Relationships Between Sunfleck Dynamics and Red Fir Seedling Distribution

S. L. Ustin, R. A. Woodward, M. G. Barbour
Department of Botany
University of California
Davis, California 95616 USA
 
J. L. Hatfield
Department of Land, Air, and Water Resources
University of California
Davis, California 95616 USA
Manuscript received 25 April 1983;
revised and accepted 17 October 1983.

Abstract

Red fir (Abies magnifica) seedlings show a patchy distribution in much of the species' range. Patterns of irradiance in the understory of a red fir forest in the central Sierra Nevada Mountains of California were measured in an effort to determine whether a correlation existed between the irradiance patterns on the forest floor and the distribution of seedlings. Replicate pairs of plots on a south exposure with significant differences in seedling density were compared with each other and with plots on a contiguous north exposure. No significant differences between plots on south exposures were found for either physical characteristics, soil chemistry, water, or litter layer traits. On the south aspect, plots with few seedlings had mean daily irradiances 2.1 times higher than plots with many seedlings, primarily due to 3.5 times more frequent occurrence of sunflecks at irradiance levels above 1025 m E m-2× s-1. Analysis of solar tracks on fish-eye-lens photographs of overstory canopies and measurement of sunflecks on the forest floor indicated that plots with few seedlings had larger sunflecks, particularly during midday hours. In contrast, seedling distribution on the north exposure was not correlated with patterns of irradiance or temperature, apparently because of less intense direct-beam irradiance on these slopes. Apparently the high irradiance on open south slopes is inhibitory to red fir seedlings compared with the low-intensity irradiance on more shaded south slope sites and on all north slope sites.

Photon flux densities > 500 m E m-2× s-1 are beyond the light saturation point for net photosynthesis, as determined in the laboratory from field-collected seedlings. Absorption of light >500m E m-2× s-1set by seedlings will substantially increase the energy load without corresponding increases in carbon gain. We suggest seedlings are absent from high-light plots because of temperature and water stresses induced by higher irradiances early in the growing season.

Key words: Abies magnifica; California forests; irradiance photon flux density; photosynthesis; red fir; seedling demography; Sierra Nevada Mountains; sunflecks.

Introduction

Although utilization of high-elevation forests for lumber is increasing, our knowledge of factors controlling stand establishment in these forests is limited. In a heterogeneous environment the distribution and abundance of individuals reflects in part the availability of "safe sites" meeting the requirements for seedling establishment (Harper 1977).

The importance of the light regime for plant growth in the highly variable environment of understory plants has been recognized in several studies (Evans 1956, Bray 1958, Anderson 1966, Anderson et al. 1969). In the present study we examine the role of light in natural regeneration of Abies magnifica A. Murr. (red fir). Although the effect of variation in irradiance is readily observable in the mosaic of different communities as aspect varies, the effects within a community are less apparent. In some cases, higher light intensities might be expected to favor seedling establishment. Red fir seedlings have been widely reported to occur under small openings in the canopy (Sudworth 1908, Oosting and Billings 1943, Emmingham and Waring 1973, Rundel et al. 1977), and Seidel (1977) found release from shade increased red fir sapling growth. This suggests that low irradiance conditions characteristic of the understory might be inhibitory to red fir seedlings and that some minimal irradiance conditions are required for growth and survival. In other cases, however, higher light might inhibit seedling survival. In the northern hemisphere, the high total insolation on south-facing exposures, especially at midday, may result in higher temperatures and greater water stress relative to other exposure aspects. During the period of initial root penetration of the soil, such stresses might have a significant effect on seedling establishment. These conditions should be especially pronounced in California due to the strongly Mediterranean climate, where seed germination coincides with the onset of annual summer drought.

Red fir is a dominant tree in the upper montane forests of the Sierra Nevada Mountains, southern Cascade Range, Klamath Mountains, and southern Yolla Bolly Mountains of California (Hemphill 1952, Griffin and Critchfield 1972, Rundel et al. 1977, Sawyer and Thornburgh 1977). Previous analysis revealed significant aggregation of young red fir seedlings in an apparently homogeneous understory at our study site in the central Sierra Nevada. Similar patchiness of seedling and sapling regeneration has been recognized in other parts of the red fir range (Pitcher 1981). Our focus was to determine if a correlation existed between the irradiance distribution on the forest floor and the aggregation of seedlings.

