r 0.9 1 1 0.2 Pasture PA 0.2 0 0.2 0.1 Pine Savana PS n 0.7 0.6 0.5 0.4 Railway RL 0 0 0 0 River RI 0.8 0 0.8 0 Road RZ 0 0 0 0 hd 0 0 0 0.1 Rural RU ld 0.4 0.4 0.4 0.4 md 0.3 0.2 0.2 0.3 Silt Bluff SB 0.2 0 0.2 0.1 Side Channel SC 0.8 0 0.7 0 hd 0.4 0 0.4 0.1 ld 0.7 0 0.6 0.1 Shrub-Steppe SS md 0.6 0 0.5 0.1 n 0.8 0 0.7 0.1 hd 0.6 0 0.5 0.1 ld 0.8 0 0.8 0.4 Wetland WN md 0.6 0 0.6 0.2 n 1 0 1 0.4
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4.3 AHI Logic, Calibration, and Ranking
As part of the index development for the South Thompson River RIM, index development and calibration involved multiple iterations - assigning different weights to each of the parameters within the various habitat units, life history and ecological matrices. Following each iteration, the resultant sensitivity outputs were reviewed by fisheries biologists both on the project team and from DFO. Calibration of the index was ultimately finalized using professional judgment.
The AHI provides a categorical scale of relative habitat value that ranks the centerline and shoreline segments in a range between Very High and Very Low sensitivity. The index is relative, because it only assesses the sensitivity of one shoreline area relative to another within the extents of the river being examined. Thus index scores and rankings developed for the Lower Shuswap River may not be directly transferable to the South Thompson River or other river systems without re-calibration. The following provides a definition for each AHI ranking:
Very High – Reaches/Segments ranked as Very High are considered integral to the maintenance of fish and wildlife species and generally contain important natural riparian and floodplain areas, complex mosaics of habitat units supporting high biodiversity and productivity values, and high value/use salmonid spawning, rearing, and general living habitats. These areas should be considered the highest priority for conservation and protection.
High - Reaches/Segments ranked as High are considered to be very important to the maintenance of fish and wildlife species along and within the river and areas can be ranked as High for a variety of reasons. These areas should be considered a priority for maintaining current conditions and a high prioritization for conservation should be given to these areas.
Moderate - Reaches/Segments ranked as Moderate are areas that are common along the river, and have likely experienced some habitat alteration. These areas may contain important habitat areas, such as shore holding areas (deep pools), but these areas are generally considered more appropriate for development. Because areas of high habitat value may be present, caution should be taken when considering changes in land use to avoid unnecessary harm or degradation to existing habitat values.
Low – Reaches/Segments that are generally highly modified. These areas have been impaired through land development activities. A common symptom along the river is high bank instability and bank erosion exacerbated by the removal/absence of riparian vegetation. Development within these areas should be carried out in a similar fashion as Moderate shoreline areas. However, restoration objectives should be set higher in these areas during redevelopment.
Very Low – Segments that are extremely modified and not adjacent to any known important habitat characteristics.
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After reviewing the distribution of the data from the iterations, logical breaks in the scores were used to determine the AHI rankings (discussed above). The breaks created reflect the clustering of scores based upon the output of the results, which somewhat mimic a normal distribution (although an analysis of data distribution was not conducted).
4.3.1 Centerline – Instream Zone AHI Logic
The AHI for each channel reach was calculated as the sum of life history scores for each reach. Table 13 presents the categories, relative category weightings, and logic for the Centerline AHI scoring.
The centerline AHI scores for respective reaches (AHIreach) was calculated using the following,
퐴ℎ 퐴푠푝 퐴ℎ표푙푑 퐴퐻퐼푟푒푎푐ℎ = ∑ [ × 푊ℎ] + ∑ [ × 푊푠푝] + ∑[푃푠푢푏 × 푊푠푢푏] + ∑ [ × 푊ℎ표푙푑] 퐴푡 퐴푡 퐴푡
(1)
:where A represents the area of a described river feature (such as h is habitat, sp is spawning, and hold is holding), P represents a percentage of the area, At represents the total area of the river channel contained with the subject reach, and W represents the relative weighting given to the described river feature (Tables 8-11).
Table 13. The parameters and logic for the Centerline of the South Thompson River Category Criteria Category Weighting Logic Instream Habitat unit and Hydraulic General Living % Area * Category Score Class polygons 5.75 (5%) Instream Habitat unit and Hydraulic Rearing % Area * Category Score Class polygons 28.5 (25%) Chinook Mapped polygons % Area * Category Score Holding 11.5 (10%) High 11.5 Moderate - High 9.2 Spawning1 Moderate 5.75 % total spawning area * Category 34.5 (30%) Low - Moderate 3.45 Score scores combined for Chinook, and Sockeye Low 2.3 Unknown 1.15 % composition estimated during Substrates % Area * Category Score field inventory 17.25 (15%) Instream Habitat unit and Hydraulic Cover Class polygons 17.25 (15%) % Area * Category Score 1. For the AHI spawning polygons were split according to identified reach breaks to allow a reach by reach analysis. To accomplish this, the data was transformed and described as a percentage of the total river area available for individual reaches for mapped anadromous spawning use.
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4.3.2 River Bank – Riparian Band AHI Logic
The left and right bank AHI segment scores (AHIbank) were calculated using Equation 2.
퐿푑표푐푘 퐴퐻퐼푆푒𝑔푚푒푛푡 = ∑[푃푛푎푡 × 푊푛푎푡] + ∑[푃푟푒푡푎𝑖푛 × 푊푟푒푡푎𝑖푛] + ∑ [ × 푊푑표푐푘] + 퐿푡 퐿푒푟표푠𝑖표푛 ∑ [ × 푊푒푟표푠𝑖표푛] − 푀표푑푖푓푒푟 퐿푡
(2)
:where L is the length of the bank of a described river feature. Modifiers are either railways, roads or other large modifications to the bank or near the bank. Table 14 presents the categories, relative category weightings, and logic for the river bank AHI scoring.
Table 14. The parameters and logic for the banks of the South Thompson River Maximum Percent of Category Criteria Relative Logic the Category Value (Score) % Natural Value (% )* Category Percent Natural Percent Natural 5 100 nat Score (Pn) Wildlife a Wildlife 5 100 % Area * Category Score Large Woody Large Woody Debris Debris 5 100 % Area * Category Score Recruitment a Recruitment Biodiversity a Biodiversity 5 100 % Area * Category Score Leaf and Leaf and Litterfall a 5 100 % Area * Category Score Litterfall Low -0.75 5 % of Segment Length * Score Moderate -1.5 10 % of Segment Length * Score Erosion High -4.5 32 % of Segment Length * Score
Extreme -7.5 53 % of Segment Length * Score Retaining wall, Bank Armouring -2 % of Segment Length * Score rip rap Dock -0.25 #/km * Score Modifications Impairments Boat Launch -1 # * Score Rail -5 If yes = Score Shore Modifier Road -5 If yes = Score Other -2 If yes = Score a. See Table 11 for rating matrix and relative habitat values
4.4 Restoration and Segment Prioritization Analysis
To assess the viable restoration potential of a segment, the following changes were made to existing polygons occurring within the 100-m riparian band as well as to the bank inventory data. This involved the following:
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1. Polygons of lesser quality than a natural or minimally disturbed riparian, wooded, or grassland/shrub-steppe community (i.e., where a cultivated field or cleared area extended to the river’s edge), were replaced with a low disturbance seral site for the respective polygon position (implying restoration to the site potential vegetation type).
2. Lengths of “high” and “severe” bank erosion, inventoried and mapped during the 2015 field inventory, were removed from the bank segment data - representing bank restoration, stabilization, and bioengineering.
Cultivated field (Cf)
Cultivated field (Cf) Restored 30-m riparian band (Fm-ld)
Extreme Bank restoration/ erosion bioengineering
Natural cottonwood Natural cottonwood ecosystem (Fm – N) ecosystem (Fm – N) Existing Right bank restoration
3. Once steps 1 and 2 were completed, the AHI was re-run – outputting improved scores for reaches that had higher levels of impact and consequently lower Bank AHI scores and ratings. Bank segments demonstrating the greatest AHI score differential between AHInow and AHIpotential were identified as higher priority areas for mitigative action.
On the South Thompson River, the primary concern is riparian loss, river encroachment, and bank erosion.
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5.0 INVENTORY SUMMARY OF RESULTS
The South Thompson River flows from Little Shuswap Lake to Kamloops Lake, a distance of approximately 70 km.
The River was broken into a total of 21 reaches. The left bank (looking downstream) was divided into 64 Segments and the right bank was broken into 90 Segments. The total length of the left (LB) and right river banks (RB) was 81.4 km and 82.8 km respectively
5.1 Stream Primary Character
5.1.1 Shore Type Relative Distribution
The STHM forms a straight to mildly sinuous channel thorough glaciolacustrine sediments. This results in the predominance of benched to mildly sloping river banks that are composed primarily of silt. Bench associations account for about 71% of the left bank and 69% of right bank (Figure 2). Low and Middle Bench site associations combined account for about 52% of the left bank and about 68% of the right bank. Low and Middle Bench Site Associations occur in the geomorphologically dynamic portion of the floodplain and are maintained by a combination of prolonged flooding and site erosion/sedimentation (Mackenzie and Moran 2004). Low bench ecosystems occur on sites that are flooded for moderate periods (< 40 days) of the growing season, conditions that limit the canopy to tall shrubs, especially willows and alders. Middle bench ecosystems occur on sites briefly flooded (10–25 days) during freshet, allowing tree growth but limiting tree species to only flood-tolerant broadleaf species such as black cottonwood (Mackenzie and Moran 2004). The high bench sites are generally beyond the top of steep to vertical silt banks. Dry upland ecosystems generally predominate with grassland and shrub-steppe (big sagebrush) ecosystems and open ponderosa pine savanna.
Rocky shores begin to occur in the area of the Monte Creek confluence where slightly increased gradients have eroded the overlying silts exposing the coarser underlying substrates. Bedrock controlled shorelines are restricted to just 0.4% of the river along the right bank situated at Hoffman’s Bluff just upstream of Pritchard Provincial Park.
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Figure 2. Relative distribution of shore types along the left and right bank of the South Thompson River.
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Low Flood Bench (shrub) Mid Flood Bench (Cottonwood riparian ecosystem)
Mid flood bench with adjacent low flood (graminoid) fringe
Russian Olive (RO) Mid-flood bench riparian fringe
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High Bench Silt Bank
Confluence Riverine Marsh and Backwater
5.1.2 Landuse Relative Distribution
Over 75% of the left bank and greater than 80% of the right bank of the STHM and THOM (downstream to Kamloops Lake) have been altered by human activities. Commercial and industrial landuse accounts for nearly 30% of the left bank. Urban single and multifamily developments accounting for about 9% on the left bank and 7% on the right bank. Less intensive rural landuse accounts for about 20% of the left bank and 35% of the right bank. Agricultural landuse, including cultivated fields and livestock use, account for about 14% of the let bank and 28% of the right bank.
Railway (infrastructure) is persistent along the left bank of the STHM, often with associated bank armouring. Rail encroachment and disturbance along the left bank amounts to over 31 km (38%) of the STHM. Secondary roads modify close to 23 km (27%) of the right bank.
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Figure 3. Relative landuse distribution of along the left and right bank of the South Thompson River. The total length of the left (LB) and right river banks (RB) was 81 km and 83 km respectively.
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Agriculture (Livestock access)
Infrastructure
Natural Area
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Rural
Single Family
Commercial/Industrial
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5.1.3 River Bank Level of Impact
Although the left bank was documented to have generally more intensive landuse activities (i.e. commercial/industrial and urbanization), the right bank of the river had a greater cumulative distance where impacts to the bank and riparian area exceeded 40% of the segment. Segments with a high level of impact (>40%) combined to over 41 km (50%) of the right bank. The combined length of highly impacted segments along the left bank totaled close to 26 km (31%) of the river from Chase to Kamloops Lake. Figure 4 summarizes the distribution of impact rating categories assigned to the left and right banks of the South Thompson River.
Figure 4. Level of impact category distribution on the left and right bank of the South Thompson River.
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5.2 Stream Channel and Hydraulic Character
The STHM forms a straight to mildly sinuous channel over a very low gradient. The river drops only about 11 m (vertically) over the approximate 70 km that it flows from Little Shuswap Lake to Kamloops Lake. As a result, greater than 40 km of the river is a glide (Figure 5). A slight increase in channel gradient within 2 km downstream of the Lafarge Bridge results in a greater prevalence of higher velocity runs and riffle-pool reaches especially prevalent around the Monte Creek confluence (Reaches 9 and 10) and then again upstream of Banana Island.
Figure 5. South Thompson River hydraulic class distribution over the 83 km river length (centerline length).
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5.3 Fish Habitat
Overall there was a marked increase in channel complexity and habitat quality beginning around the Campbell Creek fan (downstream of the Lafarge Bridge). Individual instream habitat features (e.g. deep pool, rearing/nursery, and spawning habitat) were recorded in the GPS and marked on field maps during the field inventory (Figure 6).
Key rearing areas for Chinook were described by Federenko and Pierce (1982) as flooded pastures, backwaters and sloughs adjacent to spawning areas being the preferred areas for rearing. In terms of potential rearing and nursery habitat, low flood graminoid bench sites and riverine wetlands occurring adjacent to the river channel and in backwater areas, cover about 200 ha along the STHM and THOM. These habitats are generally represented as linear bands along the river channel. In addition, the expansive lacustrine shoremarsh and backwaters situated at the east end of Kamloops Lake contribute about another 134 ha of important rearing habitat. These sites are flooded for moderate periods (< 40 days) of the growing season, during which time they provide season nursery and rearing habitat for juvenile salmonids.
Deep pools, important for cover and general living as well as holding areas for anadromous migrations, amount to about 84 ha (3%) of the river. Of this area, only about 10 ha have been identified (DFO 2015) as key holding areas. Large woody debris (LWD) provides important structural cover/complexity for fish. However, it was recorded minimally (about 840 m2) along the STHM largely due to limited recruitment and downstream drift.
Anadromous spawning data provided by Fisheries and Oceans Canada (2015) stratified polygons in the river based on spawning utilization by Chinook and Sockeye and relative use intensity (Table 15). In total, only about 4% of the STHM has documented salmon spawning use. Sockeye spawning in the STHM is only documented in the uppermost reach (21) just below Little Shuswap Lake, accounting for only about 0.1% of the river (by channel area). Moderate to Moderate–High Chinook spawning use areas occupy about 1.6% of the river. High and Very High Chinook spawning intensity is provided by about 1% and 0.5 of the river respectively. The data summarized in Table 15 and illustrated on Map Set 2 was also incorporated into the AHI (Section 6.1).
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Figure 6. Relative distribution of key habitat elements mapped during the South Thompson River inventory. Percentage values shown in the illustration represent the spatial coverage of respective key habitat features over the total instream area (~2785 ha).
Table 15. Salmon aerial cover of spawning use (by density) in the South Thompson River.
Total Sockeye Chinook Summary of Instream Moderate- Very Salmon Reach Area (ha) Moderate Unknown Low Moderate High High high spawning use 1 678 2 352 3 168 4 54 5 65 6 58 7 198 8 81 9 43 35.1% 13.6% 48.7% 10 231 5.4% 5.4% 11 31 2.0% 5.7% 7.7% 12 150 0.1% 1.6% 5.3% 7.1% 13 38 2.3% 2.0% 4.3% 14 80 15 71 16 16 2.3% 2.3% 17 28 18 57 3.0% 3.0% 19 163 13.8% 13.8% 20 89 21 134 1.6% 2.2% 1.5% 12.7% 5.5% 4.5% 28.1% Total 2785 0.1% 0.1% 0.7% 0.1% 1.5% 1.0% 0.5% 4.0% Total river channel area = 2785 ha
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Spawning habitat (Sockeye) in Reach 21.
Spawning habitat (Chinook)
Juvenile rearing and security habitat (backwaters and low flood bench)
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Holding area/deep pool – Bedrock channel constriction at Hoffman’s Bluff just beyond upstream end of Pritchard Provincial Park creates deep pool in excess of 15m deep.
5.4 Modifications
Instream and bank modifications and features were recorded in the field as points and summarized in Table 16. It should be noted that general clearing/removal of riparian vegetation and encroachment by field and urban and rural development was not recorded as individual points and instead were captured within the percent disturbed field for individual shore segments.
In total, there were 14 sanctioned and informal boat launches, 277 docks, and 106 water withdrawals (intakes) recorded. Livestock access was recorded to occur on over 5.3 km of the river bank with close to 73% of being along the right bank. Bank armouring (rip rap) and retaining walls were recorded on over 12.5 km (15%) of the left bank and 6.9 km (8%) of the right bank.
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Table 16. Summary of anthropogenic features and modifications catalogued during the South Thompson River Inventory Mapping. Feature Bank Count of Modification Type Sum of Length (m) Left 9 Boat Launch Right 5 Bridge Both 7 Left 198 Dock Right 79 Left 2 40 Garbage/Pollution Right 6 296 Left 4 1450 Livestock Access Right 5 3920 Pilings Instream 2 440 Pipe Crossing Instream 1 Left 74 12543 Retain Wall/Rip rap Right 62 6859 Left 55 Water Withdrawal Right 51 The total length of the left (LB) and right river banks (RB) was 81.4 km and 82.8 km respectively.
Dock Water Withdrawal Improperly screened intakes, result in impingement or entrainment of fish.
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Rip rap and Bank Stabilization
Discharge
5.5 Bank Stability and Erosion
High to extreme severity bank erosion was documented on approximately 6.0 k m (7%) of the left bank and 4.6 km (6%) of the right bank (Table 17). Along much of the river, bank instability is largely a function of the steep silt banks that have naturally eroded over time through the glaciolacustrine silts. However, this instability is exacerbated by riparian vegetation removal and encroachment associated with agriculture and industrial, commercial, urban, and rural developments. All erosion features are shown in Map Set 2 and are included in the data deliverables. Bank segments with prominent erosion are listed in Table 18.
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Table 17. Summary of river bank integrity and erosion along the South Thompson River. Bank Severity Sum of Length (m) Percent of respective river bank1 Extreme 886 1% High 5084 6% Left Moderate 3442 4% Low 6701 8% Total 16113 20% Extreme 1556 2% High 3080 4% Right Moderate 6439 8% Low 6799 8% Total 17874 22% 1. The total length of the left (LB) and right river banks (RB) was 81.4 km and 82.8 km respectively.
High Severity Erosion
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Extreme Severity Erosion
Table 18. Summary of prominent erosion by bank and segment. Bank Segment Extreme Erosion (m) High Erosion (m) 4 1182 12 116 19 25 22 173 23 298 146 25 664 27 159 69 29 1262 Left 32 27 33 464 36 15 37 159 39 77 40 480 44 219 62 51 383 11 41 26 163 28 823 29 240 419 33 128 224 34 143 Right 36 339 45 147 46 365 102 74 609 75 301 90 593
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5.6 South Thompson River Condition Score
A condition score was assigned to each river reach. This rating system was designed with the intent of providing a more measurable parameter in evaluating the watercourse condition and monitoring and evaluating habitat changes on local watercourses and associated riparian and floodplain communities.
The sum of weighted scores equaled 2.81 (out of 6), with the South Thompson River receiving a stream grade of 47% (Table 19).
Table 19. Level of impact rating / condition score for the South Thompson River.
Impact Rating Sum of Length (m) Condition Value Score1 % of River Weighted Score high -high 5188 0 7% 0.00 mod-high 15959 1 21% 0.21 mod-mod 8914 2 11% 0.23 low-mod 13983 3 18% 0.54 nil-high 0 3 0% 0.00 low-low 25801 4 33% 1.33 nil-mod 0 4 0% 0.00 nil-low 7937 5 10% 0.51 nil-nil 0 6 0% 0.00 Sum 77783 2.81 Condition Score 47% 1Reach condition references the condition of both banks. E.g., high-high translates to high level of impact on both banks over the reach. Numeric Bank Impact Scores: Nil=3;Low=2; Mod=1; High=0
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6.0 AQUATIC HABITAT INDEX RESULTS
The AHI results summarized below are illustrated in Map Series 2 and the raw AHI analysis scores are included in Appendix A and B with centerline and bank segment information. Section 6.1 summarizes the AHI scores and resultant rankings (i.e., Very Low – Very High) for the 21 reaches of the South Thompson River, represented in the maps and data analysis as the centerline. Section 6.2 summarizes the AHI scores and resultant rankings for the respective left and right bank segments.
6.1 The River
The centerline AHI analysis resulted in about 6% of the river being ranked as Very High, 29% of the river being ranked as High, and 31% of the river ranked as Moderate (Table 20). The centerline/reach AHI rankings are illustrated in Figure 7.
Table 20. Relative AHI rank distribution (by length) of the South Thompson River.
AHI Category Total Length (m) Percent of River Very High 4403 6 High 22762 29 Moderate 24316 31 Low 26302 34
Figure 7. Centerline/reach AHI scores and AHI Rank values (Low/Moderate/High/Very High).
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6.2 Riverbanks
About 42% of the left bank of the South Thompson River is ranked Very Low to Low according to Bank AHI scores (Table 21). Similarly, about 40% of the right bank is ranked between Very Low and Low. Moderate AHI segments accounted for 39% of both the left and right banks of the STHM. Approximately 18% and 20% of the left and right bank received High to Very High AHI scores respectively. Figures 8 and 9 illustrates respective segment scores on the left and right banks.
Table 21. Relative AHI rank distribution (by length) of the left and right bank (looking downstream) of the South Thompson and Thompson River (Little Shuswap Lake to Kamloops Lake). Segment/AHI Ratings Sum of Segment Length (m) Percent of Bank Very High 6475 8% High 8507 10% Left Bank Moderate 31643 39% Low 31330 38% Very Low 3474 4% Very High 6109 7% High 11128 13% Right Bank Moderate 32190 39% Low 32468 39% Very Low 949 1%
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Figure 8. Left bank segment AHI scores.
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Figure 9. Right bank segment AHI scores.
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6.3 Restoration Analysis and Priorities
Eighteen bank segments were extracted from the restoration analysis as those with the greatest potential AHI score differential between AHInow and AHIpotential (Table 22). These segments represent high priority sites warranting more immediate attention in regards to bank and riparian restoration. Of these 18 priority segments, 14 occur on the left bank and 4 on the right bank. Figures 10 and 11 illustrate the differences between the AHInow and AHIpotential scores.
Table 22. Summary of priority bank segments extracted from the AHI Restoration analysis. High priority sites are in bold. Existing Bank Existing Bank Potential Potential Bank Score Segment Bank1 AHI2 Category Bank AHI Category Difference 54 Right 19.0 Very High 22.4 Very High 3.4 34 Left 17.4 Very High 19.1 Very High 1.8 48 Left 13.7 Very High 14.9 Very High 1.1 3 Left 13.0 High 14.2 Very High 1.2 37 Right 11.8 High 12.8 High 1.0 32 Left 7.1 Moderate 12.8 High 5.7 61 Right 11.5 High 12.6 High 1.1 60 Left 11.0 High 11.9 High 1.0 57 Right 9.0 High 11.4 High 2.4 55 Right 8.8 High 10.6 High 1.8 59 Right 6.9 Moderate 10.5 High 3.6 35 Right 7.4 Moderate 9.9 High 2.5 38 Right 8.4 High 9.8 High 1.4 66 Right 8.4 High 9.5 High 1.1 35 Left 7.9 Moderate 9.2 High 1.3 57 Left 7.7 Moderate 9.1 High 1.5 45 Left 7.4 Moderate 9.0 High 1.6 50 Left 7.4 Moderate 8.9 High 1.5 41 Left 7.0 Moderate 8.7 High 1.8 52 Right 6.5 Moderate 8.6 High 2.1 71 Right 7.2 Moderate 8.5 High 1.3 58 Right 3.7 Moderate 6.4 Moderate 2.7 84 Right 3.9 Moderate 6.5 Moderate 2.6 51 Left 1.7 Low 4.3 Moderate 2.6 56 Right 2.1 Low 4.5 Moderate 2.4 78 Right 3.6 Moderate 6.0 Moderate 2.4 88 Right 1.4 Low 3.7 Moderate 2.2 6 Right 3.9 Moderate 6.1 Moderate 2.2 46 Left 5.5 Moderate 7.7 Moderate 2.1 69 Right 2.5 Low 4.6 Moderate 2.1 1. The left and right banks are determined when looking downstream 2.AHI scores used in the restoration analysis were not adjusted according to the adjacent centerline AHI scores
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Figure 10. Left bank potential AHI score differential (Potential bank AHI scores - Current AHI score) based on the results of the restoration analysis.
Figure 11. Right bank potential AHI score differential (Potential bank AHI scores - Current AHI score) based on the results of the restoration analysis.
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7.0 DISCUSSION
Flood ecosystems are intensively used by many wildlife species. These are lush habitats with structural elements often not found in adjacent uplands. In addition, the low flood sites may provide critical rearing habitat for juvenile salmoinds during seasonal inundation periods. The High and Very High AHI scores/ranks supports this ecological statement; where the mosaic of riparian habitats and complex instream habitat subunits and diverse fish life history utilization combine to represent the highest centerline and bank AHI scores throughout the South Thompson River.
The areal extent of flood associated ecosystems remains constant in a stream reach over time, given no fundamental change in water regime or sediment load, but their location in the floodplain changes in response to stream channel changes (Mackenzie and Moran 2004). Flood ecosystems are maintained by a combination of annual flooding, erosion, channel movement, and deposition, which modify the site conditions on the floodplain regularly. Middle bench ecosystems will succeed low benches as sites accumulate sediments and become raised above the stream. With human influence, continued isolation of middle or low bench ecosystems from the regular flooding, through sediment accumulation or stream channel changes, hastens the natural succession and can lead to the formation of seral ecosystems that progress towards modified high bench ecosystems (Mackenzie and Moran 2004).
Recognizing the above, it is paramount that landuse planning and management of the South Thompson River focus on conservation and restoration of floodplain and riparian ecosystems. Russian olive (Elaeagnus angustifolia), is recognized by the British Columbia Invasive Plant Council as a species that is out-competing native vegetation around the province. In particular, Russian olive is displacing native riparian vegetation on disturbed low and mid flood bench sites that would otherwise be predominated by willow species and cottonwood and associated vegetation. Russian olive was especially prevalent along the South Thompson River. Efforts should be implemented to control the further spread of this species and to rehabilitate native low and mid bench flood associations.
Upland activities can impact floodplains. Instead of conventional hard armouring techniques, riparian and channel-bank restoration using bioengineering techniques should be investigated. Benefits of these activities will include bank stabilization and habitat restoration.
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Large woody debris revetment and bank stabilization
The restoration analysis extracted priority segments requiring more immediate attention. To fully realize the benefit of such biophysical inventories, actions need to be taken to begin to address concerns or issues identified above. In doing so, this information must be presented to pertinent groups and stakeholders to direct appropriate action and management decisions.
The South Thompson River is a high value anadromous and resident system regardless of individual reach AHI scores. A low AHI reach score does not imply that particular reach is of low value. Rather the combination of habitat attribute values in that reach contribute less to fisheries and aquatic production than other reaches. Reaches 2, 6-8, and 12 had Low centerline AHI scores. The Low ranking is a result of more limited habitat complexity (i.e., being a slow glide with fine-textured substrates), absence of salmonid spawning habitat, and being generally limited in instream cover. However, these lower reaches are still important and more sensitive for both spawning migration and fry outmigration.
