
Preliminary Field Evaluation of Harvester on Pines
and Stweetgum in the Southeastern United States
In the spring of 1994, the biomass harvester was transported to Alabama for
a demonstration for a Short Rotation Intensive Culture (SRIC) mechanization
workshop and then to South Carolina and Georgia for field trials harvesting
dense pine stands and sweetgum regrowth sites.
At the Alabama site, the harvester was examined on 1 year old coppice
regrowth from several year old sycamore, sweetgum, and water oak stools, and on
3 year old sycamore seedlings. When sycamore, sweetgum or water oak stems were
less than 5 cm in diameter and the height less than 2.4 m tall, the harvester
passed through the material at about 3.5 km/hr capturing nearly all of the
stems and then passing it through the blower. Given the 2.6 m width of the
cutterhead, a 3.5 km/hr forward speed corresponds to 0.91 ha/hr.
There was concern that the flail cutterhead did not cut the coppice cleanly
enough to allow adequate resprouting. Clearly the severed stems were split
several cm below the site of the cut. If shoots will emerge below the location
where the stems are split, it should be possible to have a high percentage
resprouting by cutting the shoots higher on the stump. It is important to base
the decision on whether to pursue development of a harvester for hardwood
coppice upon quantitative measurements of percentage stool resprout as a
function of knife geometry rather than conjecture.
While the harvester was capable of mowing down the 4.5 m tall 10 to 12 cm
diameter sycamore seedlings, the trees were not severed and captured by the
shredder. We found that a major contributing factor to the failure to capture
the 4.5 m tall sycamore trees was the geometry of the cutterhead. The knives on
the cutterhead extended only 5 cm beyond the disk that held them to the head.
Since none of the knives overlapped, the maximum depth of cut was only 5 cm. As
a result, trees with a greater diameter than 5 cm were merely pushed over and 2
parallel 5 cm deep gouges extending the length of the tree were found on the
trees.
When operating in the southeast, it was necessary to operate the engine at
1,700 rpm rather than the desired 2,100 rpm due to excessive pressure on some
hydraulic components. This also slowed the blower paddle speed giving the chips
less trajectory and provided less horsepower to the cutterhead. This problem is
currently being corrected in Texas.
The harvester was examined on 2 pine sites near Greenwood, South Carolina.
Both sites were hand planted, but large numbers of additional pine seedlings
became established from natural seedlings. At the first site, the originally
planted trees were about 13 cm in diameter and 6 m tall. The naturally
established pine seedlings were less than 6 m tall but so thick that it was
often not possible to discern where the original rows were. At the second site
of pine, the trees were typically 1.8 to 2.4 m tall. As discussed later, some
portions of this field had pine seedling densities as high as 13 trees per
square m (130,000 trees/ha). On this site 1.8 m square plots were clipped to
measure the standing biomass.
The goal at both of the South Carolina pine sites was to clear 2.6 m wide
paths, leaving a width of 0.5 m between the 2.6 m wide lanes. The trees in the
0.5 m width could then grow faster with reduced competition. Six lanes about
230 m long were made in the 6 m tall trees at 1.6 km/hr, before it was decided
these trees were just too large and the terrain too difficult for the
harvester.
In contrast to the flat agricultural type field sites in Alabama, the South
Carolina sites had old windrows, 30 cm diameter rocks and ditches that required
that the cutterhead be maintained about 10 to 20 cm above ground. This in turn,
created 10 to 20 cm diameter stumps that precluded pulling an agricultural type
trailer behind the harvester.
On two occasions the harvester became stuck despite no indications of
moisture from the surface. This was no doubt compounded by the fact that the
2,270 kg head was mounted in front of the front tires. It is clear that future
harvesters will have to be mounted on a 4 wheel drive "skidder type"
frame to provide greater maneuverability, clearance and traction in moist
conditions.
At the second South Carolina site the trees were 1.6 to 2.4 m tall with pine
tree densities as great as 130,000/ha. At this site the harvester was capable
of mowing and harvesting the trees at 3.6 km/hr thus clearing 0.93 ha/hr. If
one included the 0.5 m width in which the trees remained, then the area treated
for thinning was about 1.08 ha/hr. The harvesting speed at this site was more
dependent on the terrain than the amount of biomass to be processed.
Following testing at the South Carolina pine sites, the harvester was tested
on a sweetgum regrowth site near Athens, Georgia. The sweetgum was typically 5
to 10 cm in basal diameter and 6 m tall but there were some 15 to 20 cm basal
diameter 9 m tall trees. This site was scheduled for bulldozing, stacking into
windrows in preparation for planting back to pines. To measure the biomass at
this site, trees were harvested and weighed for regression equation development
in three plots of 40 square m.
The following regression equation was developed based on 13 trees ranging in
circumference and weight of 1.04 cm and 0.68 kg to 6.00 cm and 15.25 inches and
28.8 kg.
log biomass (kg)=2.145908 log circumference (cm) - 1.90783
The detransformed r square was 0.928 and the root mean square error 2.13 kg.
The biomass estimates were derived from basal diameter measurements on 3
plots of 40.5 m2. By applying the regression equation to the 3 plots we
estimated the biomass/ha as follows:
- Plot 1 with 25 trees had a brush biomass of 89.72 kg (22,161 kg/ha) (each
of the plots were 40.5 m2).
- Plot 2 with 19 trees had fresh biomass of 117.26 kg (28,963 kg/ha).
- Plot 3 with 23 trees had a fresh biomass of 129.87 (32,078 kg/ha).
Thus, the mean biomass/ha was 27,733 kg/ha with a standard deviation of
5,078 kg/ha. The mean and standard deviation for the number of trees per ha was
5,515 +/- 755 trees/ha.
When harvesting the sweetgum trees at 1.6 km/hr, we harvested about 0.4
ha/hr. Given the fact that the standing biomass of this site was 27,731 kg/ha,
the theoretical maximum capture would be 11,092 kg/hr. Thus, there is enough
biomass at this site to provide 11 ton/hr of biomass which at $9/green ton
would be a $90/hr credit. If 85 percent capture could be achieved, the
harvesting could generate $76/hr of revenue.
While we had mechanical problems at this site, related to trees hitting
exposed hydraulic lines, we cleared about 1 ha at a harvesting rate of about
1.6 km/hr (0.4 ha/hr). For the first time at this site, the power of the
harvester became limited in harvesting isolated 17 cm basal diameter, 9 m tall
sweetgum trees which fell in front of the harvester and entered the cutterhead
to be chipped. This resulted in slower cutterhead and engine speed which
resulted in some large wood pieces (15 cm by 4 cm) becoming lodged in the
augur. Nevertheless, with improved cutterhead geometry, and the harvester
operating at 2,100 rpm instead of 1,700 rpm (due to excessive hydraulic
pressures at heat exchanger), it should be possible to routinely harvest 10 to
12 cm diameter sweetgum trees at 1.6 km/hr.
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