Materials And Methods

Description of research site

Study plots were located at » 2160 m elevation on south and north aspects of Mount Lincoln (39°15'N, 120°20'W), along the west slope of the Sierra Nevada Mountains, California. The surrounding virgin red fir forest is part of the Onion Creek Experimental Forest.

The environment, flora, and vegetation of the Experimental Forest have been described by Talley (1977), Smith (1978a, b), and Palmer et al. (1983). Briefly, mean annual precipitation is » 1.3 m, >90% of which falls from mid-October to early June, mostly as snow. Average snowpack duration is 192 d and depth is 3.1 m. Mean annual temperature is » 4°C, mean daily maximum July temperature is 28°, and mean daily minimum January temperature is - 10°. The soil is a moderately shallow (» 0.5 m) Entisol in the Ahart soil series, derived from weathered rhyolitic tuff. There is a continuous duff layer ~50 50 mm thick, with scattered limbs and twigs on the surface. More than 95% of the trees in every size class are red fir. Density of overstory trees (>0.2 m dbh) is » 190 per ha; we estimate they are 100-600 yr old. Cover by shrubs and herbs is only » 1-2%, and species richness is low (15 taxa). In comparison to forests described by Oosting and Billings (1943), we found less basal area per hectare of intermediate-age and mature red fir, a greater density of sapling fir, and fewer species of shrubs and herbs, but otherwise the same community physiognomy and overwhelming dominance of red fir in all age categories.
 

Description of study plots at the research site

On the south aspect, where seedlings occurred in clumped patches, three pairs of study plots within a homogeneous 0.5-ha area of red fir forest were selected and monitored for two summers. Each pair consisted of one plot with many 1-9 yr old red fir seedlings (S) and one plot with very few seedlings (NS). The plots in each pair were selected to be equal in area (23-28 m2), close together (1-8 m between adjacent perimeters), and similar in physiographic characteristics. During the time of selection (1500-1800) plots exhibited no evident differences in light intensity. Total percent canopy cover was more obviously variable among plots, but 1S and 2S had more cover and 3S less cover than corresponding NS plots.

After permanent marking (July 1981), microenvironmental measures of overstory and understory plant cover, litter depth, soil texture, and soil chemistry (top 0.2 m) were taken. Soil texture, pH, electrical conductivity, cation exchange capacity, and concentrations of soil cations and nitrate were determined by the University of California Agricultural Extension Service in Davis. All seedlings were counted and aged, and the presence of other species noted. Seedlings were aged by counting the terminal bundle scars, previously found to have a high correlation with tree rings.

Seven evenly dispersed locations within each plot were chosen as permanent sample points for recording light and temperature data. Within S plots, the points were located adjacent to 1-yr-old seedlings.

During the first summer we noted that seedlings were more abundant and more continuously distributed on north than on south slopes. Therefore, in 1982 we established thirty 5 x 5 m contiguous plots along five transects where seedling density varied on a north exposure. These plots were located at the same elevation as those on the south slope and about I km from them, within the same continuous stand of red fir. Here, transect locations were subjectively chosen to cross areas where seedling densities varied. Subsequently, 14 plots were selected to span the range of canopy cover and seedling densities, including 3 having high and 3 low numbers of seedlings and 8 having intermediate seedling densities.
 

Dates of measurements

The following measurements were made over a 10-wk period (27 July-30 September) in 1981: soil moisture, soil and air temperatures, photosynthetically active radiation (PAR), and total irradiance (using the ozalid paper technique). In 1982 soil moistures were determined over 10 wk (13 June-25 August), soil and air temperatures from 25 August to I September and ozalid papers from 25 August to 1 September.
 

Monitoring of temperature and soil moisture

Once a week temperature profiles were taken at midday at each permanent sample point on south slope plots and from four points on the perimeter and one in the center of each north slope plot. Shielded thermistors were placed 0.01 m above the ground and 0.01 and 0.1 m below the surface. Percent soil moisture of three soil samples, from 0.01-0.2 m depth beneath the litter layer, at the perimeters of plots was determined gravimetrically, by weighing before and after drying at 105° .
 

