3 SPECIFIC AREA PLAN DISTRICTS AND OVERLAY ZONES
Table 16.34.060-1 Water Quality Resources | |||
|---|---|---|---|
Protected Water Feature | Upstream Drainage Area | Slope Adjacent to Sensitive Area | Width of Vegetated Corridor (Buffer) |
Intermittent creeks, rivers, streams | Less than 50 acres | Any slope | 25 feet |
50 to 100 acres | <25% | 25 feet | |
50 to 100 acres | ≥25% | 50 feet | |
Greater than 100 acres | <25% | 50 feet | |
Greater than 100 acres | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-2 | |
Perennial creeks, rivers, streams | Any upstream area | <25% | 50 feet |
Any upstream area | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-2 | |
Wetlands, lakes (natural), and springs. | Any drainage | <25% | 50 feet |
Any drainage | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-3 | |
Figure 16.34.060-2 Vegetated Corridors (Buffers) for Intermittent and Perennial Creeks, Rivers, Streams* |
* | Streams are considered perennial until proven intermittent with adequate field documentation (photos, field data), or determination by Oregon Division of State Lands. |
Table 16.34.060-2 Method for Locating Boundaries of Class I and II Riparian Areas | ||||
|---|---|---|---|---|
Distance from Water Feature | Development/Vegetation Status1 | |||
Developed areas not providing vegetative cover | Low structure vegetation or open soils | Woody Vegetation (shrub and scattered forest canopy) | Forest Canopy (closed to open forest canopy) | |
Surface Streams | ||||
0—50′ | Class II | Class I2 | Class I | Class I |
50′—100′ | Class II3 | Class I | Class I | |
100′—150′ | Class II3 if slope>25% | Class II3 if slope>25% | Class II3 | |
150′—200′ | Class II3 if slope>25% | Class II3 if slope>25% | Class II3 if slope>25% | |
Wetlands (Wetland Feature Itself is a Class I Riparian Area) | ||||
0—100′ | Class II3 | Class I | Class I | |
100′—150′ | Class II2 | |||
Flood Areas | ||||
Within 300′ of river or surface stream | Class I | Class I | Class I | |
More than 300′ from river or surface stream | 4 | Class II3 | Class II3 | Class I |
0—100′ from edge of flood area | Class II3, 5 | Class II3 | ||
Notes: |
|---|
1 The vegetative cover type assigned to any particular area was based on two factors: the type of vegetation observed in aerial photographs and the size of the overall contiguous area of vegetative cover to which a particular piece of vegetation belonged. As an example of how the categories were assigned, in order to qualify as "forest canopy," the forested area had to be part of a larger patch of forest of at least one acre in size. |
2 Except that areas within 50 feet of surface streams shall be Class II riparian areas if their vegetation status is "Low structure vegetation or open soils," and if they are high gradient streams. High gradient streams are identified on the Metro Vegetative Cover Map. If a property owner believes the gradient of a stream was incorrectly identified, then the property owner may demonstrate the correct classification by identifying the channel type using the methodology described in the Oregon Watershed Assessment Manual, published by the Oregon Watershed Enhancement Board, and appended to the Metro's Riparian Corridor and Wildlife Habitat Inventories Report, Attachment 1 to Exhibit F to Metro Ordinance No. 05-1077C. |
3 Areas that have been identified as habitats of concern, as designated on the Metro Habitats of Concern Map (on file in the Metro Council office), shall be treated as Class I riparian habitat areas in all cases, subject to the provision of additional information that establishes that they do not meet the criteria used to identify habitats of concern as described in Metro's Technical Report for Fish and Wildlife. Examples of habitats of concern include: Oregon white oak woodlands, bottomland hardwood forests, wetlands, native grasslands, riverine islands or deltas, and important wildlife migration corridors. |
