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Bryology and Lichenology |
Department of Biological Sciences, Union College, Schenectady, New York 12308 USA
Received for publication September 11, 2003. Accepted for publication April 22, 2004.
| ABSTRACT |
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F/Fm') were monitored. In the field (N = 18, 434 cm diameter cushions), Lr, but not Ld, controlled rates of evaporation due to additional turbulence that reduced size dependence of cushions along the forest floor. However, the duration of positive net carbon gain varied from 1.4 to 4.4 d and was significantly longer in larger diameter cushions. Thus, under field conditions, size-dependent changes in surface-area-to-volume relationships influence the duration of net carbon gain more than differences in water flux and lead to a strong size dependence of water balance and carbon flux.
Key Words: allometry boundary layer bryophyte growth form Leucobryaceae Leucobryum glaucum life form water budget
| INTRODUCTION |
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In lichens, increases in thallus size lead to reduced rates of evaporation, increased water storage, and prolonged periods of net carbon gain under laboratory conditions (Larson, 1984
; Hestmark et al., 1997
; Gauslaa and Solhaug, 1998
). Similar patterns have been shown recently in bryophytes. Zotz et al. (2000)
explored the size dependence of water and carbon budgets in the cushion moss Grimmia pulvinata (Hedw.) Sm. ex Sm. & Sowerby (Grimmiaceae). In their laboratory studies, increased cushion size was associated with lower rates of net photosynthesis on a mass basis. However, rates of evaporation declined and water storage capacity increased in larger cushions, leading to more favorable water balance. A carbon budget model developed from these relationships predicted that larger cushions should experience longer duration of positive carbon gain, and thus, enhanced growth rates. Unfortunately, although they evaluated the size dependence of evaporation rates in controlled conditions, they did not adequately explore this relationship across variation in one of the most important environmental factors that controls water fluxes in bryophytes: wind. Previous studies indicate that variation in wind speed causes between a 0.91 and 1.54 exponential increase in evaporation rates (Proctor, 1980
; Rice et al., 2001
). Thus, the mechanisms that underlie size dependence of water flux and consequently water budgets have not been well characterized. In addition, previous studies of size and wind dependence of water fluxes have been performed under laboratory conditions and there has yet to be an adequate field test of such phenomena for either lichens or bryophytes.
Unlike water flux in vascular plants, which is controlled physiologically by the opening and closing of stomata, water loss from most bryophytes is determined by canopy size and structural properties (i.e., "life form" sensu Mägdefrau, 1982
; Bates, 1998
) that influence the development of boundary layers adjacent to plant surfaces (Proctor, 1980
, 1982
, 2000
; Rice and Schuepp, 1995
; Rice et al., 2001
). Boundary layers can be considered regions of still air that develop adjacent to surfaces due to friction (see Nobel, 1991
; Jones, 1992
; Schuepp, 1993
; Campbell and Norman, 1998
for reviews). Water from leaves must move through boundary layers via molecular diffusion, and in bryophytes the boundary layer presents the major impediment to water loss (Proctor, 1980
). In simple geometric shapes, like those of many vascular plant leaves, but also in spherical plant parts, boundary layer development is related functionally to linear dimensions. In general, as the linear size (i.e., organ diameter) increases, boundary layers thicken and evaporation rates decline by the 0.5 power both for flat (Schuepp, 1993
) and spherical (Nobel, 1974
) plant organs. In studies of bryophytes, this relationship has been assumed to have the same form as that which occurs in flat plates (Proctor, 1980
). The scaling function that relates canopy diameter to water fluxes in bryophytes may not conform to that observed in previous studies. Unlike vascular plant organs that exist within a free air stream, many bryophytes persist on a substrate. Consequently, drag associated with the surface may submerge bryophyte canopies within thickened boundary layers or, alternatively, generate turbulence, both of which would reduce or eliminate the size dependence of water flux.
Fine-scale variation in branch and leaf structure also affects boundary layer properties in bryophyte canopies. Wind-tunnel measurements using 11 species performed by Rice et al. (2001)
demonstrated that variation in the architecture of moss canopies alters boundary layer thickness and leads to differences in evaporation rates. This difference is caused by the generation of turbulence, by enhanced flow-through within canopies, and by increased exchange area in rough canopies, all of which increase mass transport from rough bryophyte surfaces. Overall, variation in surface properties as measured by a surface roughness metric (see below) causes a 0.33 power increase in rates of boundary layer conductance and evaporation.
Differences in canopy size will also affect water storage. Many bryophytes store water within external capillary spaces, in specialized hyaline cells and/or in decaying organic matter formed following tissue senescence. Within a given anatomical and structural type, differences in plant volume relate directly to variation in water holding capacity, and surface area-to-volume ratio (SA : V) characterizes the exchange area relative to storage capacity. When there are no allometric changes with increased size, water storage should increase to the third power of increases in canopy diameter and SA : V will scale to the power of 1 (Niklas, 1994
). However, changes in canopy shape or leaf area ratio (leaf area per projected surface area) could increase or decrease the magnitude of that scaling function.
