Cook Inlet Wetlands |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Home
|
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
SPRING FEN Wetlands
LEFT: An idealized cross-section of a Spring Fen wetland showing the most common mapping components. Forested Spring Fens (SF4) and Spring Fen ponds (SF1) are less common. Drawing by Conrad Field. RIGHT: Range map showing the distribution of Spring Fen wetlands. Spring Fens are concentrated in the area between Wasilla & Palmer, where evapotranspiration exceeds precipitation, and wetlands are fed by ground water orginiating to the north, on the slopes of Baldy Ridge. Spring Fen wetlands are small peatlands surrounded by uplands. They are connected to other wetlands and to streams through shallow, unconfined groundwater movement through underlying permeable sediments. As such, they can be thought of as outcroppings of the local water table. They occur in the region of moisture deficit, between Butte and Houston below 1000 feet elevation, where evapotranspiration generally exceeds precipitation. Wetlands are not expected in such an area, and must be driven by groundwater discharge. The thick glacial sediments underlying the area of moisture deficit are well-sorted and coarse-grained in places, allowing ample groundwater discharge where surface topography intersects the relatively shallow water table (Jokela and Munter, 1991). Spring Fen wetlands occur in these topographic positions. Because of the steady supply of shallow groundwater, water table elevations in Spring Fens vary the least of any geomorphic wetland type in this classification. |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| Table 1. Wetland Indicators in Spring Fen map components. | |||||||
Map Component |
Peat Depth (cm) | Water Table (cm) |
Redox features (cm) | Saturation (cm) | pH | Specific Conductance µS/cm | Plant Prevalence Index |
SF1 |
6.1(15) |
64.5 (15) |
|||||
SF2 |
167 (19) | 2 (22) |
0.3 (22) | 5.5(14) | 90.1 (14) | 1.61 (19) | |
SF3 |
246 (6) | 11 (6) | 5.5 (6) | 4.8(5) | 79.4 (5) | 1.96 (6) | |
SF4 |
180 (5) | 7 (6) | 2.3 (6) | 5.6(4) | 85.0 (4) | 1.99 (5) |
|
Explanation:
Numbers in paraentheses indicate number of samples.
Peat depth is a minimum, because some sites had thicker peat deposits than the length of the auger used (between 160 - 493 cm).
Water table depth is a one time measurement. At sites with seasonally variable water tables this measurement reflects both the conditions that year, and the time of year.
Redox features with deep depths typically indicate deeper peat deposits, which mask redox indicators so the depth corresponds to the peat thickness.
pH and specific conductance measured in surface water or a shallow pit with a YSI 63 meter calibrated each sample.
Plant Prevalence Index calculated based on Alaska indicator status downloaded from the USDA PLANTS database, which may use different values than the 1988 list.
| Table 2. Common soils and plant communities found in Spring Fens. | ||
Map Component |
COMMON SOILS | COMMON PLANT COMMUNITIES |
SF2 |
HISTOSOLS |
|
SF3 |
HISTOSOLS |
Myrica gale - Betula nana / Equisetum fluviatile Sphagnum spp. - Carex rotundata Leatherleaf - Dwarf birch |
SF4 |
HISTOSOLS |
Picea mariana / Ledum palustre ssp. decumbens White spruce - Black spruce / Thinleaf alder |
| HISTOSOLS are any organic soils greater than 40 cm deep. | ||

Cation chemistry by Geomorphic Component. Spring Fens (highlighted in blue) have higher cation concentrations than the other hydrologically isolated Geomorphic Component, Depressions. This indicates a strong groundwater discharge influence on porewater chemistry. Although calcium and silicon show the greatest concentrations, magnesium and iron concentrations in our area are high for natural waters. DW = Drainageway, K = Kettle; S = Discharge Slope; LB = Lakebed; SF = Spring Fen; RT = VLD Trough; R= Riparian; H = Headwater Fen; D = Depression.
Samples were collected from a surface pool where possible, otherwise from a separate shallow pit excavated to just below the water table. All samples were filtered through either a 0.2 micron filter using a disposable syringe, or pumped through a 0.45 micron filter using a peristaltic pump. Samples were acidified with ultra-pure nitric acid and kept cool until analysis on a direct current plasma spectrometer to about 5% accuracy (except K, 10-20% accuracy).
SF1: Spring Fen Ponds.
SF2: Spring Fens with water table near the surface. Often dominated by creeping sedge, marsh cinquefoil, and/or bluejoint reedgrass.
SF3: Spring Fens dominated by shrubs, especially thinleaf alder and dwarf birch.
SF4: Spring fens with deeper fluctuating water table, forested.
| Table 3.Summary of Cook Inlet Spring Fen Map Unit occurrence. Spring Fens are only mapped in the Matanuska-Susitna Valley. | ||||
| Map Unit | N | Hectares | % Polygons | % Area |
| SF1 | 85 | 188 | 0.35 | 0.10 |
| SF12 | 10 | 12 | 0.04 | 0.01 |
| SF12d | 2 | 2.4 | 0.01 | 0.00 |
| SF1-3 | 6 | 16 | 0.02 | 0.01 |
| SF1-4 | 1 | 0.4 | 0.00 | 0.00 |
| SF1c | 7 | 19 | 0.03 | 0.01 |
| SF2 | 156 | 203 | 0.65 | 0.11 |
| SF21 | 17 | 35 | 0.07 | 0.02 |
| SF21d | 1 | 1.9 | 0.00 | 0.00 |
| SF23 | 37 | 115 | 0.15 | 0.06 |
| SF23d | 2 | 4.0 | 0.01 | 0.00 |
| SF2-4 | 13 | 56 | 0.05 | 0.03 |
| SF24d | 1 | 0.5 | 0.00 | 0.00 |
| SF2-4d | 1 | 1 | 0.00 | 0.00 |
| SF2c | 3 | 1.6 | 0.01 | 0.00 |
| SF2d | 3 | 1.9 | 0.01 | 0.00 |
| SF3 | 35 | 45 | 0.15 | 0.02 |
| SF31 | 1 | 1.2 | 0.00 | 0.00 |
| SF32 | 17 | 46 | 0.07 | 0.02 |
| SF34 | 20 | 60 | 0.08 | 0.03 |
| SF3d | 2 | 7.4 | 0.01 | 0.00 |
| SF4 | 22 | 159 | 0.09 | 0.08 |
| SF42 | 1 | 1.3 | 0.00 | 0.00 |
| SF43 | 17 | 92 | 0.25 | 0.46 |
Contact:
Mike Gracz
PO Box 15301
Fritz Creek, AK 99603
19 October, 2011