The Very High and High river bank areas and those adjacent to High and Very High ranked reaches are considered the most important areas and mechanisms to protect these key habitat features need to be developed. This analysis highlights the importance of conserving important natural areas that remain and prioritizing habitat improvements where feasible.
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While the restoration analysis extracted 18 priority segments requiring more immediate attention, conservation of existing riparian conditions is paramount to prevent a reduction in Bank AHI scores for respective segments. The scores and corresponding rankings established in this analysis should form the baseline when reviewing current and proposed activities along the River. The review of existing or proposed activities should be measured against these baseline AHI scores using the metrics and relative habitat value scores for riparian band habitat units of the Bank AHI (net change analysis). In doing so, such activities and the potential impacts and modifications they may cause can be evaluated in accordance with the Canadian Policy for the management of fish habitat; where No Net Loss is the guiding principle.
8.0 CLOSURE
This Document has been prepared for the exclusive use of the Fraser Basin Council and project partners. It has been prepared based upon information collected during the comprehensive field inventory and other related documentation.
Questions or comments in reference to this report, and the data presented should be forwarded to the undersigned.
Respectfully Submitted, ECOSCAPE Environmental Consultants
Kyle Hawes, R.P.Bio. Robert Wagner, B.Sc. Senior Aquatic Biologist GIS Analyst
Rachel Plewes, M.Sc. Jason Schleppe, M.Sc., R.P.Bio. Data Analyst Senior Fisheries Biologist
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REFERENCES
Department of Fisheries and Oceans. 1997. Strategic Review of Fisheries Resources for the South Thompson-Shuswap Habitat Management Area. Fraser River Action Plan.
Dorova, J. and G. Moore, 1997. Effects of boatwakes on streambank erosion, Kenai River, Alaska. Technical Report 97-4105, U.S. Geological Survey, Anchorage, Alaska, prepared in cooperation with the Alaska Department of Fish and Game.
Fedorenko, A.Y. and B.C. Pearce. 1982. Trapping and coded wire tagging of wild juvenile Chinook salmon in the South Thompson/Shuswap River system, 1976, 1979, and 1980. Can. MS. Rep. Fish. Aquat. Sci. 1677. 63pp.
Griffith, R. P. 1986. Rainbow Trout production and Implications of Coho Salmon Enhancement in the Bessette Creek Drainage, Tributary to the Middle Shuswap River. Fisheries Improvement Unit. BC Fisheries Branch.
Groot, C. and L. Margolis (eds). 1991. Pacific Salmon Life Histories. University of British Columbia Press, Vancouver, B.C.
Hawes, K., J. Schleppe, and B. Jantz. 2011. Lower Shuswap River Inventory, Mapping, and Aquatic Habitat Index. Ecoscape Environmental Consultants Ltd. Project File: 10-642. 72 pp. + appendices.
Hill, D.F., M.M. Beachler, and P.A. Johnson. 2002. Hydrodynamic Impacts of Commercial Jet-Boating on the Chilkat River, Alaska. Department of Civil & Environmental Engineering, The Pennsylvania State University. 115pp.
Irvine, J.R., K. Wilson, B. Rosenberger and R. Cook. 1999. Stock Assessment of / Upper Fraser River Coho Salmon. Fisheries and Oceans Canada. Canadian Stock Assessment Secretariat. Research Document 99/28.
Jantz, Brian. 1984. Creel Survey and Life History Characteristics of Rainbow Trout and Kokanee in Mabel Lake. 1984.
Jantz, Brian. 1984Memo to file: Kingfisher Creek Rainbow Trout Tagging Project 1984. Ministry of Lands, Parks and Housing. Okanagan Region. Penticton.
Jantz, Brian. 1987. Memo to file 40.3403 Shuswap River. Ministry of Lands, Parks and Housing 1986 and 1987. Okanagan Region. Penticton.
Jantz, Brian. 1992. Effects of Winter Flow Reductions on Kokanee Salmon Spawning Habitat in the Middle Shuswap River. 1992. Province of B.C. Ministry of Environment, Lands and Parks. Penticton, B.C.
Lloyd, D., K.Angove, G. Hope, and C. South Thompson. 1990. A guide to site identification and interpretation for the Kamloops Forest Region. Land Management Handbook No. 23. February, 1990. BC Ministry of Forests.
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Lorz, H. W., and T. G. Northcote. 1965. Factors affecting stream location, timing and intensity of entry by spawning Kokanee (Oncorhynchus nerka) into an inlet of Nicola Lake, British Columbia. J. Fish. Res. Board Can. 22; 665-687.
Mackenzie, W.H., and Jennifer Moran. 2004. Wetlands of British Columbia - A guide to identification. British Columbia Ministry of Forests, Forests Science Program. 287pp.
Mason, B., and R. Knight. 2001. Sensitive Habitat Inventory and Mapping. Community Mapping Network, Vancouver, British Columbia. 315pp + viii. M. Johannes, Editor.
McPhail, J.D. 2007. The Freshwater Fishes of British Columbia. University of Alberta Press.
Ministry of Forests, Lands and Natural Resource Operations Lake and River Files. 2011. Fish and Wildlife Branch, Penticton, B.C.
Ministry of Water, Land and Air Protection. 2003. 2000 Survey of Sport Fishing in British Columbia with summary information from the 1985, 1990 and 1995 surveys. Province of BC, Victoria, BC.
Ministry of Water, Land and Air Protection. 2004. Accounts and Measures for Managing Identified Wildlife. Identified Wildlife Management Strategy. Version 2004.
Minns, C. 1997. Quantifying “no net loss” of productivity of fish habitats. Can. J. Fish. Aquat. Sci. 54: 2463-2473 (1997).
Redfish Consulting. 2005. Final Survey Results of Select Lakes in the Kamloops Area Inhabited by Kokanee – Year 4. 2004.
Resource Inventory Committee. 2001. Reconnaissance (1:20000) fish and fish habitat inventory: Standards and procedures. Version 2. 170pp.
Resource Inventory Committee. 2001. Standards for Fish and Fish Habitat Maps. Version 3.0. Province of British Columbia. 66pp.
Schleppe, J., 2010. Okanagan Lake Foreshore Inventory and Mapping. Ecoscape Environmental Consultants Ltd.. Project File: 10-596. 2011. Prepared for: Okanagan Collaborative Conservation Program
Slaney, P.A., and T.G. Northcote. 1974. Effects of prey abundance on density and territorial behavior of young Rainbow Trout (Salmo gairdneri) in laboratory stream channels. J. Fish. Res. Board Can. 31:1201-1209.
Webster, J. 2007. 2007 Kokanee Fry Out-migration, Mission Creek Spawning Channel - 2006 Brood Year.
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MAPS
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APPENDIX A
South Thompson River Reach Data (centerline survey) with AHI Scores
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix A May 2016
REACH_NUMB AHI_Category RIVERNAME WTRESHEDCD WTRBDYID DATE CREW WEATHER STAGE LINE_TYPE LINE_SRC PHOTONUM PRIMARY IMPACT_RAT HYDRAULIC PATTERN 1 High Thompson 120 THOM 11/2/2015 0:00 KH;BH;TT;JP Clear low Trimble RIM2014 DSCN0495.jpg Natural nil_low Lake Straight 2 Low Thompson 120 THOM 11/2/2015 0:00 KH;BH;TT;JP Clear low Trimble RIM2014 DSCN0247.jpg Modified mod_high Glide Sinuous 3 Moderate Thompson 120 THOM 11/2/2015 0:00 KH;BH;TT;JP Clear low Trimble RIM2014 DSCN0566.jpg Modified high_high Run Sinuous 4 Very High Thompson 120 THOM 11/2/2015 0:00 KH;BH;TT;JP Clear low Trimble RIM2014 DSCN0071.jpg Modified mod_high Glide Straight 5 High South Thompson 128 STHM 11/3/2015 0:00 KH;BH;TT;JP Clear low Trimble RIM2014 DSCN0014.jpg Modified mod_high Glide Sinuous 6 Moderate South Thompson 128 STHM 11/3/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN0731.jpg Modified mod_high Glide Sinuous 7 Moderate South Thompson 128 STHM 11/3/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN0942.jpg Modified mod_mod Glide Sinuous 8 Low South Thompson 128 STHM 11/4/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1147.jpg Modified low_mod Glide Straight 9 Very High South Thompson 128 STHM 11/4/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1246.jpg Modified low_mod Run Sinuous 10 Very High South Thompson 128 STHM 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1542.jpg Modified low_mod Riffle/Pool Sinuous 11 Moderate South Thompson 128 STHM 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1598.jpg Modified mod_high Lake Straight 12 Moderate South Thompson 128 STHM 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1680.jpg Modified low_low Glide Sinuous 13 Very High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1732.jpg Natural low_low Run Sinuous 14 High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1814.jpg Modified low_low Glide Sinuous 15 High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1869.jpg Natural nil_low Glide Sinuous 16 High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1911.jpg Natural nil_low Pool Straight 17 Moderate South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN1945.jpg Modified low_mod Glide Straight 18 Very High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN2009.jpg Modified low_low Run Sinuous 19 Very High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN2052.jpg Modified low_low Run Sinuous 20 High South Thompson 128 STHM 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN2154.jpg Modified low_low Glide Straight 21 Very High South Thompson 128 STHM 11/9/2015 0:00 KH;BH;TT;JP Partly Cloudy low Trimble RIM2014 DSCN5590.jpg Modified low_low Riffle/Pool Regular Meanders 15-1588 Appendix A May 2016
COMT_CLASS PERCENT_GR SPAWNING_H LIVESTOCK_ BARS ISLANDS COMT_SCHAR SUB_ORGANI SUB_FINES SUB_GRAVEL SUB_PEBBLE 0 Unknown Side Occasional 0 100 0 0 0.1 Unknown Mid-channel Occasional 0 100 0 0 0.1 Unknown Side Split 0 95 4 1 Confluence of North Thompson 0.2 Anadromous None None Pink Salmon redds identified in gravel just upstream of confluence 0 55 45 0 High impact along both banks in lower half of reach with reduced alteration along r.b. in upper half 0.1 Unknown None None 0 95 5 0 Rail and industrial impacts along left bank 0.1 Unknown None None 1 95 4 0 0.1 Unknown None None 0 95 5 0 0.1 Unknown None None 0 100 0 0 Increased gradient with run in upper section and pool morphology in low 1/3 of reach 0.2 Anadromous None None 0 30 30 35 Increased gradient and spawning habitat 0.3 Anadromous Mid-channel None Critical CK spawning reach 0 15 35 35 Lake form with Monte Creek fan creating outlet control at downstream end 0 Unknown None None 10 90 0 0 0.1 Unknown None None 0 100 0 0 Riffle-Run 0.2 Anadromous Yes Side None Side gravel bars associated with tributary fans - gravel source 0 40 30 30 Slow moderately deep glide 0.05 Unknown Yes Side None 0 70 20 10 Glide-Pool 0.05 Unknown Yes None None 0 90 10 0 0 Unknown Yes None None Holding area 0 15 15 15 Livestock grazing along right bank 0 Unknown Yes None None 0 95 5 0 Riffle-Run 0.2 Anadromous Yes None Split 0 45 20 25 Riffle-Run-Glide 0.2 Anadromous Yes Side None 0 8 30 40 Run-Glide 0.2 Unknown Mid-channel None Channelization and excavation to create navigable channel through reach 0 55 30 10 Riffle-Pool-Run 0.3 Anadromous Yes Mid-channel None 0 5 35 45 15-1588 Appendix A May 2016
SUB_COBBLE SUB_BLDER SUB_BEDRK EMBEDDEDNE COMPACTION COMT_SUB WIDTH_W WIDTH_BF WIDTH_LFP WIDTH_RFP DEPTH_W DEPTH_BF DEPTH_FP COMT_CHAN TOTAL_COVE B DP IV LWD OV SWD UC LWD_COUNT LOG_JAM_CO DP_COUNT 0 0 0 High (75%+) Low 0 800 0 0 0 0 0 1 0 50 0 0 0 0 50 0 0 0 0 0 0 High (75%+) Low 0 650 0 0 0 0 0 3 0 100 0 0 0 0 0 1 0 1 0 0 0 High (75%+) Low 0 250 0 0 0 0 0 4 0 100 0 0 0 0 0 0 0 0 0 0 0 High (75%+) Low 0 250 0 0 0 0 0 10 0 100 0 0 0 0 0 0 0 1 0 0 0 High (75%+) Low 0 150 0 0 0 0 0 10 0 70 20 10 0 0 0 1 0 3 0 0 0 High (75%+) Low 0 200 0 0 0 0 0 7 0 70 20 10 0 0 0 1 0 2 0 0 0 High (75%+) Low 0 180 0 0 0 0 0 7 0 25 70 5 0 0 0 3 0 1 0 0 0 High (75%+) Low 0 275 0 0 0 0 0 4 0 50 50 0 0 0 0 0 0 0 5 0 0 Medium (25-75%) Low 0 175 0 0 0 0 0 20 0 90 10 0 0 0 0 0 0 2 15 0 0 Low (0-25%) Medium 0 245 0 0 0 0 0 10 0 30 70 0 0 0 0 0 0 0 0 0 0 High (75%+) Low 0 190 0 0 0 0 0 8 0 75 25 0 0 0 0 0 0 1 0 0 0 High (75%+) Low 0 245 0 0 0 0 0 5 0 50 50 0 0 0 0 1 0 0 0 0 0 Low (0-25%) Medium 0 210 0 0 0 0 0 8 0 75 25 0 0 0 0 0 0 0 0 0 0 High (75%+) Low 0 300 0 0 0 0 0 8 0 75 25 0 0 0 0 0 0 0 0 0 0 High (75%+) Low 0 230 0 0 0 0 0 15 0 75 25 0 0 0 0 0 0 1 15 10 30 Low (0-25%) Medium Scour area from bedrock pinch point 0 130 0 0 0 0 0 60 0 100 0 0 0 0 0 0 0 1 0 0 0 High (75%+) Low 0 200 0 0 0 0 0 10 0 100 0 0 0 0 0 0 0 0 5 2 3 Medium (25-75%) Low 0 120 0 0 0 0 0 20 0 100 0 0 0 0 0 0 0 3 20 2 0 Low (0-25%) Medium 0 235 0 0 0 0 0 7 0 100 0 0 0 0 0 0 0 1 5 0 0 High (75%+) Low 0 380 0 0 0 0 0 3 0 100 0 0 0 0 0 0 0 0 15 0 0 Low (0-25%) Medium 0 275 0 0 0 0 0 10 0 90 0 10 0 0 0 0 0 3 15-1588 Appendix A May 2016
COMT_COV CMMNTFLORA CMMNTFAUNA MAX_PDOP CORR_TYPE RCVR_TYPE GPS_DATE FEAT_NAME DATAFILE LENGTH Shape_Length AHI BW CO FL_hd FL_ld Very low cover 0 Postprocessed Code Geo 7X 11/2/2015 0:00 RIVER_CE THOMP-RIM-NOV2.cor 4340 4339.546972 Moderate 399833.714 0 0 0 Generally low instream cover 0 Postprocessed Code Geo 7X 11/2/2015 0:00 RIVER_CE THOMP-RIM-NOV2.cor 5921 5921.12677 Low 11708.3674 0 0 12812.4838 Deeper run in left channel provides some increased cover for migrating fish 0 Postprocessed Code Geo 7X 11/2/2015 0:00 RIVER_CE THOMP-RIM-NOV2.cor 5188 5188.383574 Low 0 0 0 0 Deeper cover along left portion of channel - important staging for NTHM runs 56 Postprocessed Code Geo 7X 11/2/2015 0:00 RIVER_CE THOMP-RIM-NOV2.cor 1518 1517.953325 High 0 214565.2628 0 0 Deeper glide with instream LWD 3 Postprocessed Code Geo 7X 11/3/2015 0:00 RIVER_CE THOMP-RIM-NOV3.cor 3693 3692.679191 Moderate 0 0.109721595 0 1711.39473 0 Postprocessed Code Geo 7X 11/3/2015 0:00 RIVER_CE THOMP-RIM-NOV3.cor 3191 3191.1221 Low 0 0 0 414.0447886 Instream vegetation (pondweed sp. providing increased juvenile cover 0 Postprocessed Code Geo 7X 11/3/2015 0:00 RIVER_CE THOMP-RIM-NOV3.cor 8914 8914.349746 Low 0 11970.66072 10544.8082 11064.07736 0 Postprocessed Code Geo 7X 11/4/2015 0:00 RIVER_CE THOMP-RIM-NOV4.cor 3043 3042.941443 Low 13421.63825 0 254.3346958 0 Prominent holding area/deep pool below run 0 Postprocessed Code Geo 7X 11/4/2015 0:00 RIVER_CE THOMP-RIM-NOV4.cor 2152 2152.112374 High 0 9828.871046 0 0 Good vegetation cover at hig flows 4.3 Postprocessed Code Geo 7X 11/5/2015 0:00 RIVER_CE THOMP-RIM-NOV5.cor 7590 7590.069991 High 0 13371.16946 23497.65383 560.2367805 Lake character provides more deep water cover for fish 4.3 Postprocessed Code Geo 7X 11/5/2015 0:00 RIVER_CE THOMP-RIM-NOV5.cor 1636 1636.250235 Low 0 761.9385214 0 376.5241467 Moderately deep glide with no prominent pools 4.3 Postprocessed Code Geo 7X 11/5/2015 0:00 RIVER_CE THOMP-RIM-NOV5.cor 5232 5232.383008 Low 0 0 0 17914.0401 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 2425 2425.336206 Moderate 0 19615.42675 0 0 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 2514 2514.077512 Moderate 0 16009.2659 0 3063.90027 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 2765 2765.497731 Moderate 0 2744.726822 0 0 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 832 832.0823124 Moderate 0 0 1186.95861 0 Deeper glide 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 1198 1197.574785 Low 0 0 2876.07701 0 Deep pool/holdin area upstream of Banana Island 0 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 3664 3663.954916 Moderate 0 0 0 0 Deeper glide providing some cover in lower portion of reach 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 5413 5412.593022 High 0 12121.30706 3131.910936 0 Excavated channel provides limited cover through reach 4.3 Postprocessed Code Geo 7X 11/6/2015 0:00 RIVER_CE THOMP-RIM-NOV6.cor 2150 2149.635401 Moderate 15243.84167 0 0 4762.087831 LWD cover provided by let bank revetments 4.3 Postprocessed Code Geo 7X 11/9/2015 0:00 RIVER_CE THOMP-RIM-NOV9.cor 4403 4402.837279 High 24209.40629 45791.08534 0 1055.667808 15-1588 Appendix A May 2016
FL_md FL_n FLG_hd FLG_i FLG_ld FLG_md FLG_n FLS_i FLS_ld FLS_md FLS_n FM_i FM_n G LK M_i P RF RM RN RU_hd Instream_Habitat_Area 28715.86954 308205.7532 240941.057 0 7064.589489 30545.20988 107203.3795 0 0 4881.002853 414714.2231 0 0 32417.24513 4153270.804 0 0 0 1055352.293 0 0 6783145.14 9735.439058 113600.7892 0 0 0 11103.70235 0 0 0 0 27823.08397 0 0 3322339.736 14732.11571 0 0 0 0 0 0 3523855.718 0 25766.38975 0 0 0 0 0 0 0 0 0 0 332234.7208 825880.3997 0 0 25170.20165 103747.2432 0 370957.4627 0 1683756.418 0 0 0 0 0 0 83.97821071 0 0 8782.380943 0 0 0 190734.9135 0 0 123045.0204 0 0 0 0 537211.5558 0 2773.981243 0 0 2023.551162 358.8749803 4882.798122 0 4391.478848 0 9180.322988 0 0 443891.9617 0 0 59978.37826 116241.5977 0 0 0 645434.4495 925.5316519 4007.436553 0 0 0 0 1560.595668 0 1157.943719 0 937.6406633 0 0 575152.5424 0 0 0 154.0139606 0 0 0 584309.7494 889.256491 11840.83144 0 0 1073.640621 0 54203.16902 0 4262.573602 0 13695.70878 0 0 1858799.241 0 0 0 0 0 0 0 1978343.967 0 798.4613957 0 0 264.9583001 500.4468045 52236.07179 0 2866.75381 0 10805.64127 0 0 731502.211 0 0 0 0 0 0 0 812650.5173 0 8403.57455 573.2978243 0 5339.722198 0 2992.709843 0 0 0 0 0 0 75803.0699 0 0 103325.5013 0 0 225477.6276 0 431744.3742 3100.977935 33252.66836 686.6310451 0 22445.73737 0 45578.37977 0 0 0 0 0 0 1267741.045 0 0 0 418351.9883 0 478422.6755 0 2307009.163 0 0 326.6554263 0 6766.297237 1569.952509 4375.517603 0 0 0 0 0 0 274435.772 0 0 0 0 0 18489.49489 0 307102.1524 0 0 0 0 91047.27007 0 14813.36042 0 0 0 0 0 0 1262104.432 0 0 0 0 0 110977.4882 0 1496856.591 0 0 20660.83338 0 21097.97007 0 4972.584459 0 0 0 0 0 0 64844.99749 0 0 0 44275.54201 0 199744.0778 0 375211.432 10169.23065 0 40617.4595 0 4992.357782 28538.69883 11618.85865 0 2654.66599 0 0 0 0 682704.2168 0 0 0 0 0 0 3424.253198 803792.9076 15473.64943 0 23918.81165 0 0 67995.44267 29456.96864 0 0 0 0 0 0 430912.7427 0 0 136563.8254 0 0 0 0 707066.1673 0 0 18946.30731 0 0 2742.522911 0 0 0 0 0 0 0 105081.2183 0 0 33227.19667 0 0 0 0 161184.2038 0 0 12737.26961 0 0 10901.38468 5432.036926 0 0 0 0 0 0 218388.9398 0 0 34103.60639 0 0 0 0 284439.3144 0 0 0 4600.492907 3971.291177 6454.055438 61248.37969 13431.01914 0 0 0 150.4168225 0 139059.6323 0 10527.42688 81502.75987 167445.4531 0 80734.24197 0 569125.1693 0 0 0 0 8526.330779 0 225824.7155 0 0 0 381.25066 0 0 286054.305 0 0 44167.70143 236368.2784 0 817374.3627 0 1633950.162 0 13519.46246 0 0 55540.05059 0 7825.595058 0 3409.421354 0 14874.59886 0 0 586959.9731 0 0 0 182912.3606 0 0 0 885047.3915 2682.834093 29283.29088 0 31804.99445 16159.79429 434.3727149 63470.70018 0 3805.470305 0 3927.118712 16752.7678 38648.4385 0 0 0 106674.7576 737713.3349 0 221887.2561 0 1344301.29 15-1588 Appendix A May 2016
Sockeye_Spawn_Moderate Sockeye_Spawn_Total Chinook_Hold_Unknown Chinook_Spawn_High Chinook_Spawn_Low Chinook_Spawn_Moderate Chinook_Spawn_Moderate_to_High Chinook_Spawn_Unknown Chinook_Spawn_Very_high Chinook_Spawn_Total Chinook_Hold_Total NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0 58576.0684 151603.526 0 0 0 0 210179.5944 0 NA NA 0 123857.6154 0 0 0 0 0 123857.6154 0 NA NA 36914.53741 17434.04886 6194.210526 0 0 0 0 23628.25939 36914.53741 NA NA 9081.411254 0 24694.48579 0 0 2076.42598 79573.91047 106344.8222 9081.411254 NA NA 0 0 0 8553.150239 0 0 7457.723801 16010.87404 0 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 0 0 0 0 3753.409915 0 0 3753.409915 0 NA NA NA NA NA NA NA NA NA NA NA NA NA 45911.90084 0 0 0 17135.7224 0 0 17135.7224 45911.90084 NA NA 0 0 0 0 226069.2534 0 0 226069.2534 0 NA NA NA NA NA NA NA NA NA NA NA 21490.28779 21490.28779 4770.08673 74479.82227 0 20748.80996 170770.9981 29036.2935 61064.89183 356100.8157 4770.08673 15-1588 Appendix B May 2016
APPENDIX B
River Bank (Left and Right) Segment Data Base with AHI Scores
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix B May 2016
SEGMNT_NUM AHI_Category_Final FEAT_NAME RIVER_NAME DATE TIME_ CREW WEATHER JURISDICTI COMMENTS REACH_NUMB SHORE_TYPE SHORE_MODI SLOPE LAND_USE LEV_OF_IMP LIVEST_ACC PCTDISTURB 1 Moderate LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench Railway Low (5-20%) Natural Area Low (<10%) No 10 2 High LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Mid Bench None Bench Agriculture Medium (10-40%) No 40 3 High LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench None Bench Agriculture Low (<10%) No 10 4 Moderate LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Mid Bench None Bench Agriculture Low (<10%) No 10 5 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Rocky Shore Other Bench Industrial High (>40%) No 100 6 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Gravel Road Moderate (5-20%) Industrial High (>40%) No 80 7 High LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Sand None Bench Natural Area Natural Area No 5 8 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Flood Mid Bench Road Bench Industrial High (>40%) No 75 9 High LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Flood Mid Bench None Bench Industrial Medium (10-40%) No 25 10 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Gravel None Bench Industrial High (>40%) No 100 11 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Rocky Shore Road Moderate (5-20%) Industrial High (>40%) No 100 12 Very Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 3 Rocky Shore Railway Steep (20-60) Industrial High (>40%) No 100 13 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 4 Rocky Shore Railway Steep (20-60) Industrial Medium (10-40%) No 40 14 Very Low LEFT_BAN Thompson River 11/2/2015 0:00 11:19:31am KH;BH;TT;JP Clear 4 Rocky Shore Railway Steep (20-60) Industrial High (>40%) No 95 15 Low LEFT_BAN Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 4 Gravel None Moderate (5-20%) Recreation Medium (10-40%) No 40 16 Low LEFT_BAN South Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 5 Sand None Low (5-20%) Recreation High (>40%) No 80 17 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Flood Mid Bench Road Low (5-20%) Recreation Medium (10-40%) No 60 18 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Flood Mid Bench None Low (5-20%) Single Family High (>40%) No 100 19 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Flood High Bench Road Low (5-20%) Multi Family High (>40%) No 90 20 Very High LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Flood High Bench None Low (5-20%) Single Family High (>40%) No 90 21 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Rocky Shore Railway Moderate (5-20%) Industrial High (>40%) No 95 22 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 6 Rocky Shore Other Moderate (5-20%) Industrial High (>40%) No 100 23 Very Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 6 Sand Railway Moderate (5-20%) Industrial High (>40%) No 100 24 Low LEFT_BAN South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 7 Flood High Bench None Low (5-20%) Single Family High (>40%) No 95 25 Low LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood High Bench Railway Moderate (5-20%) Rural Medium (10-40%) No 60 26 Low LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood High Bench None Low (5-20%) Single Family High (>40%) No 95 27 Low LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood High Bench Railway Moderate (5-20%) Rural High (>40%) No 90 28 Moderate LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood High Bench None Low (5-20%) Single Family High (>40%) No 95 29 Low LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 8 Flood Low Bench Railway Bench Natural Area Low (<10%) No 2 30 Very High LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Flood Mid Bench None Bench Natural Area Low (<10%) No 5 31 Very High LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Confluence None Bench Natural Area None No 0 32 Moderate LEFT_BAN South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Flood Low Bench None Bench Natural Area Low (<10%) No 5 33 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Mid Bench None Low (5-20%) Industrial Medium (10-40%) No 60 34 Very High LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Mid Bench None Low (5-20%) Single Family High (>40%) No 100 35 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Other None Low (5-20%) Rural Medium (10-40%) No 50 36 Low LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Rocky Shore Railway Low (5-20%) Commercial High (>40%) No 100 37 