In this study, we employ a comprehensive approach to investigate the relationships among canopy size, canopy structure, wind, and the interaction between water and carbon balance in the common temperate forest floor moss species Leucobryum glaucum (Hedw.) Ångstr. ex Fries (the white or pin cushion moss; Leucobryaceae). We accomplish this by (1) measuring the size dependence of cushion morphology and relating it to properties that affect plant water budgets; (2) evaluating boundary layer conductance to water vapor of samples that vary in size in a laminar flow wind tunnel; (3) developing a boundary-layer conductance model based on cushion morphological attributes; and (4) evaluating predictions of the model during a 5-d drying course in the field.
| MATERIALS AND METHODS |
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Cushions of L. glaucum ranging from 4 to 34 cm in diameter were collected in a fully hydrated condition from a privately owned mature Tsuga canadensis (L.) Carrière (Pinaceae) forest near Cooperstown, New York, USA (42° 45.880 N, 74° 56.800 W). Discrete cushions across this size range were abundant on the sparsely vegetated forest floor at this site. Plants were removed from the substrate with a sharp knife. Samples for wind tunnel analysis (14 from 4 to 24 cm diameter, collected on 25 July 2002) were returned to the laboratory where they were maintained moist under full spectrum lamps over a 14-h day length. Plants used in the field study (18 from 4 to 34 cm diameter, collected on 6 August 2002) were transported to the field site (1 km distant) and kept moist under a 50% shade cloth on the forest floor for 2 d prior to the start of the field experiment.
Canopy structure
Each plant was assessed for diameter, surface area, volume, surface roughness, and leaf area. The surface roughness (Lr), a measure of the mean distance between high and low portions of the canopy, was derived from canopy depth profiles. A surface contact probe connected to a micromanipulator was used to measure canopy depth to the nearest 0.1 mm at 0.5 cm intervals along a 5 x 5 cm grid. The number of sample points varied from 121 to a minimum of 24 measurements on the smallest canopy. Larger scale shape pattern was removed from these data by performing a nonlinear regression using the formula for a parabola as employed by Hayward and Clymo (1983)
. Residuals from that regression were used in the analysis. The resulting data were used to calculate surface roughness with the semivariance method. In this analysis, surface roughness is measured from the maximal semivariance that characterizes the average of the squared differences between the mean and samples a given distance apart. In this case, the maximal semivariance occurred at <3 cm scale and reflects fine-scale variation in leaf and branch structure. The Lr parameter is calculated as the square-root of twice this value (see Rice et al., 2001
for more details on this method). The semivariance was calculated using VESPER software (Minasny et al., 1999
) with the "linear with sill" algorithm.
Cushion surface area and volume were measured following the method of Zotz et al. (2000)
. Cushions were placed under the contact probe and cushion heights were measured at the central point and at 46 regularly spaced intervals along four radial transects in four principle directions. Each cushion was treated as a series of parts of a cone between two parallel cutting planes. The resulting shape is called a frustum and its surface area and volume were calculated from the formulas presented in Zotz et al. (2000)
. The total cushion surface areas and volumes were calculated as the sum of the frustum surface areas and volumes.
The surface area determined by this method assumes that the surface is flat. Leaf area was estimated for each sample by determining the empirical relationship between leaf area ratio (leaf area : projected surface area) and surface roughness in a subset of 12 samples and using that relationship to estimate leaf area for all cushions. Leaf area ratio was measured by excising a 1.5 x 1.5 cm portion of the canopy with a razor. Brown tissue and stems were removed with a scalpel while viewing under a dissecting microscope. Leaf tissue was dried at 65°C for 24 h and weighed to the nearest 0.1 mg. Leaf area was determined by multiplying leaf mass by specific leaf area (in square centimeter per milligram). This latter quantity was estimated by measuring the surface area of both sides of 60 leaves using a digital camera system equipped with a macro lens (Model VCS-10132, Pixera, Los Gatos, California, USA) and image processing program (Scion Image version 1.62c, Scion, Frederick, Maryland, USA). These leaves were dried and weighed to the nearest 0.01 mg. In L. glaucum, leaf bases are closely overlapping and contribute little to photosynthesis or evaporative area. Consequently, measures of leaf area were reduced by subtracting the fraction of leaf area that is occupied by the leaf base (58%). This was defined by the portion of the leaf from the base to the inflection point along the leaf margin and was measured on 25 leaves.
Boundary layer conductance
Rates of evaporation of water and boundary layer conductance were measured in a laminar flow wind tunnel (Model 402B, Engineering Laboratory Design, Lake City, Minnesota, USA). The working section measured 54 cm in length with a 30.5 x 30.5 cm cross section. Wind speeds ranged from 0.7 to 4.3 m/s and were measured above the sample in the middle of the flow field. Wind speed was assessed using a hot wire anemometer (Model 06-662-73, Control Company, Friendswood, Texas, USA) calibrated with a pitot probe and micromanometer (Dwyer Instruments, Michigan City, Idaho, USA).
