VIII. SUGGESTIONS FOR MANAGEMENT

The forests of lodgepole pine in Crater Lake National Park vary in their characteristics, their environment, their potential

for supporting fir-hemlock forest, and their apparent history. This variability existed previous to white man's influence

and must be reflected in the specific management plans prepared for each area.

We feel that the only management tool reasonably available to the park is the control or use of fire. Direct control of bark

beetles and dwarf mistletoe is neither desirable nor feasible for the large areas involved; following a return to a natural

fire regime, any deviations from primeval levels in these biological factors should again eventually decrease.

We have divided the lodgepole pine communities discussed above into five management units, each of which requires

separate attention. Almost throughout, the differences from the ponderosa pine system are extreme. The species differ

(long-lived and fire proof vs. short-lived and fire susceptible) and their fire histories are usually different (frequent

ground fire vs. the five types, only one of which is like ponderosa). Thus management policy cannot be transferred from

ponderosa to lodgepole forests. Specifically, controlled ground fire designed to release larger trees seems appropriate for

only one type of lodgepole forest, and even there only in patches. There are several reasons for this. Such fires would be

very difficult to produce with all but the lightest fuel loads; most surviving lodgepole pines will be killed by bark beetles

or eventually succumb to heart rot. If it did prove possible, a series of this type of fire would allow large mistletoeinfected trees to remain, insuring heavy infection of most fire-stimulated reproduction and its subsequent deformity.

Indeed, in the one community where repeated light fires apparently did occur the forest is in precisely this condition, and

probably was so in the primeval state. In other types, when fire occurred it killed the overstory, removing the dwarf

mistletoe from the site.

Fire seems also to be inappropriate to simulate or anticipate beetle- caused mortality. Beetle kill and fire will produce

very different effects on the forest. Beetles "thin from above," killing the largest trees and opening the canopy,

accelerating growth of smaller trees, but not removing the litter. A light controlled fire "thins from below" (any trees

which survive are likely to be the largest), killing reproduction of all species and removing the litter, encouraging

lodgepole reproduction.

The adoption of the "natural fire policy" by the park will greatly reduce the need for man-initiated fire in the

management of lodgepole pine forest, since lightning was the predominant ignition source in most primeval lodgepole in

the Park.

The most obvious deviations from primeval structure were caused by white man's promiscuous use of fire, so the

suppression of man-caused fires has already served as one very large step toward returning the primeval processes. We

suggest that fires obviously of man-caused origin continue to be suppressed in all areas of the Park. They have been in

areas and forest types in a pattern which shows little correlation with natural ignition (see Fig. 1 in the Park Fire

Management Plan). Another large step has now been taken in the decision to let some natural fires burn. In only a few

types has the suppression of all fires resulted in large enough deviations from the primeval conditions to justify

prescribed fire. In some other spots outside the natural fire area, it may be necessary to prescribe fire to substitute for the

absence of natural fire, but these should be relatively few.

Some general suggestions for management we feel might be helpful are given below; specifics for each area follow: (1)

In much of the lodgepole pine forest the time between primeval fires greatly exceeded that in the ponderosa area. Plans

for management must encompass long time spans, and perhaps provide for the chance that natural fires are not solving all

problems, on a long term basis. (2) Any prescribed burning should be preceded by small scale, experimental burns,

whose effects need to be evaluated probably for several years, before management burning. There is no need to rush the

return toward primeval conditions in any case, and less in the lodgepole than in the ponderosa. We were disappointed

that the slow, cautious, experimental approach suggested for ponderosa was not followed, and hope it will be here.

Simply transporting the philosophy, methods and haste used in the ponderosa management to lodgepole would, for about

90% of the area, cause more deviation from the primeval conditions in a short time than all the man-caused perturbations

of the last 120 years. It is important to remember that repeatedly burning ponderosa pine lightly will eventually reduce

fuel loads; burning lodgepole will probably always eventually increase them. (3) Since lodgepole pine at Crater Lake

does not have serotinous cones, seed supply may limit the rate of reforestation. Since prescribed burning will probably

CRATER LAKE

Report: Lodgepole Pine—History and Management

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kill most lodgepole, directly or indirectly, small burning units with mature forest between would help aid reforestation.

Reports for lodgepole pine/sedge-needlegrass communities elsewhere in Oregon indicate that regeneration will be

sufficient (for forestry purposes) only one tree height's distance into a clearing. (4) Much of the danger associated with

heavy roadside fuel loads (e.g. along Hwy 62 in Castle Creek Valley) could be alleviated by keeping the wide shoulders

of the roads as fireproof as possible. Removing wood chips, grass, and trees which invade there all would help. (5)

Providing fire-ecology and fire-management information to visitors and local residents is important, and should be even

more vigorously pursued. (6) Some major changes in vegetation since white man's arrival are probably natural. For

example, much lodgepole invasion of the Pumice Desert and meadows occurred some years ago and trees are now large

enough to be obvious. Elsewhere in the Cascades, a similar wave of tree invasion has been related to the dry period of

late 1920s to late 1930s. It seems inappropriate to us to eliminate such changes from the primeval which are not caused

by man, in response to the Leopold Report.

