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2 Environmental Sciences Program, Oregon State University, Corvallis, Oregon 97331 USA; and 3 Department of Forest Resources, University of Idaho, Moscow, Idaho 83844 USA
Received for publication September 3, 1998. Accepted for publication July 9, 1999.
ABSTRACT
We measured carbon (respiration, photosynthesis, and production) and nitrogen allocation to male and female cones of Rocky Mountain Douglas-fir (Pseudotsuga menziesii var. glauca) to quantify gender-specific: (1) resource allocation to reproduction, and (2) contribution to carbon costs of reproduction via photosynthesis. We also measured foliar photosynthesis and nitrogen concentration ([N]) near and far from female cones to examine the relationship between reproduction and foliar physiology. Over one growing season, male cones required only 8% of all carbon allocated to reproduction, with females consuming the remaining 92%. Female cones, however, had maximum instantaneous refixation rates of 54%, which, integrated over the season, offset 6% of their total carbon requirements, while male cones were completely dependent on vegetative tissues for carbon. Male cones received 22% of all nitrogen allocated to reproduction and female cones received the remaining 78%. Foliage near female cones had elevated photosynthesis during the early stages of cone development and consistently lower [N] than foliage far from cones. Although female cones may photosynthesize, the annual sum of carbon fixed by reproductive structures is minor in comparison to the total carbon allocated to production and respiration.
Key Words: carbon gender nitrogen photosynthesis Pinaceae Pseudotsuga menziesii resource allocation respiration
The carbon costs of reproduction of many herbaceous, woody, and crop plants is partially offset by photosynthesis of the reproductive tissues (Bazzaz, Carlson, and Harper, 1979
; Linder and Troeng, 1981
; Werk and Ehleringer, 1983
; Jurik, 1985
; Williams, Koch, and Mooney, 1985
; Koppel, Troeng, and Linder, 1987
; Reekie and Bazzaz, 1987a, b
; Dick, Smith, and Jarvis, 1990
; Whiley, Schaffer, and Lara, 1992
; Galen, Dawson, and Stanton, 1993
; Ogawa et al., 1995
; Ogawa and Takano, 1997
). This photosynthetic capacity is important for understanding carbon allocation among male, female, and vegetative tissues.
Reproductive allocation theory assumes that the availability of plant resources, such as carbon or nitrogen, is fixed and that a trade-off exists between allocating resources to male vs. female tissues (reviewed in Charnov, 1982
; Goldman and Willson, 1986
; Charlesworth and Charlesworth, 1987
; Charlesworth and Morgan, 1991
). Both theoretical and quantitative research have concluded that female reproduction is generally more carbon-demanding than male (Goldman and Willson, 1986
; Ashman, 1992
). This conclusion is based on the greater biomass of female reproductive tissues, including the seeds and fruit, relative to that of males. However, resource allocation is an active process and biomass reflects a state at one point within that process. When resource allocation to reproduction is considered a process, it becomes informative to include measurements of both carbon loss by respiration and carbon gain by photosynthesis of the reproductive tissues. In many native and crop species, female organs photosynthesize, thus contributing to their own carbon needs, while male structures are usually nonphotosynthetic, so their carbon demands are met entirely by vegetative tissues (Galen, Dawson, and Stanton, 1993
; Eckhart and Chapin, 1997
).
In addition to supplying carbon to a plant's resource pool, reproductive organs also act as carbon and nutrient sinks. The strong carbon sink of developing fruits increases photosynthetic rates of neighboring foliage in herbaceous and crop species, thus increasing total available carbon (de Jong, 1986
; Reekie and Bazzaz, 1987a
; Bazzaz and Ackerly, 1992
). Such an increase in carbon availability opposes the assumption that resource availability is fixed. However, reproductive tissues are also sinks for nitrogen from neighboring foliage (Chapin, 1989
; Ashman, 1994
). Nitrogen concentration ([N]) is usually positively correlated with photosynthetic rates (Field and Mooney, 1986
). Therefore, any depletion of foliar nitrogen due to reproductive nitrogen demand may reduce foliar photosynthesis, confounding the increased photosynthesis associated with a reproductive carbon sink. Therefore, the sink activity of plant reproductive tissues has several counteracting effects on resource allocation within the entire plant.