Monitoring of photosynthetically active radiation and total irradiance

Each week a different plot pair was monitored for PAR on the ground with seven quantum sensors per plot, constructed according to Biggs et al. (1971) and Pearcy (1983). Irradiance was calibrated for photosynthetic photon flux density (PPFD) with a LI-COR quantum sensor. Each sensor was taped to a nail and pressed to the ground surface, so that its aperture was horizontal. The sensors were attached to a Campbell Scientific CR21 data logger, signal inputs at 1-min intervals were averaged for 10 min. and the data were stored on cassette tape by an audio tape recorder.

An additional, integrated measure of irradiance was obtained during both summers by use of the ozalid paper method. Peak spectral sensitivity for this technique is 410 nm. Stacks (20 sheets) of ozalid paper (Dietzgen) in seven covered Petri dishes with 100-mm2 apertures were placed in each plot pair and collected weekly, following the method of Friend (1961).
 

Monitoring of sunfleck size

To gain an estimate of the area and number of sunflecks, each plot on the south slope was sampled for one 9-h period on a clear day in mid-September 1981 using the method of Miller and Norman (1971) and Norman et al. (1971). Two parallel line transects 2.45 m long and marked into 5-mm intervals were placed 2 m apart in each plot. Every hour, we recorded the length of all sunflecks along each transect. Although the edges of sunflecks are blurted by penumbral effects, we checked our ability to determine their size by passing a quantum sensor along the transect and found we could consistently differentiate the edges of sunflecks as low as 50 m E m-2× s-1 from background skylight of 25 m E m-2× s-1
 

Description of overstory canopy cover

Initially we measured overstory cover from the center of each plot with a "moose horn" device which projects a view directly overhead through a grid of dots (Garrison 1949). To analyze canopy architecture in relation to solar path, we photographed the canopy over each plot using a Soligor fish-eye lens on a f1.4 Nikon lens on a leveled camera 0.5 m above the ground in 1981, and a Canon 7.5 mm fish-eye lens in 1982. Potential number of minutes of full sun per hour throughout the growing season was determined by summing the length of canopy openings along solar tracks from Smithsonian Institute tables (List 1951), covering the potential growing season from 1 May to 6 October (Evans and Coombe 1959). Solar tracks for 1981 were adjusted to compensate for the distortion of the Soligor lens.
 

Measurement of seedling net photosynthesis

Twice during the first summer we excavated six 38 yr old fir seedlings with surrounding soil in a way that minimized root disturbance. These were brought to the Davis campus, watered, and allowed to stabilize for 4-7 d in a growth chamber at a 16-h photoperiod of 300 m E m-2× s-1 and a day/night thermoperiod of 17°/11°.

Net photosynthesis was measured with an open gas exchange system described elsewhere (Pearcy and Ustin 1984). An attached shoot was placed inside a glass-windowed, temperature-controlled chamber. Vapor pressure and CO2 concentration within the chamber were controlled with a dew point condenser and a Wosthoff G 27 mixing pump. The air within the chamber was thoroughly mixed. Light was supplied from a 1500-W metal halide lamp, and irradiance was varied with aluminum screens of different mesh size. Light was measured with a photosynthetic photon flux density (PPFD)-calibrated silicon cell mounted on the chamber lid. CO2 concentrations were determined with a differential infrared gas analyzer (Beckman Instruments, model 865), and water vapor concentrations with a relative humidity probe (Weathermeasure, model HMP 11). During the experiments, needle temperatures were maintained at 25.5° ± 1°, vapor pressure deficits at < 1.0 kPa, and ambient partial pressure of CO2 at 37 ± 2 Pa. Fir needles were later removed and dried. Net photosynthesis was expressed on a dry mass basis.

Results

Microenvironment of the south aspect study plots

Biotic and abiotic environmental parameters for each of the six south aspect plots are summarized in Table 1. Despite a 20-fold difference in seedling density in 1981, there was no statistically significant difference in measured environmental factors between S and NS plots (Student's t test, P < .05). In general, soil traits were similar to those reported for other Sierran conifer sites by Stangenberger (1979). Overhead estimates of canopy cover did not differ significantly between S and NS plots.

Nearly half of all seedlings in both S and NS plots in 1981 were estimated to be in their 1st yr (Fig. 1). There was a nearly continuous distribution of seedling ages in the S plots but not in the NS plots: plot INS contained only three lst-yr seedlings, 2NS only two 16-40 yr old suppressed saplings, and 3NS five seedlings up to 7 yr old. The span of ages in S plots indicated that these plots had been suitable for germination and establishment for many years.

