HomeMy WebLinkAboutHANSEN FARM - FDP190010 - SUBMITTAL DOCUMENTS - ROUND 2 - WETLANDS DOCUMENTSHansen Natural Habitat Buffer Zone
Uplands and Wetlands Restoration and Monitoring Plan
The project creates Natural Habitat Buffer Zones within a 50-foot buffer along the Mail Creek Ditch
(Upland Buffer), initiates restoration activities to the isolated, non-jurisdictional wetland (Wetland),
and improvements to the associated 50-foot buffer (Wetland Buffer) on the Hansen Development Site
(Site). In accordance with City of Fort Collins guidelines, these Buffers should be managed to:
1. Preserve or enhance the ecological character or function and wildlife use of the natural
habitat or feature and to minimize or adequately mitigate the foreseeable impacts of
development.
2. Preserve or enhance the existence of wildlife movement corridors between natural habitats
and features, both within and adjacent to the site.
3. Designed to enhance the natural ecological characteristics of the site. If existing
landscaping within the buffer zone is determined by the decision maker to be incompatible
with the purposes of the buffer zone, then the applicant shall undertake restoration and
mitigation measures such as regrading and/or the replanting of native vegetation.
4. Designed to provide appropriate human access to natural habitats and features and their
associated buffer zones in order to serve recreation purposes, provided that such access is
compatible with the ecological character or wildlife use of the natural habitat or feature.
Essentially, this plan aims to define an approach and provide specific treatments to improve ecological
function and enhance the ecological characteristics of Upland Buffer, Wetland Buffer, and Wetland.
Specifically, this plan will attempt to 1) increase both species and structural diversity of the Upland
and Wetland Buffer vegetation communities using native species, and 2) restore the isolated, non-
jurisdictional Wetland in the central portion of the Site. This plan strictly applies to centrally located,
isolated wetland, and does not apply to wetlands within the banks of Mail Creek Ditch as they will not
be disturbed by the proposed development.
Step 1: Creating Opportunity or Niches
Vegetation currently inhabiting the Mail Creek Ditch Upland Buffer is primarily aggressive, non-native
perennial grasses (smooth brome – Bromus inermis) and forbs (alfalfa – Medicago sativa). The
central, wettest portion of the isolated wetland is dominated by perennial forbs (smartweed –
Polygonum sp.) and a perennial noxious weed (perennial pepperweed – Lepidium latifolium), while
the Wetland Buffer is dominated by a native perennial grass (reed canarygrass - Phalaris
arundinacea). These species tend to dominate an ecosystem by outcompeting minor, desirable
species. Therefore, creating opportunities for a variety of native species to establish is vital. Some
method of vegetation control must be used on these aggressive grasses and forbs. Typically,
mechanical or chemical control is used. Mechanical control entails scraping or plowing to increase
bare ground exposure which will serve as a seedbed / planting medium. Chemical control entails the
use of herbicide to diminish dominance of perennial grasses and fobs. Mechanical control is an
appropriate method for the Upland Buffer but not for the Wetland and Wetland Buffer due to the
ability of both perennial pepperweed and Canada thistle to reproduce by root fragments. If chemical
control is selected, only City of Fort Collins approved herbicide should be used by a qualified
contractor, in accordance with the label.
Step 2: Soil Preparation
The soil surface should be optimized for seeding or planting. An agronomic assessment should be
implemented to evaluate the chemical and physical properties of the soil. This information can be
used to determine whether soil amendments would benefit the establishing plant communities and
allow for optimization of the seed mix to soil conditions. Prior to seeding, the soil surface should be
loose, allowing for good soil/seed contact. A disc harrow prior to seeding is best on the Upland Buffer,
while hand raking is suitable for the Wetland and Wetland Buffer to avoid the spread of perennial
pepperweed and Canada thistle.
Step 3: Seeding and Planting
The species used should be native and suitable to the soil and moisture conditions of the Buffers and
Wetland. Seed mixes should be designed to facilitate growth of appropriate and sustainable species.