The integration of photosynthesis and respiration in whole-tree carbon budgets is becoming increasingly common (reviewed in Ryan et al., 1994
, and Sprugel et al., 1995
). However, most carbon budgets assume carbon allocation to reproduction is negligible, despite evidence of high respiratory rates in reproductive tissues. For example, in a review of the genus Pinus, Ryan et al. (1994)
found that female cones commonly had high respiration rates similar to those of fine roots and foliage. Linder and Troeng (1981)
quantified respiration of female cones of Pinus contorta and estimated that the carbon allocated to a single year of female cone production and respiration may equal as much as 1015% of a tree's annual stem wood production and respiration. However, female cone photosynthesis may offset 1631% of these high respiratory costs over the entire growth period of the cones (Linder and Troeng, 1981
; Koppel, Troeng, and Linder, 1987
; Dick, Smith, and Jarvis, 1990
). Few data are available on the costs of male reproduction in coniferous trees, yet they may be a significant carbon investment for the tree due to their large numbers. Although cone respiration may be a large carbon sink, neither it nor cone photosynthesis has been well studied and consequently it is difficult to draw conclusions regarding the magnitude of carbon allocation to reproduction.
We examined the seasonal course of carbon allocation to respiration and growth, nitrogen allocation to growth, and photosynthesis in male and female cones of Rocky Mountain Douglas-fir [Pseudotsuga menziesii var. glauca (Mirb.) Franco]. We used these measurements to: (1) quantify the resource allocation of carbon and nitrogen of each gender, (2) determine the contribution of each gender to the carbon costs via photosynthesis, and (3) examine the relationship between foliar photosynthetic rates and reproductive activity.
MATERIALS AND METHODS
Study species and site
Pseudotsuga menziesii var. glauca is the Rocky Mountain variety of Douglas-fir and is common in low- to mid-elevation forests of the interior western United States and Canada. It is a monoecious tree that produces cones on a 2-yr cycle by initiating reproductive buds in the early summer of one growing season and completing bud emergence, pollination, fertilization, seed development, and dispersal in the following (Owens, 1991
). This study was conducted during the 1997 growing season at two sites within 300 m of each other in a forest near Deary, Idaho (latitude 46°45' N, longitude 116°33' W, elevation 884 m). On nine dates between 3 May and 14 September, samples were collected from at least six of 13 different trees of approximately equal age, height, and light exposure in order to capture the entire course of cone development. Intervals between sampling dates were shorter during early cone development in order to capture the high rates of change of photosynthesis and respiration associated with the rapid growth rates during this period. Capturing this variability would then improve our annual estimates of carbon fluxes from cones. Sampling intervals increased as growth, photosynthesis, and respiration rates stabilized. Trees were ~80 yr-old, 30 m tall, and had fully exposed, south-facing canopies with crowns extending the full height of the trees. We collected 26 samples per tree for each type of needle and cone.
Field measurements
Gas exchange measurements were made with the LI-6200 Portable Photosynthesis System (LI-COR Instruments, Lincoln, Nebraska, USA). Measurements were made between 0900 and 1400 local time to insure full sunlight exposure on the south-facing sites. Samples were cut from the trees and measurements begun within 1 min. Cones and needles were randomly selected from throughout the canopy between 1.5 and 11.5 m above the ground.
Male cones were sampled on the first three sampling dates (3 May, 11 May, and 18 May), after which they senesced. Pseudotsuga menziesii male cones develop on a 1-yr-old shoot in clusters of 315 cones between needles. In order to measure gas exchange of the male cones while minimizing handling of the fragile cones and resultant pollen loss, needles were removed from the twig around the cones and the entire shoot was placed in the cuvette for respiration measurement (Rtot). Then, on several samples, the cones were removed from the twig and twig respiration was measured (Rtwig). Linear regression between measured total cone and twig respiration predicted twig respiration for those samples for which only Rtot was measured (N = 30, r2 = 0.83). Cone respiration (Rcone) is the difference between Rtot and Rtwig. An independent sample t test between Rtot measurements made with needles removed immediately prior to placement in the cuvette and Rtot measurements with needles removed several hours prior showed no significant wound respiration on the twigs resulted from needle removal (df = 28, t = -0.41, P = 0.680).
