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Two eucalyptus selections yielded 23 cords of firewood per acre over a 43-month period.
Low-elevation foothill fuelwood plantation
Janine K. Hasey
P
Richard B.Standiford o J. M. (Mike) Connor o
I n March 1984,we established a test planting of selected eucalyptus and poplar species and clones in the Yuba County foothills. The main objectiveswere to evaluate
survival and growth characteristics over a
six-year period and to determine optimum harvest time of intensively managed
hardwood trees grown as energy crops
under foothill conditions.
The species, clones, and seed sources of
the trees in this study (table 1) were chosen
for their cold tolerance, fast growth, or
both, based on previous research at the
University of California Sierra Foothill
Range Field Station and elsewhere in the
state. This report summarizes the results
after 3.5 years of growth.
Roy M. Sachs
applied ranged from 40 to 65 gallons per
tree per week.
Herbicides and hand weeding were
needed for successful weed control during
the first year. Simazineat 0.5 pound active
ingredient ( a i ) per acre) and Surflan
(oryzalin) at 4 pounds a.i. per acre were
applied in late May to control summer
annuals. Even at this low rate of simazine,
some herbicide injury occurred, especially
to Eucalyptus uirninalis (manna gum). Subsequent hand hoeing was required two or
three times on most plots. Bermudagrass
and bindweed were successfully controlled by spot-spraying with 1.5%
glyphosate in late August and September.
Surflan (4 pounds a.i. per acre) was applied in November 1984. In the summer of
Methods
1985, the canopy had mostly closed and no
Eucalyptus seedlings 6 to 10 inches tall, further weed control has been necessary.
rooted eucalyptus cuttings, and poplar
Grasshopper damage was limited the
cuttings were planted in Auburn-Las first summer after planting by two appliPosas-Argonaut rocky loam soils with 7 cations of malathion spray and Sevin (carpercent slope at a 575-foot elevation at the baryl) bait. Light deer browsing occurred
Sierra Foothill Range Field Station.
on several Eucalyptus species, but was exPreplant preparation consisted of tensive on many of the poplars during the
spraying with 1 percent Roundup first season and, to a lesser extent, the sec(glyphosate)two weeks before planting to ond year. Two commercial deer repellents
kill native annual grasses and forbs. Trees were used in 1984. Their effectivenesswas
were sprinkler-irrigated during the first of short duration, possibly because of the
growing season, beginning within two sprinkler irrigation. Although early
weeks of planting and continuing until growth may have been slowed, the popmid-September. A drip irrigation system lars survived the browse damage and, by
was installed in 1985. Since then, trees the end of the second summer, all had
have been drip-irrigated weekly from grown too tall for deer to reach.
May through September at the rate of 80
No fertilizer was used in 1984. Since
percent of pan evaporation. Actual water 1985, a total of 75 pounds of nitrogen per
acre as urea has been applied in equal
monthly applications through the drip
system from June through September.
Trees were planted in a randomized
complete block design with four replications on a 6- by 6-foot spacing (1,210 stems
per acre). Diameter at breast height (DBH)
and total height were measured yearly in
October after 1985. Diameter was also
measured along the stem in 1986 and 1987
to calculate stem taper and volume. Only
the interior nine trees of each 49-tree plot
were measured to avoid an edge effect.
ResuIts
Over the three years compared, E. globulus (blue gum) consistently had the greatest average height and diameter, and the
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TABLE 1. Species or clones studied
Species or clone
(and common name)
Eucalyptus globulus
(blue gum)
E. camaldulensis
(river red gum)
E. camaldulensis.
C-1 clone
E. camaldulensis.
C-2 clone
E. viminalis
(manna gum)
E. dalrympleana
(mountain gum)
Populus deltoides
X niwa (wplar)
Seed source
Barnback,
Australia
Lake Albacutya,
Australia
Unknown - random
selection
Improved Spanish
seed
South coast, New
South Wales,
Australia, 200-ft
elevation,
Australia, longitude
unknown, latitude 35 S,
800-ft elevation
'Giacometti' hybrid
clone
CALIFORNIA AGRICULTURE,NOVEMBER-DECEMBER 1988
21
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TABLE 3. Stand characteristics at two ages
TABLE 2. Comparison of tree characteristic at various ages
Average DBH'
Species/clone
19
mo
31 mo
Average height'
43 mo
19 mo
31
mo
43
mo
. . . . . . . . . . . . . . . inches . . . . . . . . . . . . . . . . . . . . . . . . . . . . . feet . . . . . . . . . . . . . . .
E. globulus
E. camaldulensis
E. camaldulensis
C-2 clone
Poplar clone
E. dalrympleana
E. virninalis
E. carnaldulensis
C-1 clone
*
2.45 a
2.21 a
3.22 a
3.14 ab
3.93 a
3.48 c
25.6 a
19.5 cd
36.5 a
26.0 cd
46.5 a
31.9 c
2.16 a
1.82 b
1.80 b
1.79 b
2.99 abc
2.84 bcd
2.92 abcd
2.81 cd
3.90 ab
3.50 bc
3.56 abc
3.34 c
22.6 b
20.4 bc
17.6 de
17.9 de
34.5 a
29.7 b
27.1 bcd
27.4 bc
43.4 a
38.2 b
34.2 bc
34.1 bc
1.65 b
2.64 d
3.32 c
15.8 e
24.4 d
31.9 c
Age Survival.