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Gravel Railway Low (5-20%) Natural Area Low (<10%) No 10 38 Very High LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Confluence None Bench Natural Area Low (<10%) No 2 39 Low LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 11 Flood Mid Bench Railway Moderate (5-20%) Rural Medium (10-40%) No 50 40 Low LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Other Railway Bench Rural High (>40%) No 85 41 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Low Bench None Bench Agriculture Medium (10-40%) No 40 42 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 13 Flood Low Bench None Bench Rural Medium (10-40%) No 40 43 Moderate LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 13 Confluence None Bench Rural High (>40%) No 70 44 Low LEFT_BAN South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 14 Flood Low Bench Railway Bench Rural Medium (10-40%) No 40 45 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 14 Flood Low Bench None Bench Rural Low (<10%) No 10 46 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 14 Flood Low Bench None Bench Rural High (>40%) No 50 47 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 15 Flood Low Bench None Bench Agriculture Medium (10-40%) Yes 60 48 Very High LEFT_BAN South Thompson River 11/6/2015 0:00 10:58:14am KH;BH;TT;JP Partly Cloudy 15 Flood Mid Bench None Bench Natural Area Low (<10%) Yes 10 49 Very High LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 15 Flood Mid Bench None Bench Natural Area Low (<10%) No 2 50 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 16 Flood High Bench None Low (5-20%) Rural Medium (10-40%) No 20 51 Low LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 17 Flood Mid Bench None Bench Agriculture High (>40%) Yes 90 52 Very High LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 17 Flood Low Bench None Bench Natural Area Low (<10%) No 10 53 High LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 18 Flood Low Bench Railway Steep (20-60) Natural Area Medium (10-40%) No 20 54 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 19 Rocky Shore Railway Moderate (5-20%) Commercial Medium (10-40%) No 80 55 Low LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 19 Other Railway Low (5-20%) Commercial High (>40%) No 100 56 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 19 Flood High Bench Railway Low (5-20%) Commercial Low (<10%) No 20 57 Moderate LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 20 Flood Low Bench None Bench Agriculture Low (<10%) No 10 58 Low LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 20 Flood Low Bench Road Bench Agriculture Low (<10%) No 10 59 Low LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Flood High Bench None Low (5-20%) Single Family High (>40%) No 90 60 High LEFT_BAN South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Flood Mid Bench None Bench Natural Area Low (<10%) No 10 61 Moderate LEFT_BAN South Thompson River 11/9/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Flood High Bench None Low (5-20%) Rural Medium (10-40%) No 40 62 Low LEFT_BAN South Thompson River 11/9/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Other None Low (5-20%) Agriculture High (>40%) No 100 63 High LEFT_BAN South Thompson River 11/9/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Flood Mid Bench None Bench Natural Area Low (<10%) No 25 64 Moderate LEFT_BAN South Thompson River 11/9/2015 0:00 KH;BH;TT;JP Partly Cloudy 21 Confluence None Bench Rural Medium (10-40%) No 40 1 Moderate RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench Road Bench Natural Area Low (<10%) No 20 2 Moderate RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench Road Bench Natural Area Low (<10%) No 10 3 Low RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench Road Steep (20-60) Natural Area High (>40%) No 95 4 High RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Flood Low Bench None Bench Natural Area Low (<10%) No 5 5 Moderate RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Wetland None Bench Agriculture Low (<10%) Yes 5 6 Moderate RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 1 Wetland None Bench Agriculture High (>40%) No 70 7 Very High RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Flood Mid Bench None Bench Natural Area Low (<10%) No 10 8 Low RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Rocky Shore Other Bench Commercial High (>40%) No 100 9 Low RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Rocky Shore Other Bench Rural High (>40%) No 100 10 Low RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Rocky Shore Other Bench Single Family High (>40%) No 100 11 Low RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 2 Flood High Bench None Bench Single Family High (>40%) No 100 12 High RIGHT_BA Thompson River 11/3/2015 0:00 10:57:12am KH;BH;TT;JP Clear 2 Flood Mid Bench None Bench Multi Family Low (<10%) No 15 13 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 2 Flood Mid Bench None Bench Single Family High (>40%) No 90 14 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 2 Flood Mid Bench None Bench Single Family High (>40%) No 80 15 Moderate RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Flood Mid Bench None Bench Urban Park Medium (10-40%) No 20 15-1588 Appendix B May 2016
SEGMNT_NUM AHI_Category_Final FEAT_NAME RIVER_NAME DATE TIME_ CREW WEATHER JURISDICTI COMMENTS REACH_NUMB SHORE_TYPE SHORE_MODI SLOPE LAND_USE LEV_OF_IMP LIVEST_ACC PCTDISTURB 16 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Flood Mid Bench Road Bench Urban Park High (>40%) No 80 17 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Flood Mid Bench Road Bench Urban Park High (>40%) No 50 18 Very Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Rocky Shore Road Bench Single Family High (>40%) No 100 19 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Rocky Shore Other Bench Multi Family High (>40%) No 100 20 Low RIGHT_BA Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 3 Flood Mid Bench None Bench Single Family High (>40%) No 90 21 Moderate RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 4 Flood Mid Bench None Bench Commercial Medium (10-40%) No 40 22 High RIGHT_BA Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 4 Confluence None Moderate (5-20%) Urban Park Low (<10%) No 10 23 Very High RIGHT_BA South Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 5 Confluence None Bench Natural Area None No 0 24 Low RIGHT_BA South Thompson River 11/2/2015 0:00 10:24:02am KH;BH;TT;JP Clear 5 Flood Mid Bench Railway Bench Industrial High (>40%) No 90 25 Low RIGHT_BA South Thompson River 11/2/2015 0:00 KH;BH;TT;JP Clear 5 Sand None Moderate (5-20%) Industrial High (>40%) No 100 26 Low RIGHT_BA South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 5 Flood Mid Bench Road Bench Rural High (>40%) No 90 27 High RIGHT_BA South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 6 Flood Low Bench None Low (5-20%) Rural Low (<10%) No 10 28 Low RIGHT_BA South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear Vertical silt bank - eroding. Flat bench beyond TOB cultivated and old field (grassland conversion) 6 Other None Bench Agriculture Medium (10-40%) No 40 29 Low RIGHT_BA South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 6 Flood Low Bench Road Low (5-20%) Rural High (>40%) No 70 30 Very High RIGHT_BA South Thompson River 11/3/2015 0:00 KH;BH;TT;JP Clear 7 Flood Low Bench None Bench Natural Area Low (<10%) No 2 31 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Mid Bench None Bench Rural High (>40%) No 60 32 High RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Mid Bench None Bench Rural Low (<10%) No 5 33 Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Mid Bench None Bench Agriculture High (>40%) No 95 34 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Mid Bench None Bench Agriculture Medium (10-40%) Yes 40 35 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Mid Bench None Bench Rural High (>40%) No 100 36 High RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Other None Low (5-20%) Natural Area Low (<10%) No 10 37 High RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Flood Low Bench None Bench Natural Area None No 0 38 High RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Confluence None Bench Rural Medium (10-40%) No 40 39 Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 7 Other Road Bench Rural High (>40%) No 70 40 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 8 Flood Low Bench Road Bench Natural Area Low (<10%) No 5 41 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 8 Flood Mid Bench None Bench Rural Medium (10-40%) No 95 42 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 8 Flood Low Bench None Bench Rural High (>40%) No 80 43 Moderate RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Confluence None Bench Rural High (>40%) No 70 44 Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Other Road Low (5-20%) Rural High (>40%) No 100 45 Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Other Road Low (5-20%) Rural Medium (10-40%) No 40 46 Very Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Other Road Low (5-20%) Rural High (>40%) No 100 47 Low RIGHT_BA South Thompson River 11/4/2015 0:00 KH;BH;TT;JP Clear 9 Flood Low Bench Road Low (5-20%) Rural Medium (10-40%) No 40 48 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Low Bench Road Bench Rural Low (<10%) No 20 49 Low RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Low Bench None Low (5-20%) Rural High (>40%) No 70 50 Low RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Low Bench None Low (5-20%) Rural High (>40%) No 70 51 Low RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Mid Bench None Low (5-20%) Single Family High (>40%) No 95 52 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Low Bench None Low (5-20%) Rural Medium (10-40%) No 40 53 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 10 Flood Low Bench Road Steep (20-60) Natural Area Low (<10%) No 10 54 Very High RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 11 Rocky Shore None Steep (20-60) Rural Medium (10-40%) No 40 55 High RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 11 Flood Mid Bench None Moderate (5-20%) Rural High (>40%) No 70 56 Low RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Mid Bench Road Low (5-20%) Rural Medium (10-40%) No 50 57 High RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Low Bench None Bench Rural Medium (10-40%) No 40 58 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Low Bench None Bench Agriculture High (>40%) No 70 59 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Confluence None Bench Rural Medium (10-40%) No 50 60 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Low Bench None Bench Agriculture High (>40%) No 70 61 High RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Other None Steep (20-60) Natural Area None No 0 62 Moderate RIGHT_BA South Thompson River 11/5/2015 0:00 KH;BH;TT;JP Partly Cloudy 12 Flood Low Bench None Bench Agriculture Medium (10-40%) Yes 60 63 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Partly Cloudy 13 Flood Low Bench None Bench Agriculture High (>40%) Yes 95 64 High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 13 Gravel None Moderate (5-20%) Rural Low (<10%) Yes 10 65 High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 13 Gravel None Moderate (5-20%) Agriculture High (>40%) Yes 80 66 High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 13 Gravel None Low (5-20%) Agriculture Medium (10-40%) No 40 67 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 14 Flood Low Bench None Bench Agriculture High (>40%) Yes 100 68 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 14 Flood Low Bench Road Bench Natural Area Medium (10-40%) No 30 69 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 15 Flood Low Bench None Bench Agriculture High (>40%) Yes 90 70 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 15 Flood Low Bench None Bench Agriculture Medium (10-40%) Yes 30 71 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 15 Flood Mid Bench None Bench Agriculture Medium (10-40%) Yes 30 72 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 16 Flood Mid Bench None Bench Agriculture High (>40%) Yes 80 73 High RIGHT_BA South Thompson River 11/6/2015 0:00 11:50:38am KH;BH;TT;JP Over cast 16 Cliff/Bluff None Steep (20-60) Natural Area None No 5 74 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 17 Other None Bench Agriculture High (>40%) Yes 100 75 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 18 Flood Low Bench None Bench Agriculture High (>40%) Yes 100 76 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 18 Gravel None Low (5-20%) Rural High (>40%) Yes 80 77 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 18 Flood Low Bench None Bench Agriculture High (>40%) No 70 78 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Sand None Bench Rural High (>40%) No 70 79 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Flood Mid Bench None Bench Agriculture Medium (10-40%) No 50 80 Very High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Confluence None Bench Natural Area Medium (10-40%) No 40 81 Very High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Flood Low Bench None Bench Natural Area Low (<10%) No 20 82 High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Gravel None Bench Rural Medium (10-40%) No 40 83 Very High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Gravel None Bench Natural Area Low (<10%) No 10 84 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Gravel None Bench Rural Medium (10-40%) No 40 85 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 19 Flood Low Bench Road Bench Rural Medium (10-40%) No 40 86 Moderate RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 20 Other None Bench Rural Medium (10-40%) Yes 40 87 Very High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 20 Flood Mid Bench None Bench Rural Low (<10%) Yes 10 88 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 21 Gravel None Low (5-20%) Agriculture High (>40%) Yes 90 89 High RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 21 Flood Mid Bench None Bench Natural Area Low (<10%) No 5 90 Low RIGHT_BA South Thompson River 11/6/2015 0:00 KH;BH;TT;JP Over cast 21 Other None Moderate (5-20%) Rural High (>40%) No 95 15-1588 Appendix B May 2016
PCTNATURAL PHOTONUM TAPE_NUMB VIDEO_TIME CMMNT_CLAS CLIFF_BLUF ROCKY GRAVEL SAND CONFLUENCE WETLAND OTHER FLOOD_LOW_ FLOOD_MID_ FLOOD_HIGH 90 Railway traverses hillslope above riverbank/lakeshore and seasonally flooded field in upper portion 0 0 0 0 0 50 0 50 0 0 60 0 0 0 0 0 25 0 25 50 0 90 0 0 0 0 0 40 0 40 20 0 90 Willow thicket along river bank with previously cleared mid flood bench beyond top of bank 0 0 0 0 0 0 0 20 80 0 0 0 100 0 0 0 0 0 0 0 0 20 0 0 40 20 0 10 0 15 15 0 95 Seasonally flooded area with recreational disturbance 0 0 0 30 0 5 0 35 30 0 25 15-20 riparian band more intact in upper portion of segment 0 0 0 10 0 0 0 10 80 0 75 0 0 0 0 0 0 0 0 100 0 0 0 30 50 20 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 60 20 20 0 0 0 0 0 0 60 10-20m riparian fringe not recently modified, although historic armouring has occurred 0 30 20 20 0 0 0 10 20 0 5 0 20 60 0 0 0 0 10 10 0 60 0 10 50 0 0 0 0 10 30 0 20 0 0 0 80 0 0 0 0 20 0 40 discontinuous natural riparian fringe with extensive recreation use beyond top of bank 0 0 0 20 0 0 0 30 50 0 0 0 0 0 30 0 0 0 0 40 30 10 0 0 0 0 0 0 0 10 20 70 10 0 0 0 0 0 0 0 10 20 70 5 0 50 20 0 0 0 0 0 20 10 0 0 95 0 0 0 0 0 0 0 5 0 0 20 0 80 0 0 0 0 0 0 5 0 0 0 0 0 0 75 5 10 10 40 0 0 0 40 0 0 0 10 10 40 5 0 0 0 0 0 0 75 5 10 10 10 0 0 0 40 0 0 0 10 10 40 5 0 0 0 0 0 0 75 5 10 40 98 0 0 0 0 0 0 0 80 20 0 95 Historic evidence of disturbance with respect to old log dump. Rural mods. at top of segment 0 0 0 0 0 0 0 30 70 0 100 Campbell Creek 0 0 0 0 20 0 0 30 50 0 95 0 0 0 0 0 0 0 40 60 0 40 Industrial landuse proximal to Lefarge Bridge with more historic riparian altertions beyond 0 0 0 0 0 0 0 30 50 20 0 DSCN1394.jpg 0 15 0 0 0 0 0 25 50 10 50 DSCN1438.jpg Narrow low fllood band along river with adjacent steep bank with disturbed grassland/high flood benc 0 0 0 0 0 0 50 5 15 30 0 DSCN1474.jpg 0 75 0 0 0 0 25 0 0 0 90 DSCN1541.jpg 0 0 50 0 0 0 0 0 25 25 98 DSCN1567.jpg 0 0 30 0 40 0 0 10 20 0 50 DSCN1597.jpg 0 0 0 0 0 0 0 20 80 0 15 DSCN1661.jpg 0 0 0 0 0 0 55 10 10 25 60 DSCN1694.jpg 0 0 0 0 0 0 0 50 40 10 60 DSCN1754.jpg 0 0 20 0 0 0 0 40 30 10 30 DSCN1773.jpg Neds Creek fan 0 0 20 0 40 0 0 20 20 0 60 DSCN1777.jpg 0 0 0 0 0 0 30 70 0 0 90 DSCN1796.jpg 0 0 25 0 0 0 0 55 10 10 50 DSCN1825.jpg 0 0 15 15 0 0 0 40 30 0 40 DSCN1843.jpg 0 0 15 0 0 0 0 55 30 0 90 DSCN1868.jpg 0 0 0 0 0 0 0 30 70 0 98 DSCN1900.jpg 0 0 0 0 0 0 0 20 80 0 80 DSCN1914.jpg 0 0 30 10 0 0 0 0 20 40 10 DSCN1934.jpg 0 0 0 0 0 0 0 30 60 10 90 DSCN1941.jpg 0 0 0 0 0 20 0 70 10 0 80 DSCN2018.jpg 0 0 0 0 0 20 0 60 10 10 20 DSCN2045.jpg 0 50 0 0 0 0 0 20 15 15 0 DSCN2080.jpg 0 0 0 0 0 0 100 0 0 0 80 DSCN2138.jpg 0 0 0 0 0 0 0 10 10 80 90 DSCN2198.jpg 0 0 0 0 0 0 0 30 70 0 90 DSCN2221.jpg 0 0 0 20 0 20 0 50 10 0 10 DSCN2237.jpg 0 0 0 0 0 0 0 0 30 70 90 DSCN5524.jpg 0 0 0 0 0 0 0 20 80 0 60 DSCN5579.jpg 0 0 0 0 0 15 20 20 15 30 0 DSCN5623.jpg 0 0 0 0 0 0 100 0 0 0 75 DSCN5649.jpg Small natural area with adjacent cultivated field 0 0 0 0 0 15 0 35 50 0 60 DSCN5684.jpg 0 0 15 0 40 0 0 15 30 0 80 0 0 0 0 0 0 0 60 40 0 90 0 0 0 0 0 20 0 50 30 0 5 0 0 0 0 0 20 40 30 10 0 95 0 0 0 0 0 20 0 80 0 0 95 Seaonally flooded field (hay) 0 0 0 0 0 50 0 50 0 0 30 0 0 0 0 0 60 0 40 0 0 90 0 0 0 20 0 10 0 20 50 0 0 Airport 0 100 0 0 0 0 0 0 0 0 0 entire bank aroured but riparian area moderately intact - although perforated 0 50 0 0 0 0 0 0 0 50 0 Mixed rock, rip rap, and concrete debris armouring bank 0 50 0 0 0 0 0 0 0 50 0 More tree canopy along bank comapred to segment 10 0 0 0 0 0 0 50 0 0 50 85 DSCN522.jpg 0 0 0 0 0 0 0 20 60 20 10 0 0 0 0 0 0 0 10 90 0 20 Intermittently natural riparian fringe 0 0 0 0 0 0 0 20 70 10 80 Predominnatly natural riparian band with perimeter road setback 0 0 0 0 0 0 0 10 70 10 15-1588 Appendix B May 2016
PCTNATURAL PHOTONUM TAPE_NUMB VIDEO_TIME CMMNT_CLAS CLIFF_BLUF ROCKY GRAVEL SAND CONFLUENCE WETLAND OTHER FLOOD_LOW_ FLOOD_MID_ FLOOD_HIGH 20 0 0 0 0 0 0 0 0 80 20 50 0 0 0 0 0 0 0 0 100 0 0 0 100 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 10 0 0 0 0 0 0 0 0 70 30 60 0 0 0 0 0 0 0 30 60 10 90 0 0 0 20 30 0 0 20 30 0 100 0 0 0 0 20 0 0 40 40 0 10 DSCN0015.jpg 0 10 30 0 0 0 20 10 30 0 0 0 0 5 95 0 0 0 0 0 0 10 0 10 0 0 0 0 0 20 70 0 90 Low flood fringe with adjacent mid flood community 0 0 0 0 0 20 0 50 30 0 60 DSCN0731.jpg 0 0 0 0 0 0 100 0 0 0 30 0 0 0 0 0 0 30 50 20 0 98 DSCN0878.jpg 0 0 0 0 0 25 0 50 25 0 40 DSCN0890.jpg 0 0 15 0 0 0 0 25 60 0 95 DSCN0902.jpg Historic alteration/disturbance but naturalizing 0 0 0 0 0 0 0 20 80 0 5 DSCN0916.jpg 0 0 0 25 0 0 30 10 35 0 60 DSCN0996.jpg 0 0 0 0 0 0 0 40 50 10 0 DSCN0992.jpg Rip rap with LWD revetment 0 20 0 0 0 0 0 0 80 0 90 DSCN1024.jpg 0 0 0 0 0 0 80 10 10 0 100 DSCN1057.jpg 0 0 0 0 0 0 0 70 30 0 60 DSCN1120.jpg 0 0 0 0 50 0 0 25 25 0 30 DSCN1130.jpg 0 0 0 0 0 0 70 10 20 0 95 DSCN1145.jpg 0 0 0 0 0 0 0 60 40 0 5 DSCN1169.jpg 0 0 0 0 0 0 0 0 100 0 20 DSCN1216.jpg 0 0 0 0 0 0 0 50 50 0 30 DSCN1224.jpg 0 0 0 0 40 0 0 30 30 0 0 DSCN1241.jpg High vertical silt bank/bluff with gravel toe 0 0 20 0 0 0 80 0 0 0 60 DSCN1249.jpg 0 0 20 0 0 0 20 20 40 0 0 DSCN1255.jpg 0 0 0 0 0 0 100 0 0 0 60 DSCN1263.jpg 0 0 10 0 0 0 0 50 40 0 80 DSCN1283.jpg 0 0 0 0 0 20 0 50 30 0 30 DSCN1444.jpg 0 0 0 0 0 0 10 50 40 0 30 DSCN1491.jpg 0 0 0 0 0 0 25 45 30 0 5 DSCN1511.jpg 0 0 0 0 0 0 0 30 50 20 60 DSCN1545.jpg 0 0 0 0 0 0 0 50 30 10 90 DSCN1565.jpg 0 0 0 0 0 20 20 40 20 0 60 DSCN1572.jpg 0 50 30 0 0 0 0 10 0 0 30 DSCN1605.jpg 0 0 10 0 0 0 0 10 80 0 50 DSCN1646.jpg 0 0 0 0 0 0 0 20 80 0 60 DSCN1655.jpg 0 0 0 0 0 0 0 60 40 0 30 DSCN1687.jpg 0 0 0 0 0 0 0 70 30 0 50 DSCN1696.jpg 0 0 0 0 40 20 0 20 20 0 30 DSCN1701.jpg 0 0 0 0 0 0 30 60 10 0 100 DSCN1717.jpg 100 0 0 0 0 0 0 0 0 0 40 DSCN1723.jpg 0 0 0 0 0 0 0 60 40 0 5 DSCN1725.jpg 0 0 0 0 0 0 0 80 20 0 90 DSCN1739.jpg 0 0 50 0 0 0 20 10 20 0 20 DSCN1750.jpg 0 0 40 0 0 0 0 30 30 0 60 DSCN1758.jpg 0 0 40 0 0 0 30 10 20 0 0 DSCN1779.jpg 0 0 10 20 5 0 0 45 20 0 70 DSCN1814.jpg 0 0 0 10 0 0 0 75 15 0 10 DSCN1845.jpg 0 0 0 0 0 0 0 80 20 0 70 DSCN1861.jpg 0 0 0 0 0 0 0 80 20 0 70 DSCN1869.jpg Higher benched terrace 0 0 0 10 0 0 0 40 50 0 20 DSCN1905.jpg 0 0 0 0 0 0 0 70 30 0 95 DSCN1911.jpg 80 10 0 0 0 0 0 0 0 0 0 DSCN1928.jpg 0 0 0 0 0 0 90 10 0 0 0 DSCN1945.jpg 0 0 0 0 0 0 40 50 10 0 20 DSCN2030.jpg 0 10 50 0 0 0 0 20 10 10 30 DSCN2036jpg 0 0 20 0 0 10 0 40 30 0 30 DSCN2040.jpg 0 0 0 40 0 15 0 15 30 0 50 DSCN2057.jpg 0 0 0 0 0 0 0 40 60 0 60 DSCN2058.jpg 0 0 30 0 40 0 0 0 30 0 80 DSCN2074.jpg 0 0 0 0 0 0 0 60 40 0 60 DSCN2092.jpg 0 0 40 0 0 0 0 30 30 0 90 DSCN2100.jpg 0 0 40 0 0 0 0 10 30 20 60 DSCN2120.jpg 0 0 40 0 0 0 20 20 20 0 60 DSCN2128.jpg Low flood with adjacent mid flood fringe and road 0 0 30 0 0 0 0 40 30 0 60 DSCN2171.jpg 0 0 0 0 0 0 45 10 20 25 90 DSCN2227.jpg 0 0 10 0 0 0 0 20 70 0 10 DSCN2242.jpg Gravel shore with steep eroding bank to high bench on top. 0 0 40 0 0 0 20 0 10 30 95 DSCN5584.jpg 0 0 10 0 0 0 0 35 55 0 5 DSCN5584.jpg Steep silt-gravel bank eroding and providing gravel source for adjacent spawning 0 0 50 0 0 0 50 0 0 0 15-1588 Appendix B May 2016
STYPE_COMM AGRICULTUR COMMERCIAL CONSERVATI FORESTRY INDUSTRIAL INFRASTRUC INSTITUTIO MULTI_FAMI NATURAL_AR PARK RECREATION RURAL SINGLE_FAM URBAN_PARK Kamloops Lake 10 0 0 0 0 10 0 0 80 0 0 0 0 0 70 0 0 0 0 0 0 0 30 0 0 0 0 0 20 0 0 0 0 0 0 0 80 0 0 0 0 0 10 0 0 0 0 0 0 0 90 0 0 0 0 0 Shore is completely armoured with rip rap 0 0 0 0 100 0 0 0 0 0 0 0 0 0 Mixed embedded gravel and sand. Road floows top of bank with adjacent rail and aggregate extraction 0 0 0 0 30 40 0 0 15 0 0 15 0 0 0 0 0 0 0 0 0 0 50 0 0 50 0 0 Shallow sand bar adjacent vegetated shoreline 0 0 0 0 60 10 0 0 30 0 0 0 0 0 0 0 0 0 25 0 0 0 75 0 0 0 0 0 steep grvel-cobble bank nearly devoid of vegetation 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 25 75 0 0 0 0 0 0 0 0 Eroding silt bluff with rubble and concrete debris along toe 0 10 0 0 50 40 0 0 0 0 0 0 0 0 0 0 0 0 0 60 0 0 30 0 10 0 0 0 Opposite North Thompson River confluence 0 0 0 0 0 60 0 0 10 0 30 0 0 0 0 0 0 0 0 0 0 0 50 0 50 0 0 0 Beach 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 20 0 80 0 0 0 0 0 0 0 0 0 0 30 0 0 10 0 60 0 0 0 0 0 0 10 0 90 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 50 50 0 0 0 0 0 0 0 0 Narrow discontinuous riparian fringe along upper slope 0 0 0 0 100 0 0 0 0 0 0 0 0 0 Silt-sand vertical eroding bank 0 0 0 0 40 60 0 0 0 0 0 0 0 0 Anthropognic shore type 0 0 0 0 0 0 0 0 0 0 0 0 100 0 Silt-sand vertical bank. Rural agricultural beyond TOB 20 0 0 0 0 30 0 0 0 0 0 50 0 0 Anthropognic shore type 0 0 0 0 0 0 0 0 0 0 0 0 100 0 Silt-sand vertical bank. Rural agricultural beyond TOB 20 0 0 0 0 40 0 0 0 0 0 40 0 0 Anthropognic shore type 0 0 0 0 0 0 0 0 0 0 0 0 100 0 Railway set back from top of bank and having low impact on channel and riparian character 0 0 0 0 0 5 0 0 95 0 0 0 0 0 0 0 0 0 0 0 0 0 95 0 0 5 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 95 0 0 5 0 0 0 0 0 0 40 0 0 0 10 0 0 50 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 25 0 0 75 0 0 Steep armoured bank 0 0 0 0 0 100 0 0 0 0 0 0 0 0 Gravel shore with Mid bench comms along slope toe and high bench and grassland beyond TOB 0 0 0 0 25 0 0 0 50 0 0 25 0 0 Monte Creek 0 0 0 0 0 0 0 0 95 0 0 5 0 0 Russian Olive disclimax riparian 10 0 0 0 0 0 0 0 0 0 0 75 15 0 20 0 0 0 0 30 0 0 25 0 0 25 0 0 Russian Olive predominant tree - displacing cottonwood 60 0 0 0 0 0 0 0 20 0 0 20 0 0 45 0 0 0 0 0 0 0 35 0 0 20 0 0 30 0 0 0 0 0 0 0 30 0 0 40 0 0 Adajacent shrub 0 0 0 0 0 30 0 0 70 0 0 0 0 0 low gravel bench/lateral bar transitions to low flood bench to mid flood elevation 10 0 0 0 0 0 0 0 60 0 0 30 0 0 0 0 0 0 0 0 0 0 40 0 0 60 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 90 0 0 0 0 0 10 0 0 0 0 0 0 0 100 0 0 0 0 0 40 0 0 0 0 0 0 0 20 0 0 40 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 80 0 0 20 0 0 0 0 0 0 0 40 0 0 60 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 High silt bank - mix roding and armoured 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 30 0 0 40 0 0 30 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Rural road along top of bank 60 0 0 0 0 0 0 0 0 0 0 40 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 90 0 0 10 0 0 35 0 0 0 0 0 0 0 30 0 0 35 0 0 Steep eroding bank 80 0 0 0 0 0 0 0 0 0 0 20 0 0 30 0 0 0 0 0 0 0 70 0 0 0 0 0 Chase Creek 0 0 0 0 0 0 0 0 40 0 20 40 0 0 Kamloops Lake 30 0 0 0 0 0 20 0 50 0 0 0 0 0 Kamloops Lake 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Other relating to road fill into low flood and shore marsh communities 0 0 0 0 0 80 0 0 20 0 0 0 0 0 Adjacent grassland shrub-steppe above bench 0 0 0 0 0 20 0 0 80 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Private rural road and farming occur adjacent to top of bank 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Prominent lateral sand bar 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Entire bank hard armoured 0 100 0 0 0 0 0 0 0 0 0 0 0 0 broadleaf canopy (Aspen and cottonwood) along top of bank 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 Concrete debris armouring nearly 50% of bank 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 30 30 0 0 0 40 0 Urban encroachment to top of bank 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 15-1588 Appendix B May 2016
