Some areas are thermally or mechanically disturbed. Thermally disturbed areas are unsuitable for native vegetation, while mechanically disturbed areas are devoid of vegetation. In the project area, native plants have been successfully reestablished with revegetation efforts following the construction of pipelines from past projects.
One special-status plant, pine fritillary, a plant of limited distribution in California, was observed in the project area in two locations, with a population size of about 24 individuals.
Other vegetation communities noticed on site include:
Jeffrey pine forest
Sagebrush scrub
Wright buckwheat dwarf scrub
Singleleaf pinyon woodland
Douglas' sedge meadow/creeping rye grass meadow
Federal: Federal Endangered Species Act (FESA) legally protecting special-status plant species. NEPA (national environmental policy act), CWA (clean water act), BLM (Bureau of land management) Sensitive species, U.S. Forest Service (USFS) are all involved in protection of vegetation resources.
State: California Endangered Species Act (CESA), CEQA (California environmental quality act), California Native Plant Protection Act (NPPA), Special-Status Natural Communities, California Native Plant Society,
Local: Mono County and Town of Mammoth Lakes General Plan both contains goals related to vegetation resources.
39.56 acres (0.16 km2) of big sagebrush scrub and 36.86 acres (0.15 km2) of Jeffrey pine will be affected. There is a potential risk that pine fritillary, a non-listed special status tree, will be permanently impacted.
Direct impacts include loss and fragmentation of habitat and the introduction of weeds and non-native species. Temporary indirect impacts are the production of dust and soil disturbance, which can affect plant metabolic processes. Effects in downstream water caused by sedimentation are also possible.
Alternative 3 has the least impact on disturbed vegetation area due to shorter pipeline length, but it was not chosen as the preferred option possibly because of trade-offs in other valued ecosystem components.
Mitigation
Due to the low impact on pine fritillary and to the commonness of big sagebrush scrub and Jeffrey pine, no species-specific mitigation is planned.
To control weeds dispersal, equipment at the site will respect strict cleaning procedures and weed-free certified materials will be used. Non-native species will be removed at decommissioning.
Mitigation success criteria
1. After a three year follow-up period, non-native weeds shall not increase by more than 5% compared to the baseline at decommissioning, excluding cheatgrass.
2. The project shall introduce no new non-native species.
Residual impacts
None mentioned.
The mitigation success criteria seem negligent, as it ignores the most invasive species, cheatgrass. Mitigation focuses on avoiding the introduction of new non-native species, but this technique could become necessary to increase competition on cheatgrass if it ever establishes.
No reason is given to justify why the risk of pine fritillary being affected is low.
Wildlife species observed in the Project area during surveys include:
Mule deer
Jackrabbits
Cottontail rabbits
Ground squirrels
Chipmunks
Kangaroo rats & wood rats
Black-billed magpie
Gray flycatcher
Pinyon jay
Sage thrasher
Sparrows
Hawks
Special-status species in the area include:
Owens sucker (special concern; may be affected indirectly from project)
Owens tui chub (endangered; springs are critical habitat)
Golden eagle (sensitive and fully protected; no documented nest within ten miles of project and thus no anticipated impact)
Northern goshawk (special concern and sensitive; protected activity centers within project)
Greater sage-grouse (special concern and sensitive; project area is an unsuitable habitat for this species)
Bald eagle (endangered and sensitive; no anticipated potential impact)
Pallid bat (special concern and sensitive; thought to be present in the vicinity of the project)
Townsend’s big-eared bat (special concern and sensitive; found in the region but not specifically on the project site)
Western white-tailed jackrabbit (special concern; could potentially use the scrub habitats of the project for burrowing and foraging)
Sierra marten (sensitive; found within project site)
Mule deer (special interest; use the proposed project site for foraging, resting, shelter, and rearing fawns from August to October)
Sierra Nevada red fox (threatened and sensitive; the project site is a suitable habitat, although the nearest sighting are more than five miles [8.05 km] away)
Federal: FESA, Migratory Bird Treaty Act, The Bald and Golden Eagle Protection Act, BLM Sensitive Species, USFS.
State: CESA, CEQA, California Fish and Game Code.
Local: Mono County and Town of Mammoth Lakes General Plan.
Direct impacts are noise, night lighting, fugitive dust, entrapment in site basins, habitat loss, and migration obstruction.
Habitat loss will impact the northern goshawk, the pallid bat, the Townsend’s big-eared bat and the Sierra martens.
Rodents will be attracted to well site basins as they become a suitable habitat when filled with water. This source of food will attract birds of prey and trap them in the basins.
Thermal discharge is predicted to have no impact on water temperature due to conductive buffering. Thus, no impact is predicted for the Owens tui chub fish.
The proposed alternative has the least impedance to movement.
Cumulative effects
None mentioned.
Mitigation
As the bat species’ habitat spans a large range, no mitigation is needed.
Survey of bird nests will be done prior to construction, and protection buffers will be implemented if nests are discovered. Effort will be made to schedule construction activities outside of breeding season.
Site basins will be designed to allow trapped wildlife to escape, and no water will be allowed to accumulate.
Crossings will be built to accommodate mule deer migration across pipeline corridors (see figure below). Annual surveys will be done to observe signs of obstruction.
To compensate for the habitat loss of the Sierra marten, wood debris will be left on the ground in disturbed areas to replicate their natural habitat.
Conductive buffering is effective until a tipping point is reached. The EIA mentioned that temperature change due to the project cannot be measured properly because of the confounding effect of climate change. This is an unreasonable excuse because it is possible to use a control river to calculate baseline warming. Moreover, it is surprising that no cumulative effect is mentioned even if the EIA reported the existence of another thermal plant in the vicinity of the current project.
1.89 acres (7,648.56 m2) of potential jurisdictional wetland areas have been mapped within the project area and in close proximity to the existing power plant facilities. These wetlands are subject to general US Forest Service (USFS) goals for Riparian Conservation Areas (RCAs), which states that they should be managed to preserve, enhance, and restore habitat for riparian and aquatic-dependent species.
Federal: CWA for regulated wetlands and other water of the U.S., NEPA.
State: Porter-Cologne Act, Lake and Streambed Alteration Program.
An assessment made by a third party determined that the unnamed stream flowing through the project area was not likely jurisdictional under the CWA.
The assessment was not reviewed by USACE (United States Army Corps of Engineers) and should be considered preliminary. There was no further information as to whether it has been done at the end.