Annals of Botany 88 (Special Issue): 745-751, 2001 doi:10.1006/anbo.2001.1432, available online at http://www.idealibrary.com on IE l ® Adaptation to Winter Stress in Nine White Clover Populations: Changes in Non-structural Carbohydrates During Exposure to Simulated Winter Conditions and 'Spring' Regrowth Potential B. E. FRANKOW-LINDBERG* Department of Ecology and Crop Production Science, Swedish University of Agricultural Sciences, Box 7043, SE-750 07 Uppsala, Sweden Received: 17 January 2001 Returned for revision: 22 February 2001 Accepted: 22 March 2001 Nine white clover populations: Grasslands Huia (HO, New Zealand), AberHerald (AHO, bred in the UK from material of Swiss origin) and Sandra (SO, Sweden); sub-populations of these (survival populations) collected after exposure to two (H2 and AH2) and four (H4, AH4 and S4) years of winter stress, respectively, at Uppsala (59°49'N, 1739'E); and a wild ecotype (WE) from the area were subjected to two simulated winter environments [+2 °C, no light (W1) and +2/-2 C, 4 h photoperiod (W2) for 3 weeks] after hardening. After hardening, concentrations of total non-structural carbohydrates (TNC) differed little among the populations. However, the changes in these carbohydrates during the winter treatments differed between genetic backgrounds and populations selected for winter survival. Populations SO, S4 and WE showed lower reductions of TNC at low constant temperatures compared with H and AH populations. These populations were also able to maintain the TNC concentration in both stolons and roots despite frequent exposure to sub-lethal frosts, whereas H populations and AHO and AH2 lost both starch and water soluble carbohydrates from the stolons in treatment W2. The ability to cope with frequent sub-lethal frosts thus appears to play a crucial role in adaptation to northern climates. There appears to have been sufficient genetic variation in AHO for selection for this trait in the field. The amount of biomass accumulated and the rate of node production during regrowth were generally greatest after treatment W2, when the plants tended to have the highest concentrations of TNC. © 2001 Annals of Botany Company Key words: Trifolium repens L., white clover, cold tolerance, non-structural carbohydrates, starch, water soluble carbohydrates, winter stress, spring regrowth. INTRODUCTION White clover (Trifolium repens L.) is a temperate species which occurs from the Arctic to the subtropics over a wide altitudinal range (Williams, 1987). The accumulation and subsequent use of non-structural carbohydrates in the stolons (Collins and Rhodes, 1995; Frankow-Lindberg et al., 1996; Frankow-Lindberg and von Fircks, 1998; Turner and Pollock, 1998) and in the roots (Boller and N6sberger, 1983; Harris et al., 1983; Frankow-Lindberg, 1997; Guinchard et al., 1997) during autumn and winter ensures the energy supply of the plant during periods of poor radiation interception. The plant must also develop a sufficient degree of cold hardiness to survive periods of subzero temperatures (Junttila et al., 1990). The temperature in the field fluctuates considerably, but in a field trial performed in Sweden (Uppsala, 59°49'N, 17°39'E) it was rare for the temperature at the level of white clover stolons to fall below -6 The objective of the present study was to test the hypotheses that white clover plants adapted to long periods of winter stress (1) have low rates of utilization of total non-structural carbohydrate (TNC) reserves at low positive temperatures and (2) have physiological/morphological strategies to cope with repeated sub-lethal frosts. Changes in the concentration of TNC, divided into starch and water soluble carbohydrates (WSC), were recorded in the stolons and roots of three contrasting white clover cultivars, and subpopulations of these, during simulated autumn and winter cycles in a controlled environment study. The effect of winter environment on 'spring' regrowth potential (measured as rate of node production and biomass accumulation) was also evaluated. The plant material used included a cultivar bred for the Swedish environment, cultivars bred for milder environments, sub-populations of these that were collected after exposure to a number of winters at Uppsala, Sweden, and a local wild ecotype. C, a temperature which hardened white clover plants should be able to survive (e.g. Junttila et al., 1990; Frankow-Lindberg and von Fircks, 1998). Despite this, winter damage to cultivars of southern origin was substantial in this trial (Frankow-Lindberg and von Fircks, 1998). This raises the question of how white clover plants are affected by frequent or lengthy exposure to