RiologiralJoumal ofthe Linnean Society. 1 3 : 155- 166. With 3 ligures March 1980 Experimental manipulation of patterns of resource allocation in the growth cycle and reproduction of Smyrnium olusatrum L. J. LOVETTDOUST* School ofPlant Biology, U . C . N .W., Bangor, Gwynedd, Wales Accepted/orpublication October I979 Plants of the monocarpic (normally biennial) Srnymrurn olusatrurn (Umbelliferae)were grown in pots in soil at a high or low nutrient regime. Some plants receiving full nutrients were grown in a heated glasshouse with 16 h days. The remainder were grown without supplementary lighting o r heat and included control plants and others which received surgical treatment after ten months growth: deradication (removal of half of the root stock); defoliation; deradication and defoliation. The distribution ofplant biomass and of phosphorus were analyzed at the time of seed set. Patterns of allocation of dry matter and phosphorus were quite different and were significantly altered by treatments, which produced a range of allocation to reproductive structures ranging from 21 to 74%oftotalphosphorusand 12 to M%ofdrymatter. Distribution patterns of total phosphorus are discussed in terms of the potential demands being made by alternative structures and functions over the life cycle of the plants. CONTENTS Introduction , , Materials and methods Results . , , , Discussion . . , Acknowledgements References . , , . , , . . , , , , , . , , , , , , , , , , , , . , . . . . . . . . . , . , . . . . . . , , , , , , , , , . , , , , , , , , , , , , , , . . . . . . , , . , . , , . . . . . . . . . , . , . . . . , . . . . , . , , . . , , . . . . . , , , . . I55 1.56 157 16 I 165 16.5 INTRODUCTION In a previous paper (Lovett Doust, 1980) it was shown that plants of Smyrnium olusatrum from three field sites differed in their patterns of biomass allocation among organs. The internal resource economy of plants has, with very few exceptions, been considered only with respect to biomass, essentially in a ‘currency’ of carbon or energy. However, the ecological implications of plant growth patterns in relation to the accumulation and distribution of nutrients have yet to be considered, and many of the questions about resource allocation originally posed by Harper (1967) and partially answered for carbon (Harper, 1977 ) might usefully be asked with respect to the partitioning of other resources. The distribution of phosphorus may be particularly important because it is known to be concentrated in seeds and is vital in reporduction. The previous study had * Present address: Department of Botany, University of British Columbia, Vancouver, B.C., Canada V6T 2B1 0024-4066/80/020 155- 12/$02.00/0 155 @ 1980 The Linnean Society of London I56 J . LOVETT DOLIST shown that, at the time of fruit set in S. olusatrum, 31.5% of the total biomass including 59%of the total phosphorus is allocated to reproductive organs (Lovett Doust, 1980). Gregory (1953) has shown that, in the developing cereal plant, over 90%of the phosphorus (and nitrogen) is accumulated before the plant has made 25% of its growth in dry weight. This store of accumulated nutrient is the reserve upon which later growth and development depend, and its level determines the final yield. Smyrnium olusatrum is a semelparous species (biennial or longer-lived) and has a longer period than the annual cereals in which to capture the nutrients that are ultimately allocated at flowering and seed set. A series of treatments was applied to plants of S. olusatrum in experiments that were designed to severely alter sourcehink relationships within the plants. MATERIALS AND METHODS Seed of S. olusatrum was sampled from a single plant, collected at Glanrafon, Bangor and the plants were grown individually in urpose-built pots (50 cm high x 20 cm diameter) made of asphalt paper a n 8 lined with perforated black polythene bags filled with John Innes Compost (No. 3) (except for treatment 6, see below). The experiment was started in January 1976 and ran for approximately 550 days, until July 1977. Twenty plants were grown for each of six treatments. The plants in Treatments 1 to 5 received liquid nutrient (‘Vita-Feed’) every week in the second year of growth. Plants for Treatment 6 were germinated and grown in a 5050 mixture of washed sand and John Innes Compost No. 3, and did not receive weekly watering with liquid nutrient. Harvest 1 consisted of five plants taken from