Specific Recommendations

Natural Fire Areas - Units I and II

In the discussion below, units I, II and III refer to the Park Fire Management Plan; unit I has natural fire, unit II has

natural fire except with high fire danger, and in unit III all fires are suppressed.

A key to the five Management Types we suggest is given in Table 1. Their general location in the Park is shown in

Figure 2.

Given the natural fire policy, prescribed burning is neither necessary nor justified for three of the five management types

in units I and II, where natural fires will burn.

Table 1. Key to Management Types listed on pp. 32-37. Suggestions for management may vary depending on whether

the type is inside or outside the boundary of the natural fire area as shown on the Fire Management Plan. See the text for

details.

A. Less than 10% of tree reproduction is fir and hemlock.

I. Forest is quite open; fuels are generally discontinuous

..... MANAGEMENT TYPE C

II. Thickets of lodgepole pine are common; fuels are often continuous and heavy.

... .MANAGEMENT TYPE E

AA. Greater than 10% of tree reproduction is fir and hemlock.

I. Subalpine fir is conspicuous ....MANAGEMENT TYPE B

II. Subalpine fir is rare or absent.

1. Overstory is dense, primarily of lodgepole pine. Fuels are heavy and

often continuous

..... MANAGEMENT TYPE A

11. Overstory is relatively open, including other pines or shasta fir. Fuels

are discontinuous. Pinemat manzanita is often conspicuous

..... MANAGEMENT TYPE D

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Figure 2. Approximate location of lodgepole forests in Crater Lake National Park, with suggested Management Type (AE) noted. See text for definitions. X= non-lodgepole type surrounded by lodgepole. The heavy line which more-or-less

parallels the park boundary is the inner limit of the fire suppression zone, as shown on the Park's Fire Management Plan.

(click on image for a larger size in a new window)

Type A:

Fire history type

(1)Communities:

a) Shasta Fir-Mountain Hemlock/Sedge-Lupine

b) Mountain Hemlock/Grouse Huckleberry

Suggestions: No prescribed burning necessary.

Reasons: Presently, more of the park that can support fir-hemlock is in lodgepole than during primeval

time. Through time, lack of man-caused fire will allow the balance of fir-hemlock to lodgepole to return

toward an equilibrium to be determined by the natural fire regime. Exactly what this balance was in

primeval times we cannot determine, but we are sure there was less lodgepole pine. Use of fire to reduce

the heavy fuel loads in these types is not justified-- the resulting dead lodgepole would raise ground fuels

to even greater levels within a few years. The fire danger and beetle kill now associated with these stands

is the price to be paid for a return toward primeval conditions.

Type B:

Fire history type (2)

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Communities:

a) Subalpine Fir/Goldenweed/Aster-Blue Wildrye

b) Subalpine Fir/Collomia-Peavine

Suggestions: No prescribed burning necessary.

Reasons: Much of this area, on the west slope and in the Pinnacles Valley, was burned since 1855, and is

thus relatively early in its development. A gradual encroachment of forest on meadow is probably the

"natural" condition, with small fires periodically eliminating some tree islands and meadow reproduction.

Hopefully, natural fire will fill this role. Our interpretation of this system's dynamics is open to

considerable question, but unless a detailed re-examination shows it to be erroneous, no use of prescribed

fire should be necessary. In perhaps 30-60 years the situation should be reassessed if these areas are not

following the patterns we predict or if natural fire has not occurred in at least some spots.

Type C:

Fire history type (5)

Communities:

a) Lodgepole Pine/Sedge-Needlegrass

b) Lodgepole Pine/Bitterbrush/Sedge

c) Portions of Lodgepole Pine/Sedge-Lupine

The more open areas, best represented in the following locations:

1) South and West of Timber Crater

2) SW of Sharp Peak

3) Upper Western Pinnacles Valley

Suggestions: No prescribed fire necessary.

Reasons: These forests are somewhat to very open, with light and discontinuous fuel. It is doubtful that

(1) fires have ever been large or severe and (2) these areas will produce enough. fuel to support such fires

in the foreseeable future.

Type D:

Fire history type (3)

Communities:

a) Mixed Conifer/Manzanita

b) Mixed Conifer/Bitterbrush-Manzanita/Sedge

Suggestions: Prescribed burning should be carried out in the not-too-distant future, perhaps following the

higher priority areas in the ponderosa pine (after priority 4). The fire should be a low-intensity ground

fire; it should miss many areas and be intense enough to scar, but not kill, some lodgepole (if possible)

and white pine. The ignition pattern should not be so all-encompassing that all pockets of fuel burn in any

one fire. This type should be burned over a long period--perhaps 30 years--to produce a variety of age

classes. Fires could be repeated at 30-50 year intervals in any given area. Areas burned by natural fire

need no treatment.