Net respiration of female cones was measured in full sunlight on each of the nine sampling dates. The cones were then shaded for 1 min, and gross respiration (Rcone) was measured. Gross respiration was also measured on some cones after 30 min of shading, and a paired t test showed no significant effect of these shade times on Rcone rates (df = 3, t = 0.125, P = 0.908). Photosynthesis was calculated as the difference between net respiration and Rcone. The temperature response (Q10), or change in respiration with a 10°C change in temperature, was estimated on male and female cones during one diel period on 18 May. Temperature and respiration of male and female cones were measured every 34 h over a temperature range of 14°31°C.
Net photosynthesis of needles was measured in full sunlight. Needles were sampled from 1-yr-old shoots that both did and did not terminate with a female cone. On those shoots with cones, the cone was left attached to the twig, but was not placed in the cuvette with the needles.
Daily maximum and minimum temperatures were measured with a thermometer located ~400 m from the field site. For the dates on which no temperature data were recorded, a regression using nearby weather station temperatures was used to predict field site temperatures.
Laboratory measurements
After field measurements were made, samples were kept frozen until they could be oven dried at 60°C for 24 h and weighed. Rates were then calculated per kilogram dry mass. Carbon and nitrogen concentrations were determined using a LECO 600 CHN analyzer (LECO, Inc., St. Joseph, Michigan, USA). Due to the low mass of individual samples, particularly at early dates, samples (i.e., male cones, female cones, needles) were pooled for each date and ground using a mortar and pestle. Three subsamples of a pooled sample per date were analyzed.
Calculations
Relative growth rates (RGR) were calculated for male and female cones for each sample date using the following equation:
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We normalized all respiration rates to a common temperature of 15°C using the gender-specific Q10 for statistical comparisons and seasonal scaling. The relationship between respiration and temperature was expressed as (Lavigne, 1987
):
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Annual respiration from male and female cones was estimated using gender-specific Q10's and site temperature data with the following equation:
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Seasonal photosynthesis for female cones was calculated by estimating daily photosynthetic rates via linear interpolation between measurement dates. We then assumed that cone photosynthesis was active for 2 h less than total daylength each day based on the light response of the cones (S. McDowell, unpublished data). This estimate of photosynthesis is an upper limit because it assumes no light limitation. However, light limitation for the cones was minimal because of few cloudy days during the measurement period at this site, the well-lit south-facing canopies, and the minimal within-canopy shading of cones due to cone position on branch tips. The annual percentage of cone carbon needs supplied by cone photosynthesis was calculated as the sum of photosynthesis for the season, divided by total cone respiration and production.
We determined the relationship between respiration and [N] for male and female cones via linear regression of the mean respiration rates and [N] from each date. Likewise, mean photosynthetic rates for female cones from each date were regressed against tissue [N] to determine the relationship between female photosynthesis and nitrogen.
All statistical analyses were done with the SYSTAT 5.03 statistical package (Wilkinson, 1992
) with
= 0.05 level of significance.
RESULTS
Male cones
Growth of male cones was rapid, but their lifetimes were short. When they emerged from the bud on 1 May, the cones were purple. They achieved their greatest measured dry mass within 2 d of emergence (Table 1). RGR was not calculated because growth was finished before the second sampling date on 11 May. The cones lost 36% of their dry mass, 67% of their nitrogen content, and 39% of their carbon content by 11 May (Table 1). Male cones senesced and began to fall within 3 wk of budbreak.
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The dry mass of the female cones increased rapidly for the first 2 mo after emergence (Table 2). The dry mass continued to increase until the final sampling date when the cones lost 0.5 g, or 11% of their maximum dry mass, from the previous sampling date. The maximum RGR of 0.10 g·g-1·d-1 was reached on 20 June, after which it continually declined (Table 2). Carbon and nitrogen contents of the cones increased throughout the growing season until a decrease of both on the final sampling date (Table 2).