4 If development prior to the effective date of Metro Ordinance No. 05-1077C within a contiguous, undeveloped flood area (to include contiguous flood areas on adjacent properties) that was not mapped as having any vegetative cover has reduced the size of that contiguous flood area to less than one half of an acre in size, then the remaining flood area shall also be considered a developed flood area and shall not be identified as habitat. |
5 Only if within 300 feet of a river or surface stream. |
Table 16.34.060-3 Method for Identifying Habitat Conservation Areas (HCA) | ||||
|---|---|---|---|---|
Fish and Wildlife Habitat Classification | High Urban Development Value1 | Medium Urban development Value2 | Low Urban development Value3 | Other Areas: Parks and Open Spaces, No Design Types Outside UGB |
Class I riparian | Moderate HCA | High HCA | High HCA | High HCA / High HCA+4 |
Class II riparian | Low HCA | Low HCA | Moderate HCA | Moderate HCA / High HCA+4 |
Class A upland wildlife | No HCA | No HCA | No HCA | No HCA / High HCA5 / High HCA+4 |
Class B upland wildlife | No HCA | No HCA | No HCA | No HCA / High HCA5/ High HCA+4 |
NOTE: The default urban development value of property is as depicted on the Metro Habitat Urban Development Value Map. The Metro 2040 Design Type designations provided in the following footnotes are only for use when a City or County is determining whether to make an HCA adjustment. |
1 Primary 2040 design type: regional centers, central City, town centers, and regionally significant industrial areas |
2 Secondary 2040 design type: main streets, station communities, other industrial areas, and employment centers |
3 Tertiary 2040 design type: Inner and outer neighborhoods, corridors |
4 Cities and counties shall give Class I and II riparian habitat and Class A and B upland wildlife habitat in parks designated as natural areas even greater protection than that afforded to High Habitat Conservation Areas. |
5 All Class A and B upland wildlife habitat in publicly-owned parks and open spaces, except for parks and open spaces where the acquiring agency clearly identified that it was acquiring the property to develop it for active recreational uses, shall be considered High HCAs. |
Development Standards | Water Quality Resources | HCAs |
|---|---|---|
Nondiscretionary (16.34.070(C)) | No | Yes |
Special use (16.34.070(D)) | Yes | Yes |
Discretionary (16.34.075) | Yes | Yes/No |
Table 16.34.070-1 HCA Total Disturbance Area Limitations for Detached SFR Uses | |
|---|---|
HCA Type | Total Disturbance Area |
High | 50 percent of the lot area, up to maximum of 5,000 sq. ft. |
Moderate/Low | 65 percent of the lot area, up to maximum of 6,000 sq. ft. |
Table 16.34.070-2 HCA Disturbance Area Limitations for all Uses other than Detached SFR | |
|---|---|
HCA Type | Maximum Disturbance Area |
High | 10 percent of HCA on site |
Moderate | 20 percent of HCA on site |
Low | 50 percent of HCA on site |
Table 16.34.070-3 Tree Replacement | |
|---|---|
Size of Tree to be Removed (Inches in Diameter) | Number of Trees and Shrubs to be Planted |
6 to 12 | 2 trees and 3 shrubs |
13 to 18 | 3 trees and 6 shrubs |
19 to 24 | 5 trees and 12 shrubs |
25 to 30 | 7 trees and 18 shrubs |
over 30 | 10 trees and 30 shrubs |
Table 16.34.075-1 Ecological Functional Values of Riparian Corridors | |
|---|---|
Ecological Function | Landscape Features Providing Functional Values |
Microclimate and shade | Forest canopy or woody vegetation within 100 feet of a stream; a wetland1; or a flood area2. |
Streamflow moderation and water storage | A wetland or other water body3 with a hydrologic connection to a stream; or a flood area2. |
Bank stabilization, sediment and pollution control | All sites within 50 feet of a surface stream; |
Forest canopy, woody vegetation, or low structure vegetation/open soils within 100 feet of a stream or a wetland; or forest canopy, woody vegetation, or low structure vegetation/open soils within a flood area; and | |
Forest canopy, woody vegetation, or low structure vegetation/open soils within 100—200 feet of a stream if the slope is greater than 25 percent. | |