Even in S plots, there were some years during which few or no seedlings became established. This was the case during our 2nd yr of observation, despite a large cone crop in the previous year. In fact, in 1982 there was no statistically significant difference in the numbers of 1 st yr seedlings between S and NS plots (means = 10.3,6.7). However, in 1982 the pattern of germination and mortality appeared to be quite different on S and NS plots. Germination began 2-3 wk after snow melt on all plots, but further germination ceased and significant seedling mortality began » 1 mo earlier on NS plots than on S plots. By mid-July the resulting patchiness in seedling distribution was again apparent.

Root systems of all but the oldest seedlings were within the upper 0.2 m of mineral soil. Mean root length (+SD) of Ist-yr seedlings in August was 52.2 + 22.6 mm (N= 25 seedlings). Minimum soil moisture (10-11%) and the pattern of soil moisture depletion within this depth during the latter part of the growing season were not significantly different (ANOVA) for S and NS plots in either year. In 1982 the soil moisture declined rapidly from 25 to 10% 30-45 d after the snowpack melted. There was no evident difference in snowpack depth or date of snow melt between plot pairs.

Midday air and soil temperatures in both 1981 and 1982 were similar and were markedly and consistently warmer on NS plots (Fig. 2), by an average of 5°C in the air and just below the soil surface, 2° in the subsoil ( - 0.1 m).
 

Quantum flux density on the forest floor

A summary of mean PPFD for 6 wk is presented in Table 2. Mean daytime PPFD from 0600-1800 was consistently greater on NS plots (with few seedlings), averaging 3 11 m E m-2× s-1 for all 6 wk which was 2.1 times that for S plots (ANOVA, P < .001). When the PPFDs are expressed in frequency histograms (Fig. 3), it can be seen that the difference in means is largely due to the greater frequency of bright sunflecks (> 1025 m E m-2× s-1 on NS plots. The frequency of readings at low PPFD (below 75 m E m-2× s-1) is not significantly different on S and NS plots, but there was a 3.5 times higher frequency of PPFD above 1025 m E m-2× s-1 on NS plots: 14.5% of all readings were in this irradiance class for NS plots, but only 4.1% for S plots. Conversely, the frequency of PPFD between 75-1025 m E m-2× s-1 in the NS plots was only 0.77 times that observed in the S plots. Because of the large sample size (n > 27,000), these differences are highly significant (ANOVA, P < .001).

Results of the ozalid paper technique, which integrates irradiance over time, indicated consistently higher total irradiance on the NS plots. For S plots a mean of 8.9 ozalid sheets were exposed per week for 10 wk in 1981, and for NS plots a mean of 10.0 sheets. In 1982, a 1-wk period showed means of 7.7 and 8.4, respectively. These differences between pairs are statistically significant (Student's t test, P < .01) and, because increasing amounts of light are required to expose additional ozalid sheets through the packet, probably underestimate the ecological significance of the considerably greater total irradiance on the NS plots.

The daily pattern of PPFD during three randomly selected days appears to show a timing difference in all three plot pairs. For example, the daily course of mean PPFD at 10-min intervals on 4 September, a representative day (Fig. 4) indicated that plot 1 NS received 2-4 times as much irradiance as 1 S between 0600 and 1300. These differences are greatest during midday; however, in the late afternoon differences were less pronounced, and IS received more light than INS.
 

Sunfleck size

Sunflecks rarely occurred on the transects before 0900 and after 1600. It was obvious that sunflecks varied greatly in irradiance. Repeated spot measurements with a quantum sensor along one transect revealed that sunflecks varied from a low of 31 to a high of 624 m E m-2× s-1. Large sunflecks were of considerably higher light intensity than small ones, due to penumbral effects.

Data on sunfleck size and number between 0800 and 1700 show that sunflecks in NS plots were similar in number (S = 18.2 ± 8.4 SD, NS = 15.9 ± 6.5 SD) but larger by 40% than sunflecks in S plots (S = 0.20 ± 0.04 m SD, NS = 0.28 ± 0.16 m SD, ANOVA). This size difference was not significant. When considered at individual hourly intervals or over the entire day, mean (n = 6 transects, two transects per plot) total percentage ground area covered by all sunflecks [S (number sunflecks x length of sunfleck)] was not significantly different between S and NS plots (S = 24.2% ± 12.3 SD, NS = 28.8% ± 16.7 SD), probably because of the large variance and the inverse relationship between sunfleck size and number (ANOVA). A comparison of mean individual sunfleck size (Fig. 5) did reveal a daily pattern consistent with the differing pattern of irradiance in the 1S and 1NS plots shown in Fig. 4. Although the differences are not statistically significant, S plots had larger sunflecks than NS plots during early morning and late afternoon hours when irradiance was lower. In contrast, NS plots had larger sunflecks than S plots at midday when irradiance is higher. These differences in sunfleck size, consistent on all transects, are significant between 1000 and 1400 (ANOVA, P < .01).
 