An initial seed mix for the Upland Buffer, Wetland, and Wetland Buffer is presented below but may be
changed based on the agronomic assessment results. Seeding can be accomplished using both
broadcasting and drilling techniques, following final contouring and amendment
application/incorporation, if appropriate. If seed is broadcast, a light disc harrowing (Upland Buffer)
perpendicular to the flow of energy (wind and/or water) or hand raking (in the Wetland and Wetland
Buffer) should immediately follow seeding to increase seed to soil contact and provide some
protection from wind or water erosion and granivory, in addition to doubling the seeding rate. If seed
is drilled, final drilling pass must occur on the contour, to create subtle ridges perpendicular to the
flow of energy. The following guidelines are provided by the City of Fort Collins:
1. Prepare soil as necessary and appropriate for native seed mix species through aeration and
addition of amendments, then seed in two directions to distribute seed evenly over the entire
area. Drill seed all indicated areas as soon as possible after completion of grading operations.
2. If changes are to be made to the seed mix based on site conditions, then approval must be
provided by a city Environmental Planner.
3. Appropriate native seeding equipment will be used (standard turf seeding equipment or
agriculture equipment shall not be used).
4. Drill seed application recommended per specified application rate to no more than ½ inch depth
(or appropriate depth for selected species). For broadcast seeding instead of drill seeding
method, double the specified application rate.
5. After seeding, the area shall be covered with crimped straw, jute mesh, or other appropriate
methods.
Planting of native shrubs in the Upland Buffer should occur to provide structural diversity. Species to
be used should be approved by a city Environmental Planner. According to the NRCS Web Soil Survey,
the following native shrubs, sub-shrubs, and agavoids are found on these soils and presumably would
be appropriate to plant:
Fourwing Saltbush (Atriplex canescens)
Rubber Rabbitbrush (Ericameria nauseosa var. nauseosa)
Winterfat (Krascheninnikovia lanata)
Prairie Sagewort (Artemisia frigida)
Soapweed Yucca (Yucca glauca)
Shrubs should be planted using industry Best Management Practices.
WETLAND MIX
Common Name Scientific Name lbs/PLS/ Acre
Wildflowers
Marsh sunflower Helianthus nuttallii 1.51
Pennsylvania smartweed
Polygonum pensylvanicum
(Persicaria pensylvanica)
3.13
Goldenglow daisy Rudbeckia ampla 1.36
Blue verbena Verbena hastata 0.2
Grasses
American sloughgrass Beckmannia syzigachne 0.39
Inland Saltgrass Distichlis stricta 0.67
Giant mannagrass Glyceria grandis 0.27
Fowl bluegrass Poa palustris 0.35
Prairie Cordgrass Spartina pectinate 1.9
Wet Species
Spikerush Eleocharis palustris 0.42
Arctic rush Juncus balticus (J. arcticus) 0.03
Hardstem bulrush Schoenoplectus acutus 0.65
Alkali bulrush
Scirpus maritimus
(Bolboschoenus maritimus)
1.14
Common three-square Schoenoplectus pungens 0.65
Total for Wetland Mix 12.68 lbs/PLS/Acre
Substitutes
ACCEPTABLE SUBSTITUTES FOR WILDFLOWERS
Black-eyed Susan (Rudbeckia hirta ) 0.19 lbs/PLS/Acre
Beebalm (Monarda fistulosa var. menthifolia ) 0.23 lbs/PLS/Acre
If one or more species is unavailable, double the quantity of an available wildflower (In mix above).
ACCEPTABLE SUBSTITUTES FOR GRASSES
Salt and Pepper grass (Deschampsia caespitosa ) 0.14 lbs/PLS/Acre
Switchgrass (Panicum virgatum ) 1.35 lbs/PLS/Acre
Alkali sacaton (Sporobolus airoides ) 0.20 lbs/PLS/Acre
ACCEPTABLE SUBSTITUTES FOR WET SPECIES
If one or more species is unavailable, double the quantity of an available wet species (In mix above).
Requirements
*Contractor is responsible for locating and purchasing all species listed in mix. If a species can’t be located, contractor must replace
each missing species with the acceptable substitutions (listed above). Contractor is responsible for providing seed tags to appropriate
City staff. This mix is based on 100 seeds/ square foot and is only calculated for one acre. This mix is based on the contractor using a
broadcast seed application. Contractor is responsible for calculating the appropriate seed amounts to purchase. Please note that the
pounds per acre are in PLS (Pure Live Seed) and must be ordered that way. All materials furnished shall be free of Colorado State
noxious weeds as defined in Article III, Section 21-40 of the Code of the City of Fort Collins.