each treament in mid-November 1976, i.e., at the end of the first year of growth. At about the same time various defoliation and deradication treatments were applied to the remaining plants. Harvest 2 was made in July 197 7 and consisted of the remaining 15 plants per group, whether flowering of not. The plants that flowered bore ripe mericarps at this stage. Treatments were as follows : Treatment I . Defoliation: the lamina was removed from basal leaves and from the cauline leaves as and when they appeared. Treatment 2. Deradication: the lower half of the root stock which had developed in the first 10 months was removed; a water displacement technique was used to ensure that as exactly as possible 50% of the root system was removed. The cut surface was washed in a solution of ‘Benylate’ to protect against fungal attack and the plants were repotted. Treatment3.Both Deradication and Defoliation treatments were applied. Treatment 4. Control: no treatments were applied. Treatment 5 . Plants were grown as the controls but in a heated glasshouse with 16 h day length. Treatment 6 . Low soil nutrient: the plants were germinated and grown in a 5 0 5 0 mixture of washed sand and John Innes Compost No. 3 and did not receive the weekly watering with ‘Vita-Feed’. All plants except those in treatment 5 were grown in a coldframe house with no supplementary lighting or heat. Pots were arranged in a randomized design. At both harvests plants were washed and separated into component organs, dried and then weighed. The dried organs were then milled and subsamples were RESOURCE ALLOCATION IN SMYRNIUM OL(ISATR1IM 157 ashed. Total phosphorus content was estimated using the molybdate-blue method described in Allen (1974). R ES CJ LTS Approximately two-thirds of the plants in all treatment groups flowered. Two of the plants died early in the low nutrient treatment and there was precocious death at flowering time of several of the plants which had been both deradicated and defoliated. Harvest 1 was taken a month after the experimental plants had been deradicated or defoliated and at this harvest there was very little difference in mean dry weight per plant (Table 1), The most spectacular effects of treatment appeared at Harvest 2 as a five-fold range of weight of the flowering plants, varying from 52 g in the deradicated-defoliated group (this included the weight of tissues removed) to 275 g in control plants (Table 1). Deradication had surprisingly little effect on the weight of flowering plants though it depressed by about 80% the weight of those plants that remained vegetative. Defoliation drastically reduced the dry weight of plants at the second harvest and these plants added little extra dry matter during their second season of growth. Plants that had been both deradicated and defoliated did not increase their total dry matter beyond that present at Harvest 1. Plants in the low nutrient regime and those grown in the heated glasshouse accumulated very little dry matter in year 2 and the yield per plant was no greater than that of defoliated individuals. Plants grown in a heated glasshouse, like the control plants, achieved a greater dry weight if they remained vegetative. The effect of treatments on phosphorus content was considerably less marked than that on plant dry weight (Table 2). The mean total phosphorus per plant at flowering was reduced by about 25% in plants that had been deradicated and by 50% in plants that were defoliated. At Harvest 2, plants in almost all treatment groups contained less phosphorus than the control plants at Harvest 1. The fraction of total biomass represented in reproductive tissue was 35% but the very high value of 68 to 74% of total plant phosphorus was present in reproductive tissues, in both the control and deradicated plants (Figs 1, 2). After defoliation (with or without deradication) and in the low nutrient and heated Table 1. Mean (kS.E.) total dry weight per plant (g) in vegetative and flowering plants (totals are calculated to include tissue which had been removed experimentally) Control Harvest 1 Vegetative plants Harvest 2 Vegetative plants Harvest 2 Flowering plants Deradicated Defoliated Deradicated and Defoliated Low nutrient Heated glasshouse 74.5(10.1) 59.0(11.31 56.0(9.9) 52.8(9.2) 51.1 (9.3) 55.3 (8.9) 337. (15.5) 247.5 (17.6) 34.2 (5.6) 37.4 (4.9) 58.0 (7.5) 105.7 (7.9) 276.7 (17.6) 266.8 ( 9.3) 72.6 (9.9) 52.4 (2.3) 70.6 (2.9) 62.4 (2.4) 1. LOVETT