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The percentage of daytime respiratory carbon costs met by female cone photosynthesis declined during the growth period (Fig. 5). Photosynthesis as a percentage of respiration ranged from a maximum on 18 May (mean ± 1 SE = 54 ± 2.3%) to a low on 22 August (mean ± 1 SE = 30 ± 3.9%) (Fig. 5). Over the entire 136-d growing season, an average female cone respired 0.15 mol C·cone-1·yr-1 and photosynthesized 0.02 mol C·cone-1·yr-1, thus photosynthesis reduced annual respiratory costs by 13%. The production of an average female cone was 0.18 mol C·cone-1·yr-1. Therefore, the total carbon cost of a female cone was 0.33 mol C·cone-1·yr-1, with respiration consuming 46% of the total carbon allocation and dry matter production the remaining 54%. The total cost was reduced to 0.31 mol C·cone-1·yr-1 when cone photosynthesis was included. In other words, 6% of the carbon cost of female reproduction of P. menziesii was covered by cone photosynthesis. Changes in nitrogen concentration of female cones through the year were strongly correlated with both respiration rates (N = 9, r2 = 0.945, P < 0.0001) and photosynthetic rates (N = 9, r2 = 0.988, P < 0.0001) (Fig. 6).
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Resource allocation to cones
Male cones of P. menziesii are completely dependent on vegetative tissues for their carbon and nutrient needs. The life cycle of the male cones of P. menziesii, including emergence from the bud, elongation, and pollen dispersal, was finished in <3 wk. The rapid loss of mass and nitrogen and decrease of Rcone of P. menziesii cones by 11 May, ~10 d after budbreak, was associated with pollen dispersal (S. McDowell, personal observation), confirming that the critical period of development was prior to that date. Although our sampling captured broad patterns of male cone development, it is possible that we missed details of development between 3 and 11 May. Future work with male cone development could benefit from more frequent sampling. Rcone of male P. menziesii cones (14 µmol C·kg-1·sec-1) was higher than that of expanding Pinus contorta male cone buds, which ranged from 6.3 to 9.9 µmol C·kg-1·sec-1 (Dick, Smith, and Jarvis, 1990
). These differences may be in part due to the timing of measurements; ours were made on fully expanded cones while those on Pinus contorta were made while the cones were still in bud (Dick, Smith, and Jarvis, 1990
). While frequent early measurements are important to capture the carbon fluxes from male cones, it is similarly important to make measurements on mature cones. Although male cones did not photosynthesize, their total carbon and nitrogen requirements are relatively minor.
Whereas the life cycle of female P. menziesii cones was longer than that of the male cones, the female cones contributed to their own carbon demands. Photosynthesis, RGR, and Rcone per unit dry mass were at their greatest during the first few weeks of cone development. These results are similar to those from cones of Pinus sylvestris, Picea abies, and Pinus contorta for which photosynthesis, respiration, and growth peaked in early spring at pollination and then declined throughout the growth period (Linder and Troeng, 1981
; Koppel, Troeng, and Linder, 1987
; Dick, Smith, and Jarvis, 1990
). Similar declining trends have been observed in the photosynthetic rates on fruits of flowering plants (Jurik, 1985
; Blanke and Lenz, 1989
; Galen, Dawson, and Stanton, 1993
). Dehydration and loss of stomatal function on the photosynthesizing fruit or flower surface appear to be the common cause for these reduced photosynthetic rates. Further research on the water balance of female cones of P. menziesii may provide more understanding of their declining photosynthetic rates.
Cone carbon balance
The percentage of daytime respired carbon met by female cone photosynthesis decreased over the growth period, from 54% on 18 May to 30% on 22 August. Over the entire growing season, cone photosynthesis reduced the respiration costs of reproduction by only 13%, substantially less than that reported for other conifer species. For Pinus sylvestris, refixation reduced the seasonal respiratory losses of cones by 31% (Linder and Troeng, 1981
). For female cones of Pinus contorta it was estimated that daily respiration was reduced 25% by photosynthesis over the entire year (Dick, Smith, and Jarvis, 1990
). Annual respiratory costs of Picea abies cones were reduced 1617% by cone photosynthesis (Koppel, Troeng, and Linder, 1987
). Although the percentage of annual cone respiratory costs met by cone photosynthesis appears to be variable across species, there is a pattern related to the cone development period. The female cones of both Pinus species, which develop on a 3-yr cycle (according to Owens, 1991
), have higher net refixation, while the cones of Pseudotsuga and Picea, both of which develop on a 2-yr cycle (Owens, 1991
), have lower net refixation rates. Further quantification of the relationship between cone carbon balance and development period may simplify our understanding of carbon allocation to reproduction in conifers.
