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Title: FENS David J' Cooper Rodney Chimner Joanna Lemly


1
FENSDavid J. Cooper Rodney Chimner Joanna Lemly
2
Wetland
  • Any ecosystem that has saturated soils for at
    least 2 weeks during the growing season of most
    years, creates hydric soils, supports hydrophytes
  • Many different wetland types due to stability of
    the water table, water depth, erosive power of
    moving water
  • Riparian
  • Marshes
  • Wet Meadows
  • Salt Marshes and Flats
  • Peatlands

3
Wetland Types of Interior West
Riparian
Marsh
Salt Flat
Peatland (fen)
Wet Meadow
4
PEATLAND
  • Production gt decomposition due to water-logging
  • Saturated, anaerobic soils, lack free oxygen
    limits decomposition rates
  • Organic matter (roots, rhizomes, mosses, woody
    stems) accumulates (20 cm/1000 yrs) and organic
    soils form
  • Peat accumulation create landforms
  • Plants are rooted entirely in peat body
  • Plants derive all water nutrients from peat
  • Isolated from mineral sediment inputs

5
Simplified Peatland Carbon Budget
6
Two types of peatlands
BOGS
Peatlands
FENS

7
BOGS
  • Ombrogenous and Ombrotrophic
  • Usually raised, but also blanket bogs
  • Sphagnum dominated, with low pH (lt4.2)
  • Nutrient and mineral ion poor, Ca lt 2.0 mg/L
    in water
  • Typically occur in humid regions with cool
    temperatures, but also in drier areas of C.
    Canada
  • Some consider peatlands with pH lt5 to be bogs, gt6
    to be fens (Wheeler and Proctor 2000)
  • No bogs in Rocky Mts of US or Sierra Nevada

8
FENS
  • Ground water, not precipitation provides main
    water source. Minerotrophic
  • Fen characteristics determined by chemical
    content of source waters and water flux
  • pH varies from lt4 to gt8
  • Very sensitive to changes in ground water supply
    or flow paths
  • Vegetation can be conifer forest, shrub, sedge,
    or moss dominated

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Fen Characterization and Identification
  • Hydrologic regime
  • Soils
  • Vegetation

11
Ground Water Flow Paths That Sustain Fens
12
Water Table near Surface
  • Air diffuses 10,000 times slower into saturated
    than in unsaturated soils
  • Soils become isolated from atmospheric gasses
  • Oxygen in soil is rapidly used up and anoxic
    soils develop and limit organic matter
    decomposition
  • Ground water input keeps soils cooler
  • Duration of water table near surface? All summer

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Ground Water Monitoring Well
15
Natural Range of Variation-8 of 11 yearsnear
surface
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Rain and Water Levels in Fens
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What is peat or organic soil?30-40 cm thick
21
Drepanocladus moss fibers
Sedge roots/rhizomes
Soil colors and fibers indicate organics vs.
color of mineral soils - as well as redox features
22
No International Criteria
  • For organic matter composition
  • For organic carbon composition
  • For presence of mineral soil layers
  • For type of inorganic matter present

23
  • Boreal peatlands with little mineral sediment
    influx

24
Mineral soil influx from mountains
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Organic Soil Criteria
  • Hydrologic Regime
  • Saturated with water for gt30d each year
  • Composition ( OC that controls soil function
    the more clay present the less OC influences
    soils)
  • Must be gt18 organic carbon if gt60 clay
  • 12 organic carbon if 0 clay
  • 12 (0.1 clay) so if 20 clay need 14 OC
  • Horizon Thickness
  • 40 cm of organic horizons in top 80 cm of soil
    (dominates root zone)
  • Or, on lithic contact

ftp//ftp-fc.sc.egov.usda.gov/NSSC/Soil_Taxonomy/t
ax.pdf
27
How determine OC or OM?
  • Must be done in lab
  • OC can be determined using a CHN analyzer, must
    first treat with acid to remove carbonates
  • OM can be determined by loss on ignition in
    muffle furnace, but OM is not all C, and OM
    must be converted to OC

28
Peat vs. Muck
  • Soil taxonomy identifies 3 suborders of histosols
    (ist) fibrist, hemist, saprist, based upon the
    level of decomposition of the organic matter.
  • Fibrist soils are considered peat
  • Hemist and saprist soils are muck
  • HOWEVER, from an ecological perspective any
    ecosystem with organic soil is a peatland

29
Peat forming vegetation
  • Most organic matter in western U.S. fens is
    produced by clonal sedges and mosses,
  • deposited in anaerobic zones below the soil
    surface
  • Litter on surface decomposes
  • Woody peat in alder or willow fens, and some
    partially forested fens
  • Carex, Eleocharis, Scirpus are the key vascular
    plant genera
  • Moss peat from Drepanocladus, Sphagnum,
    Aulacomnium, Tomenthypnum
  • California has unusual peat formers Narthecium
    (also in Britain), Darlingtonia