Large wood and channel dynamics | Forest canopy within 150 feet of a stream or wetland; or within a flood area; and |
The channel migration zone is defined by the floodplain, but where there is no mapped floodplain a default of 50 feet is established to allow for the channel migration zone. | |
Organic material sources | Forest canopy or woody vegetation within 100 feet of a stream or wetland; or within a flood area. |
NOTES: |
|---|
1 Refers to "hydrologically-connected wetlands," which are located partially or wholly within one-quarter mile of a surface stream or flood area. |
2 Developed floodplains are not identified as HCAs because they do not provide primary ecological functional value. |
3 "Other water body" could include lakes, ponds, reservoirs, or manmade water feature that is not a water quality facility or farm pond. |
Table 16.34.075-2 Habitat-Friendly Development Practices* | |
|---|---|
Part (a): Design and Construction Practices to Minimize Hydrologic Impacts | |
1. | Amend disturbed soils to original or higher level of porosity to regain infiltration and stormwater storage capacity. |
2. | Use pervious paving materials for residential driveways, parking lots, walkways, and within centers of cul-de-sacs. |
3. | Incorporate stormwater management in road rights-of-way. |
4. | Landscape with rain gardens to provide on-lot detention, filtering of rainwater, and groundwater recharge. |
5. | Use green roofs for runoff reduction, energy savings, improved air quality, and enhanced aesthetics. |
6. | Disconnect downspouts from roofs and direct the flow to vegetated infiltration/filtration areas such as rain gardens. |
7. | Retain rooftop runoff in a rain barrel for later on-lot use in lawn and garden watering. |
8. | Use multifunctional open drainage systems in lieu of more conventional curb-and-gutter systems. |
9. | Use bioretention cells as rain gardens in landscaped parking lot islands to reduce runoff volume and filter pollutants. |
10. | Apply a treatment train approach to provide multiple opportunities for stormwater treatment and reduce the possibility of system failure. |
11. | Reduce sidewalk width and grade them such that they drain to the front yard of a residential lot or retention area. |
12. | Reduce impervious impacts of residential driveways by narrowing widths and moving access to the rear of the site. |
13. | Use shared driveways. |
14. | Reduce width of residential streets, depending on traffic and parking needs. |
15. | Reduce street length, primarily in residential areas, by encouraging clustering and using curvilinear designs. |
16. | Reduce cul-de-sac radii and use pervious vegetated islands in center to minimize impervious effects, and allow them to be utilized for truck maneuvering/loading to reduce need for wide loading areas on site. |
17. | Eliminate redundant non-ADA sidewalks within a site (i.e., sidewalk to all entryways and/or to truck loading areas may be unnecessary for industrial developments). |
18. | Minimize car spaces and stall dimensions, reduce parking ratios, and use shared parking facilities and structured parking. |
19. | Minimize the number of stream crossings and place crossing perpendicular to stream channel if possible. |
20. | Allow narrow street rights-of-way through stream corridors whenever possible to reduce adverse impacts of transportation corridors. |
Part (b): Design and Construction Practices to Minimize Impacts on Wildlife Corridors and Fish Passage | |
1. | Carefully integrate fencing into the landscape to guide animals toward animal crossings under, over, or around transportation corridors. |
2. | Use bridge crossings rather than culverts wherever possible. |
3. | If culverts are utilized, install slab, arch or box type culverts, preferably using bottomless designs that more closely mimic stream bottom habitat. |
4. | Design stream crossings for fish passage with shelves and other design features to facilitate terrestrial wildlife passage. |
5. | Extend vegetative cover through the wildlife crossing in the migratory route, along with sheltering areas. |
