Refuge Notebook
Article
August
13, 2004
Windy Point burn provides food for through, and for moose, hares
by Ed Berg
It has been five years since I visited the 1994 Windy
Point Burn south of Tustumena
Lake , and the vegetation has grown up dramatically.
Doghair-thick stands of birch saplings 5 to 8 feet high hide fallen burn poles
and uprooted throw mounds of tipped-over snags. It can take an hour and a well-scratched
hide to travel 1,000 meters in this thicket. It would be a good candidate for
an article in Alaska Magazine about Alaska's 10 worst hikes.
From the point
of view of hungry moose in the winter, however, the burn is about as close to
heaven as most moose get. These birch saplings are prime eating size and there
is a virtually infinite supply of them. We saw abundant piles of winter moose
pellets, so we know the moose are putting the area to good use.
This burn
will be good hare habitat when the hare cycle rises again in the next few years.
We saw only two or three hare pellets in three days of tramping through the burn.
We have been in the low part of the 10- to 14-year Kenai cycle since about 2000.
At the high point of the cycle I would expect to see dozens of pellets per square
meter in a place like this.
The Windy Point fire in 1994 was an extremely
severe, mineral soil-exposing fire, 2,800 acres in size. It started from a campfire
Aug. 30 at the end of a long dry summer and kept burning until fall rains extinguished
it. Much of the forest was mature upland black spruce with a foot-thick peat moss
carpet. The "residence time" of the fire at a given spot was probably many days,
providing complete consumption of the organic layer. It was as if someone had
simply picked up the vegetative carpet and taken it out of the room, leaving the
mineral soil floor completely exposed.
When we surveyed the burn in 1995
we found a muddy "moonscape" with soil that had been thoroughly sterilized. Nevertheless,
we saw thousands of baby birch seedlings sprouting in the soil. Birch trees drop
their seeds in the winter and the seeds are blown far and wide across the crusty
snow. We found seeds especially profuse in swales where they had been concentrated
by spring melt waters.
I remember seeing only a few spruce seedlings in
1995 and wondering if the burn area would ever host a spruce forest again. Now,
10 years later, we saw numerous spruce both white and black growing up in the
understory, as textbook examples of "shade tolerance."
According to ecological
theory, these spruce seedlings should ultimately overtop the birch trees and shade
them out to produce a continuous old growth spruce forest. On the Kenai, however,
spruce bark beetles and fire tend to derail ecological theory. Our white spruce
forests see some degree of bark beetle thinning every 50 years on average and
the black spruce forests typically burn on a rotation of about 90 years, so our
forests never reach the kind of genuine old growth stage that one sees in Southeast
orthe Pacific Northwest.
In 1997 we installed four permanent survey plots
in the burn, which we revisited in 1999 and 2004. The plots are 20 by 50 meters
and we measure densities of woody seedlings, herbaceous plants, mosses and lichens,
as well as estimating tons per acre of dead and down woody fuels and duff and
litter thickness. This year it took my technicians, Doug Fisher and Matt Bowser,
and myself five hours of crawling over and under fallen logs to survey each plot.
For these surveys we always camp on the beach at Windy Point on the south
side of Tustumena Lake and use a Zodiac to motor down the lake to a spot where
we can take the shortest route from the lake to a plot. This usually involves
trying to pull the Zodiac up on a gravel beach not much bigger than the boat itself
in a dense shoreline alder thicket. We have learned from experience to take the
motor off the boat and park it well above the water level. When we come back to
the beach six to eight hours later, the wind may have come up and waves can be
crashing on the beach, swamping the boat.
In 1995 we returned late in the
day to the beach and found Tustumena Lake had gone berserk with down-glacier winds
and 4- to 6-foot waves, in what we later found out was a typhoon. Fortunately
we had Mustang suits and a tarp, so we built a fire, ate a few candy bars and
hunkered down for a rather long night. By morning the wind and rain had slacked
off, so we bailed out the boat and headed back to camp.