sub-lethal frosts. * Fax +46 18 672209, e-mail bodil.frankow-lindberg(aevp.slu.se 0305-7364/01/100745 + 07 $35.00/00 MATERIALS AND METHODS Plant material The experiment included three cultivars of medium leaf size: Grasslands Huia (H, New Zealand), AberHerald (AH, bred in the UK from material of Swiss origin) and Sandra (S, Sweden), sub-populations of these collected from a field © 2001 Annals of Botany Company 746 Frankow-Lindberg--Adaptation to Winter Stress in White Clover experiment performed in Uppsala between 1993 and 1996, and a wild ecotype. The field experiment was sown with Huia, AberHerald and Sandra cultivars in bi-species mixtures together with perennial ryegrass (Lolium perenne L. cultivar Preference) in a randomized block design, and was harvested by mowing three four times per growing season. The plots with species mixtures were separated by all-grass plots and the borders of the plots were kept free from vegetation by regular mechanical treatment. The white clover populations were monitored by frequent samplings during 1993 1996 and no seedlings were observed after autumn 1993. Thus, the white clover plants in the plots can be assumed to have established during 1993. Further details of this experiment are given in Frankow-Lindberg and von Fircks (1998). Stock plants (eight genotypes per population) from which plant material for this experiment were taken were generated as follows: (1) Original populations were grown from the same clover seed lots that were used to establish the field experiment. (2) Sub-populations exposed to two winters. Fifty stolon tips, each representing one genotype, from plots with H and AH were collected in the field experiment in 1995. These stolons were propagated and, during summer 1996, each population was polycrossed separately in an isolation house by the Legume Breeding Group at IGER, Aberystwyth, UK. Stock plants were grown from the seeds obtained. (3) Sub-populations exposed to four winters. Stolon tips were again collected in the field experiment in 1997, this time from all plots, and these were directly propagated and grown as stock plants. (4) In addition, eight genotypes of a wild ecotype from the area were also collected in 1997 from a field that had been mechanically mown during the past 15 years at similar intervals to those used in the field experiment. These were also propagated and grown as stock plants. Codes used for the different populations are presented in Table 1. All stock plants were grown in an unheated glasshouse during the summer. Plants from populations H4, AH4 and S4 could be expected to exhibit more clearly the traits that were selected for in the Uppsala environment, since the recombination of genes during polycrossing of populations TABLE 1. Treatment codes Treatment Code Huia, original population Huia, subpopulation collected after exposure to two winters Huia, subpopulation collected after exposure to four winters HO H2 H4 AberHerald, original population AberHerald, subpopulation collected after exposure to two winters AberHerald, subpopulation collected after exposure to four winters AHO AH2 Sandra, original population Sandra, subpopulation collected after exposure to four winters Wild ecotype collected from the Uppsala area SO S4 WE 'Winter' environment with +2 °C and no light 'Winter' environment with +2/-2 C and 4 h photoperiod Wl W2 AH4 H2 and AH2 might have made traits that had supposedly been selected for in the field less discernible. A test of the cyanogenic potential revealed great differences between the Swedish populations on the one hand and the foreign material on the other (Frankow-Lindberg, 1999), which indicates that the sub-populations used were indeed true sub-populations of the sown cultivars. There were nine populations in total and stolon cuttings from eight separate stock plants of each population were used for the experiment. Experimental setup and treatments A total of 432 stolon tips containing one fully-expanded leaf were planted in a fully- fertilized mixture of Perlite, peat and sand in plastic containers (10 x 10 x 14 cm 3 ). The pots were placed at random in an illuminated glasshouse providing a minimum of 250 mol m -2 s PAR, and were left to establish for 5 weeks at 18/15 C (day/night) with a 12 h photoperiod (natural photoperiod outside the glasshouse < 12 h). Plants were supplied weekly with 50 ml of a low-N nutrient solution of the following composition: 2-3 mM N; 10 mM P; 4.9 mM K; 17 mM Mg; 58 mM Ca; 3.7 mM S; 27.0 pM Fe; 17-0 [tM Mn; 11 pM Cu; 3.2 p.M Zn: Mo and 0-1 }IM Co during the establish22-0 tM B; 0-3 LttM ment phase, once during hardening and once before regrowth. Water was supplied