Age distribution of trees on Watershed 5 at the time of harvest:

        The harvesting of W5 provided a one time opportunity to obtain cross sections of trees. These cross sections record the tree's age, and in the growth rings, considerable information about the stand history.  Chemical information on a year by year basis may also be obtained by analysis of the wood. All of the tree cross-sections referred to in this summary are stored in the Hubbard Brook archive building.  Four separate sets of cross sections were obtained as follows:

        1. All white ash trees
        2. Most of the trees on the "biomass" plots on the lower third of the watershed
        3. Most of the trees on one of the upper biomass plots
        4. A set of 25 fir trees harvested for dimension analysis/allometry
 
 
 

1. White ash

        White ash is a shade intolerant species that can only come into a stand in large natural gaps or following major harvesting activities.  Its initial success in establishment is probably also enhanced by the availability of mineral soil.  In the  forest inventory completed before the cut ( in the summer of 1982), all the trees > 10-cm dbh were measured on all the 360 grid units which comprise the whole of the watershed. (See Forest plot inventory). Based on the trees recorded in this inventory, we were able to locate all the white ash trees.  For most of them, we were able to cut a section off the remaining stumps, or in a few cases in which the stump was cut too low, count the rings on the stump in the field. A total of 93 ash sections were obtained and returned to the lab. Sections were allowed to air dry and then were sanded and the rings counted.  The results are summarized in the figure below.  It is quite obvious that the ash initiated in large numbers starting around 1915, although there were some which initiated in the decade before that. Since these trees were basically cut at ground level, the ages we measured are very close to tree age, in contrast to tree cores which may be taken higher in the lower bole.  There were also a few ash which initiated at intervals back to 1865. It is interesting that there were very few white ash which established after the 1920's. The 1938 hurricane, which shows up as major release in this area, did not result in any ash establishing in this stand. It is also interesting that back before the 1915 cutting of the stand, there was enough disturbance or gaps forming for an occasional white ash to get started.





2. Trees on the  lower "biomass" plots

         When the forest was cut and chipped we took the opportunity to test the reliability of the allometric equations prepared by Whittaker et al. (1965) for Hubbard Brook.  We selected three one quarter hectare areas (each comprised of four contiguous 25 x 25-m plots which were established on the watershed). The biomass of these plots was estimated by using the allometric equations and then the trees were very carefully cut and weighed in total for each plot (See Biomass plots for further details (future link)).  After the cut, sections were taken from most of the stems remaining on these plots. These sections were dried and sanded and their ages determined as for the ash trees discussed above.  The results for yellow birch, sugar maple and beech are shown in the figure below.  It appears that there was a fairly sharp increase in the number of yellow birch coinciding with the 1915 -1920 period. Sugar maple and beech, both shade tolerant species, have a much broader age distribution.  This broader distribution probably reflects the release of seedlings and saplings in the understory, whereas the yellow birch may have begun from seed at that time.  Regardless, the center of the initiation of all these species is still in the 1915-1920 period.

 
 
 
 

3. Upper biomass plot

        At the time of the logging, we had hoped to have six biomass plots to study. However, due to various problems, only the lowermost four were studied. The upper ones were marked, but as outlined in the history section, were not skidded off the watershed during the primary operation.  We did cut cross sections from as many of the stumps as we could find on one of these plots on the plateau at the top of the watershed. The forest here is primarily composed of balsam fir, white birch and red spruce. All these trees had been cut with a feller buncher and thus the stems were very macerated.   As a result, for some trees on the plot it was impossible to remove clean sections.  Data for all the species noted above are illustrated in the following figure. It appears that on the ridge there may have been a disturbance around 1895 and then another around 1920 - 1925. This later disturbance is about 5 years later than the timing of the original cut on the lower portion of the watershed.

 
 
 
 

4. Fir tree age from allometry trees

        In the summer of 1985, when they had just completed removing the remaining logs from the ridge area of W5, we took the opportunity to cut down and conduct bole allometry analysis on a number of fir trees right next to the upper limits of W5. The watershed boundary is ambiguous in this area of rolling irregular terrain. These trees are of the same forest that was cut on the adjacent upper part of W5.  We cut and analyzed 20 fir and one spruce, and another researcher who was simultaneously cutting some spruce (4) in the same area, allowed us access to the basal sections of his trees.  Of these 25 trees, 8 were between 50 and 65 years old, 5 were between 80 and 95 years, and 12 were between 100 and 110 years.   We selected average canopy-size trees for this study and thus probably captured the 1891-1985 cohort indicated in the trees from the upper biomass plots discussed in the previous section.

        These 25 trees provide somewhat more insight into the forest history on the ridge in that we measured ring widths on all of them, and thus can illustrate the forest growth and release history of the upper area of  W5.   The patterns of fir growth are shown in the figure below. These trees established in 1881, were released in 1914, and growth slowed until 1940, after which they again increased in growth rate, presumably in response to release by the 1938 hurricane. After 1957, growth more or less decreased up until when we harvested them.  We do not know the cause of the especially slow growth in 1972. It is possible that it has something to do with trail maintenance in the area, but there is no obvious reason.


 

[ W5 front page | main HBES homepage ]


Web page created June 2000
by Thomas Siccama and Ellen Denny