Boundary layer conductance to water vapor (ga) was evaluated by measuring evaporation of water. Cushions were sprayed with deionized water, weighed to the nearest 0.01 g, and placed within the wind tunnel. Samples remained inside the wind tunnel at a given wind speed until at least 0.10 g of mass were lost (316 min). The plants were removed and their mass recorded. At each of six wind speeds, evaporation was measured two times with the cushion placed at right angles in the two trials. Means of these values were used in the analyses.
During each trial, the relative humidity and air temperature were measured using probes on a photosynthesis system (see below) placed at the intake of the wind tunnel. Boundary layer conductance to water was calculated using the evaporation rates and environmental data following formulas presented in Jones (1992)
. Both evaporation rates and boundary layer conductance were expressed on a leaf area basis. Surface temperature was obtained by tying two 0.5 mm thermocouples (temperature to the nearest 0.1°C; Physitemp Instruments, Clifton, New Jersey, USA) to branches on the surface of the cushion. Due to the difficulty measuring cushion mass with the thermocouples attached, surface temperatures were measured in separate trials immediately following the evaporation ones.
A boundary layer conductance (ga) model was constructed to relate ga to variation in canopy structure. The model structure was derived from a dimensionless form that uses Sherwood (Sh), Schmidt (Sc) and Reynolds (Re) numbers. The Sh number characterizes conductance (Sh = ga x L x D1, where ga, D, and L represent conductance, diffusivity of water in air, and characteristic length, respectively), Sc is a property of the fluid (Sc = v/D, where v equals the kinematic viscosity of air), Re describes the flow environment (Re = u x L x v1, where u is the wind speed). Under a wide range of conditions, these are related via the following relationship ShSc0.33 = cRen, with c and n representing model parameters (Schuepp, 1993
) that are estimated empirically.
This model requires the designation of a characteristic length (L). For spherical or cylindrical plant organs, the organ diameter has been used as a length scale to model flow and mass transfer. Under conditions when the geometry departs from a true sphere or cylinder, the diameter of the sphere or cylinder that has the same surface area has been employed as a length scale (Nobel, 1974
). We follow this convention and calculate the diameter length (Ld) by multiplying this value by 0.81 to reflect the mean not maximal width in the direction of flow (Campbell and Norman, 1998
). In rough surfaces, the magnitude of the roughness elements also determines boundary layer properties (Raupach et al., 1991
) and correlates with mass transfer from bryophyte canopies (Rice et al., 2001
). We included this in our model by adding surface roughness as a predictor variable. We converted the surface roughness (Lr) to dimensionless form by dividing it by the maximal Lr value in the study. We call this the surface roughness index (Lr-in).
These characteristic lengths may or may not scale with conductance similarly to each other or with changes in wind speed due to the effects of cushion geometry, sheltering, and turbulence generated by substrate roughness (Bandyopadhyay, 1987
; Raupach et al., 1991
; Krogstad and Antonia, 1999
; also see Gurevitch and Schuepp, 1990
for discussion as applied to plants). Therefore, to allow these to influence boundary layer properties independently, we have factored them out of the Re number and assigned them individual scaling exponents. Thus, the complete mass transfer model is represented by ShSc0.33 = c x (u/v)n x Ldn' x Lr-inn'', where the Sh number employs Ld as a length scale. When this is solved for ga, the model becomes ga = C x (u/v)n x Ld(n'1) x Lr-inn''. The parameter C is the product of the constants D, Sc0.33, and the variable c. The exponents n, n' 1, and n'' and the C parameter were estimated by performing a multiple linear regression following log transformation. Given that each of the 14 samples was evaluated across a range of six wind speeds, sample points in this analysis were not independent and confidence intervals derived using parametric statistics would not be appropriate. Thus, the significance of the exponents and their 95% confidence intervals were calculated using bootstrap analysis on 1000 resampled data sets using SIMSTAT software (Provalis Research, Montreal, Quebec, Canada).