Volume
E. globulus
mo
31
43
%
94
86
cu ft/ac cu ft/ac/yr
1.075.18 416.74
1.970.55
550.43
C-2 clone
31
43
100
100
1,040.57
1.969.88
403.32
550.25
E. dalrympleana
31
43
97
94
837.56
1.508.74
324.64
443.78
E. viminalis
31
43
83
83
770.41
1,449.27
301.71
404.82
E. camaldulensis
31
43
100
100
754.21
1,435.15
292.33
400.88
Poplar clone
31
43
100
100
659.43
1,286.25
255.59
359.29
C-1 clone
31
43
100
100
566.33
1.086.27
219.51
303.43
Treatments followed by the same letter are not significantly different. LSD (.05)
E . camaldulensis (river red gum) C-1 clone was 15.5 percent and of the hybrid poplar
had the lowest. At 3.5 years, the C-2 clone clone, 16 percent. In contrast, the CV for E.
had reached an average diameter equal to globulus seedlings was 51 percent and for
that of the E . globulus and was almost as E. viminalis, 76 percent.
The large growth differences between
tall (table 2).
The largest yields per acre at 43 months the C-1 and C-2 clones point out the seedwere the same for E. globulus and the E. ling variability inherent within a species.
camaldulensis C-2 clone (table 3). Both E. Both clones were selected from E .
globulus and the C-2 clone yielded 23.2 camaldulensis seedlings. C-1, which has
cords (1,972 cubic feet) per acre over the consistently performed poorly, was
43-month period (fig. 1). All mortality cloned from a random selection, whereas
occurred within the first growing season the superior performing C-2 was cloned
except for E. globulus and E. dalrympleana from trees from improved Spanish seed.
All the Eucalyptus species have endured
(mountain gum). Several small E. globulus
trees died at 41 months, presumably from temperatures in the low 20s for several
lack of sunlight and competition within consecutive days, with a minimum of
16"F, showing virtually no frost injury.
the stand.
The E . globirlus seedlings are fairly uni- Minor tip dieback has occurred on the C-1
form, and most trees have single, straight clone, E. viminalis, and E . globulus. The Cstems, a desirable characteristic for fuel- 1 clone has suffered branch dieback from
wood trees. The C-2 clone is even more drought stress in the fall when the irrigauniform, as would be expected from a clo- tion system was off.
nal population. It too has a very upright,
Conclusions
single stem.
Early rates of growth during these 43
As an example of the lower variability in
clonal populations, the coefficient of vari- months show that there is considerable
ation (CV) for 1987 DBH of the C-2 clone promise for the production of large vol-
Fig. 1 . Eucalyptus globulus and the E. camaldulensisC-2 clone produced the greatest volume
at nearly 2000 cubic feet per acre at 3.5 years.
22 CALIFORNIA AGRICULTURE.NOVEMBER-DECEMBER1988
MAlt
Specier/clone
' Survival of interior nine trees of each plot from which
data were taken.
t MA1 = mean annual increment.the average annual
growth in cu ftlaclyr.
umes of woody biomass from intensively
managed plantations of exotic hardwood
species on low elevation foothill rangeland sites. The high uniformity of the clonal blocks of both eucalyptus and hybrid
poplars contrasts with the larger variability of the natural seedling stands. The
uniformity of the clonal stands may be
particularly useful in design of harvesting
and processing technology.
We will continue this study for at least
another two years to determine the age at
which biological growth reaches a maximum. Annual measurement of DBH,
height, and per acre volume will continue.
At final harvest, specific gravity and other
wood properties will be sampled, and actual volumetric and weight yields will be
determined. Superior individual trees
will be identified from the seedling blocks,
and cuttings from these maintained for
future genetic improvement work.
Janine K. Hasey is Farm Advisor, Cooperative
Extension, Sutter-Yuba counties; Richard B.
Standiford is Extension Natural Resources
Specialist, Forestry, University of California,
Berke1ey;Mike Connor is Superintendent, UC
Sierra Foothill Range Field Station, Browns
Valley; and Roy M . Sachs is Chair, Department of Environmental Horticulture, UC
Davis.
The authors are grateful to John Le Blanc,
Staff Research Associate, Berkeley; Don
Springsteen and staff at the Sierra Foothill
Range Field Station; Doug McCreary, Natural Resource Specialist; Dean Donaldson,
County Director, and Sherri Gallagher, Field
Assistant, Napa County; Glen Forister, Jerry
Ripperda, Vicki Keresztury, and Roy
Woodward, Department of Environmental
Horticulture, UC Davis, for field assistance;
Zappettini Nursery, California Department of
Forestry, and Agroforestry Associates for
plant material.