Part (c): Miscellaneous Other Habitat-Friendly Design and Construction Practices | |
1. | Use native plants throughout the development (not just in HCA). |
2. | Locate landscaping (required by other sections of the code) adjacent to HCA. |
3. | Reduce light spill-off into HCAs from development. |
4. | Preserve and maintain existing trees and tree canopy coverage, and plant trees, where appropriate, to maximize future tree canopy coverage. |
* | These development practices represent the state of scientific knowledge at the time of this Code's enactment; if more effective habitat-friendly practices become available, they should be used. |
Table 16.34.080-1 (Required Planting Option 1) | |
|---|---|
Size of Tree to be Removed (DBH) | Number of Trees and Shrubs to be Replanted |
6 to 12″ | 2 trees and 3 shrubs |
13 to 18″ | 3 trees and 6 shrubs |
19 to 24″ | 5 trees and 12 shrubs |
25 to 30″ | 7 trees and 18 shrubs |
Over 30″ | 10 trees and 30 shrubs |
Table 16.36.040-1 Street Classifications and Right-of-Way Requirements | ||
|---|---|---|
Street Classification | Minimum ROW | Cross-section |
SE Foster Road Parkway – Minor Arterial | 85 feet (42.5 ft from centerline) | TSP Figure 8-11 |
SE 177th Avenue – 3 Lane Collector With No Parking | 69 feet (34.5 ft from centerline) | TSP Figure 8-12 |
SE Hemrich Road – 3 Lane Collector With No Parking | 69 feet (34.5 ft from centerline) | TSP Figure 8-12SE |
Scouter's Mountain Road – 3 Lane Collector With Parking | 85 feet | TSP Figure 8-13 |
Required Local Streets – Local Street, Parking on Both Sides | 53 feet | TSP Figure 8-15 |
Flexible Local Streets – Local Street, Parking on Both Sides | 53 feet | TSP Figure 8-15 |
Table 16.37.040-1 Street Classifications and Right-of-Way Requirements | ||
|---|---|---|
Street Classification | Minimum ROW | Cross-section |
OR 224 – Major Arterial | 103 feet (51.5 ft from centerline) | TSP Figure 8-11 |
Required Local Streets | 54 feet | TSP Figure 8-15 |
Flexible Local Streets | 54 feet | TSP Figure 8-15 |
3 SPECIFIC AREA PLAN DISTRICTS AND OVERLAY ZONES
Table 16.34.060-1 Water Quality Resources | |||
|---|---|---|---|
Protected Water Feature | Upstream Drainage Area | Slope Adjacent to Sensitive Area | Width of Vegetated Corridor (Buffer) |
Intermittent creeks, rivers, streams | Less than 50 acres | Any slope | 25 feet |
50 to 100 acres | <25% | 25 feet | |
50 to 100 acres | ≥25% | 50 feet | |
Greater than 100 acres | <25% | 50 feet | |
Greater than 100 acres | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-2 | |
Perennial creeks, rivers, streams | Any upstream area | <25% | 50 feet |
Any upstream area | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-2 | |
Wetlands, lakes (natural), and springs. | Any drainage | <25% | 50 feet |
Any drainage | ≥25% | 100 to 200 feet depending on adjacent slope—see Figure 16.34.060-3 | |
Figure 16.34.060-2 Vegetated Corridors (Buffers) for Intermittent and Perennial Creeks, Rivers, Streams* |
* | Streams are considered perennial until proven intermittent with adequate field documentation (photos, field data), or determination by Oregon Division of State Lands. |
Table 16.34.060-2 Method for Locating Boundaries of Class I and II Riparian Areas | ||||
|---|---|---|---|---|
Distance from Water Feature | Development/Vegetation Status1 | |||
Developed areas not providing vegetative cover | Low structure vegetation or open soils | Woody Vegetation (shrub and scattered forest canopy) | Forest Canopy (closed to open forest canopy) | |
Surface Streams | ||||
0—50′ | Class II | Class I2 | Class I | Class I |
50′—100′ | Class II3 | Class I | Class I | |
100′—150′ | Class II3 if slope>25% | Class II3 if slope>25% | Class II3 | |
150′—200′ | Class II3 if slope>25% | Class II3 if slope>25% | Class II3 if slope>25% | |
Wetlands (Wetland Feature Itself is a Class I Riparian Area) | ||||
0—100′ | Class II3 | Class I | Class I | |
100′—150′ | Class II2 | |||
Flood Areas | ||||
Within 300′ of river or surface stream | Class I | Class I | Class I | |