Physiological characteristics
Chlorophyll fluorescence parameters were compared to rates of net photosynthesis and dark respiration during drying at a range of temperatures under laboratory conditions; the resulting relationships were used to estimate physiological states in the field. Twelve 78 cm diameter cushions were collected on 1 September 2002 and maintained hydrated under 100 µmol · m2 · s1 light from full spectrum lamps over a 14-h day length. Beginning on 5 September, net photosynthesis and dark respiration were measured using a closed-chamber photosynthesis system (LI-COR 6200, LI-COR, Lincoln, Nebraska, USA) connected to a 1.1-L chamber enclosed within a circulating water bath constructed for the purpose. Net photosynthesis was measured as net CO2 uptake expressed on a leaf area basis during 40-s measurement intervals where CO2 concentrations changed between 0 and 15 ppm. Initial CO2 level within the chamber was 380 ppm and relative humidity values ranged from 75 to 90%, with lower values present in dehydrated samples. Measurements were performed at a light intensity of 220 µmol · m2 · s1 provided by a 50-W halogen source filtered through 2 cm of water. Between measurements, plants were maintained under similar light conditions at the measurement temperature. This light intensity is within the range of common light in the natural environment and provided 75% of maximal rates of photosynthesis determined from four additional samples over a range of light intensities from 20 to 900 µmol · m2 · s1. Cushions were exposed to wind from a fan to facilitate drying; drying from a fully hydrated state to negligible net photosynthetic rates took between 29 and 36 h. Two groups of four samples were used to characterize photosynthesis across a range of temperatures that occurred in the field. During measurements, surface temperatures ranged from 20° to 24°C in the first group and from 25° to 29°C in the second. Higher temperatures occurred with dry samples in each group, a pattern also evident in the field. Rates of dark respiration were measured over 4080 s intervals at similar temperatures periodically during the course of the drying cycle.
Parameters derived from chlorophyll fluorescence measurements correlate with rates of photosynthesis and photosynthetic capacity. The effective quantum yield (
PSII) can be estimated under ambient light conditions by measuring the ratio of the additional fluorescence yield achieved above the steady state value relative to the maximal yield (
PSII =
F/Fm'; Genty et al., 1989
; Maxwell and Johnson, 2000
). Variation in
F/Fm' relates to differences in net photosynthesis in bryophytes (Tuba et al., 1997
; Csintalan et al., 1999
; Marschall and Proctor, 1999
). This parameter was measured using a 5.5-mm fiber optic probe interfaced with a modulated fluorometer (MINI-PAM Fluorometer, Walz, Effeltrich, Germany) at three sample points on each cushion following each photosynthesis measurement. The probe, conducting saturating pulses, measuring and actinic light, was held 1.2 cm from the surface at a 60° angle using a standard leaf clip. Light intensity was the same as occurred during photosynthesis (220 µmol · m2 · s1) and was evaluated at the plant surface.
Field water and net CO2 exchange
Predictions of the boundary layer conductance model on evaporation and on the duration of positive net carbon gain were evaluated in a field experiment. The field site was 1 km from the collecting site and within a young Acer rubrum L. (Aceraceae) stand adjacent to Muskrat Pond, Otsego County, New York, USA. Leucobryum glaucum was present at the site, but was not abundant enough across a range of canopy sizes to provide samples for the study. Rates of evaporation were assessed during a 5-d drying course on 18 cushions that varied in diameter between 4 and 34 cm. Cushions were set on flat plastic trays on a raked carpet of commercial pine bark mulch (5.1 x 2.9 x 1.8 cm mean dimensions) within an open area of the forest floor. Plants were at least 3 m from the nearest tree bole and were distributed evenly around two concentric circles. Twelve cushions were placed in the outer circle and six in the inner one. Cushions were all at least 1 m apart, and locations were rearranged arbitrarily at each sampling time.
Air temperature, relative humidity, and wind speed were measured 30 cm above the forest floor and 60 cm from the outer circle using a weather station connected to a data logger (RM Young Wind Sentry with a cup-type anemometer, interfaced with a CR10X Datalogger, Campbell Scientific, Logan, Utah, USA). Surface temperature was measured using two temperature probes placed in a hydrated L. glaucum cushion near the weather station. This cushion was comparable in size to the largest cushion in the sample. Environmental data were sampled at 2-min intervals and represent averages taken at 10-s periods over the course of each interval.
Plants were collected moist and kept hydrated at the field site under a shade cloth for 1 d prior to the start of the experiment. Beginning at 0600 the first day and at approximately 90-min intervals throughout each day, samples were weighed to the nearest 0.1 g to assess rates of evaporation.
Initially, plants were assessed for the Fv/Fm fluorescence parameter following dark adaptation, which correlates well with photosynthetic capacity (Tuba et al., 1997
; Csintalan et al., 1999
; Maxwell and Johnson, 2000
). This was accomplished by performing measurements on cushions at night at the beginning of the experiment. Three Fv/Fm measurements (instrument described above) were performed within the middle one-half of each cushion with a minimum of 10 min dark adaptation between measurements. During the remainder of the field experiment,
F/Fm' was measured. This was preferred because it does not require dark adaptation and correlates well with photosynthetic performance under particular light and temperature regimes. This parameter was measured at 0900 the following morning and again at 1600 and continued for 5 d. On the last day, only the 1600 measurement was obtained. The
F/Fm' parameter was measured on three evenly spaced sample points within the top one-half of each cushion. Surface temperature and light intensity were recorded using a leaf clip attachment to the fluorometer (model 2060B, Walz). Light intensity for the measurements was maintained at 220 µmol · m2 · s1 using a 50-W halogen light dispersed through a diffuser. Measurements were collected within a covered shelter to control light intensity. In addition, at the fluorescence sampling times and at approximately 90-min intervals throughout each day, samples were weighed to the nearest 0.1 g to assess water status and rates of evaporation.