Reasons: This area has low fuel loads except in spots. Small scars on living lodgepole give evidence of

ground fires. The only scars with 2 fires, on white pine, had a 30-year interval. The relatively great ages

and heavy dwarf mistletoe of these stands indicate that fires which destroy the entire stand are rare.

Type E:

Fire history type (4)

Community: Denser parts of Lodgepole Pine/Lupine-Sedge, best represented at:

a) East of North Entrance

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b) Lower Western Pinnacles Valley

c) ESE of Bald Crater

Suggestions: Prescribed fire appears justified and desirable in some of this type, with a goal of its all

burning (by nature or prescription) within the next 70 to 100 years. The first burns (following preliminary

experimental work) could begin any time, and should be aimed at breaking the extensive areas of this type

(1) between Timber Crater and the north entrance road, and (2) in lower Pinnacles Valley into smaller

units, to decrease the hazard of very large, intense fires. After that, burning should be periodic, in Unit III

first, to fulfill the 70-100 year burning cycle and provide a mosaic of stands of several different ages.

After the first burning cycle, in which prescribed fire will help remove the accumulated fuel and thickets

that fire suppression has allowed, a natural fire regime should be sufficient. Even now, prescribed burning

should be applied only as necessary to assure that new stands are generated more or less evenly over the

next 70-100 years, assuring that areas of high fire danger remain relatively small and discontinuous at any

one time. Prescribe-burning large areas, or the whole area within a few years, will only result in a

probably unnatural concentration of fire danger both now (large expanses of dead fuel) and at some future

date (extensive thickets of mature forest again). Reburning after snags fall (10-20 years) will be necessary

to keep fire danger low. Extreme caution will be necessary.

Reasons: It appears that these areas burned in intense fires in primeval conditions, destroying the old

lodgepole forest, and replacing it with a young one. Fuel loads are very heavy in extensive areas;

prescribed burning to break up the expanse will reduce the danger of a wild fire here moving over large

areas or out of the Park. Only in this type has the fire suppression since 1902 allowed fuel build-up to

exceed our perception of primeval conditions in a lodgepole type whose area does not need to be reduced.

Fire Suppression Area - Unit III

We suggest that prescribed burning in Unit III be concentrated at first in the ponderosa and lodgepole pine types, in a

pattern which isolates Units I and II from surrounding lands. This should eventually allow the expansion of Units I and II

and thus reduce the amounts of prescribed burning necessary in most types. Recall that, in lodgepole (1) a repeat burn

will be necessary after snags fall and (2) living fuel loads will rapidly increase after fire in the dense seral stands, even

though ground fuels will be reduced.

Type A (Unit III only):

Communities:

a) Fir-Hemlock/Sedge-Lupine

b) Hemlock/Grouse Huckleberry

c) White Fir/California Brome-Lupine

Suggestions: There is no way to estimate the exact proportion of the whole area capable of supporting firhemlock which really was lodgepole in primeval times. We are certain, however, that it was smaller than

at present. We feel that prescribed burning should be kept to a minimum for the present. Clearing of heavy

ground fuels (for firewood) might help reduce fire danger along highways. Assessment of the role of

natural fire in these forests will be possible after a long enough time under the natural fire policy. Some re

conversion of primeval lodgepole to lodgepole certainly occurred; this gives a natural rationale for some

prescribed burning in these lodgepole types.

Type A is represented in Unit III at many places. (1) Several are small and away from the boundary; we

suggest no treatment; (2) In the following areas, burning across the narrow spots in the types near the Park

boundary should be sufficient: S of Castle Creek, NE of Bald Crater, E of the North Entrance (where

burns should coordinate with those in Type E). (3) Along Hwy 62 S of Cold Spring, between the highway

and the canyon, seems a good place to experiment with fire in this type. It might also serve as a visitor

exhibit. (4) The White Fir community NE of the panhandle should be treated only along the boundary,

also.

Type B (Unit III only ):

Communities: a) Subalpine Fir/Goldenweed/Aster-Blue Wildrye

b) Subalpine Fir/Collomia-Peavine

Suggestions: In Unit III, this type is quite young, and the forest patchy. No treatment is necessary at

present, except perhaps in its denser parts which are right along the Park boundary. Later assessment of

community change, as in Units I and II, will be necessary.

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Type C (Unit III only):

Communities:

a) Lodgepole Pine/Sedge-Needlegrass

b) Open areas of Lodgepole Pine/Sedge-Lupine

Suggestions: These have very sparse litter. As long as this remains true,no treatment is necessary.

Type D and Type E:

Prescribed burning should proceed as in Units I and II. Unit III should have higher priority.

http://www.nps.gov/crla/lodgepole/lodgepole8.htm

Date: 29-May-2001

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