as needed. The plants were inoculated with a slurry containing Rhizobium (Biomethod Research AB, Uppsala, Sweden) a week after planting. There were no signs of mineral nutrient deficiencies and all plants developed healthy nodules on the roots. The hardening treatment started after 5 weeks; the temperature in the glasshouse was reduced to + 10 C for 1 week. Plants were then moved to growth rooms with a temperature of +2 C and an irradiance of 110 pmol m- 2 s- 1 PAR. The photoperiod was 10 h for 2 weeks and 8 h for 1 week. At the end of the hardening period (a total of 4 weeks), all fully-expanded leaves were removed and one full set of plants (=72 plants) was subjected to a single controlled frost of -5 C. The temperature was decreased over a 6 h period from +2 C to the minimum temperature (-5 C), and then increased to +2 C during the following 6 h. These plants were then placed in a heated glasshouse and scored for survival after 2 and 4 weeks, after which they were discarded. The purpose of this treatment was to establish whether or not the plants had become hardened. No damage was observed to any of the plants after a single exposure to -5 'C. The remaining plants were divided between two different 'winter' environment treatments. These were: (1) +2 "C and no light (Wl); and (2) +2 CC for 12 h, and then -2 'C every night (W2). The temperature was lowered over 4 h, held constant for 4 h, and increased over 4 h. The photoperiod in W2 was limited to 4 h with an irradiance of 110 pmol m - 2 s- ' PAR; the light period occurred in the middle of the +2 C period. 'Winter' treatments lasted for 3 weeks. All fully-expanded leaves were again removed at the end of the 'winter' treatments. This served as a starting point for node production but also distinguished between old stolon material and stolon regrowth. Thereafter, plants Frankow-Lindberg-Adaptationto Winter Stress in White Clover 747 were placed in a heated glasshouse for a 3 week regrowth TABLE 2. Starch concentration of stolons (mg g-' d. wt) period. This coincided with spring and no supplementary from nine artificially hardened white clover populations light was provided. All treatments are presented in Table 1. exposed to two simulated 'winter' conditions Measurements and analyses Harvesting was carried out on three occasions: (1) after hardening; (2) after 'winter' treatments; and (3) after 'spring' regrowth (SW1 and SW2). The plants were washed free of all soil, all remaining leaves and petioles were discarded at the two first harvests and all stolons and roots from these harvests were dried at 105 C for I h and thereafter at 40 °C for 6 h. After drying, the samples were ground in a mill through a 084 mm mesh sieve. The milled samples were analysed for TNC (all carbohydrates except cellulose) using the anthrone-reduction method after extraction with a weak acid solution as described by Smith (1973), and the WSC concentration, i.e. chiefly glucose, fructose and sucrose, was determined using an automated anthrone procedure (Thomas, 1977). Starch levels were estimated by the difference between TNC and WSC. The choice of preparative and analytical methods was determined by the wish to compare the results with data obtained in a field experiment using the same cultivars (Frankow-Lindberg and von Fircks, 1998). The carbohydrate analysis used does not detect pinitol; however this occurs at a rather low concentration in white clover (Turner and Pollock, 1998). At the final harvest, the plants were dissected into roots, old stolon material, stolon regrowth and leaves. The number of apices and the number of nodes produced during regrowth were recorded. All component parts were dried at 105 C for 24 h and weighed separately. The rate of node production during 'spring' regrowth (nodes per apex) was calculated. Data were analysed statistically by a two-way ANOVA, using SAS (1988), as a completely randomized design with eight replicates. Main factors were population, harvest occasion and their interaction. RESULTS Starch concentration of the stolons There were rather small differences among the populations in the starch concentration of the stolons after the initial hardening treatment (Table 2). However, the effects of the treatments on starch concentration interacted strongly with population (P < 0-001). Treatment WI generally caused a reduction in starch concentration of the stolons (P < 005), while treatment W2 significantly reduced starch concentrations in all H populations, AHO, AH2 and WE, but not in AH4, SO or S4 populations (P < 0.05). Starch concentration of the roots There was a strong interaction between treatment and population on root concentration