We have seen some
dramatic changes in seedling density since we started counting seedlings in 1997.
Like most plants, birch trees produce a lot of seeds. Only a few of these seeds
germinate as seedlings and each year these seedlings try to crowd each other out.
On one plot we counted 1,628 tiny birch seedlings in 1 square meter in 1997. On
the same square meter this count had fallen to 890 in 1999 and to 304 in 2004.
Still, 304 seedlings per square meter works out to 1.2 million stems per acre.
Most of these stems were less than 6 inches tall, which shows that seedlings still
are being recruited. Nevertheless, in a mature birch forest we might expect only
several hundred stems per acre, so we know that most of these seedlings will never
make it to adulthood.
On our two less prolific plots we had counts of
5,000 and 8,000 birch stems per acre and many of the saplings were 6 feet high
or more quality growth rather than quantity, and still very difficult to walk
through. These plots showed similar values for black spruce seedlings, which still
are much shorter than the birch.
The most aggressive colonist of the post-fire
bare soil was fire moss (ceratodon). This is a short green moss with copper wire-like
stalks that often is seen in sidewalk cracks and on roof shingles. A year after
the fire, ceratodon covered 90 to 100 percent of the bare ground. Three years
after the fire, ceratodon was being over topped by juniper haircap moss (polytrichum
juniperinum), which today forms a continuous brown ground cover over much of the
burn. As the birch grows up, however, the trees shed leaves and the developing
leaf litter layer is starting to shade out the juniper haircap moss.
We
saw very little grass in the Windy Point Burn. People often have remarked about
how fast our native bluejoint grass (calamagrostis) seems to take over after a
forest has been beetle-killed or logged. In truth, this rapid takeover is an illusion.
The calamagrostis was already there but mostly underground as buried stems (rhizomes).
When the forest canopy is thinned or removed, sunlight hits the ground and the
calamagrostis rhizomes shift into high gear for grass production.
If,
however, you start with hundreds of acres of sterilized seedbed, the grass seed
must be transported by wind and germinated on the bare soil. The underground network
of rhizomes must then be rebuilt, which can take many decades.
Extreme
mineral soil-exposing fires like the 1994 Windy Point fire are somewhat rare on
the relatively wet Kenai Peninsula . The forest rarely dries out enough to allow
full consumption of the organic layer. The 1969 Kenai - Swanson River fire was
such a fire, occurring during a second summer of drought, separated by a low-snow
winter. Again, the 1969 burn produced phenomenal amounts of birch and has been
the prime wildlife area on the refuge in recent decades. The 1969 burn is the
favorite habitat of moose, hares and everything that eats moose and hares.
The
1987 prescribed burn in the Skilak Loop Recreation Area was, inadvertently, another
extreme mineral soil-exposing fire. In this area the trees were mechanically crushed
in 1984, and allowed to dry for three years. After the fire was ignited, a low-pressure
system moved in and the wind died down. The fire smoldered for weeks, smoking
out Anchorage and consuming the entire organic layer, just like Windy Point. Today
much of the area is covered with doghair-thick birch saplings. The moose and hares
love this area, as does everything that eats moose and hares.
When I first
visited the Skilak Loop burn in 1994, seven years after the fire, the area still
looked like a moonscape, with acres of sterile soil and only a sprinkling of fireweed.
I thought this was an extreme example of "over achievement" with prescribed fire
and that it was something I should seek to avoid in my new job as the refuge ecologist.
As the years pass, however, and I watch these burn areas grow, I have
come to view the most severe burns as the best burns for wildlife. As the climate
warms, we will no doubt have more and longer dry periods and more opportunities
for mineral soil-exposing fires. We humans will lament these dry periods as threats
to our homes and fortunes, but the fires will be a great boon to the moose and
hairs and everything that eats moose and hairs.
Ed Berg has been the ecologist
at the Kenai National Wildlife Refuge since 1993.
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