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How old are peatlands?
34
Basal Ages of Rocky Mt fens
  • Big Meadows 11,180
  • Green Mt. Fen 11,650
  • East Lost Park 11,200
  • Cottongrass Fen 10,300
  • Caribou Fen 10,500
  • Zapfs Fen 4,800

35
Some meadows have small fen area, others are
nearly all fen
Wet Meadow
Fen
Round fen Sequoia NF
36
Several plant communities in most fens should
sample each
5
4
3
1
2
37
Within fen variation
recharge
4
5
6
Carex limosa
Flow through
7
3
2
discharge
1
38
Processes Driving Variation Among Fens and Fen
Vegetation
  • Water flow variation, high to low flow rates
    influences vegetation production peat accum.
    rate
  • Standing water depth
  • Stable pond water level supports floating mats
  • Chemistry of source waters due to bedrock
  • Climate, including elevation, patterns of
    precipitation, supports unique floristic elements
  • Disturbance processes, including ditches,
    livestock grazing etc.

39
Four major landform/hydrologic systems support
fens
  • Basins
  • Slopes
  • Spring mounds
  • Geological discontinuities

40
Limnogenous or Basin fenssurface or ground water
fed
41
Basin fens typically have floating mats, but
depending upon rate of succession, basin
infilling may have been completed have
distinctive flora
42
Sloping Fens
43
Poison Fen Sierra NF
44
hillslope fens may support conifer trees
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Spring moundspecialized type of soligenous fen
with point discharge
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Geological discontinuity creates hillside flow
systems
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Chemistry of source waters rich to poor
gradient of Sjörs and DuRietz
52
Southern Rocky Mt. Fens Geochemical Classes
Extreme Rich Fens
Transitional Rich to Rich Fens
Iron Fens
53
Convict Creek Basin Inyo NFHanging Fen pH
7.87, EC 257 uS, Ca 49 mg/L
54
St. Marys Fen Stanislaus NFpH 6.7, high Ca,
HCO3
Rich Fen
55
Transitional Fens
Pat-Yore-Flat (Tahoe NF) (Butterfly valley
(Plumas) Narthecium californicum, Darlingtonia,
Rhynchospora alba, Carex echinata, Ledum
glandulosum
pH 6.1, EC 17.8 uS Ca 1.8 mg/L
56
Transitional Fen McKinstry Fens - Eldorado NFpH
5.7, EC 28 uS, Ca 2.1 mg/L, Carex echinata,
Drosera rotundifolia, Sphagnum subsecundum
57
Poorest fens Dinky Lake Sierra NFSphagnum
fuscum, Kalmia polifolia
pH 5.75, EC 13 uS, Ca 0.3 mg/L, K 1.8 mg/L
58
Iron Fens
59
Conclusions
  • Many fens in most mountain regions
  • Large range of fen landforms, hydrologic regimes,
    mineral ion and nutrient fluxes, vegetation
    types, flora, history during Holocene, land
    use/condition
  • Community types unique to fens, disjunct species
  • Many communities are similar throughout North
    America and Holarctic (Scirpus pumilus,
    Eleocharis pauciflora, Carex aquatilis, C.
    utriculata, C. limosa, Meesia triquetra,
    Sphagnum subsecundum)
  • Others more localized Carex illota, Narthecium
    californicum, cushion plants in tropical alpine
  • Many fens impacted by human uses

60
Impacts few fens are pristine
  • ON SITE IMPACTS
  • Filling
  • Hydrologic changes drainage ditches
  • Snow compaction on ski runs
  • Trampling livestock, humans
  • Mining, metal and peat
  • OFF SITE IMPACTS
  • Timber operations
  • Hydrologic changes diversions, ground water
    pumping
  • N deposition?

61
Drainage
  • Common in agricultural areas
  • Particularly wet meadows, marshes, to completely
    dry areas out
  • May be cropped

62
Water Diversions/Ditches
What are hydrological and ecological impacts and
how restore?
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64
Mason Fen
Rate of flow in open channel compared to ground
water flow through peat/muck
Exotic plant invasion
Plant death
65
Dewatering allows pocket gopher and vole invasion
-- proliferates drainage and channel development
Digging exposes peat to oxidation, and digging
undermines plants
66
Prospect Basin Fens
Pre-development air photograph
Ski runs
Watersheds
67
Snow compaction changed thermal characteristics
of snow from insulation to conducting cold
allowing peat to freeze deeply
68
Ground Water Withdrawal
  • Daily, seasonal or permanent lowering of water
    tables
  • May stop peat accumulation, and cause peat
    oxidation in fens
  • May cause subsidence
  • May dry out wetlands

69
Ground Water Pumping
70
Trampling from hikersLoss of vegetation and peat
71
Livestock Grazing
Eliminates species with rhizomes and favors
taprooted and short-lived species
Hummocks formed in areas without caespitose
species indicate compaction and erosion, and
increase surface area and oxidation
Bare ground facilitates channel development and
head cutting
72
RMNP established 1915
Vegetation changes
Fen dry in summer
73
Ditch Blockage
74
Water Table Changes Relative to Controls
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