of starch (P < 0.001). After the hardening treatment, the differences among populations were rather small (Table 3). Treatment WI resulted in a general decrease in root starch concentration in Population HO H2 H4 AHO AH2 AH4 SO S4 WE Mean Hardened W1 W2 Mean 178 171 158 172 181 153 161 156 163 166 122 121 136 153 132 118 144 145 144 135 92 92 88 108 128 146 183 153 101* 121 131 128 127 144 147 139 163 151 136 Plants were destructively harvested after hardening and after the respective 'winter' treatments. Error d.f = 188, n = 8 or 7*. LSDo.os0 = 9 (when n = 8 for both values to be compared) and = 10 (when n = 7 for one of the values to be compared). TABLE 3. Starch concentration of the roots (mg g-' d. wt) from nine artificially hardened white clover populations exposed to two simulated 'winter' conditions Population HO H2 H4 AHO AH2 AH4 SO S4 WE Mean Hardened WI W2 Mean 121* 131 146* 144 149* 144* 148 107* 109* 133 62 77 56 111 101 106 110 106 96 92 121* 126* 125 119 138 129 144 138 133 130 101 112 109 125 129 126 134 117 113 Plants were destructively harvested after hardening and after the respective 'winter' treatments. Error d.f= 179, n = 8 or 7*. LSD.05 = 8 (when n = 8 for both values to be compared) and = 9 (when n = 7 for one of the values to be compared). all populations, particularly in the H populations (P < 005). With the exception of populations S4 and WE, treatment W2 also reduced root starch concentration (P < 005) in all populations. The increase in root starch concentration in S4 and WE was significant (P < 005). Water soluble carbohydrate concentration of the stolons There was a strong tendency for interaction between population and treatment on the concentration of WSC in the stolons (P < 0.08). Thus, the WSC concentration was generally reduced in all Grasslands Huia and AberHerald populations after both 'winter' treatments, while only treatment W1 reduced the concentrations in the SO, S4 and WE populations (P < 005, Table 4). However, H2 and H4 on the one hand and AH2 and AH4 on the other contained 748 Frankow-Lindberg-Adaptationto Winter Stress in White Clover TABLE 4. Water soluble carbohydrate concentration of the stolons (mg g-l d. wt) from nine artificially hardened white clover populations exposed to two simulated 'winter' conditions TABLE 5. Water soluble carbohydrate concentration of' the roots (mg g-/ d. wt) from nine artificially hardened white clover populations exposed to two simulated 'winter' conditions -^-^---^---- - - - Population Hardened WI W2 Mean HO H2 H4 246 236 211 142 142 126 170 193 184 186 190 174 AH AH2 AH4 230 232 245 157 194 182 181 210 208 S S4 WE 264 245 232 197 200 176 229 246 257 Mean 238 168 209 Population Hardened WI W2 Mean HO H2 H4 146* 142 146* 88 101 110 133* 152* 159 122 132 138 190 212 211 AHO AH2 AH4 152 166* 133* 138 147 147 140 147 152 143 153 144 230 231 222 SO S4 WE 160 177* 170* 153 147 138 169 176 151 161 168 153 Mean 155 130 153 Plants were destructively harvested after hardening and after the respective 'winter' treatments. Error d.f = 189, n = 8. LSD. 05 = 14 (for comparing any two values). Plants were destructively harvested after hardening and after the respective 'winter' treatments. Error d.f = 179, n = 8 or 7*. LSD.o 05 = 9 (when n = 8 for both values to be compared) and = II (when n = 7 for one of the values to be compared). TABLE 6. Weight (g d. wt per plant) of nine artificially hardened white clover populations exposed to two simulated 'winter' conditions TABLE 7. The effect of hardening and winter treatments on weight (g d. wt per plant) of white clover plants Population Old stolon weight Root weight 'Spring' regrowth Treatment Old stolon weight Root weight HO H2 H4 1.03 1-00 0-97 0.96 0.86 0.77 4.29 4-00 3.59 Hardened 1.37 0.86 W1 W2 1.17 1.24 0.73 0.69 - AHO AH2 AH4 1.41 1.50 1.35 0.73 0.73 0-71 4.02 4.47 3-81 SWI SW2 1.09 1.09 0-88 0.90 3.72 4.11 SO S4 WE 1.17 0.96 1-32 088 0-78 0-90 3-99 3-32 3.77 LSDo.os 0.04 0.03 0.10 LSDo.os0 0-06 0.04 0.21,/022* Old stolon weight and root weight are means of three harvest occasions (after hardening, after 'winter' treatments and after 'spring' regrowth). 'Spring' regrowth consists of leaves + stolons produced during the regrowth period. Error d.f. = 307 for old stolon and root weights, and 118 for 'spring' regrowth. *0.22 for comparisons where HO, H2 or H4 are involved. higher WSC concentrations after treatment W2 compared with HO and AHO populations, respectively (P < 0.05). Water soluble carbohydrate concentration of the roots There was a significant interaction between treatment and population on root concentration of WSC (P < 005). The WSC concentration of the roots differed little among populations after the hardening treatment, although all Grasslands Huia populations contained slightly less (P < 0-05, Table 5). Treatment Wl generally reduced the WSC concentration, but less so in the H2 and H4 populations compared with HO, and AH2 and AH4 'Spring' regrowth Means for nine white clover populations. 