We estimated the average total carbon cost of reproductive production and respiration of male and female cones for a typical tree at the site. Using binoculars to count cones on representative branches, the numbers of male and female cones per tree were estimated. There were ~50 000 male cones/tree. Total seasonal cone respiration for one male cone equaled 0.19 x 10-3 mol C·cone-1·yr-1, so the respiratory cost of male cones for one tree was ~9 mol C·tree-1·yr-1. The dry matter production of male cones equaled ~40 mol C·tree-1·yr-1. Therefore, the total carbon cost of male reproduction for a single P. menziesii tree was ~50 mol C·tree-1·yr-1. For female cones, there were ~2200 cones/tree. The seasonal respiratory flux of female cones was 0.15 mol C·cone-1·yr-1, or ~320 mol C·tree-1·yr-1. With cone photosynthesis included, this rate was reduced to ~280 mol C·tree-1· yr-1. The production cost of female cones was 390 mol C·tree-1·yr-1. The total carbon cost of female reproduction for P. menziesii using these estimates was 710 mol C·tree-1·yr-1, or 670 mol C·tree-1·yr-1 with photosynthesis included.
We also estimated the carbon costs of reproduction for a typical closed forest stand of Rocky Mountain P. menziesii. Respiration and production of male and female cones were scaled to the stand using an average stem density 0.05 trees/m2 and assuming cone production was limited to the upper 20% of the tree height. We calculated the annual costs as 6.6 mol C·m-2·yr-1 for female cones with photosynthetic contributions included and 0.5 mol C·m-2·yr-1 for male cone carbon costs. The female cone estimate is greater than total carbon allocation to female cones of Picea abies (2.06 mol C·m-2·yr-1; Koppel, Linder, and Troeng, 1987
) and of Pinus sylvestris (1.3 mol C·m-2·yr-1; Linder and Troeng, 1981
), but less than aboveground litter estimates of Rocky Mountain P. menziesii (13 mol C·m-2·yr-1; Gower, Vogt, and Grier, 1992
; 15 mol C·m-2·yr-1; N. McDowell et al., unpublished data).
Effects of reproduction on P. menziesii needles
Although female P. menziesii cones cover some of their own reproductive costs, the remaining carbon and all nutrients must be contributed by the vegetative tissues of the trees. Most evidence suggests that the alternative source of cone carbon is photosynthesis of current needles. The biomass of female cones of coastal P. menziesii is negatively correlated with current-season stem growth, implying that carbon allocated to reproduction decreases available carbon for vegetative growth (Eis, Garman, and Ebell, 1965
; El-Kassaby and Barclay, 1992
). In a study of 14C mobilization in Pinus resinosa, Dickmann and Kozlowski (1970)
found that pollinated cones were the priority sink of current needle photosynthate, even while new needles were expanding.
The period of highest cone RGR and respiration per unit dry mass was associated with accelerated photosynthesis in needles adjacent to developing cones, potentially increasing available carbon (Fig. 7). However, carbon demand per cone (production and respiration per cone) continued to increase without an associated increase in vegetative photosynthesis. Throughout the rest of the growing season, needle photosynthesis showed no relationship with developing cones, in spite of declining photosynthetic rates by the cones. In several plant species, the increasing sink strength of a developing fruit is known to elevate photosynthetic rates (de Jong, 1986
; Reekie and Bazzaz, 1987a, b
). However, in experimental shadings of photosynthetic fruits, vegetative photosynthesis did not increase, but seed number and mass, and thus seed viability, decreased (Hole and Scott, 1981
; Galen, Dawson, and Stanton, 1993
). For these species, the fruit photosynthetic contributions were critical to seed development, even though the fruit photosynthetic rates declined over the growing season like those of the cones. In a study using labeled carbon applied to cones of coastal P. menziesii, 34 times as much 14C-glucose was recovered from seeds as from the cone scales (Ching and Fang, 1963
). Thus, the role of cone photosynthesis may be to cover the costs of seed development rather than assist in the carbon costs of other cone tissues such as scales and bracts.