More than 300′ from river or surface stream | 4 | Class II3 | Class II3 | Class I |
0—100′ from edge of flood area | Class II3, 5 | Class II3 | ||
Notes: |
|---|
1 The vegetative cover type assigned to any particular area was based on two factors: the type of vegetation observed in aerial photographs and the size of the overall contiguous area of vegetative cover to which a particular piece of vegetation belonged. As an example of how the categories were assigned, in order to qualify as "forest canopy," the forested area had to be part of a larger patch of forest of at least one acre in size. |
2 Except that areas within 50 feet of surface streams shall be Class II riparian areas if their vegetation status is "Low structure vegetation or open soils," and if they are high gradient streams. High gradient streams are identified on the Metro Vegetative Cover Map. If a property owner believes the gradient of a stream was incorrectly identified, then the property owner may demonstrate the correct classification by identifying the channel type using the methodology described in the Oregon Watershed Assessment Manual, published by the Oregon Watershed Enhancement Board, and appended to the Metro's Riparian Corridor and Wildlife Habitat Inventories Report, Attachment 1 to Exhibit F to Metro Ordinance No. 05-1077C. |
3 Areas that have been identified as habitats of concern, as designated on the Metro Habitats of Concern Map (on file in the Metro Council office), shall be treated as Class I riparian habitat areas in all cases, subject to the provision of additional information that establishes that they do not meet the criteria used to identify habitats of concern as described in Metro's Technical Report for Fish and Wildlife. Examples of habitats of concern include: Oregon white oak woodlands, bottomland hardwood forests, wetlands, native grasslands, riverine islands or deltas, and important wildlife migration corridors. |
4 If development prior to the effective date of Metro Ordinance No. 05-1077C within a contiguous, undeveloped flood area (to include contiguous flood areas on adjacent properties) that was not mapped as having any vegetative cover has reduced the size of that contiguous flood area to less than one half of an acre in size, then the remaining flood area shall also be considered a developed flood area and shall not be identified as habitat. |
5 Only if within 300 feet of a river or surface stream. |
Table 16.34.060-3 Method for Identifying Habitat Conservation Areas (HCA) | ||||
|---|---|---|---|---|
Fish and Wildlife Habitat Classification | High Urban Development Value1 | Medium Urban development Value2 | Low Urban development Value3 | Other Areas: Parks and Open Spaces, No Design Types Outside UGB |
Class I riparian | Moderate HCA | High HCA | High HCA | High HCA / High HCA+4 |
Class II riparian | Low HCA | Low HCA | Moderate HCA | Moderate HCA / High HCA+4 |
Class A upland wildlife | No HCA | No HCA | No HCA | No HCA / High HCA5 / High HCA+4 |
Class B upland wildlife | No HCA | No HCA | No HCA | No HCA / High HCA5/ High HCA+4 |
NOTE: The default urban development value of property is as depicted on the Metro Habitat Urban Development Value Map. The Metro 2040 Design Type designations provided in the following footnotes are only for use when a City or County is determining whether to make an HCA adjustment. |
1 Primary 2040 design type: regional centers, central City, town centers, and regionally significant industrial areas |
2 Secondary 2040 design type: main streets, station communities, other industrial areas, and employment centers |
3 Tertiary 2040 design type: Inner and outer neighborhoods, corridors |
4 Cities and counties shall give Class I and II riparian habitat and Class A and B upland wildlife habitat in parks designated as natural areas even greater protection than that afforded to High Habitat Conservation Areas. |
5 All Class A and B upland wildlife habitat in publicly-owned parks and open spaces, except for parks and open spaces where the acquiring agency clearly identified that it was acquiring the property to develop it for active recreational uses, shall be considered High HCAs. |