STYPE_COMM AGRICULTUR COMMERCIAL CONSERVATI FORESTRY INDUSTRIAL INFRASTRUC INSTITUTIO MULTI_FAMI NATURAL_AR PARK RECREATION RURAL SINGLE_FAM URBAN_PARK 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 20 20 0 0 0 0 0 0 60 Bank completely altered/armoured 0 0 0 0 0 0 0 0 0 0 0 0 100 0 Bank completely altered/armoured 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 60 0 0 0 0 0 0 0 0 0 0 40 0 0 0 0 0 0 0 20 40 0 0 0 0 0 40 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Narrow riparian fringe - upland industrial alterations 0 0 0 0 95 5 0 0 0 0 0 0 0 0 Steep sandy bank 0 0 0 0 100 0 0 0 0 0 0 0 0 0 Campground, trailer park and interrelated rural disturbance 0 0 0 0 0 0 30 0 0 0 0 40 30 0 0 0 0 0 0 0 0 0 30 0 0 70 0 0 Unvegetated silt bank 50 0 0 0 0 20 0 0 0 0 0 20 0 0 low flood bench fringe along slope toe with other areas being silt bank 20 0 0 0 0 0 0 0 30 0 0 50 0 0 0 0 0 0 0 0 0 0 90 0 0 10 0 0 0 0 0 0 0 0 0 0 30 0 0 70 0 0 0 0 0 0 0 0 0 0 80 0 0 20 0 0 Vertical, unvegetated silt bank - active erosion. 80 0 0 0 0 0 0 0 0 0 0 20 0 0 80 0 0 0 0 0 0 0 20 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 Silt bank/bluff with grassland (shrub-steppe) beyond top of bank 0 0 0 0 0 0 0 0 80 0 0 20 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Russian Olive displacing native mid flood bench vegetation 0 0 0 0 0 0 0 0 50 0 0 50 0 0 Silt bank, partly armoured with road following top of bank 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Russian Olive predominant tree - displacing cottonwood 0 0 0 0 0 0 0 0 0 0 0 100 0 0 45 0 0 0 0 0 0 0 0 0 0 55 0 0 0 0 0 0 0 0 0 0 30 0 0 0 0 0 Silt bluff with partly armoured rock toe. 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 20 0 0 80 0 0 Actively eroding silt bank 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 40 0 0 60 0 0 Narrow low flood and mid flood bands with road occuring upslope adajcent through more arid (shrub-st 10 0 0 0 10 0 0 0 40 0 0 40 0 0 Narrow low flood fringe and Russian Olive mid level band with adajcent golf course 0 20 0 0 0 0 0 0 0 0 60 20 0 0 40 0 0 0 0 0 0 0 0 0 0 60 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 5 0 0 95 0 0 Backwater area with organic substrates 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 Russian Olive disclimax riparian 0 0 0 0 0 0 0 0 0 0 0 100 0 0 30 0 0 0 0 0 0 0 30 0 0 40 0 0 Narrow disclimax Russian Olive band along fields 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Shallow water wetland downstream of gravel fan (ephemeral tributary) 0 0 0 0 0 0 0 0 0 0 0 100 0 0 Vertical silt bank with sloughing occurs at upstream end of segment 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Silt bluff 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Narrow low and mid flood bench along toe of steep hillslope 60 0 0 0 0 0 0 0 0 0 0 40 0 0 80 0 0 0 0 0 0 0 0 0 0 20 0 0 Gravel and silt bank. Narrow Russian Olive band along mid slope below TOB. Shrub-steppe beyond TOB. 10 0 0 0 0 0 0 0 90 0 0 0 0 0 Gravel fan associated with ephemeral tributary - not classed as confluence due to ephemeral nature 60 0 0 0 0 0 0 0 0 0 0 40 0 0 70 0 0 0 0 0 0 0 40 0 0 0 0 0 Ephemeral tributary fana are minor gravel source 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Urban subdivision across road 0 0 0 0 0 0 0 0 80 0 0 20 0 0 80 0 0 0 0 0 0 0 0 0 0 20 0 0 60 0 0 0 0 0 0 0 20 0 0 20 0 0 70 0 0 0 0 0 0 0 30 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 Eroding silt bank with high bench above river with persistent livestock impacts 100 0 0 0 0 0 0 0 0 0 0 0 0 0 Unstable but low bench still present 85 0 0 0 0 0 0 0 0 0 0 15 0 0 10 0 0 0 0 0 0 0 0 0 0 90 0 0 90 0 0 0 0 0 0 0 10 0 0 0 0 0 60 0 0 0 0 0 0 0 20 0 0 20 0 0 Associated steep vegetated silt bank to top of bank 50 0 0 0 0 0 0 0 25 0 0 25 0 0 0 0 0 0 0 0 0 0 70 0 0 30 0 0 Low flood bench and adjacent mid flood ecosystem 0 0 0 0 0 0 0 0 90 0 0 10 0 0 0 0 0 0 0 0 0 0 25 0 0 75 0 0 0 0 0 0 0 0 0 0 85 0 0 15 0 0 Primarily gravel shore with adajcen low flood and disturbed mid flood with disturbed gra 0 0 0 0 0 0 0 0 0 0 0 100 0 0 0 0 0 0 0 0 0 0 60 0 0 40 0 0 Narrow mid flood fringe along slope toe with steep bank-disturbed high bench and grassland beyon 40 0 0 0 0 0 0 0 0 0 0 60 0 0 0 0 0 0 0 0 0 0 80 0 0 20 0 0 60 0 0 0 0 0 0 0 0 0 0 40 0 0 0 0 0 0 0 0 0 0 95 0 0 5 0 0 40 0 0 0 0 0 0 0 0 0 0 60 0 0 15-1588 Appendix B May 2016
LANDU_COMM RETAIN_WAL PERRETAIN_ RETAIN_MAT DOCKS DOCKS_KM BOAT_HOUSE GROYNES GROYNES_KM BOAT_LAUNC PERRAIL_MO PERROAD_MO MARIN_RAIL MARINAS SUB_MODIFI PERSUB_MOD Railway and seasonlly flooded field - although area largely natural 0 0 0 0 0 0 0 0 0 0 5 0 No 0 Seasonally flooded hay field 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 100 Rock 0 0 0 0 0 0 0 0 0 0 Yes 100 2 25 Rock 0 0 0 0 0 0 0 0 0 0 Yes 25 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 18 0 0 0 0 0 0 0 0 0 0 No 0 1 30 Rock 0 0 0 0 0 0 0 0 0 0 Yes 30 Road and rail follow/establish top of bank 1 20 Rock 0 0 0 0 0 0 0 90 0 0 Yes 90 3 50 Mixed 0 0 0 0 0 0 100 0 0 0 Yes 80 3 20 Rock 0 0 0 0 0 0 100 0 0 0 Yes 20 Railway 3 100 Concrete 0 0 0 0 0 0 100 0 0 0 Yes 30 Moderately natural riparian fringe with adjacent recreation 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 Yes 50 3 30 Rock 2 0 0 0 0 2 0 0 0 0 Yes 5 0 0 8 0 0 0 0 0 0 0 0 0 Yes 10 1 10 Rock 2 0 0 0 0 0 0 10 0 0 Yes 10 4 65 Rock 6 0 0 0 0 0 0 0 0 0 No 0 1 40 Rock 0 0 0 0 0 0 0 0 0 0 No 0 1 100 Rock 0 0 0 0 0 0 0 0 0 0 Yes 100 3 48 Rock 0 0 0 0 0 0 0 0 0 0 Yes 48 41 96 Mixed 41 0 0 0 0 1 0 0 0 0 Yes 10 0 0 0 0 0 0 0 0 30 0 0 0 No 0 10 42 Mixed 34 0 0 0 0 1 0 0 0 0 Yes 10 1 15 Rock 2 0 0 0 0 0 0 0 0 0 No 0 24 50 Mixed 71 0 0 0 0 0 0 0 0 0 Yes 25 1 1 Rock 0 0 0 0 0 0 0 0 0 0 No 0 1 5 Rock 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 2 21 Rock 1 0 0 0 0 0 0 0 0 0 Yes 20 1 15 Rock 13 0 0 0 0 0 0 0 0 0 Yes 15 0 0 1 0 0 0 0 0 0 0 0 0 No 0 1 86 Rock 0 0 0 0 0 0 100 0 0 0 Yes 86 0 0 0 0 0 0 0 0 10 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 9 0 0 0 0 0 15 0 0 0 No 0 0 0 0 0 0 0 0 0 30 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 25 0 0 0 No 0 0 0 1 0 0 0 0 0 0 0 0 0 No 0 0 0 3 0 0 0 0 0 0 5 0 0 No 0 Persistent livestock use 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Rail and Hwy encroachment 0 0 0 0 0 0 0 0 30 0 0 0 No 0 Rail and Hwy encroachment 1 30 Rock 0 0 0 0 0 0 100 0 0 0 Yes 30 1 16 Rock 0 0 0 0 0 0 80 0 0 0 Yes 16 0 0 0 0 0 0 0 1 30 0 0 0 No 0 Moderately intact riparian band 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Side channel an backwater 0 0 0 0 0 0 0 0 0 50 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 1 0 0 0 0 0 0 0 0 0 Yes 0 3 28 Rock 2 0 0 0 0 0 0 0 0 0 Yes 28 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 10 Rock 1 0 0 0 0 1 0 0 0 0 Yes 12 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 Yes 70 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Disturbance more attributed to seaonal mowing of grasses within low flood graminoid community 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Airport beyond natural area 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 100 Rock 1 0 0 0 0 1 0 0 0 0 Yes 100 1 100 Rock 0 0 0 0 0 0 0 0 0 0 Yes 100 3 100 Mixed 3 0 0 0 0 0 0 5 0 0 Yes 95 2 49 Concrete 2 0 0 0 0 0 0 5 0 0 Yes 49 Natural riparian band with urban developmnt set bank 0 0 0 0 0 0 0 0 0 0 0 0 No 0 2 37 8 0 0 0 0 0 0 5 0 0 Yes 37 1 3 Rock 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 10 0 0 No 0 15-1588 Appendix B May 2016
LANDU_COMM RETAIN_WAL PERRETAIN_ RETAIN_MAT DOCKS DOCKS_KM BOAT_HOUSE GROYNES GROYNES_KM BOAT_LAUNC PERRAIL_MO PERROAD_MO MARIN_RAIL MARINAS SUB_MODIFI PERSUB_MOD 1 2 Rock 0 0 0 0 0 0 0 0 0 0 No 0 0 0 1 0 0 0 0 0 0 20 0 0 Yes 10 1 100 Rock 0 0 0 0 0 0 0 100 0 0 Yes 100 1 100 Rock 0 0 0 0 0 0 0 0 0 0 Yes 100 14 43 Mixed 12 0 0 0 0 0 0 0 0 0 Yes 43 1 3 Mixed 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 2 23 Rock 0 0 0 0 0 0 30 0 0 0 Yes 0 1 37 Mixed 0 0 0 0 0 0 0 0 0 0 No 0 14 39 Mixed 1 0 0 0 0 0 0 0 0 0 Yes 39 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 2 Rock 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 3 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 38 Rock 1 0 0 0 0 0 0 0 0 0 Yes 38 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 8 0 0 0 0 0 0 0 100 0 0 Yes 8 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Rock and LWD stabilization and habitat enhancement 1 100 Rock 0 0 0 0 0 0 0 0 0 0 No 0 3 54 Mixed 1 0 0 0 0 0 0 0 0 0 Yes 54 1 43 Rock 0 0 0 0 0 0 0 0 0 0 Yes 43 1 17 Rock 1 0 0 0 0 0 0 40 0 0 Yes 17 0 0 0 0 0 0 0 0 0 30 0 0 No 0 1 20 Rock 0 0 0 0 0 0 0 100 0 0 Yes 20 0 0 0 0 0 0 0 1 0 10 0 0 No 0 0 0 0 0 0 0 0 0 0 15 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 2 0 0 0 0 0 0 0 0 0 No 0 3 17 Mixed 9 0 0 0 0 0 0 0 0 0 Yes 17 0 0 7 0 0 0 0 0 0 0 0 0 Yes 2 0 0 0 0 0 0 0 0 0 20 0 0 No 0 0 0 2 0 0 0 0 0 0 0 0 0 No 0 8 18 Mixed 17 0 0 0 0 0 0 0 0 0 Yes 18 2 22 Mixed 2 0 0 0 0 0 0 10 0 0 Yes 22 0 0 3 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 1 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 1 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Heavily grazed site 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 1 0 5 0 0 No 0 0 0 1 0 0 0 0 0 0 2 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 Heavier grazing pressure 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 1 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 More intact riparian fringe 0 0 0 0 0 0 0 0 0 0 0 0 No 0 1 5 Wood 1 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 0 0 0 0 0 0 0 0 0 0 0 0 No 0 15-1588 Appendix B May 2016
COMMNT_MOD L_BKSTBILI PCTERODING L_BANK_MAT L_COMMENT VETERANS SNAGS CMMNT_FLRA CMMNT_FAUN CORR_TYPE RCVR_TYPE GPS_DATE DATAFILE LENGTH Bank High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 3694.975494 Left High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 13847.65662 Left High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 944.6028467 Left Low 80 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1243.463784 Left High 0 RipRap No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1906.108456 Left Medium 10 Gravel No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1411.430414 Left Medium 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1132.80852 Left Medium 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1061.839918 Left Medium 5 Fines No 25-May Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1034.892421 Left High 0 Cobble No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1338.675449 Left High 0 RipRap No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 335.3624697 Left Medium 30 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1489.138284 Left High 5 Cobble Mixed silt/sand and rock armouring No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 634.6829332 Left High 0 Gravel No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 335.0805903 Left High 1 Gravel No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 417.940366 Left Beach grooming High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 244.1221053 Left Beach grooming High 0 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 2290.229377 Left Beach grooming High 0 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 326.5544782 Left High 8 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 299.2929303 Left Medium 0 Fines Retaining structures providing current integrity No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 326.3686013 Left High 0 RipRap No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 476.8057859 Left High 0 RipRap No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 396.9671322 Left Low 27 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1649.738848 Left High 5 RipRap Extensive armouring and retaining with concrete, rock, and rip rap. No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1518.550952 Left Low 27 Fines No 25-May Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 3207.618514 Left High 0 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 1309.645168 Left Low 37 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 610.5836543 Left High 0 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 2439.643802 Left Low 42 Fines Disturbed shrub-steppe grassland community beyond top of bank No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 3021.976559 Left Medium 56 Fines low to moderate severity erosion - more just sloughing along lower portion of low flood bench No 25-May Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 950.4437229 Left High 0 Gravel No <5 Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 242.9160272 Left High 0 Fines No <5 Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 703.9134843 Left Low 20 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 3882.365874 Left Medium 0 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 858.2122347 Left Medium 15 Fines Minor erosion at upstream en of segment No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 534.3506704 Left Medium 12 RipRap No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 786.2917254 Left Medium 10 Fines About 160 m of severe erosion just upstream of important Chinook spawning habitat No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 2250.630126 Left High 15 Fines Minor erosion at downstream end of segment No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 612.8772922 Left Medium 18 Fines No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 2400.674696 Left Low 42 Fines No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1150.829556 Left High 0 Fines Broad, shallow instream abd flood benh to riprian fringe. No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 3469.015439 Left High 8 Fines No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1820.806363 Left High 0 Gravel No 25-May Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 549.7514599 Left High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 905.4163204 Left High 0 Gravel No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1343.328196 Left High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 468.2002057 Left High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 741.3156352 Left High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1803.286741 Left High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 925.3162375 Left High 0 Gravel No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 920.9038651 Left High 0 Fines No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 545.5905187 Left High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 755.1633599 Left High 5 Fines minor slumping along low flood bench No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 2500.366534 Left High 0 RipRap No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1767.992198 Left Low 50 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1274.453278 Left Low 30 Fines Sloughing and minor to moderate erosion No >25 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 2864.873957 Left High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 934.3615663 Left High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1026.631598 Left High 0 Fines Along side channel No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 365.0429428 Left Medium 14 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1140.216455 Left Low 30 Fines No 25-May Postprocessed Code Geo 7X 11/9/2015 0:00 THOMP-RIM-NOV9.cor 1077.694903 Left Rip rap and rock/log spurs Erosion 47 Fines No No Postprocessed Code Geo 7X 11/9/2015 0:00 THOMP-RIM-NOV9.cor 926.3819537 Left Medium 25 Fines Minot erosion on face of low flood community No 25-May Postprocessed Code Geo 7X 11/9/2015 0:00 THOMP-RIM-NOV9.cor 336.6008894 Left High 0 Gravel No 25-May Postprocessed Code Geo 7X 11/9/2015 0:00 THOMP-RIM-NOV9.cor 934.6240237 Left High 0 Fines No >25 Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1700.881789 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 317.2235512 Right High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 532.8385741 Right High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 272.3574307 Right High 0 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 2273.150007 Right Medium 35 Fines Erosion on face of low flood bench No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1702.777246 Right High 0 Fines No 25-May Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 1834.924104 Right High 0 RipRap No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 2092.443068 Right High 0 RipRap No <5 Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 191.0611375 Right High 0 RipRap No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 862.92557 Right Medium 150 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 551.7092315 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 450.0055357 Right Medium 0 Fines sand and some gravel No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 612.4396313 Right High 0 Fines During low flows, channel predominantly graminoid low flood community No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1411.748884 Right High 0 Fines No 25-May Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1364.426373 Right 15-1588 Appendix B May 2016
COMMNT_MOD L_BKSTBILI PCTERODING L_BANK_MAT L_COMMENT VETERANS SNAGS CMMNT_FLRA CMMNT_FAUN CORR_TYPE RCVR_TYPE GPS_DATE DATAFILE LENGTH Bank Medium 0 Gravel No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1339.980732 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1227.258825 Right High 0 RipRap No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 338.7963316 Right High 0 RipRap No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 468.7759883 Right Medium 5 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 807.1994381 Right High 8 Fines No <5 Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 612.351729 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 555.0425899 Right High 15 Fines Erosion minor and stable bank from low flood graminoid and mid flood communities No 25-May Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 262.4291001 Right Medium 63 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 796.1477799 Right Asphalt and concrete debris dumped over bank to provide some armouring of the slope Low 78 Fines No No Postprocessed Code Geo 7X 11/2/2015 0:00 THOMP-RIM-NOV2.cor 378.6200647 Right Medium 18 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 2367.203993 Right High 10 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 826.4618726 Right Erosion 100 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 823.1196102 Right Erosion 67 Fines No No Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 2646.660626 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/3/2015 0:00 THOMP-RIM-NOV3.cor 1221.506136 Right Medium 16 Fines No <5 Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 578.2373276 Right Low 66 Fines No <5 Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 358.975145 Right Erosion 35 Fines High to extreme erosion No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 1692.431903 Right Medium 15 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 966.0396736 Right Low 56 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 173.9971943 Right Low 38 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 1159.323757 Right High 0 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 299.7828687 Right High 0 Gravel No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 324.4305887 Right Low 0 Fines Sloughing and unstable bank but No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 1097.468691 Right Medium 5 Fines Minor sloughing along outer margin of low flood bench No 25-May Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 1979.55216 Right High 0 Boulder Boulder and LWD placement No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 692.5041517 Right Medium 12 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 783.2524006 Right High 0 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 192.4817611 Right Erosion 68 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 323.39257 Right Low 69 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 360.8123977 Right Erosion 93 Fines No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 659.2139487 Right High 14 Fines Gravel becoming more prevalent in substrates as gradient begins to increase No No Postprocessed Code Geo 7X 11/4/2015 0:00 THOMP-RIM-NOV4.cor 424.5649656 Right High 0 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 3768.580981 Right Medium 15 Fines Eroding bank vertical silt scarp slough at toe No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1155.015071 Right Low 56 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 446.0408919 Right Wells excavted in channel High 0 Gravel No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 606.0504704 Right 10 instream wet wells excavated in mid channel bar High 0 Gravel No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1100.787459 Right Road cut up slope in shrub-steppe ecosystem Medium 0 Fines Sloughing of silt bank as stabilized moderately No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 782.6708464 Right High 0 Cobble No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 186.8144621 Right Medium 5 Fines Minor sloughing along toe No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1294.377267 Right 110 m of bank stabilization consists of old tires. Road set back from bank. Medium 16 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 876.9852729 Right High 0 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 646.6010296 Right High 0 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1054.961308 Right Informal boat launch (4x4) access High 0 Gravel No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 384.8073057 Right Medium 7 Fines Minor erosion occurs along margin of low flood bench but not No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 1386.269739 Right Medium 0 Fines Currently reasonably stable silt bluff No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 573.6520579 Right Medium 18 Fines No No Postprocessed Code Geo 7X 11/5/2015 0:00 THOMP-RIM-NOV5.cor 590.838984 Right Low 60 Fines outer margin of low bench sloughing/eroding No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 278.0276199 Right Medium 22 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 453.4885025 Right High 0 Gravel Minor bank instability where persistent livestock access occurs. No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 638.9688505 Right High 0 Gravel Gravel lower bank with low and mid flood fringe. Silt bank b No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 480.1151166 Right High 0 Fines No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 2356.494552 Right High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 776.9389468 Right High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 548.3437312 Right High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 882.741787 Right High 15 Fines Minor erosion No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1657.358871 Right High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 496.0802436 Right High 0 Bed_Rock No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 358.7561191 Right Erosion 100 Fines Severe erosion No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 919.2987389 Right Low 45 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 2204.447575 Right High 0 Gravel Gravel-cobble No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 663.1691858 Right High 0 Fines No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 331.763709 Right Low 16 Fines No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 733.9834835 Right Medium 15 Fines Marked erosion along bank is low severity No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 303.7383714 Right High 0 Gravel No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 303.59269 Right High 0 Fines No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1203.247449 Right Medium 0 Gravel Mid channel gravel bar promoting some scour along right bank No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 347.7197911 Right High 0 Gravel No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 754.594723 Right High 0 Gravel No No Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 768.6753272 Right High 0 Gravel No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1060.700015 Right Medium 25 Fines Minor erosion along bank generally from loss of riparian vegetation No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1589.601074 Right Medium 30 Fines Minor erosion along tow of low flood zone exposing sand No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 341.8069494 Right Low 85 Fines About 300 m of marked erosion is lower severity. No <5 Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 1637.775539 Right High 5 Fines Two steep silt bank with little to no mid flood fringe that are more unstable No 25-May Postprocessed Code Geo 7X 11/6/2015 0:00 THOMP-RIM-NOV6.cor 2087.035829 Right Erosion 710 Gravel No No Postprocessed Code Geo 7X 11/6/2015 0:00 948.7345233 Right 15-1588 Appendix B May 2016