While the carbon demand by female cones of P. menziesii appeared to affect needles during the early weeks of cone growth, the demand for nitrogen by cones had a season-long effect. Although cone [N] decreased over the season, the nitrogen content of cones increased as the cones gained mass. Additionally, seed [N] increased throughout the season (S. McDowell, unpublished data). The [N] of needles near cones remained lower than that of needles with no nearby cones for the entire growing season. However, no significant effect of foliar nitrogen depletion on foliar photosynthesis was observed. Perhaps the strong stimulation of foliar photosynthesis via cone proximity counteracted the effect of depleted tissue [N].
Conclusions
The results of this study suggest that carbon and nitrogen allocation differ between male and female cones, both in the timing and the amount of allocation. Male cones of P. menziesii require <10% of the carbon and about one-quarter of the nitrogen allocated to reproduction in Rocky Mountain P. menziesii trees at our site, with female cones consuming the remaining carbon and nitrogen. However, male cones are completely dependent on vegetative tissues for their carbon and nitrogen needs. Female cones, on the other hand, partially offset their carbon costs via photosynthesis. They had maximum refixation rates of 54% of their daytime respiration, but this only represents 6% of their total carbon costs for the full growing season. This research also contributes evidence that female cones on conifers with 2-yr reproductive cycles have lower refixation rates than female cones on conifers with 3-yr cycles (Linder and Troeng, 1981
; Koppel, Linder, and Troeng, 1987
; Dick, Smith, and Jarvis, 1990
).
FOOTNOTES
5 Current address: Forest Science Department, Oregon State University, Corvallis, Oregon 97331 USA. ![]()
6 Current address: School of Renewable Natural Resources, University of Arizona, Tucson, Arizona 85721 USA. ![]()
LITERATURE CITED
Ågren, G. I., and B. Axelsson. 1980 Population respiration: a theoretical approach. Ecological Modeling 11: 3954.
Amthor, J. S. 1989 Respiration and crop productivity. Springer, Berlin, Germany.
Ashman, T.-L. 1992 Indirect costs of seed production within and between seasons in a gynodioecious species. Oecologia 92: 266272. [CrossRef][ISI]
. 1994 A dynamic perspective on the physiological cost of reproduction in plants. American Naturalist 144: 300316. [CrossRef][ISI]
Bazzaz, F. A., and D. D. Ackerly. 1992 Reproductive allocation and reproductive effort in plants. In M. Fenner [ed.], Seeds: the ecology of regeneration in plant communities, 126. CAB International, Wallingford, Oxon, UK.
, R. W. Carlson, and J. L. Harper. 1979 Contribution to reproductive effort by photosynthesis of flowers and fruits. Nature 279: 554555. [CrossRef]
Blanke, M. M., and F. Lenz. 1989 Fruit photosynthesis. Plant, Cell, and Environment 12: 3146. [CrossRef]
Chapin, F. S., III. 1989 The cost of tundra plant structures: evaluation of concepts and currencies. American Naturalist 133: 119. [CrossRef][ISI]
Charlesworth, B., and D. Charlesworth. 1987 The effect of investment in attractive structures on allocation to male and female function in plants. Evolution 41: 948968. [CrossRef][ISI]
Charlesworth, D., and M. T. Morgan. 1991 Allocation of resources to sex functions in flowering plants. Philosophical Transactions of the Royal Society of London B 332: 91102.
Charnov, E. L. 1982 The theory of sex allocation. Princeton University Press, Princeton, New Jersey, USA.
Ching, T. M., and S. C. Fang. 1963 Utilization of labeled glucose in developing Douglas-fir seed cones. Plant Physiology 38: 551554.
de Jong, T. M. 1986 Fruit effects on photosynthesis in Prunus persica. Physiologia Plantarum 66: 149153.
Dick, J. M., R. Smith, and P. G. Jarvis. 1990 Respiration rate of male and female cones of Pinus contorta. Trees 4: 142149.
Dickmann, D. I., and T. T. Kozlowski. 1970 Mobilization and incorporation of photoassimilated 14C by growing vegetative and reproductive tissues of Pinus resinosa Ait. trees. Plant Physiology 45: 284288.
Eckhart, V. M., and F. S. Chapin, III. 1987 Nutrient sensitivity of the cost of male function in gynodioecious Phacelia linearis (Hydrophyllaceae). American Journal of Botany 84: 10921098. [Abstract]
Eis, S., E. H. Garman, and L. F. Ebell. 1965 Relation between cone production and diameter increment of Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco), grand fir (Abies grandis (Dougl.) Lindl.), and western white pine (Pinus monticola Dougl.). Canadian Journal of Botany 43: 15531559.