'Spring' regrowth consists of leaves + stolons produced during the regrowth period. SWI and SW2 denotes plant biomass after treatments WI and W2, respectively. Errors d.f. = 307 for old stolon and root weights, and 118 for 'spring' regrowth. compared with AHO (P < 0-05). Treatment W2 affected WSC concentration less than treatment WI, and the concentrations were higher in populations H2, H4 and AH4 compared with HO and AHO, respectively (P < 0.05). Old stolon weight There was no interaction between treatment and population on old stolon weight. AberHerald populations generally had the greatest, and Grassland Huia populations the smallest stolon masses (P < 005, Table 6). Both winter treatments resulted in a similar reduction in the stolon mass of all plants (P < 005, a mean loss of approx. 12 % of the dry weight present after hardening, Table 7). After 'spring' regrowth, the mass of old stolon of all plants was further reduced (P < 005, a mean loss of approx. 20 % of the dry weight present after hardening, Table 7). Frankow-Lindberg-Adaptation to Winter Stress in White Clover Plant root weight There was no interaction between treatment and population on plant root weight. It was generally smallest in all AberHerald populations, while differences between Grasslands Huia and Swedish populations were small (P < 0.05, Table 6). Both winter treatments resulted in a general reduction in plant root weight (P < 005, mean of approx. 17 % of the dry weight present after hardening, Table 7), while root weight was generally restored to pre-winter treatment amounts after the 'spring' regrowth period (P < 005, Table 7). 'Spring' regrowth There was no interaction between treatment and population on 'spring' regrowth. The amount produced was generally smallest in the survival populations H4, AH4 and S4 compared with the other populations (P < 005, Table 6). The amount of regrowth was greater after treatment W2 compared with treatment Wl (P < 0.01, Table 7). Node production rate during 'spring' regrowth Plants from treatment W2 regrew at a faster rate than plants from Wl (5-0 vs. 44 nodes per apex, P < 0001); there were no interactions between treatment and population and no significant effects of population. DISCUSSION Both stolons and roots serve as storage organs for surplus non-structural carbohydrate accumulation when the demand of the plant is lower than the rate of synthesis of these compounds (Boller and N6sberger, 1983). It is important to bear in mind that the non-structural carbohydrates in white clover storage organs undergo a complex pattern of breakdown and synthesis during winter and that the metabolism also depends on node position within the plant (Hay et al., 1989; Turner and Pollock, 1998). This implies that any changes in the concentration of TNC from the harvest after hardening to the harvests after the winter treatments were the net effect of: carbon (C) input by photosynthesis, and the utilization of C for maintenance respiration, growth and, possibly in treatment W2, processes related to the development of cold tolerance (Smith, 1964). Active growth of white clover requires soil temperatures above 5 C (Hart, 1987). Thus, the temperatures chosen in this experiment should not have induced any substantial growth (although leaves continued to expand) during either of the simulated winters, and any changes in TNC concentrations recorded in treatment W2 should be primarily due to the net effect of C input by photosynthesis less C losses due to maintenance respiration and the possible development of cold tolerance. Net changes in TNC between hardening and the extraction after treatment W1 (no photosynthesis and no frosts) should thus reflect the basal metabolism of the plants at 749 near freezing temperatures and are used here as a measure of the maintenance respiration of the plants. TNC after hardening After the hardening treatment, the starch and WSC concentrations in the stolons of all plants were high and of a similar magnitude to those observed during autumn in the field experiment from which the plant material used in this experiment was derived (Frankow-Lindberg and von Fircks, 1998). All populations had similar amounts of TNC in both stolons and roots. This suggests that there is little genetic variation in the capacity to accumulate reserve carbohydrates in either stolons or roots within white clover cultivars adapted to a broad range of environments. After the hardening treatment, the plants exhibited a level of cold tolerance similar to that observed during late autumn in field-grown plants of the cultivars used [unhardened plants of these cultivars survive to approx. -1 C (Frankow-Lindberg and von Fircks, 1998)] and no visible damage to any of the plants was observed after the brief exposure to -5 C. Thus, the repeated exposure to -2 C in treatment W2 was indeed sub-lethal and should not have caused any frost damage to the tissues of the plants in this experiment. 