Development Standards | Water Quality Resources | HCAs |
|---|---|---|
Nondiscretionary (16.34.070(C)) | No | Yes |
Special use (16.34.070(D)) | Yes | Yes |
Discretionary (16.34.075) | Yes | Yes/No |
Table 16.34.070-1 HCA Total Disturbance Area Limitations for Detached SFR Uses | |
|---|---|
HCA Type | Total Disturbance Area |
High | 50 percent of the lot area, up to maximum of 5,000 sq. ft. |
Moderate/Low | 65 percent of the lot area, up to maximum of 6,000 sq. ft. |
Table 16.34.070-2 HCA Disturbance Area Limitations for all Uses other than Detached SFR | |
|---|---|
HCA Type | Maximum Disturbance Area |
High | 10 percent of HCA on site |
Moderate | 20 percent of HCA on site |
Low | 50 percent of HCA on site |
Table 16.34.070-3 Tree Replacement | |
|---|---|
Size of Tree to be Removed (Inches in Diameter) | Number of Trees and Shrubs to be Planted |
6 to 12 | 2 trees and 3 shrubs |
13 to 18 | 3 trees and 6 shrubs |
19 to 24 | 5 trees and 12 shrubs |
25 to 30 | 7 trees and 18 shrubs |
over 30 | 10 trees and 30 shrubs |
Table 16.34.075-1 Ecological Functional Values of Riparian Corridors | |
|---|---|
Ecological Function | Landscape Features Providing Functional Values |
Microclimate and shade | Forest canopy or woody vegetation within 100 feet of a stream; a wetland1; or a flood area2. |
Streamflow moderation and water storage | A wetland or other water body3 with a hydrologic connection to a stream; or a flood area2. |
Bank stabilization, sediment and pollution control | All sites within 50 feet of a surface stream; |
Forest canopy, woody vegetation, or low structure vegetation/open soils within 100 feet of a stream or a wetland; or forest canopy, woody vegetation, or low structure vegetation/open soils within a flood area; and | |
Forest canopy, woody vegetation, or low structure vegetation/open soils within 100—200 feet of a stream if the slope is greater than 25 percent. | |
Large wood and channel dynamics | Forest canopy within 150 feet of a stream or wetland; or within a flood area; and |
The channel migration zone is defined by the floodplain, but where there is no mapped floodplain a default of 50 feet is established to allow for the channel migration zone. | |
Organic material sources | Forest canopy or woody vegetation within 100 feet of a stream or wetland; or within a flood area. |
NOTES: |
|---|
1 Refers to "hydrologically-connected wetlands," which are located partially or wholly within one-quarter mile of a surface stream or flood area. |
2 Developed floodplains are not identified as HCAs because they do not provide primary ecological functional value. |
3 "Other water body" could include lakes, ponds, reservoirs, or manmade water feature that is not a water quality facility or farm pond. |
Table 16.34.075-2 Habitat-Friendly Development Practices* | |
|---|---|
Part (a): Design and Construction Practices to Minimize Hydrologic Impacts | |
1. | Amend disturbed soils to original or higher level of porosity to regain infiltration and stormwater storage capacity. |
2. | Use pervious paving materials for residential driveways, parking lots, walkways, and within centers of cul-de-sacs. |
3. | Incorporate stormwater management in road rights-of-way. |
4. | Landscape with rain gardens to provide on-lot detention, filtering of rainwater, and groundwater recharge. |
5. | Use green roofs for runoff reduction, energy savings, improved air quality, and enhanced aesthetics. |
6. | Disconnect downspouts from roofs and direct the flow to vegetated infiltration/filtration areas such as rain gardens. |
7. | Retain rooftop runoff in a rain barrel for later on-lot use in lawn and garden watering. |
8. | Use multifunctional open drainage systems in lieu of more conventional curb-and-gutter systems. |
9. | Use bioretention cells as rain gardens in landscaped parking lot islands to reduce runoff volume and filter pollutants. |
10. | Apply a treatment train approach to provide multiple opportunities for stormwater treatment and reduce the possibility of system failure. |
