Báo cáo khoa học: "Gas exchange and water relations of 3 sizes of containerized Picea mariana seedlings subjected to atmospheric and edaphic water stress under controlled conditions"
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Nội dung Text: Báo cáo khoa học: "Gas exchange and water relations of 3 sizes of containerized Picea mariana seedlings subjected to atmospheric and edaphic water stress under controlled conditions"
- article Original Gas exchange and water relations of 3 sizes of containerized Picea mariana seedlings subjected to atmospheric and edaphic water stress under controlled conditions JD Stewart PY Bernier 1 Centre de Recherche en Biologie Forestière, Faculté de Foresterie et de Géomatique, Université Laval, Sainte-Foy, Quebec G1K 7P4; 2 Natural Resources Canada, Canadian Forest Service-Quebec Region, PO Box 3800, Sainte-Foy, Quebec G1V 4C7, Canada 12 17 (Received April 1994; accepted August 1994) Summary — Containerized black spruce (Picea mariana [Mill] BSP) seedlings of 3 sizes (heights of 18, 35 and 45 cm) were placed in growth chambers and subjected to conditions of low evaporative (20°C, 60% RH) or high evaporative (30°C, 40% RH) demand, with 3 levels of soil water availability in each environment. The large seedlings had the highest rate of net photosynthesis in the cooler environ- ment, but showed the greatest reduction in net photosynthetic rate in the warmer and drier environment, under conditions of limited water supply. The small seedlings were least affected by the warmer and drier environment in which they maintained photosynthetic rates higher than those of the larger seedlings. The decrease in net photosynthesis experienced by the large seedlings in the warmer and drier environment under conditions of limited water availability was associated with a large decrease in stomatal conductance. However, the maintenance of a high level of intercellular CO concentration 2 suggests that most of the limitations to net photosynthesis were of non-stomatal origin. Water content of the root plug was also reduced by increased seedling size, but the differences were least evident under conditions that produced the largest differences in net photosynthetic rates. These results, obtained under controlled conditions, suggest that after outplanting, large seedlings would experience greater reduc- tion in growth than smaller ones only under conditions of high evaporative demand and low water availability. Picea mariana / polyethylene glycol / net photosynthesis / shoot water potential / stomatal con- ductance * Current address: Department of Renewable Resources, of Alberta, Edmonton, Alberta University T6G 2H1, Canada ** and Correspondence reprints
- Résumé — Échanges gazeux et relations hydriques chez des semis de Picea mariana de 3 tailles différentes cultivés en conteneurs et soumis à différentes conditions de sécheresse atmosphérique et édaphique. Nous avons soumis en chambre de croissance des semis d’épinette noire (Picea mariana [Mill] BSP) de 3 tailles différentes (18, 35 et 45 cm de hauteur) et cultivés en conteneurs, à des conditions de demande évaporative faible (20°C, 60% HR) et élevée (30° C, 40% HR) conjointe- ment à 3 niveaux de disponibilité en eau du sol. Les semis de plus forte taille avaient les taux de pho- tosynthèse nette les plus élevés dans l’environnement frais, mais la plus forte réduction de ce paramètre dans l’environnement plus chaud et sec, sous des conditions de faible disponibilité en eau. Cette forte réduction de photosynthèse nette était associée à une fermeture des stomates. Cependant, le taux élevé de concentration intercellulaire en CO indique que des facteurs non stomatiques étaient principalement 2 à l’origine de cette réduction. Les semis de plus faible taille ont maintenu en conditions chaudes et sèches des taux de photosynthèse nette supérieurs à ceux des semis de plus forte taille. L’accroissement de la taille des semis a réduit la teneur en eau de la motte racinaire, mais principalement sous des condi- tions n’engendrant pas de différences dans les taux de photosynthèse nette entre les tailles de semis. Les résultats obtenus en conditions contrôlées indiquent que la croissance des semis d’épinette noire de plus forte taille serait plus affectée à la suite de la plantation que celle des semis de plus faible taille à condition seulement que la demande évaporative soit forte et la disponibilité en eau faible. Picea mariana / polyéthylène xylème / du glycol / photosynthèse / potentiel hydrique nette conductance stomatique INTRODUCTION not be matched by seedlings may or may increase in the soil water absorption an capacity of the root system. A reduction in One of the problems faced by outplanted the soil water absorption capacity per unit seedlings is competition from other veg- tree leaf area in larger seedlings may result in etation. This problem has often been lower stomatal conductances and lower net addressed by attempting to decrease the assimilation. Negative effects of increased establishment and growth of the unwanted seedling size on survival and growth have species through practices such as burning, been observed with Douglas-fir (Pseudot- cultivation, or herbicide application (eg, suga menziesii [Mirb] Franco) on harsh Stewart, 1987; Wood and Dominy, 1988; planting sites (Hahn and Smith, 1983). Campbell, 1990). Another approach is to increase the competitive ability of the planted In order to anticipate problems with stock by using