'Winter' at a low constant temperature Starch and WSC concentrations both in stolons and roots of all plants declined during treatment W1. The relative reduction was greatest for starch stored in the roots, irrespective of population. However, the effect was small in the Swedish populations, and all Grasslands Huia populations generally lost considerably more starch and WSC than did the AberHerald populations. Harris et al. (1983) found that a cultivar (Olwen) originating from southern France had a potential for greater respiration rates at low temperatures than the cultivar S 184 which is a winter-hardy cultivar of British origin. This suggests that a low maintenance respiration at low positive temperatures has an adaptive value for the survival of white clover plants at northern latitudes. However, this trait was not selected for in survival populations of H and AH populations. 'Winter' with repeated sub-lethalfrosts and a short photoperiod The Swedish cultivar was able to maintain starch and WSC concentrations in both stolons and roots during treatment W2. This implies that current photosynthesis was sufficient to restore C consumed in maintenance respiration and for the development of cold tolerance. However, all H populations, AHO and AH2 had reduced stolon starch concentrations in treatment W2 compared to levels following hardening, with H populations having the greatest reductions. Population AH4, on the other hand, was able to maintain its starch concentration in the stolon at a similar level to that of the Swedish cultivar, which could indicate a selection in the AH population for this characteristic. The concentration of WSC in the stolons of all plants, on the 750 Frankow-Lindberg--Adaptationto Winter Stress in White Clover other hand, was greater after treatment W2 than after treatment W1. This suggests that stolon starch was broken down into WSC at sub-freezing temperatures. Similar results have been reported by Guinchard et al. (1997). The ability to maintain a positive C balance in the presence of frequent sub-lethal frosts thus appears to have a strong adaptive value in northern climates. Higher rates of net photosynthesis have been recorded in Sandra compared with Grasslands Huia and AberHerald populations in another experiment at low temperatures (Frankow-Lindberg, 1997), but when they were grown at higher temperatures no such differences were observed (FrankowLindberg, 1999). It is hypothesized that adaptation involves the ability to maintain net photosynthesis despite frost events. Biomass changes of old stolons and roots All plants lost stolon weight during the winter treatments and a further loss in the weight of old stolon material was recorded during the 'spring' regrowth. Plant root weight was also reduced during the winter treatments, but it was restored to pre-winter treatment levels at the end of the regrowth period. An interesting, but not quantified, observation was that pink, healthy nodules were present on all roots at the harvests made at the end of the hardening treatment and also at the end of the 'spring' regrowth. However, at the harvests made after the respective winter treatments, there were still nodules on the roots, but these were small and colourless. Furthermore, Gordon et al. (1986) reported that defoliation per se induced a reduction in the leghaemoglobin concentration of white clover nodules and the plants used in the experiment reported here were defoliated before winter treatments began. Thus, part of the change in root weight was probably due to changes in the leghaemoglobin content, a conclusion which is consistent with the observation that the amount of a protein identified as leghaemoglobin increased in the roots of white clover plants during regrowth at increasing temperatures (Corbel et al., 1999). The concentrations of TNC in the plant roots in this study were much higher than those reported for plants grown at higher temperatures (Boller and N6sberger, 1983; Baur-H6ch et al., 1990). This suggests that TNC storage in the roots complements storage in the stolons, particularly during autumn and winter, and that the C-metabolism of the roots during winter is important since starch stored in the roots was, relatively, reduced more than starch stored in the stolons in treatment W1. 