Canopy structure and solar tracks on the south exposure

S and NS plots show consistent differences in mean openness of the canopy as determined from four solar tracks on fish-eye photographs spanning the potential growing season (Fig. 6). NS plots had large canopy gaps along the solar tracks at midday, but such gaps were absent on the S plots. These plots consistently receive direct sun for nearly 60 min/h around midday, while S plots had smaller canopy gaps distributed more uniformly throughout the day and rarely receive full sun for > 30 min/h. The differences in distribution of canopy openings result in greater variation in levels of light exposure on NS plots than on S. Total daily canopy gap lengths along the solar tracks, however, were not significantly different between plots (ANOVA). Thus, analysis of the canopy gap structure for potential sunflecks closely corresponded with the actual patterns of sunfleck distribution and intensity measured on the forest floor.
 

Seedling density and canopy structure on the north exposure

Seedling density on 30 north-aspect plots varied widely, from 0 to 400 seedlings, with an average of 95.3 seedlings/25 m2. Plots with no fir seedlings had > 50% Arctostaphylos cover. No germination occurred during 1982; all seedlings were therefore older than 1 yr and represented survivorship in many age classes. In contrast to the south-aspect plots, no correlations were found between seedling density and midday temperatures, canopy structure relative to the solar path, or total irradiance (Table 3). However, there was one striking difference between north and south exposures: all plots on the north aspect, regardless of seedling density, had canopies with relatively large gaps at midday. Solar track measurements show that these canopy openings permit penetration of direct irradiance for substantial periods of time throughout the day, but particularly at midday, as in NS plots on the southfacing slope (cf. Fig. 6). While total time that canopy was open along solar tracks was greater on the north aspect than on either set of south aspect plots (Table 3), the mean number of ozalid sheets actually exposed, indicative of total irradiance received, was the same as in south-facing plots.
 

Seedling net photosynthesis

The mean net photosynthetic response is shown in Fig. 7. There was some variation among seedlings in photosynthetic rates for a given PPFD, which could reflect either some seedling damage during transport or actual differences in photosynthetic capacity. We detected no differences in photosynthetic rates between the collections in August and September. These rates are low, but within the ranges reported for other conifers (Larcher 1980), especially under canopies (Watts et al. 1976, Trong and Linder 1982), and for field measurements of red fir (S. R. Radosevich, personal communication). The light compensation point was 60 m E m-2× s-1 and the light saturation point was » 500 m E m-2× s-1, » 3% and 25% of full sun, respectively. Consequently, we estimate that even low-irradiance sunflecks, between 50 and 75 m E m-2× s-1 will contribute toward a favorable carbon balance, while sunflecks of PPFD greater than 500 m E m-2× s-1 will not contribute further to a positive carbon balance, and may have a negative impact by increasing temperature and water stress.

Discussion

Our data show a strong correlation between the aggregated distribution of red fir seedlings and the distribution of sunflecks on south-aspect slopes and suggest mechanisms by which these patterns are related. Both ground-level sunfleck measurements and solar tracks plotted on the canopy photographs revealed larger canopy gaps for sunflecks in the south-aspect plots with few seedlings. These large gaps permit a long time interval at midday during which full-intensity, direct solar irradiance can penetrate to the forest floor. No large gaps permitting sunflecks of greater than a few minutes duration were found on the south exposure plots with many seedlings. Although sunflecks varied greatly in size, duration, irradiance, and frequency, these differences between south-aspect plots having high and low seedling densities are consistent and predictable over the entire growing season and must substantially alter the microclimate. South aspect plots with seedlings have a canopy structure which modifies the pattern of irradiation such that irradiance on the forest floor resembles the diurnal pattern of direct-beam irradiation characteristic of north-facing slopes, with morning and afternoon maxima. Gaps in the canopy on the north aspect were larger than those on all the south-aspect plots, permitting a greater proportion of the incident irradiation to reach the forest floor.