larger seedlings than is cur- respect to water flux, and the resulting neg- rently the practice. Large planting stock can ative effects seedling water relations and on overtop competing herbaceous or shrubby photosynthesis, we undertook a controlled vegetation faster than small planting stock environment study using containerized black (Overton and Ching, 1978; Newton et al, spruce (Picea mariana [Mill] BSP). The 1993), because of its enhanced ability to seedlings, grown to different sizes in differ- capture light, and in some cases, to over- ent types of containers, were subjected to 2 come browsing damage (Hartwell, 1973, in sets of atmospheric environmental condi- Newton et al, 1993). In climates with sub- tions and 3 levels of soil water availability. stantial snow accumulation, seedlings with Our objectives were 1 ) to determine if a greater stem diameter are also more resis- increased canopy size led to an increase in tant to the flattening effect of snow and dead the susceptibility of the seedlings to water vegetation (Burdett, 1990). stress; and 2) to determine the relative importance of soil and atmospheric drought Large seedlings may also have some disadvantages compared with smaller ones. in the generation of drought stress in the The greater transpiring surface of the larger seedlings.
- growth chambers, with 3 levels of soil water avail- MATERIALS AND METHODS ability. Replications of the atmospheric environ- ment treatments were performed over time Containerized black spruce seedlings from a sin- because of the limited availability of growth cham- gle provenance (EPN-N1-5A-J23-1288) were bers. The seedlings were removed from cold stor- obtained in 3 sizes from local nurseries in the fall age and treated in an identical manner for each of of 1992. Differences in size were achieved the 4 replicates needed to achieve statistical valid- through differences in length of culture, container ity of the results. The length of cold storage there- size and fertilization regime. The smallest (size 1) fore varied from 8 to 14 weeks, with no signifi- seedlings were grown in 67-50 (67 cavities per cant effect on any of the measured variables tray, 50 cm per cavity) Rigipot containers (IPL 3 (non-significance of replicate effect, table II). Industries, Saint-Damien, QC, Canada) over an 8- For each of the replicates, a set of 40 seedlings month production schedule, with sowing carried from each size class was removed from cold stor- out in a heated glasshouse in February, and age and allowed to recover their metabolic func- plants moved outdoors in May. The medium-size tions for 2 weeks in a pretreatment controlled (size 2) seedlings were grown in 25-200 Rigipot environment chamber. Conditions in the cham- containers. The large (size 3) seedlings were ber were set at 20/15°C, 50/100% day/night tem- grown in 45-340 Vent-Block containers (Beaver perature and relative humidity, respectively, with Plastics, Edmonton, AB, Canada). Both size 2 a 12-h photoperiod. Seedlings were kept well and 3 seedlings were produced over a 16-month watered. production schedule, with sowing in June in After the pretreatment, the seedlings were pre- unheated polyethylene tunnels, and seedlings pared for the experiment. Root plugs were inserted moved outdoors in August for the remainder of into Spectro-Por 1 dialysis tubes (molecular cut- the period. Size 1 seedlings received a total of off weight of 8 000, Spectrum Industries, Los about 15 mg N per cavity. Size 2 and 3 seedlings Angeles, CA, USA) that were folded and clamped received about 110 and 170 mg N per cavity, closed at the bottom end. A sandy loam was used respectively. In all cases, the potting medium was to backfill between the root plugs and the mem- a 3:1 peat/vermiculite mix. brane to ensure the continuity of water films Upon reception from the nursery in Novem- between the root plug and the membrane. ber 1992, the seedlings were sorted for unifor- Solutions of polyethylene glycol (PEG) 20 000 mity in shoot volume within each size class using (JT Baker Inc, Phillipsburg, NJ, USA) were pre- displaced water volume. Initial morphological pared with concentrations of 0, 40, and 80 g characteristics of a subsample of the seedlings PEG/kg H and were used to fill 45-I basins. O 2 retained for the experiment are presented in The concentrations correspond to water poten- table I. After sorting, the seedlings were moved to tials of about 0, -0.04 and -0.12 MPa (Williams a 2°C cold room for temporary storage. and Shaykewich, 1969). Four seedlings from each The experiment was started in January 1993 of the 3 seedling sizes were placed at random into holesprecut in each basin cover and sus- and involved the exposure of the seedlings to 2 pended by their membrane tubes in the solutions different atmospheric environments in different