'Spring' regrowth A slightly smaller amount of 'spring' regrowth was observed in the wild ecotype and in the populations that were collected after exposure to four winters compared with the original populations. Frankow-Lindberg (1999) reported a comparatively smaller production potential in these populations due to their short internodes. The rate of node production during regrowth did not differ between populations studied here. Plants from treatment W1 regrew more slowly than plants from treatment W2, irrespective of population. This resulted in a smaller accumulation of biomass (on average 9 % less dry weight) in plants from treatment W1 compared with plants from treatment W2 during the regrowth period. Both carbon and nitrogen reserves are assumed to be mobilized during regrowth of white clover (Volenec et al., 1996). Since N compounds were not analysed in this experiment nothing can be said about their role in the regrowth of the plants studied here. However, it is pertinent that the overall concentrations of TNC in the stolons and roots of all plants were higher after treatment W2 than after treatment W1. In field experiments over several seasons, the amount of spring regrowth harvested correlated well with the concentration of TNC in the stolons in early spring (Frankow-Lindberg et al., 1996; Frankow-Lindberg and von Fircks, 1998). However, it is important to note that white clover plants in the Uppsala environment enter spring with a very small leaf area (Frankow-Lindberg, unpubl. res.). The physiological implications of regrowth in this situation should be similar to that after a severe defoliation. It is well-established that regrowth of white clover plants after defoliation mobilizes non-structural carbohydrate reserves from both stolons and roots, with stolon reserves being used preferentially (Danckwerts and Gordon, 1989; Baur-Hoch et al., 1990; Gallagher et al., 1997). The fact that the weight of old stolons of all plants was reduced during the 'spring' regrowth in this study suggests that compounds stored in these played an important role in sustaining 'spring' regrowth of the plants. In environments where the plant is able to maintain a greater amount of its leaf area during winter, TNC concentration may be less important in determining the plant's rate of spring regrowth and differences between cultivars in their ability to maintain leaf area during winter might play a more crucial role. In conclusion, my results support the two hypotheses presented earlier. Thus, white clover plants adapted to an environment with long overwintering periods have slower rates of C reserve utilization at low positive temperatures compared with plants of a more southern origin. However, no selection for this characteristic among plants from Grasslands Huia and AberHerald populations could be detected. The ability to cope with frequent sub-lethal frosts also appears to play a crucial role in adaptation to northern climates. The Swedish material was able to maintain TNC concentration in both stolons and roots when exposed to frequent sub-lethal frosts, while the opposite was true for non-adapted material. A selection for this characteristic was found within the AberHerald population. The mechanism behind this characteristic was not identified by the present study, but it is probable that an ability to continue net photosynthesis despite frost events is involved. This study suggests that a greater focus on the physiology of white clover plants when exposed to sub-lethal temperatures would improve understanding of overwintering mechanisms. It would also be rewarding to investigate how the absolute degree of cold hardiness is related to the response to sub-lethal temperatures (Gusta et al., 1997). Furthermore, the relative roles of stored C and N compounds in spring regrowth in different environments remain to be resolved (Bouchard et al., 1998). Frankow-Lindberg-Adaptationto Winter Stress in White Clover ACKNOWLEDGEMENTS I thank the Behms Foundation for financial support, the Institute of Grassland and Environmental Research in Aberystwyth for performing the carbohydrate analyses, the Legume Breeding Group at the same institute for developing and supplying seed of H2 and AH2, A. Andersson, Y. Schang, S. Eriksson and A. Hansson for skilful technical assistance, G. Ekbom and B. Vegerfors for statistical advice and Dr. A. 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