SOURCETHM Shape_Length B_hd B_ld B_md B_n C_e C_hd C_md C_n CF FL_hd FL_ld FL_md FL_n FLG_hd FLG_ld FLG_md FLG_n FLS_ld FLS_md FLS_n FLS_ro FM_e FM_f FM_hd FM_ld Left_bank.shp 3694.975482 0 0 0 0 0 0 0 0 0 0 0 2765.285806 0 0 0 0 2025.435668 8501.983269 0 11290.52034 0 0 0 0 1133.113216 Left_bank.shp 1417.534775 0 0 0 0 0 0 0 0 81734.34091 0 0 0 0 1787.913285 0 10260.76046 0 0 2007.636252 0 0 0 0 1463.393815 0 Left_bank.shp 944.6028833 0 0 0 0 0 0 0 0 12919.26189 0 0 0 0 15787.93189 0 506.2203601 0 3491.683958 0 0 0 0 0 0 1436.90939 Left_bank.shp 1243.463729 0 0 0 0 0 0 0 0 38614.555 0 0 13382.41523 0 7881.674034 0 37308.49075 0 160.6603403 0 0 0 0 0 0 858.7777689 Left_bank.shp 1906.108452 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2066.868246 0 0 0 0 0 0 0 0 0 Left_bank.shp 1411.430462 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4143.186872 4184.21479 0 0 0 0 0 0 Left_bank.shp 1132.808479 0 0 0 0 0 0 0 0 0 0 0 0 0 68712.54349 0 0 0 3047.996462 0 0 0 0 0 0 0 Left_bank.shp 1061.839931 0 0 0 0 0 0 0 0 0 0 0 0 0 4432.745113 0 0 0 0 0 0 0 0 0 0 86.81529109 Left_bank.shp 1034.892434 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 42131.15898 Left_bank.shp 1338.675413 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 335.3624814 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1489.138334 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 634.6829144 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 335.0805703 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 417.9403787 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 244.1220732 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 2290.229438 0 5001.849335 0 0 0 0 0 0 0 0 1525.703366 0 0 320.5179047 0 0 0 0 0 0 0 0 0 0 20300.27522 Left_bank.shp 326.5544114 0 1.559402713 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 299.2929801 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 326.3685995 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 476.8058191 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1536.787467 0 0 4427.648411 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1649.733538 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1518.551002 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 3207.618464 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1309.645244 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 610.5835791 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1929.866543 0 0 Left_bank.shp 2439.643845 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 665.5536285 0 0 Left_bank.shp 3021.97653 0 0 0 701.196732 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4929.60682 0 0 Left_bank.shp 950.4437705 0 0 0 26072.88836 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 242.9160457 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2306.653867 Left_bank.shp 703.9134945 45467.01894 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 362.2771598 0 0 Left_bank.shp 3882.365827 3236.363648 0 0 0 0 0 0 0 51226.96923 0 0 0 0 0 0 0 0 0 0 0 0 0 503.6640822 0 8345.757235 Left_bank.shp 858.2122105 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 534.3506523 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 786.2917645 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 2250.630159 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 612.8940114 0 0 0 0 0 0 0 0 109.7065015 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 2400.674639 0 0 0 0 0 0 0 0 74667.46011 0 0 0 0 0 0 0 0 0 1835.144278 0 0 0 1349.72297 0 0 Left_bank.shp 1150.829527 0 0 0 0 0 0 0 0 40913.39998 0 0 0 0 0 0 0 0 0 0 0 0 0 10235.36047 0 0 Left_bank.shp 3469.291758 0 0 0 0 0 0 0 0 206159.219 0 0 0 0 0 0 0 0 0 7076.996877 0 0 0 8248.504537 0 0 Left_bank.shp 1820.990266 0 0 0 0 0 0 0 0 5004.98793 0 0 0 0 0 0 0 0 0 0 0 0 0 8153.327963 0 0 Left_bank.shp 549.8116517 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2083.616659 0 0 Left_bank.shp 905.4162803 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1343.32826 0 0 0 0 0 0 0 0 28415.31946 0 0 0 0 0 0 0 0 0 0 0 0 0 2661.816593 0 0 Left_bank.shp 468.2001922 0 0 0 0 0 0 0 0 22637.97841 0 0 0 0 0 0 0 0 0 0 0 0 0 2580.142145 0 0 Left_bank.shp 741.315564 847.0698971 0 0 0 0 0 0 0 47651.49356 0 0 0 0 0 0 0 0 0 0 0 0 0 5216.922218 0 0 Left_bank.shp 1803.286831 14572.89773 3115.826427 0 40138.67641 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 925.3161595 0 0 0 0 0 0 0 0 5869.195481 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 920.9038543 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 545.5905287 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 755.1633819 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 19634.26231 0 0 5527.04454 0 0 0 0 0 Left_bank.shp 2500.366542 0 0 0 0 3341.281068 1671.828576 9361.537605 60348.75511 0 0 0 0 0 0 0 0 0 0 0 27109.02424 0 0 0 0 0 Left_bank.shp 1767.992212 0 0 0 0 0 0 2994.209929 42468.15251 0 0 0 0 1279.301334 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1274.453291 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 2864.873962 0 0 0 0 0 0 0 0 13030.4409 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 934.3615415 0 0 0 0 0 0 0 0 72835.82442 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1026.63159 0 0 0 0 0 0 0 0 51745.41793 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 365.0429282 0 0 0 0 0 0 0 0 7356.660137 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 1140.216445 0 0 0 0 0 0 0 0 215.6623228 0 0 0 0 5642.756692 0 0 0 0 0 0 0 0 0 1938.510306 0 Left_bank.shp 1077.694991 0 0 0 0 0 0 0 0 20007.16496 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5141.003214 Left_bank.shp 926.3819266 0 0 0 0 0 0 0 0 66164.65888 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 336.6009014 0 0 0 0 0 0 0 0 22076.11699 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Left_bank.shp 934.6239741 0 0 0 0 0 0 0 0 111.0956289 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1700.881791 0 0 0 0 0 0 0 0 52763.65563 0 0 0 0 0 10123.49433 0 0 8158.936461 0 0 0 0 884.1368192 0 1090.95234 Right_bank.shp 317.2235238 0 0 0 0 0 0 0 0 4924.631605 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 601.540286 Right_bank.shp 532.8385712 0 0 0 0 0 0 0 0 0 78.85913355 0 0 0 0 0 0 0 0 0 0 0 0 0 0 704.5394823 Right_bank.shp 272.3574293 0 0 0 0 0 0 0 0 367.7648528 7980.486504 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2273.150044 0 0 0 0 0 0 0 0 186645.3199 103.5886862 0 0 0 0 0 0 0 0 0 0 0 0 3751.096926 0 0 Right_bank.shp 1702.777266 0 0 0 0 0 0 0 0 87886.35809 0 0 0 0 0 0 0 0 4753.048592 0 0 0 0 27086.99415 0 0 Right_bank.shp 1834.924038 0 0 0 0 0 0 0 0 3767.029463 0 0 0 0 0 3936.250192 0 11178.06774 8485.339526 0 13049.12542 0 0 0 12422.37558 0 Right_bank.shp 2092.443107 0 0 0 0 0 0 0 0 3125.740227 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 191.0611488 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 862.9256053 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 551.7091617 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 450.0055701 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 612.4396244 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1411.748876 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1364.426406 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 15-1588 Appendix B May 2016
SOURCETHM Shape_Length B_hd B_ld B_md B_n C_e C_hd C_md C_n CF FL_hd FL_ld FL_md FL_n FLG_hd FLG_ld FLG_md FLG_n FLS_ld FLS_md FLS_n FLS_ro FM_e FM_f FM_hd FM_ld Right_bank.shp 1339.980683 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1227.289453 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 289.9966382 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 468.7759778 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 807.1994556 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 612.3516732 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 555.0426457 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 262.4290866 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2251.593474 0 0 0 0 0 0 0 0 Right_bank.shp 796.1478248 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6683.713754 Right_bank.shp 378.6200235 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2367.203952 0 0 0 0 0 0 0 0 114.7687406 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 826.4619113 0 0 0 0 0 0 0 0 39079.97301 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 823.1196137 0 0 0 0 0 0 0 0 71969.81875 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2646.660679 0 0 0 0 0 0 0 0 34647.5755 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2337.243006 Right_bank.shp 1221.5061 0 0 0 42775.33944 0 0 0 0 0 0 0 0 0 0 0 0 5134.170183 0 0 221.5666682 0 0 0 0 6322.472545 Right_bank.shp 578.2373117 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8320.484485 Right_bank.shp 358.9751657 0 0 0 16958.69304 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 643.0758163 Right_bank.shp 1692.431885 0 0 0 0 0 0 0 0 103704.4485 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2272.958336 Right_bank.shp 966.0397177 0 0 0 0 0 0 0 0 54792.8083 0 0 0 0 0 0 0 0 0 0 0 0 1452.768841 0 0 9770.045519 Right_bank.shp 173.9971916 0 0 0 0 0 0 0 0 481.7719536 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2100.875955 98.97482281 Right_bank.shp 1159.323675 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 299.7829046 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 324.4306388 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1097.468693 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1609.704647 0 0 0 Right_bank.shp 1979.552093 0 0 0 0 0 0 0 0 41057.58846 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 692.504213 0 0 0 0 0 0 0 0 5489.287014 0 0 0 0 0 7812.576862 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 783.252413 0 0 0 0 0 0 0 0 21703.40588 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1251.817435 Right_bank.shp 192.4817411 0 0 0 0 0 0 0 0 2849.545606 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 323.3925232 0 0 0 0 0 0 0 0 15579.36548 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 360.8124165 0 0 0 0 0 0 0 0 25075.44158 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 880.724373 Right_bank.shp 659.213913 0 0 0 0 0 0 0 0 29988.95377 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 424.5650032 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 3768.484874 0 0 0 0 0 0 0 0 68908.12923 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 568.4301038 Right_bank.shp 1155.011909 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 446.0408409 0 0 0 0 0 0 0 0 20014.98793 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 606.0504722 0 0 0 0 0 0 0 0 916.394683 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1100.808415 0 0 0 0 0 0 0 0 16481.00403 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4451.993306 Right_bank.shp 782.6923948 0 0 0 0 0 0 0 0 3321.19362 0 0 0 0 0 1372.977752 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 186.8144028 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1294.377301 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 876.985223 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 646.6010715 0 0 0 0 0 0 0 0 3969.674747 0 0 0 0 0 0 636.3967211 0 0 0 0 0 0 0 0 0 Right_bank.shp 1054.961329 0 0 0 0 0 0 0 0 76864.76207 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 384.834586 0 0 0 0 0 0 0 0 587.9770102 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1386.269822 0 0 0 0 0 0 0 0 108212.0141 0 0 0 0 0 0 0 0 0 0 0 4550.655493 0 0 0 4340.341058 Right_bank.shp 573.6519474 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1273.14152 0 0 0 0 Right_bank.shp 590.8390342 0 0 0 0 0 0 0 0 16758.43319 0 0 0 0 0 0 0 4759.883335 0 0 3590.212159 5913.431486 0 0 0 0 Right_bank.shp 278.0276436 0 0 0 0 0 0 0 0 15788.0516 0 0 0 0 2742.589866 0 0 559.6737535 0 0 7.887634776 0 0 0 0 0 Right_bank.shp 453.5328953 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 639.0338452 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 480.115107 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2356.770174 0 0 0 0 0 0 0 0 108285.9227 0 0 0 0 0 0 0 0 0 0 0 0 0 0 45509.69344 5538.604012 Right_bank.shp 776.9389187 0 0 0 0 0 0 0 0 223.9095764 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 548.3437212 0 0 0 0 0 0 0 0 6481.581488 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 630.101145 Right_bank.shp 882.7418391 0 0 0 0 0 0 0 0 59491.85694 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10233.1807 Right_bank.shp 1657.358916 0 0 0 0 0 0 0 0 42722.58848 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 18576.52146 Right_bank.shp 496.080145 0 0 0 0 0 0 0 0 30764.67731 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1034.18369 Right_bank.shp 358.7562021 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 919.2987188 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2204.447537 0 0 0 0 0 0 0 0 49407.39697 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 663.1691937 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 331.763678 0 0 0 0 0 0 0 0 0 0 0 0 0 8710.155563 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 733.9834726 0 0 0 0 0 0 0 0 482.2822448 0 0 0 0 12465.81443 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 303.7384109 0 0 0 0 0 0 0 0 16866.08521 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3440.58815 Right_bank.shp 303.5927245 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1203.24739 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 347.7198471 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 754.5947188 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 768.6753233 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1.635108176 Right_bank.shp 1060.700036 0 0 0 0 0 0 0 0 720.6343897 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9171.699762 Right_bank.shp 1589.601077 0 0 0 0 0 0 0 0 104663.878 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6165.771954 Right_bank.shp 341.8069464 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 1638.109978 0 0 0 0 0 0 0 0 50320.98158 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Right_bank.shp 2087.469221 0 0 0 0 0 0 0 0 28553.39564 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8501.657314 Right_bank.shp 948.7345225 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 15-1588 Appendix B May 2016
FM_ls FM_md FM_n FM_r FM_ro GC GN_hd GN_ld GN_md GN_n M_e M_f M_hd M_ld M_md M_n M_ro PA PS_n RI RI_hd RL RN RU_hd RU_ld RU_ls RU_md RU_ro 0 5754.605649 36045.16557 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 30677.98335 3108.026981 1841.337848 480.1776271 0 0 0 0 760.3436584 26586.59263 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1859.798821 874.2033021 0 0 0 0 19766.42134 1673.56611 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7890.667631 0 0 18904.39669 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 103.1515834 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1320.222319 12857.40346 0 8924.240362 0 0 36.54723813 0 0 0 0 0 0 19887.35467 0 0 0 0 0 0 0 0 0 0 0 0 10609.48766 0 18054.8624 9962.633789 0 0 0 0 8813.244169 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2364.378174 0 1879.462126 3725.027623 0 0 0 0 12740.65896 0 0 0 0 0 92.242606 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6820.139656 0 0 0 0 2905.966991 0 0 0 0 0 1172.299274 3020.469976 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1084.983318 1028.312167 0 12237.40024 0 0 0 0 0 0 0 4419.470686 0 0 0 0 0 416.2685546 0 0 0 0 0 4964.007478 0 0 1984.139455 0 67360.52769 2806.18672 0 1658.372759 0 0 0 0 0 0 0 4477.608974 0 0 0 0 0 2659.819042 0 0 0 0 0 14694.9893 0 0 3420.447136 0 5810.144948 0 0 0 0 0 844.0353051 0 0 0 0 2948.279234 0 0 0 0 2254.804409 5042.009437 0 0 0 0 0 0 0 0 22186.24865 0 48210.8717 1896.184039 0 0 0 0 2455.299463 0 0 0 0 0 0 0 0 0 8113.728669 0 0 0 0 0 0 0 0 0 6051.455598 0 4226.050262 8026.38542 0 2622.273029 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3274.527073 0 0 7020.715807 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1240.150913 0 0 471.6390394 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 19469.14509 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2637.09135 0 0 1108.617343 0 2836.678195 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5235.528081 0 3494.878404 5341.197138 0 867.5972149 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3386.058167 0 0 5915.70954 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 15424.71325 0 7823.009776 49635.01097 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2715.433072 0 696.8112188 1933.856195 0 6723.374427 0 0 0 0 0 8252.067079 1981.056773 0 0 63621.6384 0 0 9294.869806 0 4827.747378 2032.035417 0 0 60495.44889 0 0 0 31564.31265 0 3283.510815 37831.59331 0 13794.05412 0 0 0 0 0 0 0 0 0 6964.400164 0 0 0 0 0 0 0 0 0 0 0 0 5935.556283 0 0 8135.571545 0 1244.354885 0 0 0 0 0 0 0 0 14619.93587 9110.899091 0 0 0 0 0 0 0 0 0 0 0 0 6350.191954 0 0 6488.88419 0 12593.86894 0 0 0 0 0 0 0 0 75.92313522 6725.361082 0 0 0 0 0 0 0 0 0 0 0 0 5104.026283 0 0 558.2194869 0 0 0 0 0 0 0 8164.381928 0 11316.30817 15640.8243 60601.08597 0 0 0 0 0 0 0 0 0 0 0 0 31984.62101 0 10601.92592 8846.207433 0 0 0 0 0 0 0 0 0 0 39474.00576 352.8282265 0 0 0 0 0 0 0 0 0 0 0 0 2198.700433 0 0 0 0 24188.90453 0 0 0 4099.558078 0 0 0 4317.606973 0 0 0 0 0 1327.832132 0 0 0 0 0 0 1205.687799 0 0 0 0 0 0 7572.405461 0 0 0 1.781631188 0 0 0 9430.577203 0 0 0 0 0 2274.079485 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 13233.84339 0 0 44955.7091 0 14589.32592 0 0 0 0 2967.473243 8108.276924 0 0 0 0 0 0 0 0 26507.62497 12850.23763 0 35786.06965 5503.512674 0 0 0 0 0 0 0 0 47.21908393 0 0 870.6707384 0 165.2853104 0 0 0 0 0 0 0 0 0 49948.42266 0 0 33415.96306 0 0 0 0 0 0 0 0 8791.083548 13069.53017 0 0 9036.072284 0 3463.54268 0 0 0 0 0 0 0 5081.148206 0 559.3650513 4124.715208 0 3394.283722 0 0 0 0 0 0 0 0 37740.19512 0 0 0 674.6061798 0 0 0 0 0 0 0 0 0 8651.614691 0 0 5934.541761 0 0 0 0 0 0 0 11836.84481 0 0 134823.5515 9840.519182 0 0 0 0 6601.011649 0 2174.524215 0 0 0 0 0 20214.8945 0 24133.11364 5750.422922 0 0 0 0 0 0 0 0 0 0 15381.52051 0 0 0 0 0 0 0 27779.40903 0 0 0 1802.052216 0 0 0 10612.46005 253.1401142 0 0 0 0 0 0 0 14087.46505 0 0 0 25227.44053 0 0 0 0 810.6884489 6483.899576 1338.104421 0 0 0 0 0 21951.72171 0 46756.35204 9674.539761 0 0 0 0 0 0 0 2285.294062 0 0 6838.162132 25635.71253 0 0 0 0 0 0 0 0 0 0 0 0 11705.84526 0 0 0 0 2316.47215 0 0 38982.53891 0 0 15906.17338 0 0 0 26286.34687 0 0 0 0 0 0 2686.941198 0 0 0 0 0 10999.45853 0 203.9312025 1753.177189 0 22731.47712 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 45691.11727 0 0 0 0 0 45402.03427 0 3653.398711 22902.53482 0 0 0 0 0 0 0 0 0 2343.867152 0 0 0 1001.760508 0 0 0 0 15871.74205 0 5449.843886 0 1423.788928 0 0 0 0 21100.59357 0 0 0 0 0 0 0 19499.14319 0 18069.75937 0 0 0 18221.18215 0 0 0 0 5705.699329 0 724.6118863 0 9367.856885 0 1152.615241 0 0 7033.875566 0 0 0 0 0 0 0 6360.780061 0 16069.87551 0 0 0 0 4502.722966 0 0 0 40478.01524 0 0 0 9538.502082 0 5022.824311 0 16695.10927 339.9899861 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20187.96636 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4571.575661 0 2264.804858 9623.854417 0 1328.021643 0 0 0 2453.472421 0 0 0 0 50979.49209 0 0 0 0 0 0 0 0 0 0 0 0 0 10556.60078 0 0 12368.95718 0 0 0 0 2105.765937 39143.30482 0 0 0 0 1111.0119 0 0 0 276.966214 0 0 0 0 0 0 0 768.3646482 0 11093.71448 0 0 16653.44901 0 0 0 0 0 0 0 0 0 0 4231.614046 0 0 0 5181.813099 1251.914549 0 0 0 0 2326.587084 0 0 0 6113.834291 0 40739.48734 23932.10284 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4393.980809 0 0 0 0 0 48748.51914 0 0 0 0 0 1270.061304 0 0 0 0 0 0 3670.806937 0 0 0 0 0 16565.03151 0 0 1883.261095 6154.175726 0 0 10445.6264 0 7318.652346 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2689.416234 0 0 0 4989.617304 29465.57661 0 39956.46095 0 0 0 0 0 17348.5286 0 7403.742049 0 0 0 0 0 0 0 0 0 0 0 25105.75127 0 0 0 0 0 29084.09525 0 41204.51772 0 0 0 0 0 14817.6662 0 0 0 0 0 0 0 0 0 0 0 0 0 71469.99954 0 0 0 0 0 1984.264966 0 4459.408388 0 0 0 0 0 7268.687364 0 0 23950.00033 0 0 0 0 0 0 0 0 0 0 14028.43129 0 0 0 65.83365123 0 6454.650066 6506.825068 50764.40652 0 0 4315.577044 0 0 18058.25911 0 0 79372.44434 23299.31519 14656.82046 0 0 0 0 0 0 0 0 0 0 0 0 18579.08485 0 0 0 0 0 0 0 0 0 326.2791927 0 0 2026.340014 136.99749 0 0 0 0 0 0 0 0 0 0 0 0 0 17923.13352 0 0 0 0 0 0 0 0 0 0 0 34533.61184 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 543.1391487 0 0 0 0 0 0 0 0 0 0 0 33318.76084 0 0 0 0 22672.8905 0 0 0 0 0 0 0 0 0 0 0 12885.71532 0 0 0 0 52539.31981 0 0 0 0 0 2949.32554 0 0 1535.870292 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 23782.13047 0 0 0 0 0 21617.75618 0 0 37793.51995 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 27144.50413 0 0 0 0 0 0 9028.645871 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 15207.48306 0 0 0 2672.878253 0 0 0 0 0 0 20259.03495 0 0 952.757795 22723.11314 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22945.03887 30373.98676 0 1769.882527 0 0 94.40937499 3859.019191 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 710.0448986 0 1071.829659 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6852.448345 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2641.180841 0 118.1102292 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2426.118466 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 43784.76475 0 0 0 0 0 74003.9294 5562.450574 0 0 0 0 0 0 0 0 0 0 0 0 0 0 24652.53106 0 0 0 0 0 3371.044398 9819.192736 0 0 0 0 25.86165059 0 0 0 0 0 50216.02754 29825.33336 0 0 0 0 0 0 0 0 0 0 0 0 0 0 51117.29648 5471.61971 0 2924.454794 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 16713.1258 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 25.01820322 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 14507.09924 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 638.6727943 0 0 0 0 0 0 0 0 153.8007593 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 14313.51776 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 17552.63123 0 0 0 0 0 4944.552243 0 0 10414.85773 0 0 0 0 0 0 0 0 0 0 0 0 0 15-1588 Appendix B May 2016