- that the solution level reached the top of the exchange measurements was harvested for dry so plug. Over the course of the experiment, a weight determination in order to standardize gas- root few membranes developed leaks. Seedlings with exchange measurements by unit needle weight. leaky membranes were removed from the exper- A second shoot collected to determine shoot was iment. The solutions in the basins were stirred ) x (Ψ using a pressure chamber water potential with submerged pumps. (PMS Instruments, Corvallis, OR, USA). The remainder of the canopy was retained to mea- Three basins containing solutions with the 3 sure total foliage dry weight. Finally, the root plugs PEG concentrations were placed in each of 2 were weighed fresh, and again after drying at controlled environment chambers in which the 70°C for 48 h, to determine their volumetric water conditions were set for either a low evaporative content (Θ While in the growth chamber, ). PLUG demand (E20: 20°C, 60% RH) or a high evapo- care was taken to minimize CO fluctuations 2 rative demand (E30: 30°C, 40% RH). The corre- (Stewart and Bernier, 1994); CO concentrations 2 sponding absolute humidity deficits in the cham- were usually about 370 ppm. bers were 6.9 and 18.2 g m for E20 and E30, -3 respectively. Photoperiod in the chambers was As mentioned earlier, the experiment was maintained at 12 h. Photosynthetically active radi- 4 times, with new sets of 40 seedlings repeated ation at seedling canopy height was about 500 per size placed every second week in the pre- μmol m s -2 -1. treatment chamber. Assignment of E20 or E30 to either of the 2 chambers was done at random On days 2, 4, 6 and 8 after the start of the for each of the 4 replicates. The experimental experiment, 1 seedling of each size was randomly design was a split-split-plot. The main plots were selected from each basin for midday measure- the 2 growth chamber conditions. The split-plots ments. Gas exchange was first measured in situ were the 3 basins containing the different PEG on a branch tip using a LI-6200 Portable Photo- solutions in each chamber. The split-split-plots synthesis System (LI-COR Inc, Lincoln, NE, USA). were the 12 individual seedlings in each basin Net photosynthetic rate (P transpiration (E), ), n stomatal conductance to water vapour (g and arranged in factorial combinations of 3 sizes and ) sW intercellular CO concentration (c were calcu- 4 sampling dates. The general linear models ) i 2 lated by the LI-6200. The shoot used for gas- (GLM) procedure of SAS was used in the statis-
- increased PEG concentration and increased tical analysis. Values of stomatal conductance and shoot water potential were log-transformed in this evaporative demand (fig 1).However, order to homogenize their variance. effect was not uniform across size and PEG concentrations, as shown by the significant size x PEG interaction (table II). The effect RESULTS of size dominated at low PEG concentra- tions, but was nearly absent at 80 PEG as dropped to near- water content plug root Measurements on days 2 and 4 showed all seedling sizes. uniform low values across that the seedlings were still adjusting to Shoot conductance also decreased with treatment conditions as root plug water con- increased seedling size, increased PEG tents gradually dropped from near satura- concentration and increased evaporative tion at day 0 to levels in near-equilibrium demand (fig 2). The significant 3-way inter- with the dynamics of water exchange of action (table II) reveals that the pattern was each treatment. Initial analysis of variance not uniform. In fact, the highest values of therefore showed a systematic interaction g were obtained in the E30 environment, between all main effects and day of mea- sW in size 1 seedlings. However, the combina- surement (analysis not shown). In order to tion of high PEG concentration and large focus the present report on the effect of seedling size always yielded low values of treatment conditions at or near equilibrium, the effects of treatments were evaluated by . sW g performing an analysis of variance on the data obtained on days 6 and 8 of treatment only. Of the 144 seedlings selected for mea- surements on those 2 d in the 4 replicates, 18 developed leaks. The results obtained on the 126 remaining seedlings are pre- sented in table II. The effect of the day of measurement (day 6 or 8) was still signifi- cant for many variables (table II), but there were no interactions of the ’day’ factor with any of the other treatment factors (not shown). This indicates that seedling condi- tions were still evolving, but that the pas- sage of time would not cause changes in the conclusions reached on the relative effects of the treatments, all treatments being affected equally by the passage of time. Only data from day 6 are presented graphically in order to reduce the complex- ity in the presentation of our results. In general, the effects of seedling size, PEG concentration and atmospheric envi- ronment were highly significant on all vari- ables but c with many significant interac- , i tions among treatment factors (table II). Root plug water content generally decreased with increased seedling size,
- Shoot water potential was only moder- pattern that paralleled that of g (fig 2). sW The effect of seedling size varied both with ately responsive to any of the 3 treatment PEG levels and environment. The largest factors. In general, Ψ increased (became x seedlings showed the largest rates of net less negative) with an increase in the evap- orative demand (fig 3), a response certainly photosynthesis by unit needle dry weight under conditions of limited stress (E20, low linked to the concurrent drop in g The . sW PEG), but the lowest rates under stressful exception to this behaviour was the drop ih conditions (E30, high PEG) (fig 4). Ψ in the E30 environment in size 3 x seedlings with increasing PEG concentra- tion, a response that shows up as a signifi- DISCUSSION cant size environment interaction in x table II. The response of net photosynthesis was The initial hypothesis of this work was that quite complex as all 3 treatment factors inter- increased seedling size would lead to acted significantly (table II). In general, P increased water stress and decreased net n decreased with an increase in evaporative photosynthesis. The results show that demand and PEG concentration (fig 4) in a increased seedling size did indeed cause