The boundary layer conductance model makes predictions about the size dependence of evaporation in the field. The degree of size dependence during each sampling interval in the field was evaluated by relating Ld and Lr to rates of evaporation using multiple linear regression for each day and night interval during the study.
| RESULTS |
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Rates of dark respiration decreased during drying and were elevated at higher temperatures. At maximal water contents, rates varied between a maximum of 0.33 and 0.58 µmol CO2 · m2 · s1 at 22° and 27°C, respectively. These declined to 0.08 and 0.17 µmol CO2 · m2 · s1 at 22° and 27°C when water content was 2 g H2O/g dry plant, the water content at which rates of net CO2 exchange were zero.
The effective quantum yield assessed using chlorophyll fluorescence (
F/Fm') was nonlinearly related to rates of net CO2 exchange during cushion drying (Fig. 3). At maximum rates of photosynthesis,
F/Fm' averaged 0.570 and did not vary with temperature. This value of
F/Fm' was maintained as rates of net CO2 exchange dropped to 40% of their maximum value and then declined linearly. At low rates of net CO2 exchange, higher temperatures showed elevated
F/Fm', a trend that corresponded with higher rates of dark respiration at those temperatures.
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F/Fm' also showed no size dependency (0.401 mean and 0.068 SD; R2 = 0.02, P = 0.61). However as cushions lost water during the experiment,
F/Fm' remained nearly constant or increased before declining as tissues desiccated (Fig. 5). The length of the photosynthetically active phase varied as a function of Ld. For example, the length of time during which plants went from maximal to 10% of maximal rates of net CO2 exchange assessed using
F/Fm' values (
F/Fm' < 0.2, Fig. 3) was closely associated with cushion diameter (Fig. 6). This corresponded well with differences in hydration status expressed on a water content basis (Fig. 7).
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F/Fm' > 0.2) were used. Mean rates of evaporation calculated for all cushions were higher by a factor of three during the daytimes. The relationship between evaporation rates and the predictor variables Ld and Lr were evaluated using multiple linear regression following log transformation. For all daytime sample intervals when wind speeds were high, variation in Ld was not significantly associated with rates of evaporation (Table 1). However, during the three daytime intervals that have a sample size of at least 14, Lr was significantly and negatively associated with evaporation rates. During the fourth interval, the slope of the relationship was similar, but with only seven samples, the slope was not significant. At night, one interval showed a positive association between evaporation rate and Ld and two out of the three intervals showed an indirect relationship between Lr and rate of evaporation.
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| DISCUSSION |
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Variation in both Ld and Lr also influenced ga in the wind tunnel. Increases in Ld were associated with a 0.35 exponential decrease in ga, which was significantly closer to zero than the value observed in flat or spherical plant organs within free airstreams (0.5; Nobel, 1974
; Schuepp, 1993
). The reduced magnitude of size dependence in the present study is probably also caused by turbulence associated with the wind-tunnel wall and amplified by the roughness of the L. glaucum surface. Such a reduction in size dependence has not been observed in the smoother canopied moss G. pulvinata. In that species, samples of 3 cm diameter remain within the laminar sublayer for wind speeds from 0.2 to 4 m/s (Proctor, 1980
). Consequently, that species has a magnitude of size dependence of evaporation rates similar to organs in free airstreams, at least for small cushions between 0.5 and 4.0 cm diameter (Zotz et al., 2000
; measured only at approximately 1.2 m/s wind speed). In the rougher canopied L. glaucum, size dependence is reduced as the scale of the roughness elements approaches the thickness of the boundary layer and generates transitionally rough flow. Within these flow regimes, variation in surface roughness becomes more important in determining boundary layer properties and, thus ga, than variation in size (Raupach et al., 1991
).
Indeed, boundary layer conductance was inversely related to variation in surface roughness. Within bryophyte canopies, surface roughness elements are known to interact with wind flow generating turbulence, facilitating through-flow and enhancing conductance to water loss (Rice et al., 2001
). However, in the present study increases in surface roughness caused a reduction, not an increase, in ga. The low value and range of surface roughness in the present study may account for this difference. All L. glaucum cushions in the present study were smoother than those in the Rice et al. (2001)
analysis (1.0 2.0 mm vs. 2.111.8 mm). When densely packed, plant leaves and branches cause sheltering and reduce mass transfer (Gurevitch and Schuepp, 1990
; Rice and Schuepp, 1995
). Although surface roughness at the scale found in L. glaucum appears to generate transitionally rough flow, increases in roughness may extend the laminar sublayer above the branch tips. This would create dormant air spaces within the canopy and increase mean diffusional pathlengths, thereby reducing overall rates of evaporation. In this manner, leaf tips would function similarly to hair points on leaves of G. pulvinata and Tortula ruralis (Hedw.) Gaertn., Meyer & Scherb. (Pottiaceae), which have been shown to decrease boundary layer conductance (Proctor, 1980
). Thus, at the scale of bryophyte canopies, there may be a critical roughness height that determines whether increases in roughness enhance or inhibit water loss.