FM_ls FM_md FM_n FM_r FM_ro GC GN_hd GN_ld GN_md GN_n M_e M_f M_hd M_ld M_md M_n M_ro PA PS_n RI RI_hd RL RN RU_hd RU_ld RU_ls RU_md RU_ro 0 0 0 0 0 25228.88525 0 0 0 0 0 135.7081208 0 0 13092.38049 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20273.30988 0 0 0 0 0 0 0 22672.76102 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2.380539594 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3019.907991 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 12154.26636 0 0 6.722709177 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22150.87821 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 18985.37 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 251.3372752 0 0 0 0 1083.765547 0 0 1150.5575 1819.587723 0 0 0 2588.773395 0 0 0 0 0 0 0 0 0 0 0 0 0 0 416.2058168 0 20713.22979 0 0 0 0 0 11.05457691 0 0 0 0 203.7405963 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 29.76234395 0 0 4441.365567 0 0 11527.79169 1700.107694 0 0 0 0 0 6939.53667 0 0 0 0 4697.617824 0 0 0 0 0 0 0 0 0 0 16848.14499 0 31996.26384 0 0 0 8800.850894 0 1801.26793 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 17428.99984 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 374.7539995 21.2208757 0 6791.952986 0 0 0 0 0 7850.22311 0 18741.41104 43300.13532 3073.082338 0 0 0 0 0 0 0 0 9447.334231 0 0 0 0 0 7328.649742 19873.18788 0 32251.30664 0 0 0 0 0 0 0 0 51709.0796 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1610.840386 9383.580391 0 0 0 0 0 0 0 0 0 0 14.42049317 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 47038.82683 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 16752.40426 0 0 3266.345529 0 0 0 0 0 0 0 0 0 22591.35916 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6803.445017 0 0 29365.08732 0 0 0 0 0 3022.676059 0 0 0 938.7332138 0 0 0 0 0 0 0 0 0 0 0 0 0 0 26094.49009 0 0 145.173716 0 0 0 0 0 0 0 9825.67734 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3471.038545 0 0 0 0 0 2499.534108 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1942.64673 0 0 0 0 0 0 3477.598316 0 239.8725005 0 0 4008.223109 0 0 4749.903061 0 0 0 0 0 0 0 0 0 0 0 0 0 1388.866096 0 4690.005838 0 0 0 0 0 1874.051129 0 4856.137407 0 7089.960071 0 2.965965646 0 0 0 0 0 0 0 0 6187.256729 0 0 0 541.2734233 9177.370954 0 0 0 0 0 1008.681372 0 5015.698879 0 3535.29316 0 87661.54408 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 25529.12188 0 0 0 51867.62776 0 0 0 0 0 0 9377.969025 8669.218729 0 0 0 0 0 0 0 0 0 4345.099994 0 0 0 0 0 9754.412407 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7502.796052 0 0 0 0 0 0 0 0 0 974.3875166 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6436.341142 34477.40454 0 10412.29034 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3716.254112 0 0 0 5863.716432 2423.967796 0 1145.714082 0 0 283.924595 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 939.23175 0 0 0 0 0 0 11031.12839 0 0 981.9882873 0 0 0 0 0 0 157.5979406 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4653.055824 0 0 2203.079159 0 0 0 0 0 0 0 0 0 6666.109113 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2278.276074 16312.51761 0 4698.076203 0 0 0 0 0 30.52257627 0 1579.036289 0 4411.649629 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 7513.932264 0 20694.48587 0 0 0 8972.577666 0 50895.43154 2632.026868 29681.04353 6810.980773 15587.72287 0 0 0 0 0 0 1393.337051 0 11735.37568 0 0 0 0 0 11150.85418 81061.57494 0 47500.61319 0 0 0 0 0 4685.647727 78962.6659 0 0 0 0 0 0 0 0 6081.999785 0 0 0 0 0 0 0 0 10211.98967 0 0 0 0 0 0 0 0 0 0 324.7553524 0 0 0 0 0 0 0 3227.537981 0 0 0 0 0 0 0 0 19983.06967 0 0 0 0 0 0 0 0 573.8571867 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 58755.73329 0 0 0 0 0 0 0 0 6542.370945 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 72178.74141 0 0 4194.690564 0 0 0 0 0 10087.56179 0 0 2553.516177 10146.88762 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8357.698553 0 0 0 0 0 3890.636614 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 11014.93303 0 0 0 0 0 6774.238443 0 0 0 11170.5326 0 0 0 0 0 0 0 0 0 0 0 0 0 0 14884.7815 0 0 95369.838 0 0 0 0 0 14467.57143 0 5588.525237 0 10871.95055 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2254.051218 30687.56659 0 10010.64424 0 0 0 0 0 11320.63167 0 4919.747207 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 686.0974923 29346.41097 0 11776.4046 0 0 0 0 0 14966.102 0 0 0 5047.067593 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3542.312758 718.7714074 0 0 0 0 0 0 0 10600.44841 0 6015.291925 0 8339.775391 0 0 0 0 0 1001.650863 0 1913.795003 0 0 0 0 0 0 0 0 0 8833.779104 0 0 0 0 0 3836.278119 0 0 0 6508.834627 0 0 0 0 0 0 0 0 0 0 741.5518573 0 0 0 0 1992.10302 0 1180.645832 0 0 0 0 0 1149.335217 0 0 0 1.654021785 0 0 0 0 0 0 5273.798625 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1885.634239 0 496.1072053 0 0 0 0 0 0 0 0 0 0 0 0 0 0 372.907782 0 0 5605.615099 0 0 0 0 0 0 0 4633.919753 0 83.30406055 0 0 0 0 0 0 0 0 0 0 0 0 0 0 4492.377748 0 0 261.3072477 0 0 0 0 0 1814.688057 0 0 0 2840.300045 0 0 0 0 0 0 0 0 0 0 2606.88039 0 0 0 0 0 0 0 0 0 0 0 0 2766.203214 0 0 0 506.8372705 0 0 0 0 0 0 2247.103888 0 0 0 1416.900454 0 0 0 0 0 0 0 0 0 0 0 0 1286.694884 0 0 0 45354.37024 0 0 0 0 3412.607723 0 0 0 0 0 2498.531392 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3695.343567 0 23509.58875 0 0 0 0 0 0 0 0 0 0 1125.104931 1908.155217 0 0 30756.51977 0 0 4587.953117 0 0 0 0 0 0 0 10425.58096 0 0 0 0 0 0 0 0 0 0 11032.73003 0 0 0 0 0 9845.935259 0 0 6177.576805 0 0 3619.758938 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 24163.23282 0 0 0 0 0 14600.282 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5131.027279 0 0 0 5022.897124 0 0 0 0 0 10894.67517 0 0 0 0 0 0 0 0 0 0 9845.11588 0 7271.209277 0 0 0 0 1101.428984 542.8413056 0 0 48725.77355 0 0 0 0 0 914.5665062 0 0 2243.379168 0 0 0 0 0 0 0 4121.101615 7273.152635 0 3736.679038 0 0 0 0 0 3038.217927 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1749.873916 16070.20567 0 0 0 0 0 31.28709975 0 0 10977.37442 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 77173.65654 0 0 0 0 0 0 0 0 0 6542.502268 0 0 0 0 0 0 0 3406.689301 0 0 0 0 0 0 0 0 386.6767846 0 0 0 0 0 0 0 0 0 133153.6609 0 0 0 0 0 19405.82775 0 0 1034.553972 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 39458.57497 0 0 0 0 0 0 0 0 27037.10453 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5947.650494 0 0 0 0 0 0 0 0 13155.87486 0 0 0 0 0 0 0 1866.726113 0 0 0 0 0 0 0 0 0 0 41523.66329 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 912.2054648 8279.056255 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8763.855554 0 0 0 0 4236.924517 0 0 0 0 0 0 0 0 0 834.05609 0 2791.439479 0 0 0 0 11869.2226 0 0 0 0 0 48784.67379 0 0 0 0 0 0 0 0 0 0 0 0 0 0 60216.47983 0 0 0 0 0 0 14307.71845 0 0 0 0 0 1784.832355 0 0 0 0 0 0 0 0 0 0 5258.462082 0 0 0 8289.137485 0 0 0 0 0 0 14013.38426 0 8161.336219 0 0 0 46.66680455 0 0 0 0 0 0 0 3833.033345 0 0 5488.374299 0 30183.67602 0 19447.9012 0 0 0 0 0 2424.8534 0 0 12497.49564 0 0 0 0 0 0 0 0 0 25.70691846 0 0 0 0 0 0 1659.83691 0 74171.50525 0 0 0 0 0 669.4612815 0 0 0 0 0 0 0 0 0 0 0 0 7528.982251 0 0 0 0 0 0 0 0 33947.33622 0 0 0 0 0 53264.89701 0 0 0 0 0 0 0 0 0 0 2447.147147 0 0 0 0 0 0 5458.326674 612.7959575 0 0 21512.10823 0 0 0 0 0 8871.023856 6034.563376 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 29488.32763 0 0 892.3338539 0 0 0 0 0 3071.674917 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 8280.297561 2283.849457 0 85387.49875 0 0 0 0 0 17929.18204 0 0 617.8013382 0 0 0 10609.40864 0 0 0 0 21000.33279 15875.00291 0 7181.167925 0 0 8897.38649 0 22235.72248 0 66343.96581 0 0 0 0 0 0 1920.662384 0 4716.107373 0 0 0 1147.474674 0 0 0 0 0 0 0 0 0 0 3392.336498 0 0 0 17545.27751 0 0 0 0 0 15750.54319 0 0 40879.04057 0 15-1588 Appendix B May 2016
RZ SB SH_f SH_hd SH_ld SH_md SH_r SH_ro SS_hd SS_ld SS_md SS_n UR UR_pa WN_hd WN_ld WN_n Poly_Total Erosion_Extreme Erosion_High Erosion_Low Erosion_Moderate Erosion_Total 0 0 0 0 0 0 0 0 11996.32512 4989.415446 18940.60125 233613.7873 753.6892469 0 0 0 0 373917.4537 NA NA NA NA NA 0 0 0 0 0 0 0 0 5922.130439 0 0 0 5953.090116 0 0 0 0 139210.2037 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 63472.66256 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 31.46414225 0 0 1850.632335 0 118993.0663 0 1182.22517 0 0 1182.22517 0 0 0 0 0 0 0 0 0 0 0 0 167883.0787 0 0 0 0 193154.9646 0 0 22.55480695 0 22.55480695 18647.81008 0 7328.89972 0 0 0 0 0 0 44427.55523 812.6993481 0 595.3624138 0 0 0 0 138690.6142 0 0 460.1369143 0 460.1369143 4574.585003 0 0 0 0 0 0 0 0 6253.82007 0 0 0 0 557.7882762 3842.020331 0 103770.8657 0 0 94.43657613 0 94.43657613 15478.53676 0 0 0 0 0 0 0 0 0 0 0 66530.0247 0 0 0 0 106181.1631 NA NA NA NA NA 4121.482264 0 0 0 0 0 0 0 0 0 0 0 29260.50509 0 0 778.4930626 0 97741.07136 0 0 81.55537371 0 81.55537371 3516.265675 0 0 0 0 0 0 0 0 0 0 0 44394.88436 0 0 0 0 131520.1234 0 0 173.3592677 0 173.3592677 5164.366491 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 36227.37589 NA NA NA NA NA 13326.53783 0 0 0 0 0 0 0 0 0 10046.35602 0 39087.1505 0 0 0 0 145842.4771 0 116.1818066 48.16721547 227.7484259 392.0974479 15906.67249 0 0 1569.076696 0 0 0 0 0 1599.384542 2462.138381 0 10443.55127 0 0 0 0 63476.01582 0 0 53.35285152 0 53.35285152 0 0 0 0 0 0 0 0 0 0 0 0 24258.8591 647.596473 0 0 0 35201.69845 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 12123.72928 27874.6884 0 0 0 41710.20763 0 0 21.13535796 0 21.13535796 0 0 0 0 0 0 0 0 0 0 0 0 2295.083286 25012.55472 0 0 0 27307.63801 NA NA NA NA NA 931.9792177 0 2705.474658 0 0 0 0 0 0 0 0 0 97904.07258 60788.59816 0 0 0 208947.6155 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 30913.74698 0 0 0 0 30915.30639 NA NA NA NA NA 0 0 1852.994902 0 0 0 0 0 0 0 0 0 28018.3444 0 0 0 0 29871.33931 0 25.17030318 0 0 25.17030318 3081.543849 0 403.4784011 0 0 0 0 0 0 0 0 0 25096.48999 0 0 0 0 35163.89913 NA NA NA NA NA 22353.2865 0 4368.448659 0 0 0 0 0 8309.654334 0 0 0 2330.132604 0 0 0 0 52300.72293 NA NA NA NA NA 3843.633079 0 6911.45473 0 0 0 0 0 0 0 0 0 122130.171 0 0 0 0 146614.6749 0 172.7501379 83.63265815 0 256.382796 42673.79219 0 0 0 0 0 0 0 0 0 0 0 44559.03926 3015.582461 0 0 0 163131.1479 298.3659654 146.0372739 0 0 444.4032393 4318.043677 0 276.208094 0 0 0 0 0 0 0 0 0 133396.4598 0 0 0 0 150060.1865 0 0 23.97826896 0 23.97826896 58975.83791 0 5949.47538 3457.946587 0 4845.780829 0 3322.605825 0 0 6597.584797 0 1184.85675 0 0 0 0 321312.4227 0 664.0645226 636.2603184 33.9939593 1334.3188 4791.808981 0 0 0 0 0 0 0 0 0 0 0 100069.1135 0 0 0 0 127140.8053 NA NA NA NA NA 12736.04895 0 0 0 0 0 0 0 0 0 0 0 856.8505971 0 0 0 0 64686.54613 159.1577428 69.17927717 0 0 228.33702 2554.137174 0 0 0 0 0 0 0 0 0 0 0 221386.1021 0 0 0 0 237069.3229 NA NA NA NA NA 30743.29599 0 0 0 301.5397356 572.1599587 0 0 68641.41185 6207.720568 903.1796143 0 42669.12492 0 0 0 0 302824.5909 0 1261.556969 0 0 1261.556969 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 92287.32731 0 0 464.4709596 125.480877 589.9518366 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 20829.74431 0 0 0 43.66453101 43.66453101 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 57535.73442 0 27.05545056 0 0 27.05545056 17808.79603 0 10551.29836 0 0 0 0 0 0 0 0 0 86929.96367 0 0 0 0 343104.8858 0 463.9276105 441.7702174 291.3130351 1197.010863 0 0 54.32670464 0 0 0 0 0 0 0 0 0 0 0 0 0 0 84501.88756 NA NA NA NA NA 5543.277578 0 0 0.149829765 0 0 0 0 0 0 0 0 0 0 0 0 0 53063.16827 0 0 95.51074799 0 95.51074799 24167.15669 0 0 4937.811388 0 0 0 0 0 0 0 0 0 0 0 0 0 82105.92583 0 14.55061909 68.44024193 0 82.99086102 1452.717077 0 0 3924.178061 5105.943205 0 0 0 0 0 0 0 0 0 0 0 0 225857.7207 158.9549129 0 296.6991398 0 455.6540528 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 55938.28842 0 0 183.1578147 42.62637022 225.784185 17672.43119 0 0 0 0 17248.50816 0 0 0 0 0 0 0 0 0 0 0 239103.4782 0 77.44349656 117.277294 323.3955339 518.1163245 12862.23606 0 0 0 0 4452.859948 0 0 0 0 0 0 0 0 0 0 0 117245.3426 0 480.478584 252.8335209 0 733.312105 5340.52905 0 0 0 0 392.4867851 0 0 0 0 0 0 0 0 0 0 0 346767.7806 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 51359.38684 0 0 0 0 182166.7878 0 0 124.1906094 197.4186308 321.6092402 1185.467297 0 0 0 1234.400488 0 0 0 0 0 0 0 0 0 0 0 0 51695.08053 NA NA NA NA NA 12808.86754 0 0 0 269.8908484 0 0 0 0 0 0 0 0 0 0 0 0 92853.50201 218.5303978 0 0 0 218.5303978 5413.580524 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 135498.536 NA NA NA NA NA 1405.468728 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 46811.55565 NA NA NA NA NA 3191.918602 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 74695.66085 NA NA NA NA NA 3746.782804 0 0 0 5831.349784 0 0 0 0 0 0 0 0 0 0 0 0 143764.0556 NA NA NA NA NA 16557.44577 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 93579.21827 NA NA NA NA NA 6457.584723 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 90234.93797 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 54412.56126 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 71198.86087 NA NA NA NA NA 30359.94117 0 0 0 14189.96457 0 0 0 0 0 0 0 0 0 0 0 0 248235.6741 0 0 148.9209884 0 148.9209884 23311.23835 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 180264.9326 0 0 0 162.0639154 162.0639154 15430.70509 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 124563.0657 0 0 161.2060476 464.1453709 625.3514185 34004.99281 0 0 0 0 23010.60414 0 0 0 0 0 0 0 0 0 0 0 287568.6006 0 0 548.7858994 143.4204287 692.2063281 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 93904.52597 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 104202.1633 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 41218.56012 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 100380.0508 0 0 164.1362384 6.310414374 170.4466528 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 108341.5748 0 0 0 297.7369334 297.7369334 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 93309.16301 51.0122576 382.9219146 0 0 433.9341722 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 774.6661644 0 31879.42902 0 0 110.3160577 0 110.3160577 3665.32299 0 0 0 0 0 0 0 0 0 0 0 41157.11376 0 0 0 0 83072.92864 NA NA NA NA NA 17250.27482 0 0 0 0 0 0 0 79.00141256 0 0 0 0 0 0 0 0 169115.2309 NA NA NA NA NA 3844.480003 1070.598761 0 0 0 0 0 0 12944.74439 408.4058012 0 0 0 0 0 0 0 29529.70397 NA NA NA NA NA 5491.015674 10115.58514 0 0 0 0 0 0 16236.12116 14321.60069 0 0 0 0 0 0 0 53800.16962 NA NA NA NA NA 2789.994564 0 0 0 0 0 0 0 13622.63039 3326.67243 0 0 0 0 0 0 0 30846.83981 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 192926.124 0 0 0 1349.75492 1349.75492 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 163511.1656 0 0 0 304.7946206 304.7946206 0 0 0 0 0 0 0 0 0 0 0 0 3.541354324 0 4332.895147 0 3810.881345 178394.6539 NA NA NA NA NA 10601.90526 0 0 0 0 0 0 0 0 0 0 0 52010.01176 0 0 0 0 205318.2508 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 2510.423251 0 0 0 0 19223.54905 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 87099.48013 0 0 0 0 87099.48013 0 0 0 71.73634459 71.73634459 0 0 0 0 0 0 0 0 0 0 0 0 54972.81657 0 0 0 0 54997.83477 0 40.71530353 0 39.47038176 80.18568529 0 0 0 0 0 0 0 0 0 0 0 0 30098.64047 0 0 0 0 44605.73971 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 60438.20497 0 0 0 0 61230.67852 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 121292.1768 7129.093596 0 0 0 142734.7881 NA NA NA NA NA 0 0 0 0 0 4077.540634 0 0 0 0 0 0 29588.87711 55999.52776 0 0 0 122577.9867 NA NA NA NA NA 15-1588 Appendix B May 2016
RZ SB SH_f SH_hd SH_ld SH_md SH_r SH_ro SS_hd SS_ld SS_md SS_n UR UR_pa WN_hd WN_ld WN_n Poly_Total Erosion_Extreme Erosion_High Erosion_Low Erosion_Moderate Erosion_Total 0 0 0 0 0 0 0 0 0 0 0 0 38315.3748 44404.75308 0 0 0 121177.1017 0 0 27.53528786 0 27.53528786 0 0 0 0 0 0 0 0 0 0 0 0 94199.07971 286.6551989 0 0 0 137431.8058 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 29576.58301 0 0 0 0 29578.96355 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 42138.92093 0 0 0 0 42138.92093 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 76660.90992 0 0 0 0 79680.81791 0 0 20.32457723 19.16197317 39.4865504 1874.831519 0 0 298.8501027 0 0 0 0 0 0 0 0 46640.68138 0 0 0 0 60975.35207 0 0 54.16762343 0 54.16762343 54.62955631 0 0 0 0 0 0 0 0 0 0 0 12622.96435 19344.38978 0 0 0 54172.86189 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 22572.06629 0 0 72.7796713 0 72.7796713 1153.096983 0 0 0 0 0 0 0 0 0 0 0 44083.17677 0 0 0 0 78608.34173 0 0 117.2708351 238.5160689 355.786904 0 2500.357041 0 0 0 0 0 0 0 0 0 0 34199.81189 0 0 0 0 41386.09202 0 0 66.96175765 149.7031124 216.66487 2393.788552 0 0 0 0 0 0 0 0 0 0 0 92112.58511 48831.76289 0 6049.225018 0 223211.593 0 162.958739 152.959116 271.20616 587.124015 0 0 0 0 0 0 0 0 0 11765.72445 4682.489998 0 6029.534192 0 0 0 0 89588.84031 0 0 84.75367489 0 84.75367489 748.5691316 0 0 0 0 0 0 0 0 2452.499138 0 0 0 0 0 0 0 82358.81488 823.1383907 0 0 0 823.1383907 22405.0837 664.4231717 0 0 1019.324159 4445.630203 7603.675636 0 0 37522.07695 3076.137144 0 6498.813929 0 0 0 0 262085.3137 240.322518 418.9441933 102.0547506 186.1473759 947.4688377 3061.764893 0 0 0 0 0 0 0 0 3676.984924 503.5292829 0 0 0 0 0 0 124399.3283 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 55373.7318 0 0 0 93.57439163 93.57439163 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 37620.51864 0 0 0 235.1531574 235.1531574 0 1667.857094 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 166405.1554 127.6956231 223.8581435 0 241.5418316 593.0955983 0 2251.900388 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 98468.59612 0 143.0181662 0 0 143.0181662 0 0 0 0 0 0 0 0 0 1635.577369 0 0 0 0 0 0 0 17613.91599 0 0 0 86.3977564 86.3977564 3124.183312 7262.314484 0 0 0 0 0 0 0 99144.31549 0 0 0 0 0 0 0 113972.9941 0 339.0374462 0 11.6410238 350.67847 3023.125027 1917.745978 0 0 0 0 0 0 0 3157.84345 0 3967.868554 0 0 0 0 0 30621.05193 NA NA NA NA NA 2087.752542 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 31816.76822 NA NA NA NA NA 9474.722503 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 108305.6446 NA NA NA NA NA 16550.33453 0 0 0 0 0 0 0 0 40970.6046 0 0 0 0 0 0 0 198367.565 NA NA NA NA NA 1705.470377 0 0 0 0 0 0 0 0 0 35004.91781 0 0 0 0 1225.19033 0 68494.65086 NA NA NA NA NA 1016.465224 458.116159 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 76730.22824 NA NA NA NA NA 1496.372193 1335.0437 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 18830.61392 NA NA NA NA NA 2686.102044 2168.767429 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 32688.51969 NA NA NA NA NA 2766.211951 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 36718.09912 0 147.2554011 0 0 147.2554011 5086.058196 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 65029.99097 365.1939328 101.5132524 27.80046633 0 494.5076516 6869.577349 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 41099.20398 0 0 34.20447199 0 34.20447199 35212.66961 0 0 0 0 0 0 0 0 6324.140014 0 0 0 0 0 0 0 378434.9072 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 13125.28464 0 0 0 0 113067.5877 0 0 0 173.0723315 173.0723315 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 43550.35093 0 0 43.33344754 248.88728 292.2207276 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 60245.98516 0 0 6.263946803 0 6.263946803 3797.4026 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 107646.2029 NA NA NA NA NA 4552.801729 6177.362168 0 0 13280.22731 0 0 0 0 8697.9186 13511.74578 0 0 0 0 0 0 82059.89109 NA NA NA NA NA 0 0 0 0 615.9811272 0 0 0 0 0 0 0 0 0 0 0 0 15521.55077 NA NA NA NA NA 2464.70285 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 130664.0934 0 0 190.0646292 0 190.0646292 5746.53454 0 0 0 0 0 0 0 7794.814472 0 0 0 0 0 0 0 0 87421.65827 0 0 0 136.5910766 136.5910766 2720.399764 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 65375.76317 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 101139.0158 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 37292.7177 NA NA NA NA NA 0 2203.741851 0 0 0 0 0 0 0 2417.217049 0 0 0 0 0 0 0 135983.383 0 0 752.6947007 105.5750473 858.2697479 0 21412.85876 0 0 0 0 0 0 0 12629.75384 0 16251.05389 0 0 0 0 0 57991.59588 NA NA NA NA NA 0 3908.229884 0 0 0 0 0 0 0 0 0 18160.90639 0 0 0 0 0 61451.36077 0 0 0 99.55929726 99.55929726 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 28569.11166 0 0 0 133.1724252 133.1724252 0 680.3602907 0 0 0 0 0 0 0 32709.0516 0 0 0 0 0 0 0 40651.28038 0 0 185.1333341 94.22344418 279.3567783 0 0 0 0 0 0 0 0 0 52351.90993 3065.87222 0 0 0 0 0 0 62354.82697 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 390.462653 0 0 0 0 0 0 52942.66689 NA NA NA NA NA 3.772765305 0 0 0 0 0 0 0 0 1933.695393 0 0 40.29183572 0 0 0 0 226894.6454 NA NA NA NA NA 7528.303746 0 0 0 0 1100.376901 0 0 0 0 0 0 32845.69203 0 0 0 0 79180.10531 NA NA NA NA NA 2155.374279 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 51650.33067 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 90773.63721 0 0 7.055039572 0 7.055039572 0 0 0 0 0 0 0 0 0 1048.707625 0 0 0 0 0 0 0 132992.1322 0 0 323.0785737 0 323.0785737 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 49968.01222 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 4028.494796 0 0 0 0 0 32857.2359 NA NA NA NA NA 0 0.292225379 0 0 0 0 0 0 0 6963.67665 0 0 0 0 0 0 0 94086.81698 0 608.9859626 311.7705173 0 920.7564799 0 3104.181967 958.2355697 0 0 0 0 0 0 11150.25093 0 0 0 0 0 0 0 218600.7849 0 300.7368001 509.0310172 0 809.7678173 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 66495.67951 0 0 52.66324033 0 52.66324033 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6220.439117 0 0 34034.12004 0 0 1.892923308 0 1.892923308 0 0 0 0 0 0 0 0 0 0 0 0 0 0 14791.95695 0 0 71130.44303 0 0 348.3045748 117.4934171 465.7979919 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 29497.93508 0 0 116.8600545 0 116.8600545 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 28495.49824 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 123308.8721 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 37507.1524 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 73922.0007 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 76528.14547 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 104633.5496 NA NA NA NA NA 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 155765.6152 0 0 282.3429265 0 282.3429265 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 33452.3364 0 0 180.7131011 0 180.7131011 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 164819.6107 0 0 311.9803589 659.4258387 971.4061977 0 4192.224917 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 200027.0347 0 0 119.5128982 0 119.5128982 10910.51811 5806.838037 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 95432.0286 0 593.3180908 137.7038435 83.39245221 814.4143865 15-1588 Appendix C May 2016
APPENDIX C
Centerline and Bank Aquatic Habitat Index Analysis Matrices
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
Appendix C-1- Holding values based on spatial data (DFO 2015)
Variable Relative score Chinook Holding Total 11.5
Appendix C-2. Rearing - habitat unit : fish life history scoring matrix
Habitat Type
Species CA CO P LK RF RN G BW FL_i FL_ld FL_n FM_i FM_n M_i M_r RM_n SC LWD_1 B_i RU_i SH_i SH_n SH_r
Rainbow (Resident) 2 2 3 0 3 3 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 Rainbow (Adfluvial) 2 2 3 0 3 3 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 Bull Trout 3 3 3 2 3 2 1 0 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Dolly Varden 1 2 3 2 2 3 2 2 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Cutthroat 1 2 3 1 2 3 2 0 0 0 0 0 0 0 0 0 3 3 0 0 0 0 0 Kokanee 1 2 1 3 1 0 0 1 0 0 0 0 0 0 0 1 1 3 0 0 0 0 0 Pink Salmon 1 3 3 2 3 3 1 0 0 0 0 0 0 0 0 0 2 1 0 0 0 0 0 Chinook 3 2 3 3 3 2 1 1 1 1 1 0 0 0 0 1 1 3 0 0 0 0 2 Coho 1 2 3 0 3 3 1 3 2 2 2 0 0 0 0 2 3 3 0 0 0 0 2 Sockeye 1 2 1 2 1 0 0 1 0 0 0 0 0 0 0 1 1 3 0 0 0 0 0