- ability conditions in the peat plug that were quite comparable to those in the field. The average peat volumetric water contents ranged from 44% under the mildest condi- tions to 9% under the harshest. A moisture- release curve obtained on disturbed sam- ples of peat substrate (results not shown) reveals that the corresponding soil water tensions range from about -0.01 to -0.15 MPa. The wet portion of that range is simi- lar to tensions measured in planting areas normally targeted for black spruce (eg, Bernier, 1993). The dry portion probably represents extreme conditions for that species. The effect of seedling size on root plug water content, evident mostly under the mildest conditions, reflects the limits imposed by the different interfaces in the delivery of water from the PEG solution to the roots. Peat is a poor water transport medium at water contents corresponding to even mild tensions (Örlander and Due, 1986; Bernier, 1992). In the field, such inter- faces are therefore also present as the rel- atively coarse peat-vermiculite mix of the root plug must serve as a transmission medium between the mineral soil and the roots. Consequently, differences in root plug water content among seedling sizes should such effects, but only under the harshest also occur in the field. conditions imposed, ie highest PEG con- The lack of large variations in shoot water centrations and highest evaporative potential shows the level of stomatal regu- demand. Neither of these 2 factors taken lation of water loss by the seedlings. Water individually resulted in a greater depression potential levels were actually greater (less of net photosynthesis in larger seedlings negative) in the harsher E30 environment than in smaller ones, except in the case of than in the E20 environment for most size x the E20, 80 PEG treatment. PEG combinations, except for size 3 Stomatal conductances and rates of net seedlings under the 80 PEG treatment. As photosynthesis under the 0 PEG treatment treatments progress from the mildest (E20, in the low evaporative environment are com- 0 PEG) to the harshest (E30, 80 PEG), parable to rates observed on black spruce increasing stomatal closure is needed to both under controlled conditions (Wang and maintain such a favourable internal water Macdonald, 1993; Yue and Margolis, 1993) status. There was no clear relationship and in the field (Blake and Sutton, 1988; between shoot water potential and net pho- Macdonald and Lieffers, 1990). The treat- tosynthesis. range of water avail- ments also created a
- The similarity in the general pattern of response between shoot conductance and net photosynthesis appears to be evidence of g controlling the rate of P by limiting n sW the supply of CO However, the computa- . 2 tion of internal CO concentration reveals 2 values that do not show c as limiting P (fig n i 5). For example, the highest c values coin- i cide with the lowest P measurements (E30, n 40 PEG, sizes 2 and 3). These results sug- gest that changes in P were not caused n by internal CO depletion following stomatal 2 closure. In fact, in black spruce, stomatal limitation to P appears to be important only n at relatively low values of stomatal conduc- tance (Stewart et al, 1995). Instead, the par- allel drop in P and g suggests a com- n sW mon mechanism of regulation. Possible candidates are the chemical signals sent by root tips as soil water availability decreases. Such signals have been shown to regulate stomatal processes (Davies et al, 1990). The drying of roots has also been shown to reduce seedling growth (Coutts, 1981). The large seedlings maintained high net rates under conditions of photosynthetic mild and moderate water stress. In the field, this high rate multiplied by their foliage biomass, plus the initial greater height, should translate into absolute growth rates latter environments, the stress itself will exceeding those of the smaller seedlings. reduce the intensity of competition. Studies using bare-root Sitka spruce (Picea sitchensis [Bong] Carr) seedlings (South and Mason, 1993), and bare-root and con- ACKNOWLEDGMENTS tainerized Douglas-fir seedlings (Newton et al, 1993) have shown superior absolute growth of large stock under normal plant- The authors would like to thank M Bernier-Cardou ing conditions. Only when planted on harsh for her help in the design of the experiment and in sites did larger Douglas-fir seedlings per- the analysis of the results, P Davignon for his technical assistance, and P Therrien and D Trudel form more poorly than smaller ones (Hahn for their care of the growth chamber facilities. and Smith, 1983). Given these results, we Thanks are also extended to MS Lamhamedi and expect the largest black spruce seedlings VJ Lieffers, and to other anonymous reviewers to grow faster and be better competitors for their helpful comments on the manuscript. than the smaller seedlings in situations Financial support for JDS was provided by the where atmospheric and soil drought stresses Natural Sciences and Engineering Research are minimal. On drought-prone sites, the Council of Canada, and the CRBF, Université smallest seedlings should grow best. In the Laval.