In contrast to the dependence of ga on Ld and Lr in the wind-tunnel, in the field, rates of evaporation during the windy daytimes were affected only by variation in Lr. This result is further supported when evaporation periods within each day were analyzed separately (results not shown). The lack of size-dependent evaporation rate is likely caused by the additional turbulence encountered in the field. Together with turbulent eddies that propagate through forest canopies (Baldocchi and Meyers, 1988
; Raupach et al., 1996
), length scales associated with the forest floor and its surface roughness also generate turbulence. For example, the mulch on the forest floor has a mean roughness height at least an order of magnitude greater than the L. glaucum cushions (18 vs. 12 mm, assuming the former is the mean minimum mulch dimension). This magnitude of roughness would lead to a change from transitionally rough flow regime found in the wind tunnel to fully rough flow along the forest floor (Bandyopadhyay, 1987
). Under these conditions, boundary layer properties are determined principally by the geometry and density of roughness elements and not by other length scales (Rapauch et al., 1991
). Consequently, the size-dependent effects on evaporation that have been described in bryophytes and in lichens based on laboratory or wind tunnel investigations may not adequately predict water fluxes under field conditions. We encourage investigators to evaluate the range of turbulence intensities in the field and then condition flows in the laboratory to suitably match them.
This result suggests that under field conditions, surface roughness may be the best singular parameter to characterize differences in bryophyte water fluxes. In addition, differences in stem density and in the organization of bryophyte canopies that relate to light interception, photosynthesis and growth may also be well characterized by this parameter (van der Hoeven et al., 1993
; Hanslin et al., 2001
; Pederson et al., 2001
). Given that bryophytes can account for up to 50% of gross photosynthesis and influence ecosystem hydrological budgets in many boreal systems (Van Cleve et al., 1983
; Goulden and Crill, 1997
; Bisbee et al., 2001
), it is essential to be able to characterize functional differences of bryophyte species. Now that surface roughness can be easily determined using remote techniques employing laser scanning (S. Rice and N. Kroulicoff, Union College, unpublished data), it may allow for the development and testing of mechanistic models of bryophyte function that relate to underlying variation in their life form.
Also, the shape of L. glaucum cushions changes with increase in size and affects water budgets. Canopy height does not increase isometrically with diameter as cushions flatten and become less hemispherical as they grow, similar to the phenomenon observed in Grimmia pulvinata (Zotz et al., 2000
). Under conditions where no allometric change occurs, surface area and volume are expected to scale to the second and third power of changes in cushion diameter. Because surface area represents the site of water loss from cushion surfaces and the volume serves as a water reservoir in cushion mosses, changes in the surface area : volume ratio (SA : V) will alter water budgets and the length of positive carbon uptake. In a hemisphere, increases in size cause a decrease in SA : V to the 1 power of canopy diameter. However, when leaf area (LA) is considered the LA : V ratio scales with diameter to the 0.84 power in L. glaucum (Fig. 1d). This relationship indicates that allometric changes associated with canopy growth increase canopy LA : V ratio relative to isomorphic growth that would result in hemispherical cushions. However, even though L. glaucum cushions do not decrease SA : V ratios as dramatically as hemispheres as they enlarge, larger cushions still show increased volume for water storage relative to small ones. This causes the extreme size dependence observed in the duration of favorable water status.
Consequently, the length of net carbon gain, assessed either by water loss or by chlorophyll fluorescence characteristics increased from 1.4 to 4.4 d in the smallest to the largest cushions in the sample even with no observed size-dependent differences in evaporation rate. A similar pattern is predicted for the cushion moss Grimmia pulvinata based on laboratory investigations of water and carbon balance (Zotz et al., 2000
). However, this is the first attempt to verify these predictions in the field. Reduced lengths of favorable water status in small cushions suggests that such individuals may experience more prolonged or intense dehydration which may increase mortality in the only moderately desiccation tolerant L. glaucum (Takacs et al., 1999
). Furthermore, slow growth and high mortality would inhibit establishment, the phase that likely limits the ecological distribution of L. glaucum (McAlister, 1995
) as it does in Grimmia laevigata (Brid.) Brid. (Grimmiaceae), another cushion moss (Alpert, 1988
).