Sum 18 24 29 15 27 24 11 11 6 6 6 0 2 2 2 8 26 31 0 0 0 0 10 Relative Unit Value 0.55 0.73 0.88 0.45 0.82 0.73 0.33 0.33 0.18 0.18 0.18 0.00 0.06 0.06 0.06 0.24 0.79 0.94 0.00 0.00 0.00 0.00 0.30 Adjusted (/1) 0.58 0.77 0.94 0.48 0.87 0.77 0.35 0.35 0.19 0.19 0.19 0.00 0.06 0.06 0.06 0.26 0.84 1.00 0.00 0.00 0.00 0.00 0.32
Score (/28.75) 17 22 27 14 25 22 10 10 6 6 6 0 2 2 2 7 24 29 0 0 0 0 9
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
Appendix C-3. General Living - habitat unit/sub area : fish life history scoring matrix
Habitat Type
Species Life Stage CA CO P LK RF RN G BW FL_i FL_ld FL_n FM_i FM_n M_i M_r RM_n SC LWD_1 B_i RU_i SH_i SH_n SH_r
Rainbow Juvenile 2 2 3 0 3 3 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 (Resident) Adult 2 3 3 0 3 3 1 1 0 0 0 0 0 0 0 1 3 3 0 0 0 0 2 Rainbow Juvenile 2 2 3 0 3 3 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 (Adfluvial) Adult 0 2 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 3 3 3 2 3 2 1 0 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Bull Trout Adult 3 3 3 3 2 2 1 1 0 0 0 0 0 0 0 0 2 3 0 0 0 0 0 Juvenile 1 2 3 2 2 3 2 2 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Dolly Varden Adult 3 3 3 2 3 2 1 0 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Juvenile 1 2 3 1 2 3 2 0 0 0 0 0 0 0 0 0 3 3 0 0 0 0 0 Cutthroat Adult 1 2 3 1 2 3 2 0 0 0 0 0 0 0 0 0 3 3 0 0 0 0 0 Juvenile 1 2 1 3 1 0 0 1 0 0 0 0 0 0 0 1 1 3 0 0 0 0 0 Kokanee Adult 0 2 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 1 3 3 2 3 3 1 0 0 0 0 0 0 0 0 0 2 1 0 0 0 0 0 Pink Salmon Adult 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 3 2 3 3 3 2 1 1 1 1 1 0 0 0 0 1 1 3 0 0 0 0 2 Chinook Adult 0 2 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 2 2 3 0 3 3 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 Coho Adult 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 0 1 1 2 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 Sockeye Adult 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Sum 27 40 44 30 36 35 16 10 5 5 5 0 3 3 3 7 37 40 0 0 0 0 12 Relative Score 0.41 0.61 0.67 0.45 0.55 0.53 0.24 0.15 0.08 0.08 0.08 0.00 0.05 0.05 0.05 0.11 0.56 0.61 0.00 0.00 0.00 0.00 0.18 Adjusted (/1) 0.61 0.91 1.00 0.68 0.82 0.80 0.36 0.23 0.11 0.11 0.11 0.00 0.07 0.07 0.07 0.16 0.84 0.91 0.00 0.00 0.00 0.00 0.27
Score (/5.75) 4 5 6 4 5 5 2 1 1 1 1 0 0 0 0 1 5 5 0 0 0 0 2
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
Appendix C-4. Cover habitat unit/sub area : fish life history scoring matrix
Habitat Type
Species Life Stage CA CO P LK RF RN G BW FL_i FL_ld FL_n FM_i FM_n M_i M_r RM_n SC LWD_1 B_i RU_i SH_i SH_n SH_r Rainbow Juvenile 2 2 3 0 3 2 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 (Resident) Adult 2 3 3 0 3 2 1 1 0 0 0 0 0 0 0 1 3 3 0 0 0 0 2 Rainbow Juvenile 2 2 3 0 3 2 1 1 1 1 1 0 0 0 0 1 3 3 0 0 0 0 2 (Adfluvial) Adult 0 2 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 2 Juvenile 3 3 3 2 3 2 1 0 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Bull Trout Adult 3 3 3 3 2 2 1 0 0 0 0 0 0 0 0 0 2 3 0 0 0 0 0 Juvenile 1 2 3 2 2 3 2 2 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Dolly Varden Adult 3 3 3 2 3 2 1 0 0 0 0 0 1 1 1 0 3 3 0 0 0 0 0 Juvenile 1 2 3 1 2 3 2 0 0 0 0 0 0 0 0 0 3 3 0 0 0 0 0 Cutthroat Adult 1 2 3 1 2 3 2 0 0 0 0 0 0 0 0 0 3 3 0 0 0 0 0 Juvenile 1 2 1 3 1 0 0 1 0 0 0 0 0 0 0 1 1 3 0 0 0 0 0 Kokanee Adult 0 2 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 1 3 3 2 0 0 0 0 0 0 0 0 0 0 0 0 1 2 0 0 0 0 0 Pink Salmon Adult 2 2 3 3 1 1 0 0 0 0 0 0 0 0 0 0 2 3 0 0 0 0 0 Juvenile 3 2 3 3 3 2 1 1 1 1 1 0 0 0 0 1 1 3 0 0 0 0 2 Chinook Adult 2 2 3 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Juvenile 2 2 3 0 3 3 1 1 1 1 1 0 0 1 1 1 3 3 0 0 0 0 2 Coho Adult 2 3 3 3 2 3 1 2 0 0 0 0 0 0 0 1 3 3 0 0 0 0 2 Juvenile 2 2 3 3 1 0 0 1 0 0 0 0 0 0 0 1 2 3 0 0 0 0 0 Sockeye Adult 2 2 2 3 0 0 0 0 0 0 0 0 0 0 0 0 0 3 0 0 0 0 0 Sum 39 50 60 43 40 34 16 12 5 5 5 0 3 4 4 9 42 59 0 0 0 0 18 Relative Unit Value 0.59 0.76 0.91 0.65 0.61 0.52 0.24 0.18 0.08 0.08 0.08 0.00 0.05 0.06 0.06 0.14 0.64 0.89 0.00 0.00 0.00 0.00 0.27 Adjusted (/1) 0.65 0.83 1.00 0.72 0.67 0.57 0.27 0.20 0.08 0.08 0.08 0.00 0.05 0.07 0.07 0.15 0.70 0.98 0.00 0.00 0.00 0.00 0.30
Weight Score (/17.25) 11 14 17 12 12 10 5 3 1 1 1 0 1 1 1 3 12 17 0 0 0 0 5
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
Appendix C-5. Ecological category: riparian habitat unit rating matrix (relative habitat value). Habitat Type Code Qualifier Wildlife Rating LWD Biodiversity Rating Nutrients ld 0.7 0.4 0.7 0.8 Broadleaf Forest B md 0.6 0.4 0.5 0.6 n 0.8 1 0.8 0.9 Backwater BW 0.7 0 0.5 0 i 0.6 0.8 0.6 0.6 ld 0.5 0.8 0.5 0.6 Coniferous Forest C md 0.5 0.6 0.4 0.5 n 0.7 0.8 0.6 0.6 Cultivated Field CF 0.1 0 0.1 0.1 Golf Course GC 0.1 0 0.1 0.1 hd 0.1 0 0 0 ld 0.6 0 0.4 0.2 Grassland GN md 0.5 0 0.3 0.1 n 0.6 0 0.4 0.2 ld 0.7 0 0.7 0.3 Low Flood Bench FL n 0.9 0 0.9 0.4 hd 0.4 0.4 0.5 0.4 ld 0.8 1 0.8 0.9 Mid Flood Bench FM md 0.6 0.8 0.6 0.7 n 1 1 1 1 Flood Bench – Russian Olive ro 0.4 0.1 0.2 0.3 e 0.3 0 0.2 0.2 f 0.3 0.6 0.4 0.4 hd 0.3 0.4 0.3 0.4 Mixed Forest M ld 0.7 0.8 0.8 0.4 md 0.6 0.7 0.6 0.6 n 0.9 1 1 0.4 r 0.9 1 1 0.2 Pasture PA 0.2 0 0.2 0.1 Pine Savana PS n 0.7 0.6 0.5 0.4 Railway RL 0 0 0 0 River RI 0.8 0 0.8 0 Road RZ 0 0 0 0 hd 0 0 0 0.1 Rural RU ld 0.4 0.4 0.4 0.4 md 0.3 0.2 0.2 0.3 Silt Bluff SB 0.2 0 0.2 0.1 Side Channel SC 0.8 0 0.7 0 hd 0.4 0 0.4 0.1 ld 0.7 0 0.6 0.1 Shrub-Steppe SS md 0.6 0 0.5 0.1 n 0.8 0 0.7 0.1 hd 0.6 0 0.5 0.1 ld 0.8 0 0.8 0.4 Wetland WN md 0.6 0 0.6 0.2 n 1 0 1 0.4
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix C May 2016
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com 15-1588 Appendix D May 2016
APPENDIX D
Data Dictionary for Large River Inventory and Mapping – Version 1.2
102 – 450 Neave Ct. Kelowna, BC V1V 2M2 tel: 250.491.7337 fax: 250.491.7772 www.ecoscapeltd.com STHM_2015.txt "LRIM", Dictionary, version, 6, "SHIM/FIM adapted - Ecoscape Oct.31, 2015" "RIVER_CENTERLINE", line, "RIVER_CENTERLINE", 1, seconds, 1, Code "RIVER_REFERENCE ", caption, normal, "RIVER_REFERENCE ", normal, expanded "RiverName", text, 100, normal, "RiverName", normal, South Thompson, Label1 "LocalName", text, 100, normal, "LocalName", normal, South Thompson "Organization", text, 100, normal, "Organization", normal, Ecoscape/Fraser Basin "WtreshedCde", text, 100, normal, "WtreshedCde", normal "WtrBdyID", text, 100, normal, "WtrBdyID", normal, THOM "Date", date, auto, ymd, manual, required, "Date", required, omitFromRepeat "Time", time, auto, 24, manual, normal, "Time", normal, omitFromRepeat "Crew", text, 50, required, "Crew", required, KH;BH;TT;JP "Weather", menu, normal, "Weather", normal "Light Rain",[L] "Heavy Rain",[H] "Snow/Sleet",[N] "Over cast",[OV] "Clear",[S] "Partly Cloudy",[PC] "Other",[O] "AirTemp", numeric, 1, -25.0, 99.0, 99.0, normal, "AirTemp", normal "Water_Temp", numeric, 1, -2.0, 99.0, 99.0, normal, "Water_Temp", normal "Stage", menu, normal, "Stage", normal "dry" "low" "moderate" "high" "flood" "other" "Line_Type", menu, normal, "Line_Type", normal "Trimble", default "Garmin" "Photointerp" "Chain_Compass" "Other" "Line_Src", menu, normal, "Line_Src", normal, Label2 "RIM2014", default "shim2008" "shim2006" "trim" "DFO" "other" "Comments", text, 100, normal, "Comments", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "______", caption, normal, "______", normal, expanded "SEGMENT_CLASS", caption, normal, "SEGMENT_CLASS", normal, expanded "Reach_Number", numeric, 1, 0.0, 99999.0, 0.0, required, "Reach_Number", required "Primary", menu, required, "Primary", required "Channelized",[CH] Page 1 STHM_2015.txt "Culvert",[CV] "Ditch",[FRT] "Modified",[Md] "Natural",[N] "Other",[O] "Secondary", menu, normal, "Secondary", normal "Beaver Pond",[BP] "Ephemeral",[EP] "Flumed",[F] "Intermittent",[IN] "Side channel",[SC] "Wetland",[HMW] "Braided",[BC] "Non-channelized",[NC] "Other",[O] "Impact_rating", menu, normal, "Impact_rating", normal "nil_nil",[8] "nil_low",[7] "nil_mod",[6] "nil_high",[5] "low_low",[6] "low_mod",[5] "low_high",[4] "mod_mod",[4] "mod_high",[3] "high_high",[2] "Hydraulic", menu, normal, "Hydraulic", normal "Beaver Pond",[BP] "Cascade",[C] "Cascade/Pool",[CP] "Falls",[F] "Glide",[G] "Pool",[P] "Run",[RN] "Riffle",[RF] "Riffle/Pool",[RP] "Slough",[S] "Standing",[S] "Wetland",[HMW] "Other",[O] "Pattern", menu, normal, "Pattern", normal "Straight" "Sinuous" "Irregular Wandering" "Irregular Meandering" "Regular Meanders" "Tortuous Meanders" "Comt_Class", text, 100, normal, "Comt_Class", normal Page 2 STHM_2015.txt "______", caption, normal, "______", normal, expanded "SEGMENT_CHARACTER", caption, normal, "SEGMENT_CHARACTER", normal, expanded "Percent_Gradient", numeric, 1, 0.0, 100.0, 99.0, normal, "Percent_Gradient", normal "Spawning_Habitat", menu, normal, "Spawning_Habitat", normal "Anadromous" "Resident" "Unknown", default "Potential" "Livestock_access", menu, normal, "Livestock_access", normal "Yes" "Bars", menu, normal, "Bars", normal "None", default "Side" "Diagonal" "Mid-channel" "Spanning" "Braided" "Islands", menu, normal, "Islands", normal "None", default "Occasional" "Frequent - Irregular" "Frequent - Regular" "Split" "Anastomosing" "Comt_SChar", text, 100, normal, "Comt_SChar", normal "______", caption, normal, "______", normal, expanded "SUBSTRATE", caption, normal, "SUBSTRATE", normal, expanded "Sub_Organic", numeric, 0, 0, 100, 99, normal, "Sub_Organic", normal "Sub_Fines", numeric, 0, 0, 100, 99, normal, "Sub_Fines", normal "Sub_Gravel", numeric, 0, 0, 100, 99, normal, "Sub_Gravel", normal "Sub_Pebble", numeric, 0, 0, 100, 99, normal, "Sub_Pebble", normal "Sub_Cobble", numeric, 0, 0, 100, 99, normal, "Sub_Cobble", normal "Sub_Blder", numeric, 0, 0, 100, 99, normal, "Sub_Blder", normal "Sub_BedRk", numeric, 0, 0, 100, 99, normal, "Sub_BedRk", normal "Embeddedness", menu, normal, "Embeddedness", normal "None" "Low (0-25%)",[L] "Medium (25-75%)",[M] "High (75%+)",[H] "Unknown", default "Compaction", menu, normal, "Compaction", normal "Low",[L] "Medium",[M] "High",[H] "Comt_Sub", text, 100, normal, "Comt_Sub", normal "______", caption, normal, "______", normal, expanded "CHANNEL ", caption, normal, "CHANNEL ", normal, expanded "Width_W", numeric, 2, 0.00, 250.00, 0.00, normal, "Width_W", normal Page 3 STHM_2015.txt "Width_BF", numeric, 2, 0.00, 500.00, 0.00, normal, "Width_BF", normal "Width_LFP", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width_LFP", normal "Width_RFP", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width_RFP", normal "Depth_W", numeric, 2, 0.00, 20.00, 0.00, normal, "Depth_W", normal "Depth_BF", numeric, 2, 0.00, 20.00, 0.00, normal, "Depth_BF", normal "Depth_FP", numeric, 2, 0.00, 10.00, 0.00, normal, "Depth_FP", normal "Comt_Chan", text, 100, normal, "Comt_Chan", normal "______", caption, normal, "______", normal, expanded "INSTREAM_COVER", caption, normal, "INSTREAM_COVER", normal, expanded "Total_Cover", numeric, 0, 0, 100, 99, normal, "Total_Cover", normal "B", numeric, 0, 0, 100, 0, normal, "B", normal "DP", numeric, 0, 0, 100, 0, normal, "DP", normal "IV", numeric, 0, 0, 100, 0, normal, "IV", normal "LWD", numeric, 0, 0, 100, 0, normal, "LWD", normal "OV", numeric, 0, 0, 100, 0, normal, "OV", normal "SWD", numeric, 0, 0, 100, 0, normal, "SWD", normal "UC", numeric, 0, 0, 100, 0, normal, "UC", normal "LWD_Count", numeric, 0, 0, 999, 999, normal, "LWD_Count", normal "Log_Jam_Count", numeric, 0, 0, 999, 999, normal, "Log_Jam_Count", normal "DP_Count", numeric, 0, 0, 999, 999, normal, "DP_Count", normal "Comt_Cov", text, 100, normal, "Comt_Cov", normal "______", caption, normal, "______", normal, expanded "FLORA_FAUNA ", caption, normal, "FLORA_FAUNA ", normal, expanded "CmmntFlora", text, 100, normal, "CmmntFlora", normal "CmmntFauna", text, 100, normal, "CmmntFauna", normal
"LEFT_BANK", line, "LEFT_BANK", 1, seconds, Code "LEFT BANK REFERENCE", caption, normal, "LEFT BANK REFERENCE", normal, expanded "River_Name", text, 100, normal, "River_Name", normal, Thompson River "Organization", text, 100, normal, "Organization", normal, Ecoscape/Fraser Basin "Date", date, auto, ymd, manual, normal, "Date", normal "Time ", time, auto, 24, manual, normal, "Time ", normal "Crew", text, 50, normal, "Crew", normal, KH/BH;TT;JP "Weather", menu, normal, "Weather", normal "Light Rain",[L] "Heavy Rain",[H] "Snow/Sleet",[N] "Over cast",[OV] "Clear",[S] "Partly Cloudy",[PC] "Other",[O] "Jurisdiction", text, 100, normal, "Jurisdiction", normal "Comments", text, 100, normal, "Comments", normal "______", caption, normal, "______", normal, expanded "SEGMENT CLASS", caption, normal, "SEGMENT CLASS", normal, expanded "Segmnt_Num", numeric, 1, 0.0, 99999.0, 0.0, required, "Segmnt_Num", required, Label1 "Reach_Number", numeric, 1, 0.0, 99999.0, 0.0, required, "Reach_Number", required Page 4 STHM_2015.txt "Shore_Type", menu, required, "Shore_Type", normal "Cliff/Bluff" "Rocky Shore" "Gravel" "Sand " "Confluence" "Wetland" "Other" "Flood Low Bench" "Flood Mid Bench" "Flood High Bench" "Shore_Modifier", menu, normal, "Shore_Modifier", normal "Log Yard" "Marina_small (6-20)" "Marina_large (20+)" "Railway" "Road" "None", default "Other" "Slope", menu, normal, "Slope", normal "Bench" "Low (0-5)" "Moderate (5-20)" "Steep (20-60)" "Very Steep (60+)" "Land_Use", menu, normal, "Land_Use", normal "Agriculture" "Commercial" "Conservation" "Forestry" "Industrial" "Institution" "Multi Family" "Natural Area" "Park" "Recreation" "Rural" "Single Family" "Urban Park" "Lev_of_Imp", menu, normal, "Lev_of_Imp", normal "None", default "Low (<10%)" "Medium (10-40%)" "High (>40%)" "Livest_Acc", menu, normal, "Livest_Acc", normal "Yes" "No", default "PCTDisturbed", numeric, 0, 0, 100, 0, normal, "PCTDisturbed", normal Page 5 STHM_2015.txt "PCTNatural", numeric, 0, 0, 100, 0, normal, "PCTNatural", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Tape_Numb", text, 100, normal, "Tape_Numb", normal "Video_Time", text, 100, normal, "Video_Time", normal "Cmmnt_Clas", text, 100, normal, "Cmmnt_Clas", normal "______", caption, normal, "______", normal, expanded "SHORE TYPE", caption, normal, "SHORE TYPE", normal, expanded "Cliff/Bluff", numeric, 0, 0, 100, 0, normal, "Cliff/Bluff", normal "Rocky", numeric, 0, 0, 100, 0, normal, "Rocky", normal "Gravel", numeric, 0, 0, 100, 0, normal, "Gravel", normal "Sand", numeric, 0, 0, 100, 0, normal, "Sand", normal "Confluence", numeric, 0, 0, 100, 0, normal, "Confluence", normal "Wetland", numeric, 0, 0, 100, 0, normal, "Wetland", normal "Other", numeric, 0, 0, 100, 0, normal, "Other", normal "Flood Low Bench", numeric, 0, 0, 100, 0, normal, "Flood Low Bench", normal "Flood Mid Bench", numeric, 0, 0, 100, 0, normal, "Flood Mid Bench", normal "Flood High Bench", numeric, 0, 0, 100, 0, normal, "Flood High Bench", normal "Stype_comm", text, 100, normal, "Stype_comm", normal "______", caption, normal, "______", normal, expanded "LAND USE", caption, normal, "LAND USE", normal, expanded "Agriculture", numeric, 0, 0, 100, 0, normal, "Agriculture", normal "Commercial", numeric, 0, 0, 100, 0, normal, "Commercial", normal "Conservation", numeric, 0, 0, 100, 0, normal, "Conservation", normal "Forestry", numeric, 0, 0, 100, 0, normal, "Forestry", normal "Industrial", numeric, 0, 0, 100, 0, normal, "Industrial", normal "Infrastructure", numeric, 0, 0, 100, 0, normal, "Infrastructure", normal "Institution", numeric, 0, 0, 100, 0, normal, "Institution", normal "Multi Family", numeric, 0, 0, 100, 0, normal, "Multi Family", normal "Natural Area", numeric, 0, 0, 100, 0, normal, "Natural Area", normal "Park", numeric, 0, 0, 100, 0, normal, "Park", normal "Recreation", numeric, 0, 0, 100, 0, normal, "Recreation", normal "Rural", numeric, 0, 0, 100, 0, normal, "Rural", normal "Single Family", numeric, 0, 0, 100, 0, normal, "Single Family", normal "Urban Park", numeric, 0, 0, 100, 0, normal, "Urban Park", normal "Landu_Commnt", text, 100, normal, "Landu_Commnt", normal "______", caption, normal, "______", normal, expanded "MODIFICATIONS", caption, normal, "MODIFICATIONS", normal, expanded "Retain_Wal", numeric, 0, 0, 99999999, 0, normal, "Retain_Wal", normal "PerRetain_Wall", numeric, 0, 0, 100, 0, normal, "PerRetain_Wall", normal "Retain_Mat", menu, normal, "Retain_Mat", normal "Bio_Eng" "Concrete" "Mixed" "Stonework" "Wood" "Metal" "Tires" "Rock" Page 6 STHM_2015.txt "Other" "Docks", numeric, 0, 0, 99999999, 0, normal, "Docks", normal "Docks_km", numeric, 0, 0, 1000, 0, normal, "Docks_km", normal "Boat_House", numeric, 0, 0, 99999999, 0, normal, "Boat_House", normal "Groynes", numeric, 0, 0, 99999999, 0, normal, "Groynes", normal "Groynes_km", numeric, 0, 0, 1000, 0, normal, "Groynes_km", normal "Boat_Launch", numeric, 0, 0, 1000, 0, normal, "Boat_Launch", normal "PerRail_mod", numeric, 0, 0, 100, 0, normal, "PerRail_mod", normal "PerRoad_mod", numeric, 0, 0, 100, 0, normal, "PerRoad_mod", normal "Marin_Rail", numeric, 0, 0, 99999999, 0, normal, "Marin_Rail", normal "Marinas", numeric, 0, 0, 99999999, 0, normal, "Marinas", normal "Sub_modification", menu, normal, "Sub_modification", normal "Yes" "No" "PerSub_mod", numeric, 0, 0, 100, 0, normal, "PerSub_mod", normal "Commnt_Mod", text, 100, normal, "Commnt_Mod", normal "______", caption, normal, "______", normal, expanded "BANK STABILITY", caption, normal, "BANK STABILITY", normal, expanded "L_BkStbility", menu, normal, "L_BkStbility", normal "High",[H] "Medium",[M] "Low",[L] "Erosion",[VL] "PctEroding", numeric, 0, 0, 100, 0, normal, "PctEroding", normal "L_Bank_Material", menu, normal, "L_Bank_Material", normal "Concrete",[C] "Gabions",[GB] "Pilings",[P] "Stonework",[S] "RipRap",[RR] "Retain Wall/Bank Stb",[EHB] "Sandbags",[SB] "Wood",[W] "Bark_Mulch",[BM] "Asphalt",[AS] "Dyke",[DY] "Till",[T] "Fines",[F] "Gravel",[G] "Cobble",[CB] "Boulder",[B] "Bed_Rock",[BR] "Other",[O] "L_Comment", text, 100, normal, "L_Comment", normal "______", caption, normal, "______", normal, expanded "FLORA & FAUNA ", caption, normal, "FLORA & FAUNA ", normal, expanded "Veterans", menu, normal, "Veterans", normal "No", default Page 7 STHM_2015.txt "<5" "5-25" ">25" "Snags", menu, normal, "Snags", normal "No", default "<5" "5-25" ">25" "Cmmnt_Flra", text, 100, normal, "Cmmnt_Flra", normal "Cmmnt_Faun", text, 100, normal, "Cmmnt_Faun", normal
"RIGHT_BANK", line, "RIGHT_BANK", 1, seconds, Code "RIGHT BANK REFERENCE", caption, normal, "RIGHT BANK REFERENCE", normal, expanded "River_Name", text, 100, normal, "River_Name", normal, Thompson River "Organization", text, 100, normal, "Organization", normal, Ecoscape/Fraser Basin "Date", date, auto, ymd, manual, normal, "Date", normal "Time ", time, auto, 24, manual, normal, "Time ", normal "Crew", text, 50, normal, "Crew", normal, KH/BH;TT;JP "Weather", menu, normal, "Weather", normal "Light Rain",[L] "Heavy Rain",[H] "Snow/Sleet",[N] "Over cast",[OV] "Clear",[S] "Partly Cloudy",[PC] "Other",[O] "Jurisdiction", text, 100, normal, "Jurisdiction", normal "Comments", text, 100, normal, "Comments", normal "______", caption, normal, "______", normal, expanded "SEGMENT CLASS", caption, normal, "SEGMENT CLASS", normal, expanded "Segmnt_Num", numeric, 1, 0.0, 99999.0, 0.0, required, "Segmnt_Num", required, Label1 "Reach_Number", numeric, 1, 0.0, 99999.0, 0.0, required, "Reach_Number", required "Shore_Type", menu, required, "Shore_Type", normal "Cliff/Bluff" "Rocky Shore" "Gravel" "Sand " "Confluence" "Wetland" "Other" "Flood Low Bench" "Flood Mid Bench" "Flood High Bench" "Shore_Modifier", menu, normal, "Shore_Modifier", normal "Log Yard" "Marina_small (6-20)" "Marina_large (20+)" Page 8 STHM_2015.txt "Railway" "Road" "None", default "Other" "Slope", menu, normal, "Slope", normal "Bench" "Low (0-5)" "Moderate (5-20)" "Steep (20-60)" "Very Steep (60+)" "Land_Use", menu, normal, "Land_Use", normal "Agriculture" "Commercial" "Conservation" "Forestry" "Industrial" "Institution" "Multi Family" "Natural Area" "Park" "Recreation" "Rural" "Single Family" "Urban Park" "Lev_of_Imp", menu, normal, "Lev_of_Imp", normal "None", default "Low (<10%)" "Medium (10-40%)" "High (>40%)" "Livest_Acc", menu, normal, "Livest_Acc", normal "Yes" "No", default "PCTDisturbed", numeric, 0, 0, 100, 0, normal, "PCTDisturbed", normal "PCTNatural", numeric, 0, 0, 100, 0, normal, "PCTNatural", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Tape_Numb", text, 100, normal, "Tape_Numb", normal "Video_Time", text, 100, normal, "Video_Time", normal "Cmmnt_Clas", text, 100, normal, "Cmmnt_Clas", normal "______", caption, normal, "______", normal, expanded "SHORE TYPE", caption, normal, "SHORE TYPE", normal, expanded "Cliff/Bluff", numeric, 0, 0, 100, 0, normal, "Cliff/Bluff", normal "Rocky", numeric, 0, 0, 100, 0, normal, "Rocky", normal "Gravel", numeric, 0, 0, 100, 0, normal, "Gravel", normal "Sand", numeric, 0, 0, 100, 0, normal, "Sand", normal "Confluence", numeric, 0, 0, 100, 0, normal, "Confluence", normal "Wetland", numeric, 0, 0, 100, 0, normal, "Wetland", normal "Other", numeric, 0, 0, 100, 0, normal, "Other", normal "Flood Low Bench", numeric, 0, 0, 100, 0, normal, "Flood Low Bench", normal Page 9 STHM_2015.txt "Flood Mid Bench", numeric, 0, 0, 100, 0, normal, "Flood Mid Bench", normal "Flood High Bench", numeric, 0, 0, 100, 0, normal, "Flood High Bench", normal "Stype_comm", text, 100, normal, "Stype_comm", normal "______", caption, normal, "______", normal, expanded "LAND USE", caption, normal, "LAND USE", normal, expanded "Agriculture", numeric, 0, 0, 100, 0, normal, "Agriculture", normal "Commercial", numeric, 0, 0, 100, 0, normal, "Commercial", normal "Conservation", numeric, 0, 0, 100, 0, normal, "Conservation", normal "Forestry", numeric, 0, 0, 100, 0, normal, "Forestry", normal "Industrial", numeric, 0, 0, 100, 0, normal, "Industrial", normal "Infrastructure", numeric, 0, 0, 100, 0, normal, "Infrastructure", normal "Institution", numeric, 0, 0, 100, 0, normal, "Institution", normal "Multi Family", numeric, 0, 0, 100, 0, normal, "Multi Family", normal "Natural Area", numeric, 0, 0, 100, 0, normal, "Natural Area", normal "Park", numeric, 0, 0, 100, 0, normal, "Park", normal "Recreation", numeric, 0, 0, 100, 0, normal, "Recreation", normal "Rural", numeric, 0, 0, 100, 0, normal, "Rural", normal "Single Family", numeric, 0, 0, 100, 0, normal, "Single Family", normal "Urban Park", numeric, 0, 0, 100, 0, normal, "Urban Park", normal "Landu_Commnt", text, 100, normal, "Landu_Commnt", normal "______", caption, normal, "______", normal, expanded "MODIFICATIONS", caption, normal, "MODIFICATIONS", normal, expanded "Retain_Wal", numeric, 0, 0, 99999999, 0, normal, "Retain_Wal", normal "PerRetain_Wall", numeric, 0, 0, 100, 0, normal, "PerRetain_Wall", normal "Retain_Mat", menu, normal, "Retain_Mat", normal "Bio_Eng" "Concrete" "Mixed" "Stonework" "Wood" "Metal" "Tires" "Rock" "Other" "Docks", numeric, 0, 0, 99999999, 0, normal, "Docks", normal "Docks_km", numeric, 0, 0, 1000, 0, normal, "Docks_km", normal "Boat_House", numeric, 0, 0, 99999999, 0, normal, "Boat_House", normal "Groynes", numeric, 0, 0, 99999999, 0, normal, "Groynes", normal "Groynes_km", numeric, 0, 0, 1000, 0, normal, "Groynes_km", normal "Boat_Launch", numeric, 0, 0, 1000, 0, normal, "Boat_Launch", normal "PerRail_mod", numeric, 0, 0, 100, 0, normal, "PerRail_mod", normal "PerRoad_mod", numeric, 0, 0, 100, 0, normal, "PerRoad_mod", normal "Marin_Rail", numeric, 0, 0, 99999999, 0, normal, "Marin_Rail", normal "Marinas", numeric, 0, 0, 99999999, 0, normal, "Marinas", normal "Sub_modification", menu, normal, "Sub_modification", normal "Yes" "No" "PerSub_mod", numeric, 0, 0, 100, 0, normal, "PerSub_mod", normal Page 10 STHM_2015.txt "Commnt_Mod", text, 100, normal, "Commnt_Mod", normal "______", caption, normal, "______", normal, expanded "BANK STABILITY", caption, normal, "BANK STABILITY", normal, expanded "L_BkStbility", menu, normal, "L_BkStbility", normal "High",[H] "Medium",[M] "Low",[L] "Erosion",[VL] "PctEroding", numeric, 0, 0, 100, 0, normal, "PctEroding", normal "L_Bank_Material", menu, normal, "L_Bank_Material", normal "Concrete",[C] "Gabions",[GB] "Pilings",[P] "Stonework",[S] "RipRap",[RR] "Retain Wall/Bank Stb",[EHB] "Sandbags",[SB] "Wood",[W] "Bark_Mulch",[BM] "Asphalt",[AS] "Dyke",[DY] "Till",[T] "Fines",[F] "Gravel",[G] "Cobble",[CB] "Boulder",[B] "Bed_Rock",[BR] "Other",[O] "L_Comment", text, 100, normal, "L_Comment", normal "______", caption, normal, "______", normal, expanded "FLORA & FAUNA ", caption, normal, "FLORA & FAUNA ", normal, expanded "Veterans", menu, normal, "Veterans", normal "No", default "<5" "5-25" ">25" "Snags", menu, normal, "Snags", normal "No", default "<5" "5-25" ">25" "Cmmnt_Flra", text, 100, normal, "Cmmnt_Flra", normal "Cmmnt_Faun", text, 100, normal, "Cmmnt_Faun", normal