- Örlander G, Due K (1986) Location of hydraulic resis- REFERENCES tance in the soil-plant pathway in seedlings of Pinus sylvestris L grown in peat. Can J For Res 16, 115- 123 Bernier PY (1992) Soil texture influences seedling water stress in more ways than one. Tree Planters’ Notes Ching KK (1978) Analysis of differences in Overton WS, 43, 39-42 height growth among populations in a nursery selec- tion study of Douglas-fir. For Sci 24, 497-509 Bernier PY (1993) Comparing natural and planted black spruce seedlings. I. Water relations and growth. Can South DB, Mason WL (1993) Influence of different plant- J For Res 23, 2427-2434 ing stock size on early height growth of Sitka spruce. Forestry (Oxf) 66, 83-96 Blake TJ, Sutton RF (1988) Stomatal response: the key in newly planted jack pine and black to adaptation Stewart RE (1987) Seeing the forest for the weeds: a Plant Physiol (Life Sci Adv) 7, 125-130 spruce. synthesis of forest vegetation management. In: For- est Vegetation Management for Conifer Production Burdett AN (1990) Physiological processes in planta- (JD Walstad, PJ Kuch, eds). John Wiley and Sons tion establishment and the development of specifi- Inc, NY, USA, 431-480 cations for forest planting stock. Can J For Res 20, 415-427. Stewart JD, Bernier PY (1994) An inexpensive system for controlling carbon dioxide concentration while work- RA Herbicide for forest manage- Campbell (1990) use ing in enclosed environments. Hortscience 29, 700 ment in Canada: where and where we are we are For Chron 66, 355-360 going. Stewart JD, Zine El Abidine A, Bernier PY (1995) Sto- matal and mesophyll limitations of photosynthesis Coutts MP (1981) Effects of root or shoot exposure in black spruce seedlings during multiple cycles of before planting on the water relations, growth, and drought. Tree Physiol 15, 57-64 survival of Sitka spruce. Can J For Res 11, 703-709 Wang ZM, Macdonald SE (1993) Peatland and upland Davies WJ, Mansfield TA, Hetherington AM (1990) Sens- black spruce populations in Alberta: morphology and ing of soil water status and the regulation of plant ecophysiology. Can J For Res 23, 33-40 growth and development. Plant Cell Environ 13, 709- 719 Williams J, Shaykewich CF (1969) An evaluation of polyethylene glycol (PEG) 6000 and PEG 20 000 in Hahn PF, Smith AJ (1983) Douglas-fir planting stock the osmotic control of soil water potential. Can J Soil performance comparison after the third growing sea- Sci 49, 397-401 Tree Planters’ Notes 34, 33-39 son. Wood JE, Dominy SWJ (1988) Mechanical site prepa- Macdonald SE, Lieffers VJ (1990) Photosynthesis, water ration and early chemical tending in white spruce: relations, and foliar nitrogen of Picea mariana and 19-year results For Chron 64, 177-181 Larix laricina from drained and undrained peatlands. Can J For Res 20, 995-1000 Margolis HA (1993) Photosynthesis and dark Yue D, respiration of black spruce cuttings during rooting in Newton M, Cole EC, White DE (1993) Tall planting stock response to light and temperature. Can J For Res 23, for enhanced growth and domination of brush in the 1150-1155 Douglas-fir region. New For 7, 107-121
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