In summary, surface roughness associated with bryophyte canopies and their substrates creates inherently turbulent flow conditions that affect the wind and size dependence of water fluxes. This was observed in wind-tunnel environments where transitionally rough flow regimes caused more dramatic wind dependence than has been shown in smooth cushioned mosses and in plant organs in free air streams. In the field, fully rough flows are likely to develop that eliminate the relationship between cushion size and evaporation. In contrast, variation in cushion surface roughness controls water fluxes in the field. In smooth cushions like those in L. glaucum, increases in surface roughness cause a decrease in boundary layer conductance. However, the duration of net carbon gain is more closely related to cushion size than to surface roughness due to a strong positive relationship between canopy size and the volume of tissue available for water storage. Consequently, even though water fluxes are not size dependent in the cushion moss L. glaucum in the field, there remains a strong size dependency in water balance and net carbon flux.
| FOOTNOTES |
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| LITERATURE CITED |
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Bandyopadhyay P. R. 1987 Rough-wall turbulent boundary layers in the transition regime. Journal of Fluid Mechanics 180: 231-266[CrossRef][ISI]
Baldocchi D. D. T. P. Meyers 1988 Turbulence structure in a deciduous forest. Boundary-Layer Meteorology 43: 345-364
Bates J. W. 1998 Is "life-form" a useful concept in bryophyte ecology?. Oikos 82: 223-237[CrossRef][ISI]
Bisbee K. E. S. T. Gower J. M. Norman E. V. Nordheim 2001 Environmental controls on ground cover species composition and productivity in a boreal black spruce forest. Oecologia 129: 261-270[CrossRef][ISI]
Bonser S. P. L. W. Aarssen 2003 Allometry and development in herbaceous plants: functional responses of meristem allocation to light and nutrient availability. American Journal of Botany 90: 404-412
Campbell G. S. J. M. Norman 1998 An introduction to environmental biophysics, 2nd ed. Springer-Verlag, New York, New York, USA
Crum H. A. L. E. Anderson 1981 Mosses of eastern North America. Columbia University Press, New York, New York, USA
Csintalan Z. M. C. F. Proctor Z. Tuba 1999 Chlorophyll fluorescence during drying and rehydration in the mosses Rhytidiadelphus loreus (Hew.) Warnst., Anomodon viticulosus (Hedw.) Hook & Tayl. and Grimmia pulvinata (Hedw.) Sm. Annals of Botany 84: 235-244
de Soyza A. G. A. C. Franco R. A. Virginia J. F. Reynolds W. G. Whitford 1996 Effects of plant size on photosynthesis and water relations in the desert shrub Prosopis glandulosa (Fabaceae). American Journal of Botany 83: 99-105[CrossRef][ISI]
Dilks T. J. K. M. C. F. Proctor 1979 Photosynthesis, respiration and water content in bryophytes. New Phytologist 82: 97-114[CrossRef][ISI]
Donovan L. A. J. R. Ehleringer 1992 Contrasting water-use patterns among size and life-history classes of a semi-arid shrub. Functional Ecology 6: 482-488[CrossRef][ISI]
Gauslaa Y. K. A. Solhaug 1998 The significance of thallus size for the water economy of the cyanobacterial old-forest lichen Degelia plumbea. Oecologia 116: 76-84[CrossRef][ISI]
Genty B. J. M. Briantais N. R. Baker 1989 The relationship between quantum yield of photosynthetic electron transport and quenching of chlorophyll fluorescence. Biochimica et Biophysica Acta 990: 87-92[ISI]
Goulden M. L. P. M. Crill 1997 Automated measurements of CO2 exchange at the moss surface of a black spruce forest. Tree Physiology 17: 537-542[ISI][Medline]
Gurevitch J. P. H. Schuepp 1990 Boundary layer properties of highly dissected leaves: an investigation using an electrochemical fluid tunnel. Plant, Cell and Environment 13: 783-792[CrossRef]
Hanslin H. M. S. Bakken B. Pedersen 2001 The impact of watering regime and ambient relative humidity on the effect of density on growth in two boreal forest mosses, Dicranum majus and Rhytidiadelphus loreus. Journal of Bryology 23: 43-54
Hayward P. M. R. S. Clymo 1983 The growth of Sphagnum: experiments on, and simulation of, some effects of light flux and water-table depth. Journal of Ecology 71: 845-863[CrossRef]
Hestmark G. B. Schroeter L. Kappen 1997 Intrathalline and size-dependent patterns of activity in Lasallia pustulata and their possible consequences for competitive interactions. Functional Ecology 11: 318-322[CrossRef][ISI]
Jones H. G. 1992 Plants and microclimate, 2nd ed. Cambridge University Press, Cambridge, UK
Krogstad P.-Å. R. A. Antonia 1999 Surface roughness effects in turbulent boundary layers. Experiments in Fluids 27: 450-460[CrossRef][ISI]
Larson D. W. 1984 Thallus size as a complicating factor in the physiological ecology of lichens. New Phytologist 97: 87-97[CrossRef][ISI]