11. | Reduce sidewalk width and grade them such that they drain to the front yard of a residential lot or retention area. |
12. | Reduce impervious impacts of residential driveways by narrowing widths and moving access to the rear of the site. |
13. | Use shared driveways. |
14. | Reduce width of residential streets, depending on traffic and parking needs. |
15. | Reduce street length, primarily in residential areas, by encouraging clustering and using curvilinear designs. |
16. | Reduce cul-de-sac radii and use pervious vegetated islands in center to minimize impervious effects, and allow them to be utilized for truck maneuvering/loading to reduce need for wide loading areas on site. |
17. | Eliminate redundant non-ADA sidewalks within a site (i.e., sidewalk to all entryways and/or to truck loading areas may be unnecessary for industrial developments). |
18. | Minimize car spaces and stall dimensions, reduce parking ratios, and use shared parking facilities and structured parking. |
19. | Minimize the number of stream crossings and place crossing perpendicular to stream channel if possible. |
20. | Allow narrow street rights-of-way through stream corridors whenever possible to reduce adverse impacts of transportation corridors. |
Part (b): Design and Construction Practices to Minimize Impacts on Wildlife Corridors and Fish Passage | |
1. | Carefully integrate fencing into the landscape to guide animals toward animal crossings under, over, or around transportation corridors. |
2. | Use bridge crossings rather than culverts wherever possible. |
3. | If culverts are utilized, install slab, arch or box type culverts, preferably using bottomless designs that more closely mimic stream bottom habitat. |
4. | Design stream crossings for fish passage with shelves and other design features to facilitate terrestrial wildlife passage. |
5. | Extend vegetative cover through the wildlife crossing in the migratory route, along with sheltering areas. |
Part (c): Miscellaneous Other Habitat-Friendly Design and Construction Practices | |
1. | Use native plants throughout the development (not just in HCA). |
2. | Locate landscaping (required by other sections of the code) adjacent to HCA. |
3. | Reduce light spill-off into HCAs from development. |
4. | Preserve and maintain existing trees and tree canopy coverage, and plant trees, where appropriate, to maximize future tree canopy coverage. |
* | These development practices represent the state of scientific knowledge at the time of this Code's enactment; if more effective habitat-friendly practices become available, they should be used. |
Table 16.34.080-1 (Required Planting Option 1) | |
|---|---|
Size of Tree to be Removed (DBH) | Number of Trees and Shrubs to be Replanted |
6 to 12″ | 2 trees and 3 shrubs |
13 to 18″ | 3 trees and 6 shrubs |
19 to 24″ | 5 trees and 12 shrubs |
25 to 30″ | 7 trees and 18 shrubs |
Over 30″ | 10 trees and 30 shrubs |
Table 16.36.040-1 Street Classifications and Right-of-Way Requirements | ||
|---|---|---|
Street Classification | Minimum ROW | Cross-section |
SE Foster Road Parkway – Minor Arterial | 85 feet (42.5 ft from centerline) | TSP Figure 8-11 |
SE 177th Avenue – 3 Lane Collector With No Parking | 69 feet (34.5 ft from centerline) | TSP Figure 8-12 |
SE Hemrich Road – 3 Lane Collector With No Parking | 69 feet (34.5 ft from centerline) | TSP Figure 8-12SE |
Scouter's Mountain Road – 3 Lane Collector With Parking | 85 feet | TSP Figure 8-13 |
Required Local Streets – Local Street, Parking on Both Sides | 53 feet | TSP Figure 8-15 |
Flexible Local Streets – Local Street, Parking on Both Sides | 53 feet | TSP Figure 8-15 |
Table 16.37.040-1 Street Classifications and Right-of-Way Requirements | ||
|---|---|---|
Street Classification | Minimum ROW | Cross-section |
OR 224 – Major Arterial | 103 feet (51.5 ft from centerline) | TSP Figure 8-11 |
Required Local Streets | 54 feet | TSP Figure 8-15 |
Flexible Local Streets | 54 feet | TSP Figure 8-15 |