Because large new gaps in the overstory, caused by losses of major limbs and of entire trees, occur infrequently, microsite differences in the pattern of the light regime should be consistent over several years. Consistent with this expectation, seedlings of different ages occur within the aggregations, indicating that these sites have been suitable for establishment for many years.

No other factors account for the clumped distribution of seedlings as readily as sunfleck distribution. The presence of cone-bearing trees throughout the south exposure and of seedlings of different ages within the aggregations suggest that irregularities of dispersal are not responsible for the observed seedling distributions. The close spatial proximity between areas where seedlings are present and absent and the lack of apparent differences in physical soil characteristics indicate that topographic or edaphic factors do not account for the differences in seedling abundance.

Limited data suggest that aggregation of seedlings is the result of differential germination and seedling survival. In 1982 it appeared that germination ceased earlier and rates of mortality were higher on plots on the south exposures with few seedlings, but because seed germination was extremely low, we could not demonstrate that these differences were statistically significant. However, a study by Selter (1983) on A. magnifica shastensis (Shasta fir) on similarly paired plots in the North Coast Range of California showed significantly later cessation of germination, higher germination, and higher survival on plots with lower irradiance. Selter predicted from differential rates of seedling mortality, that by the end of the growing season seedling survival would be three times higher on the high-density plots than on the low-density plots.

In contrast to the situation on the south slopes, the results of our second-year study indicate that aggregations of red fir seedlings are not correlated with sunfleck distribution on north exposures. North exposures often had high seedling densities under canopies as open as those of the plots with few seedlings on the south-facing slope. However, these differences in seedling densities are consistent with the lower total direct-beam irradiance on the north aspect.

Possible mechanisms for the observed relationship may be envisioned in terms of the direct effects of sunflecks on plant physiological response through their influence on energy balance and water relations, and on photosynthesis and respiration (Rackham 1975). Recently, Young and Smith (1979, 1980, Smith 1981) found that stomata! response, transpiration, leaf temperatures, and lower xylem water potentials were closely coupled to changes in irradiance in several understory species. They related differences between the understory herb species Arnica cordifolia and A. latifolia in withstanding water stress, to the latter's distribution in microhabitats where intensity, duration, and frequency of sunflecks were lower. While our study provides no direct evidence for these effects, Gordon (1970) reported that shading increased survival in I st and 2nd-yr red fir seedlings, and Nobel and Alexander (1977) presented experimental evidence that shade improved seedling establishment in Picea engelmannii on the north aspect and was essential on south exposures.

Our results show that a significantly larger portion of total PPFD received on south-aspect plots without seedlings is of high irradiance. This is particularly pronounced during morning and midday when irradiance would have the most severe effect on water relations through early stomata! closure and consequently lowered carbon gain and increased leaf temperatures. In fact, midday temperatures above, at, and below the soil surface were all significantly higher in plots with few seedlings, indicating higher levels of thermal stress. These differences are expected to have a significant effect on seedling survival. Limited data of S. R. Radosevich (personal communication) suggest that it is not high levels of irradiance per se that reduce seedling survival, but induced drought stress. Additional experiments, particularly on water relations, will be necessary to identify and characterize the mechanisms by which seedling survival and distribution are influenced by the light regime under the forest canopy. Because of the low photosynthetic rates measured and because most surviving seedlings occur in sites where light levels are usually below photosynthetic saturation, it would appear that these seedlings may not maintain a positive net carbon balance, suggesting that low light intensities may also be a factor in seedling mortality. A lower irradiance limit, although not demonstrated, is also necessary.

Acknowledgments

We wish to thank Dr. R. W. Pearcy for his assistance in the quantum sensor design and use of equipment, Dr. S. Radosevich and C. Selter for generously providing their unpublished data, Dr. D. Randall for modifying the solar tracks, M. Hibberd for assistance throughout the study, S. Larson, E. Ustin, and N. Ustin for field assistance, Dr. J. A. Doyle for comments on the manuscript. This study was supported by the University of California at Davis Opportunity Program for Ecological Research (OPER)Fund, through the Institute of Ecology, and by the Intercampus Fund.

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1998, Center for Spatial Technologies and Remote Sensing (CSTARS)
University of California, Davis