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SU0007861
Environmental Health - Public
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SU0007861
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Entry Properties
Last modified
1/6/2020 11:37:03 AM
Creation date
9/4/2019 10:03:24 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0007861
PE
2675
FACILITY_NAME
PA-0800105
STREET_NUMBER
9999
Direction
S
STREET_NAME
AUSTIN
STREET_TYPE
RD
City
MANTECA
APN
20106003
ENTERED_DATE
8/11/2009 12:00:00 AM
SITE_LOCATION
9999 S AUSTIN RD
RECEIVED_DATE
7/24/2009 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\A\AUSTIN\9999\EIR PA-0800105\NOP.PDF
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EHD - Public
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Draft Supplemental Environmental Impact Report Page IV.F-3 <br /> Forward Inc. Landfill 2014 Expansion Project <br /> nonnative fortis include yellow star thistle (Centaurea solstitialis), field bindweed (Convovulus <br /> arvensis),bur-clover (Medicago polymorpha),black mustard (Brassica nigra), long-beaked storksbill <br /> (Erodium botrys),broadleaf bird's-foot trefoil (Lotus corniculatus), alkali mallow (Malvella leprosa), <br /> and English plantain(Plantago lanceolata), among others. At the time of the 2014 site visit, the <br /> proposed northeast landfill disposal area was disked and devoid of vegetation;it is expected <br /> that this area contains non-native grasses and weedy plant species between disking cycles. It <br /> should be noted that large portions of the proposed relocated southeast landfill area (south of <br /> the creek) are actively used as a composing facility and are covered with piles and rows of <br /> compost material;these areas are devoid of vegetation and in their current condition are not <br /> non-native grasslands. Nonnative annual grassland most closely conforms to the Wild Oats <br /> Grassland series as described in Sawyer, et al. (2009), and would be classified as upland, <br /> following Cowardin,et al. (1979). <br /> Nonnative annual grassland provides habitat for a wide variety of common wildlife species in <br /> the Central Valley. Nonnative annual grasslands on site are generally limited to small roadside <br /> areas and unmaintained edges of the landfill. Due to the intensive agricultural land use on <br /> surrounding parcels and in the region, the value of these small and isolated nonnative <br /> grasslands in supporting special-status wildlife is limited;the potential occurrence of special- <br /> status wildlife species on the project site is discussed later in this section. <br /> Common rodents such as California ground squirrels (Otospermophilus beecheyi) and pocket <br /> gophers (Thomomys bottae)may utilize the grassland areas and provide a prey base for hawks, <br /> owls and snakes. However, it should be noted that an active rodent control program is <br /> implemented on the landfill. Other common species potentially utilizing the grassland areas <br /> within the study area include black-tailed hare (Lepus californicus), striped skunk(Mephitis <br /> mephitis), gopher snake (Pituophis catenifer), common king snake (Lampropeltis getula),western <br /> fence lizard (Sceloporus occidentalis), red-tailed hawk(Buteo jamaicensis), American crow (Corvus <br /> brachyrhynchos), Brewer's blackbird (Euphagus cyanocephalus), mourning dove (Zanaida <br /> macroura),house finch (Haemorhous mexicanus), American kestrel (Falco sparverius), great-horned <br /> owl (Bubo virginianus),turkey vulture (Cathartes aura) and killdeer (Charadrius vociferus), among <br /> others. <br /> Freshwater Marsh. Freshwater marsh typically occurs in low-lying sites that are permanently <br /> flooded with fresh water and lacking significant current. This plant community is found on <br /> nutrient-rich mineral soils that are saturated for all or most of the year. Freshwater marsh is <br /> most extensive where surface flow is slow or stagnant or where the water table is so close to the <br /> surface as to saturate the soil from below. Freshwater marsh is distributed along the coast and <br /> in coastal valleys near river mouths and around the margins of lakes, springs, and streams <br /> (Holland 1986). This vegetation community characteristically forms a dense vegetative cover <br /> dominated by perennial,emergent monocots 1-15 feet high that reproduce by underground <br /> rhizomes. <br /> Within the study area, freshwater marsh consists of scattered patches of emergent monocots <br /> along the upper reaches of the South Branch of the South Fork of Littlejohn's Creek. At the time <br /> of the 2012 survey, the side slopes and bottom of the creek channel had been scraped by the <br /> Flood Control District,ostensibly to improve drainage;only small patches of emergent <br /> freshwater marsh habitat were beginning to sprout at that time.Based on observations made in <br /> 2008 and 2014, the dominant emergent monocots were narrow-leaved cattail (Typha angustifolia) <br /> and common tule (Schoenoplectus acutus var. occidentalis);dominant aquatic dicots included J <br /> floating water primrose (Ludwigia peploides ssp. peploides) and willow weed (Polygonum <br /> lapathifolium). Other characteristic aquatic species included umbrella sedge (Cyperus eragrostis) <br /> and eastern cocklebur(Xanthium strumarium). Occasional saplings of arroyo willow (Salix <br /> lasiolepis)were present in the channel. <br />
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