"Chan_Morph", area, "Chan_Morph", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Character", menu, normal, "Character", normal Page 11 STHM_2015.txt "Bar",[BA] "Beaver Pond",[BP] "Cascade",[C] "Cascade/Pool",[CP] "Falls",[F] "Glide",[GL] "Pool",[P] "Run",[RN] "Riffle",[RF] "Riffle/Pool",[RP] "Slough",[S] "Standing",[S] "Wetland",[HMW] "Other",[O] "Area", numeric, 2, 0.00, 1000.00, 0.00, normal, "Area", normal "Comments", text, 100, normal, "Comments", normal "______", caption, normal, "______", normal, expanded "SUBSTRATE", caption, normal, "SUBSTRATE", normal, expanded "Sub_Organic", numeric, 0, 0, 100, 0, normal, "Sub_Organic", normal "Sub_Fines", numeric, 0, 0, 100, 0, normal, "Sub_Fines", normal "Sub_Gravel", numeric, 0, 0, 100, 0, normal, "Sub_Gravel", normal "Sub_Cobble", numeric, 0, 0, 100, 0, normal, "Sub_Cobble", normal "Sub_Blder", numeric, 0, 0, 100, 0, normal, "Sub_Blder", normal "Sub_BedRk", numeric, 0, 0, 100, 0, normal, "Sub_BedRk", normal "Embeddedness", menu, normal, "Embeddedness", normal "None" "Low (0-25%)",[L] "Medium (25-75%)",[M] "High (75%+)",[H] "Unknown", default "Compaction", menu, normal, "Compaction", normal "Low",[L] "Medium",[M] "High",[H] "Comt_Sub", text, 100, normal, "Comt_Sub", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Erosion", line, "Erosion", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Source_Erosion", menu, normal, "Source_Erosion", normal, Label2 "Bank Erosion",[HCEB] "Culvert",[CV] "Headwall",[H] "Lack of Riparian Veg",[WDL] "Livestock Access",[WDC] "Streamside Grazing",[WDG] "Landslide " Page 12 STHM_2015.txt "Debris flow/torrent" "Sloughing " "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Severity", menu, required, "Severity", required "Low" "Moderate" "High" "Extreme" "Exposure", menu, normal, "Exposure", normal "Clay",[C] "Silt",[Si] "Till",[T] "Bedrock",[B] "Roots",[R] "Soil",[S] "Other",[O] "Length", numeric, 0, 0, 10000, 0, normal, "Length", normal "Width", numeric, 0, 0, 1000, 0, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Slope Degrees", numeric, 0, 0, 90, 0, normal, "Slope Degrees", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Erosion", point, "Erosion", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Source_Erosion", menu, normal, "Source_Erosion", normal, Label2 "Bank Erosion",[HCEB] "Culvert",[CV] "Headwall",[H] "Lack of Riparian Veg",[WDL] "Livestock Access",[WDC] "Streamside Grazing",[WDG] "Landslide " "Debris flow/torrent" "Sloughing " "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Severity", menu, required, "Severity", required Page 13 STHM_2015.txt "Low" "Moderate" "High" "Extreme" "Exposure", menu, normal, "Exposure", normal "Clay",[C] "Silt",[Si] "Till",[T] "Bedrock",[B] "Roots",[R] "Soil",[S] "Other",[O] "Length", numeric, 0, 0, 10000, 0, normal, "Length", normal "Width", numeric, 0, 0, 1000, 0, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Slope Degrees", numeric, 0, 0, 90, 0, normal, "Slope Degrees", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Modification", line, "Modification", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Modification", menu, normal, "Type_Modification", normal, Label2 "Boat Launch",[BL] "Bridge",[BR] "Catchbasin",[CB] "Channelization",[HOC] "Dam",[HOD] "Detention Pond",[DP] "Dock",[DK] "Dredging",[HBDD] "Fences",[HOF] "FloodGate",[FG] "Garbage/Pollution",[WP] "Gravel Pit",[GP] "Livestock Crossing",[LC] "Livestock Access",[LA] "Logging",[LG] "PipeCrossing",[PL] "Pump Station",[PS] "Rec Access",[RA] "Retain Wall/Bank Stb",[EHB] "Rip_Rap",[RR] "Road",[R] "Trail",[TR] "Water Withdrawal",[FUP] "Other",[O] "Bank", menu, normal, "Bank", normal Page 14 STHM_2015.txt "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Type_Material", menu, normal, "Type_Material", normal "Concrete",[C] "Gabions",[GB] "Pilings",[P] "Stonework",[S] "Sandbags",[SB] "Wood",[W] "Gravel",[G] "Bark_Mulch",[BM] "Asphalt",[AS] "Dyke",[DY] "Other",[O] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Modification", point, "Modification", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Modification", menu, normal, "Type_Modification", normal, Label2 "Boat Launch",[BL] "Bridge",[BR] "Catchbasin",[CB] "Channelization",[HOC] "Dam",[HOD] "Detention Pond",[DP] "Dock",[DK] "Dredging",[HBDD] "Fences",[HOF] "FloodGate",[FG] "Garbage/Pollution",[WP] "Gravel Pit",[GP] "Livestock Crossing",[LC] "Livestock Access",[LA] "Logging",[LG] "PipeCrossing",[PL] "Pump Station",[PS] "Rec Access",[RA] "Retain Wall/Bank Stb",[EHB] "Rip_Rap",[RR] "Road",[R] "Trail",[TR] Page 15 STHM_2015.txt "Water Withdrawal",[FUP] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Type_Material", menu, normal, "Type_Material", normal "Concrete",[C] "Gabions",[GB] "Pilings",[P] "Stonework",[S] "Sandbags",[SB] "Wood",[W] "Gravel",[G] "Bark_Mulch",[BM] "Asphalt",[AS] "Dyke",[DY] "Other",[O] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Fish_Habitat", line, "Fish_Habitat", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Habitat", menu, normal, "Type_Habitat", normal, Label2 "Boulder",[B] "Deep Pool",[DP] "Instream Vegetation",[IV] "Large Woody Debris",[LWD] "Over Stream Vegetn.",[OV] "Rearing_Nursery",[RE] "Small Woody Debris",[SWD] "Spawning Habitat",[HS] "Undercut Bank",[UC] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Area", numeric, 2, 0.00, 1000.00, 0.00, normal, "Area", normal Page 16 STHM_2015.txt "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Fish_Habitat", point, "Fish_Habitat", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Habitat", menu, normal, "Type_Habitat", normal, Label2 "Boulder",[B] "Deep Pool",[DP] "Instream Vegetation",[IV] "Large Woody Debris",[LWD] "Over Stream Vegetn.",[OV] "Rearing_Nursery",[RE] "Small Woody Debris",[SWD] "Spawning Habitat",[HS] "Undercut Bank",[UC] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Area", numeric, 2, 0.00, 1000.00, 0.00, normal, "Area", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Culvert", point, "Culvert", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Culvert", menu, normal, "Type_Culvert", normal, Label2 "Box Culvert",[BC] "Gated Inlet",[GI] "Gated Outlet",[GO] "Gated Multiple Inlet",[GMI] "Gated Multiple Out",[GMO] "Inlet",[I] "Inlet Stacked",[IS] "Multiple Inlet",[MI] "Multiple Outlet",[MO] "Outlet",[O] "Outlet Stacked",[OS] "Owner", menu, normal, "Owner", normal "Municipal",[MU] "Private",[PR] "Condition", menu, normal, "Condition", normal Page 17 STHM_2015.txt "Good",[G] "Partially Collapsed",[P] "Collapsed/Plugged",[C] "Barrier", menu, required, "Barrier", required "Yes",[Y] "No",[N] "Potential",[P] "unknown", default "Material", menu, required, "Material", required "Concrete",[C] "Steel",[S] "Wood",[W] "Iron",[I] "Metal_Concrete",[MC] "PVC",[P] "Asphalt coded",[AD] "Corrugated Steel",[CS] "Other",[O] "Substrate", menu, normal, "Substrate", normal "Boulders",[B] "Cobbles",[C] "Fines",[F] "Gravels",[G] "Mixed",[M] "Same as Culvert",[S] "Form", menu, normal, "Form", normal "Circular",[C] "Rectangular",[R] "Arch",[A] "Vertical Ellipse",[V] "Horizontal Ellipse",[H] "Other",[O] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Diameter", numeric, 2, 0.00, 1000.00, 0.00, normal, "Diameter", normal "ScreenSize", numeric, 2, 0.00, 100.00, 0.00, normal, "ScreenSize", normal "StormOutlets", numeric, 0, 0, 999, 0, normal, "StormOutlets", normal "Headwall", menu, normal, "Headwall", normal "Concrete",[C] "Concrete Block",[CB] "Gabion",[G] "Sand bag",[SB] "Wood",[W] "Till",[T] "Rip_rap",[RR] "Stonework",[ST] Page 18 STHM_2015.txt "Apron", menu, normal, "Apron", normal "Yes",[Y] "No",[N], default "Baffles", menu, normal, "Baffles", normal "Yes",[Y] "No",[N], default "Comments", text, 100, normal, "Comments", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Discharge", point, "Discharge", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Discharge", menu, normal, "Type_Discharge", normal, Label2 "Agricultural Runoff",[WPA] "HouseEffluent",[WE] "Landfill Leachates",[WPML] "Pollutant",[WP] "Pulp Mill/Effluent",[WPP] "Storm Drain",[WPD] "Septic Effluent",[WPMP] "Tile Drain",[WPI] "Trench",[WPE] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Material", menu, required, "Material", required "Concrete",[C] "Steel",[S] "Wood",[W] "Iron",[I] "PVC",[P] "Asphalt coded",[AD] "Corrugated Steel",[CS] "Other",[O] "Headwall", menu, normal, "Headwall", normal "Concrete",[C] "Concrete Block",[CB] "Gabion",[G] "Sand bag",[SB] "Wood",[W] "Till",[T] "Rip_rap",[RR] "Stonework",[ST] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal Page 19 STHM_2015.txt "Diameter", numeric, 2, 0.00, 1000.00, 0.00, normal, "Diameter", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Temperature", numeric, 2, 0.00, 100.00, 0.00, normal, "Temperature", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Fish_Sample", point, "Fish_Sample", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "TrapNo", numeric, 0, 0, 100, 1, normal, "TrapNo", normal, Label2 "DateIn", date, manual, ymd, manual, normal, "DateIn", normal "DateOut", date, manual, ymd, manual, normal, "DateOut", normal "Method", menu, normal, "Method", normal "Visual",[V] "Trap",[T] "Other",[O] "Species", menu, normal, "Species", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_total", numeric, 0, 0, 100, 0, normal, "Count_total", normal "Redd", menu, normal, "Redd", normal "Yes",[Y] "No",[N] "PhotoNum", text, 10, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal "______", caption, normal, "______", normal, expanded "SPECIES 1", caption, normal, "SPECIES 1", normal, expanded "Sp_1", menu, normal, "Sp_1", normal "General Fish Observn",[FSH] "Bull trout",[BT] Page 20 STHM_2015.txt "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_1", numeric, 0, 0, 1000, 0, normal, "Count_1", normal "Age_1", menu, normal, "Age_1", normal "Juvenile",[J] "Immature",[I] "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_1", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_1", normal "______", caption, normal, "______", normal, expanded "SPECIES 2", caption, normal, "SPECIES 2", normal, expanded "Sp_2", menu, normal, "Sp_2", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] Page 21 STHM_2015.txt "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Count_2", numeric, 0, 0, 1000, 0, normal, "Count_2", normal "Age_2", menu, normal, "Age_2", normal "Juvenile",[J] "Immature",[I] "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_2", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_2", normal "______", caption, normal, "______", normal, expanded "SPECIES 3", caption, normal, "SPECIES 3", normal, expanded "Sp_3", menu, normal, "Sp_3", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_3", numeric, 0, 0, 1000, 0, normal, "Count_3", normal "Age_3", menu, normal, "Age_3", normal "Juvenile",[J] "Immature",[I] "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_3", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_3", normal Page 22 STHM_2015.txt "______", caption, normal, "______", normal, expanded "SPECIES 4", caption, normal, "SPECIES 4", normal, expanded "Sp_4", menu, normal, "Sp_4", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_4", numeric, 0, 0, 1000, 0, normal, "Count_4", normal "Age_4", menu, normal, "Age_4", normal "Juvenile",[J] "Immature",[I] "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_4", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_4", normal "______", caption, normal, "______", normal, expanded "SPECIES 5", caption, normal, "SPECIES 5", normal, expanded "Sp_5", menu, normal, "Sp_5", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] Page 23 STHM_2015.txt "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_5", numeric, 0, 0, 1000, 0, normal, "Count_5", normal "Age_5", menu, normal, "Age_5", normal "Juvenile",[J] "Immature",[I] "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_5", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_5", normal "______", caption, normal, "______", normal, expanded "SPECIES 6", caption, normal, "SPECIES 6", normal, expanded "Sp_6", menu, normal, "Sp_6", normal "General Fish Observn",[FSH] "Bull trout",[BT] "Coho",[CO] "Chinook",[CH] "Chum",[CM] "Cutthroat Trout",[CT] "Westslope Cutthroat ",[WCT] "Dolly Varden",[DV] "Anadromous Dolly Var",[ADV] "Pink",[PK] "Rainbow",[RB] "Stickleback",[SB] "Salmonid",[SA] "Sculpin",[CC] "Kokanee",[KO] "Sockeye",[SK] "Steelhead",[ST] "Sucker",[SU] "Trout",[TR] "Whitefish",[WF] "Other",[O] "Count_6", numeric, 0, 0, 1000, 0, normal, "Count_6", normal "Age_6", menu, normal, "Age_6", normal "Juvenile",[J] "Immature",[I] Page 24 STHM_2015.txt "Mature",[M] "Spawning",[SPW] "Spent",[S] "Varied",[V] "Mort",[Mt] "ForkLth_6", numeric, 1, 0.0, 100.0, 0.0, normal, "ForkLth_6", normal
"Enhancement", point, "Enhancement", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Enhance", menu, normal, "Type_Enhance", normal, Label2 "Fishways",[EOF] "Hatchery",[ECAH] "Incubation Box",[ECNX] "Livestock Fencing",[LF] "LWD Placement",[EHRL] "Log/Rock Wiers",[EHRI] "Riparian Plantings",[EHBP] "Riparian Zone Fence",[EHBF] "Rock/Boulder Placeme",[EHRR] "Side Channel/Pools",[EHRS] "Spawning Gravel",[EHSP] "Veg Bank Stabilize",[EHBV] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Status", menu, normal, "Status", normal "Existing",[E] "Potential",[P] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Diameter", numeric, 2, 0.00, 1000.00, 0.00, normal, "Diameter", normal "Comments", text, 100, normal, "Comments", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Enhancement", line, "Enhancement", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Enhance", menu, normal, "Type_Enhance", normal, Label2 "Fishways",[EOF] "Hatchery",[ECAH] "Incubation Box",[ECNX] "Livestock Fencing",[LF] "LWD Placement",[EHRL] Page 25 STHM_2015.txt "Log/Rock Wiers",[EHRI] "Riparian Plantings",[EHBP] "Riparian Zone Fence",[EHBF] "Rock/Boulder Placeme",[EHRR] "Side Channel/Pools",[EHRS] "Spawning Gravel",[EHSP] "Veg Bank Stabilize",[EHBV] "Other",[O] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Status", menu, normal, "Status", normal "Existing",[E] "Potential",[P] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Diameter", numeric, 2, 0.00, 1000.00, 0.00, normal, "Diameter", normal "Comments", text, 100, normal, "Comments", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Line_generic", line, "Line_generic", 1, seconds, 1, Code "Comment", text, 100, normal, "Comment", normal, Label1
"Obstruction", point, "Obstruction", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, normal, "Point_number", normal, Label1 "Type_Obstruction", menu, normal, "Type_Obstruction", normal, Label2 "Beaver Dam",[BD] "Canyon",[CN] "Cascade",[C] "Dam",[D] "Falls",[F] "Fences",[FE] "Hydro Dam",[HD] "Log Jam",[X] "Persistent Debris",[PD] "Pump",[PU] "Rock",[R] "Velocity Barrier",[VB] "Other",[OT] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] Page 26 STHM_2015.txt "Barrier", menu, required, "Barrier", required "Yes",[Y] "Potential",[P] "unknown", default "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Diameter", numeric, 2, 0.00, 1000.00, 0.00, normal, "Diameter", normal "Height", numeric, 2, 0.00, 1000.00, 0.00, normal, "Height", normal "Slope", numeric, 0, 0, 90, 0, normal, "Slope", normal "ScreenSize", numeric, 2, 0.00, 100.00, 0.00, normal, "ScreenSize", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Photo_Location", point, "Photo_Location", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Photo_Roll_&_Frame", text, 100, normal, "Photo_Roll_&_Frame", normal, Label2 "Photo_Direction", menu, normal, "Photo_Direction", normal "Upstream",[U] "Downstream",[D] "Accross_stream",[X] "Up",[UP] "Down",[BD] "Photo_Bearing", numeric, 0, 0, 360, 0, normal, "Photo_Bearing", normal "Photo_Comments", text, 100, normal, "Photo_Comments", normal
"POINT", point, "POINT", 1, seconds, 1, Code "Type_Point", menu, required, "Type_Point", required, Label1 "Location Point",[L] "Start Point",[S] "End Point",[E] "Reference Point",[RP] "Bench Mark",[BM] "Monument",[MT] "Map Tie Point",[MTP] "Reach Break",[R] "Riparian Band",[RB] "Segment Break",[SB] "Elevation",[Alt] "Left Top of Bank",[LTOB] "Right Top of Bank",[RTOB] "Point_number", numeric, 1, 0.0, 99999.0, 0.0, normal, "Point_number", normal, Label2 "Distance", numeric, 2, 0.00, 1000.00, 0.00, normal, "Distance", normal "Bearing", numeric, 0, 0, 360, 0, normal, "Bearing", normal "Gradient", numeric, 0, 0, 90, 0, normal, "Gradient", normal "Elevation", numeric, 0, 0, 2000, 0, normal, "Elevation", normal Page 27 STHM_2015.txt "Comments", text, 100, normal, "Comments", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Point_generic", point, "Point_generic", 1, seconds, 1, Code "Comment", text, 100, normal, "Comment", normal, Label1 "Photo", filename, normal, "Photo", normal, Label2
"Tree_Wildlife", point, "Tree_Wildlife", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Tree", menu, normal, "Type_Tree", normal, Label2 "Coniferous" "Deciduous" "Unknown" "Veteran_tree", menu, normal, "Veteran_tree", normal "Yes" "DBH", numeric, 2, 0.00, 20.00, 0.00, normal, "DBH", normal "Mast_tree", menu, normal, "Mast_tree", normal "Yes" "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Nesting", menu, normal, "Nesting", normal "Potential" "Large" "Small" "State", menu, normal, "State", normal "Living" "Dead" "unknown" "Woodpkr_use", menu, normal, "Woodpkr_use", normal "Yes" "Denning", menu, normal, "Denning", normal "Yes" "Perches", menu, normal, "Perches", normal "Yes" "Cavities", menu, normal, "Cavities", normal "1" "2" "3" "4+" "CmmntFlora", text, 100, normal, "CmmntFlora", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"Waterbody", line, "Waterbody", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Page 28 STHM_2015.txt Label1 "Type_Waterbody", menu, normal, "Type_Waterbody", normal, Label2 "Beaver Pond",[BP] "Discontinued",[HMD] "Ditch",[FRT] "Natural Springs",[HMS] "Off Channel",[OffC] "OxBow",[OxB] "Side Channel",[SC] "Tributary",[HMT] "Wetland",[HMW] "Other ",[HM] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Temperature", numeric, 2, 0.00, 100.00, 0.00, normal, "Temperature", normal "PhotoNum", text, 100, normal, "PhotoNum", normal "Comments", text, 100, normal, "Comments", normal
"Waterbody", point, "Waterbody", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Waterbody", menu, normal, "Type_Waterbody", normal, Label2 "Beaver Pond",[BP] "Discontinued",[HMD] "Ditch",[FRT] "Natural Springs",[HMS] "Off Channel",[OffC] "OxBow",[OxB] "Side Channel",[SC] "Tributary",[HMT] "Wetland",[HMW] "Other ",[HM] "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Length", numeric, 2, 0.00, 1000.00, 0.00, normal, "Length", normal "Width", numeric, 2, 0.00, 1000.00, 0.00, normal, "Width", normal "Depth", numeric, 2, 0.00, 1000.00, 0.00, normal, "Depth", normal "Temperature", numeric, 2, 0.00, 100.00, 0.00, normal, "Temperature", normal "PhotoNum", text, 100, normal, "PhotoNum", normal Page 29 STHM_2015.txt "Comments", text, 100, normal, "Comments", normal
"Water_Sample", point, "Water_Sample", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "TDS", numeric, 1, 0.0, 250.0, 0.0, normal, "TDS", normal, Label2 "pH", numeric, 1, 0.0, 15.0, 0.0, normal, "pH", normal "Temp", numeric, 1, 0.0, 100.0, 0.0, normal, "Temp", normal "DO", numeric, 1, 0.0, 25.0, 9.0, normal, "DO", normal "Turbidity", menu, normal, "Turbidity", normal "Clear",[C], default "Lightly Turbid",[L] "Moderately Turbid",[M] "Turbid",[T] "Other" "Comments", text, 100, normal, "Comments", normal
"Wildlife", point, "Wildlife", 1, seconds, 1, Code "Point_number", numeric, 1, 0.0, 99999.0, 0.0, required, "Point_number", required, Label1 "Type_Evidence", menu, normal, "Type_Evidence", normal, Label2 "Calls",[Cl] "Egg masses",[EM] "Nest",[Nt] "Sighted",[St] "Scat/Droppings",[Sd] "Tracks",[Tk] "Other",[O] "Class_Wildlife", menu, normal, "Class_Wildlife", normal "Amphibian" "Large Mammal" "Songbird" "Raptor" "Reptile" "Small Mammal" "Waterbirds" "Waterfowl" "Bank", menu, normal, "Bank", normal "Both",[B] "Instream",[I] "Left",[L] "Right",[R] "Species_Wildlife", text, 45, normal, "Species_Wildlife", normal "CmmntFauna", text, 100, normal, "CmmntFauna", normal "PhotoNum", text, 100, normal, "PhotoNum", normal
"WETLAND_POINT", line, "WETLAND_POINT", 1, seconds, 1, Code "Class", menu, normal, "Class", normal Page 30 STHM_2015.txt "Shallow water" "Marsh" "Swamp" "Fen" "Bog" "Flood_High_Bench" "Flood_Mid_Bench" "Flood_Low_Bench" "Shrub Carr" "Saline Meadow" "Form", menu, normal, "Form", normal "Discharge Swamp" "Flat Swamp" "Mineral-Rise Swamp" "Riparian Swamp" "Slope Swamp" "Basin Marsh" "Hummock Marsh" "Lacustrine Marsh" "Riparian Marsh" "Slope Marsh" "Spring Marsh" "Basin Water" "Lacustrine Water" "Riparian Water" "Subform", menu, normal, "Subform", normal "Floodplain" "Delta" "Isolated" "Linked" "Bay" "Lagoon" "Shore" "Stream" "Discharge" "Spring" "Seepage" "Slope " "Basin Swamp" "Unconfined Swamp" "Swale Swamp" "Floodplain Swamp" "Channel Swamp" "Lacustrine Swamp" "Riverine Swamp" "Beach Ridge Swamp" "Island Swamp" "Levee Swamp" Page 31 STHM_2015.txt "Mound Swamp" "Floodplain Water" "Shore Water" "Stream Water" "Type", menu, normal, "Type", normal "Floating_aquatic" "Submerged_aquatic" "Forb" "Grass" "Low_rush" "Reed" "Sedge" "Tall_rush" "Lichen" "Moss" "Non_vegetated" "Low_Shrub_<2-m" "Mixed_shrub" "Tall_shrub_>2-m" "Tree_Conifer" "Tree_Mixed" "Tree_Broadleaf" "Site_Assocn", menu, normal, "Site_Assocn", normal "Wm01" "Wm02" "Wm03" "Wm04" "Wm05" "Wm06" "Wm07" "Wm51" "Ws01" "Ws02" "Ws03" "Ws04" "Ws05" "Ws06" "Ws07" "Ws09" "Ws10" "Ws50" "Ws51" "Wa" "Fl01" "Fl02" "Fl03" "Fl04" "Fl05" Page 32 STHM_2015.txt "Fl06" "Fl07" "Fm01" "Fm02" "Gs01" "Gs02" "Gs03" "Gs04" "RCG" "Gs00" "Wm00" "Ws00" "No_Veg_Forms", numeric, 0, 0, 16, 1, normal, "No_Veg_Forms", normal "Veg_Forms", text, 100, normal, "Veg_Forms", normal "Dom_Veg", text, 100, normal, "Dom_Veg", normal "REF_PHOTO", text, 100, normal, "REF_PHOTO", normal "Comment_Unit", text, 100, normal, "Comment_Unit", normal
"WETLAND_POINT", area, "WETLAND_POINT", 1, seconds, 1, Code "Class", menu, normal, "Class", normal "Shallow water" "Marsh" "Swamp" "Fen" "Bog" "Flood_High_Bench" "Flood_Mid_Bench" "Flood_Low_Bench" "Shrub Carr" "Saline Meadow" "Form", menu, normal, "Form", normal "Discharge Swamp" "Flat Swamp" "Mineral-Rise Swamp" "Riparian Swamp" "Slope Swamp" "Basin Marsh" "Hummock Marsh" "Lacustrine Marsh" "Riparian Marsh" "Slope Marsh" "Spring Marsh" "Basin Water" "Lacustrine Water" "Riparian Water" "Subform", menu, normal, "Subform", normal "Floodplain" "Delta" Page 33 STHM_2015.txt "Isolated" "Linked" "Bay" "Lagoon" "Shore" "Stream" "Discharge" "Spring" "Seepage" "Slope " "Basin Swamp" "Unconfined Swamp" "Swale Swamp" "Floodplain Swamp" "Channel Swamp" "Lacustrine Swamp" "Riverine Swamp" "Beach Ridge Swamp" "Island Swamp" "Levee Swamp" "Mound Swamp" "Floodplain Water" "Shore Water" "Stream Water" "Type", menu, normal, "Type", normal "Floating_aquatic" "Submerged_aquatic" "Forb" "Grass" "Low_rush" "Reed" "Sedge" "Tall_rush" "Lichen" "Moss" "Non_vegetated" "Low_Shrub_<2-m" "Mixed_shrub" "Tall_shrub_>2-m" "Tree_Conifer" "Tree_Mixed" "Tree_Broadleaf" "Site_Assocn", menu, normal, "Site_Assocn", normal "Wm01" "Wm02" "Wm03" "Wm04" "Wm05" Page 34 STHM_2015.txt "Wm06" "Wm07" "Wm51" "Ws01" "Ws02" "Ws03" "Ws04" "Ws05" "Ws06" "Ws07" "Ws09" "Ws10" "Ws50" "Ws51" "Wa" "Fl01" "Fl02" "Fl03" "Fl04" "Fl05" "Fl06" "Fl07" "Fm01" "Fm02" "Gs01" "Gs02" "Gs03" "Gs04" "RCG" "Gs00" "Wm00" "Ws00" "No_Veg_Forms", numeric, 0, 0, 16, 1, normal, "No_Veg_Forms", normal "Veg_Forms", text, 100, normal, "Veg_Forms", normal "Dom_Veg", text, 100, normal, "Dom_Veg", normal "REF_PHOTO", text, 100, normal, "REF_PHOTO", normal "Comment_Unit", text, 100, normal, "Comment_Unit", normal
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