Sphagnum bogs
Louise Kulzer
Water quality specialist, Aquatic ecologist
King County Department of Natural Resources
CTo understand the unique characteristics of sphagnum bogs
CTo understand how human influences can adversely impact sphagnum bogs
CTo see a peat system first-hand
What youll learn about...
Where & how bogs are formed
How sphagnum moss creates its own niche
Physical & chemical gradients in wetlands & where bogs fit in
Plant & animal communities in bogs
How human activities can disrupt bogs
Definitions (after Bridgham, 1998)
Peatland is a generic term applied to wetlands in which the rate of accumulation of organic matter exceeds the rate of decomposition, and where at least 1 foot ( 30 - 40 cm) of peat has accumulated (Glaser, 1987)
(Mire is the European name for peatlands)
Two basic divisions in peatlands:
bogs -- acidic peatlands, Sphagnum moss forms dense mat
fens-- depends on classification-- usually more sedges, less acidic
Definitions, contd
Other peatland types
muskeg-- northern peatlands covered with stunted black spruce (Crum, 1992) rooted in Sphagnum
moors-- in
heath--in
carr-- a peat system, usually not Sphagnum-dominated, supporting deciduous trees
Types of bogs
lake-fill or kettle-hole bogs
flat basin
plateau or raised bogs
Blanket bogs
flat valley
slope bogs
carpets, lawns (use differs with authors)
open hummock/hollow, usually w/ shrubs
forested
Bogs form in specific environmental situations
Precipitation exceeds evaporation
Bogs form in specific environmental situations
Drainage is poor (plateaus, drainage divides)
Poor soils, often glaciated
Kettle holes
Cool temperatures
Oceanic influence common-- rainfall higher in Na & Cl
Northern latitudes
in lakes, protected from wind, upstream flowpaths
Sequence /age of peat profile
Often underlain by blue clay
sedge peat
pumicite layer (laid down 6,700 yr b.p. (151 obs.))
sphagnum peat
11,900 yr. b.p. average for beginning of peat accumulation
41
years/ inch of peat accumulation (151 obs,
Other NW bogs: 49 years / inch (55 obs
in NE Wa,
Characteristics of sphagnum bogs
form mats which are at least somewhat buoyant
mats often form hummocks & hollows, support a unique assemblage of plants
water acidic
bacterial communities severely depressed, but aquatic fungi thrive
lack of dissolved oxygen, minerals and nutrients in water
typically have a moat or lagg at periphery
Gradients operating in peatlands
source of water
rainΰ runoff ΰ groundwater
water mobility
stagnant ΰ flowing
water chemistry (pH, cations, anions, nutrients)
low ΰ high
water levels
stable ΰ fluctuating
More gradients
sunlight shade
summer winter
hummock hollow
mat lagg or moat
Generally
water source
mobility
chemistry
pH
cations
anions
nutrients
water level
bogs fens
rainwater surface & groundwater
stagnant flowing
acid neutral or basic
scarce abundant
Cl dominant CO3, HCO3 dominant
low high
stable stable or fluctuating
Bottom line:
Sphagnum bogs are isolated from the influences of groundwater &/or surface water runoff in some way
topography (small watershed, flat area)
impermeable layers
blue clay
decomposed peat itself
raised character of hummocks or plateau
moat or lagg
Sphagnum moss
Indeterminate growth
upper portion actively grows,bottom portion sloughs away, may sink to bottom or be suspended
dozens of species, w/ own growth habits, tolerances for pH, light, wetness
leaves thin, only 1 cell thick
cell walls w/ perforations, high concentrations of polyuronic acid, an active cation exchanger
high water-holding capacity (15-23X dry weight)
Sphagnum ecology
Numerous species, 61 in European mires
wide range of pH tolerances
some species are specialists, some generalists
Coastal
degree of shading
height above water table
surface water chemistry
No definitive local taxonomy done for WA, OR
Profile through a sphagnum hummock
Sources of acidity in bogs
decomposition of peat in the acrotelm yields organic acids
humic acids
fulvic acids
redox reaction of sulfur compounds yields acids
Cation exchange by sphagnum -- H+
Bog/fen gradient
Cation exchange
Chemistry of waters: cations
data from
hardness (Ca + Mg)
alkalinity (... mg/L CaCO3)
1 10 20 30 40 50 60 70 80 90
Common bog plants
(Based on fall 1998 survey, 30 Puget Sound bogs)
30 Ledum groenlandicum (
25 Tsuga heterophylla (hemlock)
20 Kalmia microphylla (bog laurel)
17 Spirea douglasii
17 Vaccinium oxycoccus (cranberry)
15 Thuja plicata (w. red cedar)
Pink font = family Ericaceae
Other common bog plants
Drosera rotundifolia (sundew)
Cladium (reindeer lichen)
Rhynchospora alba (beakrush)
stunted
crabapple, cascara, willow, birch
blueberry, huckleberry
Eriophorum (cottongrass), Menyanthes (bogbean)
Scirpus atrocinctus (= cyperinus)
skunk cabbage
Uncommon bog plants
Carex pauciflora (few-flowered sedge)
Olympic peninsula
Myrica gale (sweet
gale)
Rhododendron macrophyllum
Gentianan sp. (bog
gentian)
Habenaria dilatata (bog orchid)
Andromeda sp. (bog rosemary)
Rubus sp. (cloudberry)
Unique bog beetles--
WA state sensitive status
Effects of human activity
Uses of sphagnum
soil amendment
fuel source, ancient times to present
acid-loving crops
cranberries
blueberries
truck
farms (
paleo-botanical record
historical record
absorbent material -- bandages WW1, diapers
Historical changes in sphagnum acreage --
24 King County Bogs, 1930s to 1990
Sphagnum acres
1930 1980 1990
Total 458 140 132
» 71% reduction in acreage
1930 acres from Rigg, Peat Resources of Washington
1980, 90 acres estimated from from air photos
Urbanization of watershed
volume of annual runoff increased ~ 40%
increases winter high
water level
increases water level fluctuation
concentration of cations, nutrients
greatly increases ( changes buffer equilibrium)
bacterial concentration increase
physical disturbance increases (pets, people)
Responses to urban runoff
Binding of cations+ greatly increased, may use up exchange sites and kill moss
buffering system equilibrium disturbed
WLF causes
increased depth of D.O., increased area of acrotelm, more decomposition of mat
higher winter, lower summer water levels
increased bacteria, more decomposition
higher nutrients favor typical emergents
Recent changes in sphagnum acreage --
Recent changes in sphagnum acreage --
Of the 50 remaining bogs in King Co. WA
most show damage
draining
dirt paths, roads
cuts for ROW, ditches
invasion by non-acid loving plants
(more overland runoff)
erosion of mat (increased O2, WLF)
trampling
Recent changes in sphagnum acreage --
Impacts of recent drainage, LCR14
ihemlock growth taller near cut face of bog
i# years of accelerated growth increase closer to the cut face
iheight of Ledum increases, little Kalmia
near cut face
iDry hummocks, no bog beetles near
cut face
King County Surface Water Design Manual
Sphagnum bog protection menu applied throughout watershed
Goals: reduce TP by 50%
reduce N by 40%
alkalinity < 10 mg/L
pH < 6
3-facility WQ treatment train
facilities which contribute organic acids
ALSO: match pre-developed volumes
So what to do?
Keep entire catchment forested-- no logging
Keep roads out of catchment
Limit any construction/ land disturbance to dry season
No cement use in catchment
Dont give mining permits, stop using peat
Construct modest, low-impact trails
Show people! You cant long protect what people dont value.
LCR16 from moat looking to bog mat