El-Kassaby, Y. A., and H. J. Barclay. 1992 Cost of reproduction in Douglas-fir. Canadian Journal of Botany 70: 14291432.
Field, C. B., and H. A. Mooney. 1986 The photosynthesis-nitrogen relationship in wild plants. In T. J. Givnish [ed.], On the economy of plant form and function, 2555. Cambridge University Press, Cambridge, UK.
Galen, C., T. E. Dawson, and M. L. Stanton. 1993 Carpels as leaves: meeting the carbon cost of reproduction in an alpine buttercup. Oecologia 95: 187193. [CrossRef][ISI]
Goldman, D. A., and M. F. Willson. 1986 Sex allocation in functionally hermaphroditic plants. Botanical Review 52: 157194.
Gower, S. T., K. A. Vogt, and C. C. Grier. 1992 Carbon dynamics of Rocky Mountain Douglas-fir: influence of water and nutrient availability. Ecological Monographs 62: 4365.
Hole, C. C., and P. A. Scott. 1981 The effect of fruit shading on yield in Pisum sativum L. Annals of Botany 48: 827835.
Jurik, T. W. 1985 Differential costs of sexual and vegetative reproduction in wild strawberry populations. Oecologia 66: 394403. [CrossRef][ISI]
Koppel, L., E. Troeng, and S. Linder. 1987 Respiration and photosynthesis in cones of Norway spruce (Picea abies (L.) Karst.). Trees 1: 123128.
Lavigne, M. B. 1987 Stem growth and respiration of young balsam fir trees in thinned and unthinned stands. Tree Physiology 3: 225233.
Linder, S., and E. Troeng. 1981 The seasonal course of respiration and photosynthesis in strobili of Scots pine. Forest Science 27: 267276. [ISI]
Ogawa, K., A. Furukawa, A. Hagihara, A. M. Abdullah, and M. Awang. 1995 In situ CO2 gas-exchange in fruits of a tropical tree, Durio zibethinus Murray. Trees 9: 241246.
, and Y. Takano. 1997 Seasonal courses of CO2 exchange and carbon balance in fruits of Cinnamomum camphora. Tree Physiology 17: 415420.
Owens, J. N. 1991 Measuring growth and development of reproductive structures. In J. P. Lassoie and T. M. Hinckley [eds.], Techniques and approaches in forest tree ecophysiology, 423452. CRC Press, Boca Raton, Florida, USA.
Reekie, E. G., and F. A. Bazzaz. 1987a Reproductive effort in plants. 1. Carbon allocation to reproduction. American Naturalist 129: 876896. [CrossRef][ISI]
, and . 1987b Reproductive effort in plants. 2. Does carbon reflect the allocation of other resources? American Naturalist 129: 897906. [CrossRef][ISI]
Ryan, M. G., S. Linder, J. M. Vose, and R. M. Hubbard. 1994 Dark respiration in pines. Ecological Bulletins 43: 5063.
Sprugel, D. G., M. G. Ryan, J. R. Brooks, K. A. Vogt, and T. A. Martin. 1995 Respiration from the organ level to the stand. In W. K. Smith and T. M. Hinckley [eds.], Resource physiology of conifers; acquisition, allocation and utilization, 255291. Academic Press, San Diego, California, USA.
Werk, K. S., and J. R. Ehleringer. 1983 Photosynthesis by flowers in Encelia farinosa and Encelia californica (Asteraceae). Oecologia 57: 311315. [CrossRef][ISI]
Whiley, A. W., B. Schaffer, and S. P. Lara. 1992 Carbon dioxide exchange of developing avocado (Persea americana Mill.) fruit. Tree Physiology 11: 8594.
Wilkinson, L. 1992 SYSTAT 5.03 for Windows. SYSTAT, Inc., Evanston, Illinois, USA.
Williams, K., G. W. Koch, and H. A. Mooney. 1985 The carbon balance of flowers of Diplaucus aurantiacus (Scrophulariaceae). Oecologia 66: 530535. [CrossRef][ISI]
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