WETLAND BUFFER (MESIC) MIX
Common Name Scientific Name lbs/PLS/ Acre
Wildflowers
Smooth aster Aster laevis 0.19
White prairie clover Dalea candida 0.65
Purple Prairie Clover Dalea purpurea 0.81
Indian blanketflower Gaillardia aristata 1.85
Black-eyed Susan Rudbeckia hirta 0.14
Grasses
Big Bluestem Andropogon gerardii 1.3
Salt and pepper grass Deschampsia caespitosa 0.07
Inland Saltgrass Distichlis stricta 0.35
Streambank wheatgrass
Elymus lanceolatus ssp.
Lanceolatus
1.36
Switchgrass Panicum virgatum 0.71
Western Wheatgrass Pascopyrum smithii 1.61
Fowl bluegrass Poa palustris 0.18
Little Bluestem Schizachyrium scoparium 0.7
Yellow Indiangrass Sorghastrum nutans 1.38
Prairie Cordgrass Spartina pectinata 1
Total for Mesic Mix 12.31 lbs/PLS/Acre
Substitutes
ACCEPTABLE SUBSTITUTIONS FOR WILDFLOWERS
Mexican hat (Ratibida columnifera ) 0.10 lbs/PLS/Acre
Marsh sunflower (Helianthus nuttallii ) 0.56 lbs/PLS/Acre
Beebalm (Monarda fistulosa var. menthifolia ) 0.09 lbs/PLS/Acre
ACCEPTABLE SUBSTITUTIONS FOR GRASSES
American sloughgrass (Beckmannia syzigachne ) 0.20 lbs/PLS/Acre
Alkali sacaton (Sporobolus airoides ) 0.11 lbs/PLS/Acre
Prairie sandreed (Calamovilfa longifolia ) 0.67 lbs/PLS/Acre
Requirements
*Contractor is responsible for locating and purchasing all species listed in mix. If a species can’t be located, contractor must replace
each missing species with the acceptable substitutions (listed above). Contractor is responsible for providing seed tags to appropriate
City staff. This mix is based on 70 seeds/ square foot and is only calculated for one acre. This mix is based on the contractor using a
drill seed application. Mix should be doubled if hand broadcasted. Contractor is responsible for calculating the appropriate seed
amounts to purchase. Please note that the pounds per acre are in PLS (Pure Live Seed) and must be ordered that way. All materials
furnished shall be free of Colorado State noxious weeds as defined in Article III, Section 21-40 of the Code of the City of Fort Collins.
Step 4: Maintenance and Management
Maintenance and management activities should be implemented to ensure success of the ecological
restoration project. After seeding, the area shall be covered with crimped straw, jute mesh, or other
appropriate soil surface stabilization methods. Temporary irrigation will be used until seed is
established; an irrigation plan will be prepared prior to seeding. The irrigation system for seeded
areas shall be fully operational at the time of seeding and shall ensure 100% head-to-head coverage
over all seeded areas. A weed management plan should be implemented to ensure that weeds are
properly managed before, during, and after seeding activities. Particular attention should be paid
Canada thistle (Cirsium arvense) in the Upland and Wetland Buffers, and perennial pepperweed
(Lepidium latifolium) in the Wetland. Overall, the contractor shall monitor seeded area for proper
irrigation, erosion control, germination and reseeding as needed to establish cover.
Step 5: Monitoring and Completion
The Upland Buffer, Wetland, and Wetland Buffer will be monitored twice a year (once in the middle
and once at the end of the growing season), for a period of three years following construction and
planting. Restored vegetation communities will be considered established when seventy percent
vegetative cover is reached with no larger than one foot square bare spots and/or until deemed
established by city planning services and erosion control. The developer and/or landscape contractor
is responsible for adequate seedling coverage and growth at the time of final stabilization, as defined
by state and local agencies. If final stabilization is not achieved to the satisfaction of the agency, the
developer and/or landscape contractor shall be responsible for additional corrective measures to
satisfy final vegetative requirements for closeout.