Mägdefrau K. 1982 Life-forms of bryophytes. In A. J. E. Smith [ed.], Bryophyte ecology, 4558. Chapman and Hall, London, UK
Marschall M. M. C. F. Proctor 1999 Desiccation tolerance and recovery of the leafy liverwort Porella platyphylla (L.) Pfeiff.: chlorophyll-fluorescence measurements. Journal of Bryology 21: 257-262
Maxwell K. G. N. Johnson 2000 Chlorophyll fluorescencea practical guide. Journal of Experimental Botany 51: 659-668
McAlister S. 1995 Species interactions and substrate specificity among log-inhabiting bryophyte species. Ecology 76: 2184-2195[CrossRef][ISI]
Minasny B. A. B. McBratney B. M. Whelan 1999 VESPER version 1.0. Australian Centre for Precision Agriculture, University of Sydney, New South Wales, Australia
Niklas K. J. 1994 Plant allometry: the scaling of form and process. University of Chicago Press, Chicago, Illinois, USA
Nobel P. S. 1974 Effective thickness and resistance of the air boundary layer adjacent to spherical plant parts. Journal of Experimental Botany 26: 120-130[CrossRef][ISI]
Nobel P. S. 1991 Physiochemical and environmental plant physiology. Academic Press, New York, New York, USA
Pedersen B. H. M. Hanslin S. Bakken 2001 Testing for positive density-dependent performance in four bryophyte species. Ecology 82: 70-88[CrossRef][ISI]
Proctor M. C. F. 1980 Diffusion resistance in bryophytes. In J. Grace, E. D. Ford, and P. G. Jarvis [eds.], Plants and their atmospheric environment, 219229. Blackwell Scientific, Oxford, UK
Proctor M. C. F. 1982 Physiological ecology: water relations, light and temperature responses, carbon balance. In A. J. E. Smith [ed.], Bryophyte ecology, 333382. Chapman and Hall, London, UK
Proctor M. C. F. 1990 The physiological basis of bryophyte production. Botanical Journal of the Linnean Society 104: 61-77
Proctor M. C. F. 2000 Physiological ecology. In A. J. Shaw and B. Goffinet [eds.], Bryophyte biology, 225247. Cambridge University Press, Cambridge, UK
Raupach M. R. R. A. Antonia S. Rajagopalan 1991 Rough-wall turbulent boundary layers. Applied Mechanics Reviews 44: 1-25
Raupach M. R. J. J. Finnigan Y. Brunet 1996 Coherent eddies and turbulence in vegetation canopies: the mixing layer analogy. Boundary-Layer Meteorology 78: 351-382
Rice S. K. D. Collins A. M. Anderson 2001 Functional significance of variation in bryophyte canopy structure. American Journal of Botany 88: 1568-1576
Rice S. K. P. H. Schuepp 1995 On the ecological and evolutionary significance of branch and leaf morphology in aquatic Sphagnum. American Journal of Botany 82: 833-846[CrossRef][ISI]
Schuepp P. H. 1993 Leaf boundary layers. New Phytologist 125: 477-507[CrossRef][ISI]
Skre O. W. C. Oechel 1981 Moss functioning in different taiga ecosystems in interior Alaska I. Seasonal, phenotypic, and drought effects on photosynthesis and response patterns. Oecologia 48: 50-59[CrossRef][ISI]
Sveinbjornsson B. W. C. Oechel 1992 Controls on growth and productivity of bryophytes: environmental limitations under current and anticipated conditions. In J. W. Bates and A. M. Farmer [eds.], Bryophytes and lichens in a changing environment, 77102. Clarendon Press, Oxford, UK
Takacs Z. Z. Csintalan L. Sass E. Laitat I. Vass Z. Tuba 1999 UV-B tolerance of bryophyte species with different degrees of desiccation tolerance. Journal of Photochemistry and Photobiology 48: 210-215[CrossRef]
Tuba Z. Z. Csintalan A. Badacsonyi M. C. F. Proctor 1997 Chlorophyll fluorescence as an exploratory tool for ecophysiological studies on mosses and other small poikilohydric plants. Journal of Bryology 19: 401-407
Tuba Z. M. C. F. Proctor Z. Csintalan 1998 Ecophysiological responses of homochlorophyllous and poikilochlorophyllous desiccation tolerant plants: a comparison and an ecological perspective. Plant Growth Regulation 24: 211-217
Van Cleve K. L. K. Oliver P. Schlentener L. A. Viereck C. T. Dyrness 1983 Productivity and nutrient cycling in taiga forest ecosystems. Canadian Journal of Forest Research 13: 703-720[CrossRef]
van der Hoeven E. C. C. I. J. Huynen H. J. During 1993 Vertical profiles of biomass, light intercepting area and light intensity in chalk grassland mosses. Journal of the Hattori Botanical Laboratory 74: 261-270
Zotz G. 2000 Size-related intraspecific variability in physiological traits of vascular epiphytes and its importance for plant physiological ecology. Perspectives in Plant Ecology, Evolution and Systematics 3: 19-28
Zotz G. S. Rottenberger 2001 Seasonal changes in diel CO2 exchange of three central European moss species: a one-year field study. Plant Biology 3: 661-669[CrossRef][ISI]
Zotz G. A. Schweikert W. Jetz H. Westerman 2000 Water relations and carbon gain are closely related to cushion size in the moss Grimmia pulvinata. New Phytologist 148: 59-67[CrossRef][ISI]
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