DOUST 158 Table 2. Mean (+ S.E.) total phosphorus per plant (g)in vegetative and flowering plants (totals are calculated to include tissue which had been removed experimentally) Control Deradicated Defoliated Deradicated and Defoliated Low nutrient Heated glasshouse ~ Harvest 1 Vegetative plants Harvest 2 Vegrtative plants Harvest 2 Flowering plants 0.230(0.033) 0.1 14 (0.021) 0.136(0.027) 0.089(0.022) 0.100(0.018) 0.190(0.018) 0.485 (0.088) 0.378(0.031) 0.140 (0.023) 0.092(0.016) 0.115 (0.017) 0.375(0.022) 0.546(0.046) 0.405 (0.008) 0.253(0.031) 0.219(0.009) 0.178(0.007) 0.158 (0.005) glasshouse regimes, very much lower fractions of total phosphorus were allocated to reproductive structures and a much greater fraction was retained in the tuberous root system or, in the plants grown in the heated glasshouse, was present as dead leaf. In the defoliated treatments (with or without deradication) a much increased proportion of plant phosphorus was held in peduncles. In plants that were both deradicated and defoliated the allocation pattern of phosphorus was changed dramatically and much more phosphorus was retained in the root system and much less allocated to reproductive organs. Plants receiving this treatment weighed only a fifth as much as control plants. One of the most striking effects of treatment is to be seen in root: shoot ratios (Fig. 3). Whereas it was not surprising to find that deradication and defoliation disturbed this ratio, the greatly increased ratio of root: shoot in the plants grown at low nutrient regime contrasts very strongly with that of control plnats and those grown in the heated glasshouse. Table 3 illustrates the changes in the concentration of phosphorus in different organs of the plant. The concentration within fruits remained relatively invariant except for the very low value for plants grow in the heated glasshouse. However, the concentration in the rays of the inflorescence was greatly increased by defoliation, low nutrient supply or growth in the heated glasshouse. The variations in concentration in the rays are paralleled by variations in peduncles and the inference is that the phosphorus was not actively translocated out of the peduncles under these conditions. The concentration of phosphorus in dead leaves may perhaps be taken as a measure of the ability of the remainder of the plant to extract a vital nutrient and transport it to sinks elsewhere. In the heated glasshouse the rate of leaf turnover was very high and the leaves died with relatively high phosphate concentrations in them (Table 3). On the control plants, leaves that died in the first year contained high phosphorus concentrations but at the second harvest dead leaves had, like the peduncles, been greatly reduced in phosphorus concentration. Deradicated plants appeared also to be ‘efficient’ in depleting dying leaves of phosphate but on plants that had been both deradicated and defoliated leaves died with a concentration of phosphate higher than 3 mg/g (cf. 0.96 mg/g in dead leaves of control plants). Concentrations of phosphorus in the tuberous roots RESOURCE ALLOCATION IN SMYRNIUM OLUSATRUM Control 159 Deradiccte Defoliate Derodicate and defoliate Low nutrient Heated qlasshouse Figure 1 . The patterns of allocation of dry matter in flowering plants at the time of ripe fruit (calculated excluding any excised tissue). varied very greatly with treatments and the level of root phosphorus was generally reduced to its lowest value in flowering plants. The only strong exception to this rule was that plants that had been both deradicated and defoliated retained a high concentration of phosphorus within the roots. The concentration of phosphorus in stems fell to very low values in control J . LOVETT DOUST I60 Control Defoliate Low nutrient Deradicate Oeradicate and defoliate Heoted glasshouse Figure 2. The patterns of allocation of total phosphorus in flowering plants at the time of ripe fruits (calculated excluding any excised tissue). and deradicated plants but after defoliation (with or without deradication) and under low nutrient regimes the stem retained high concentrations of phosphorus. The cauline leaves on defoliated plants (i.e. residual petioles) and the leaves of plants grown in a heated glasshouse died with high phosphate concentrations present (Table 3). RESOURCE ALLOCATION IN S M Y R N I U M OLUSATRUM 161 I .o 0.9 0.8 0.7 c 0.6 ._ c e P - c 0.5 f 0 a 0.4 0.3 -C 0.2 P - 0.1 0 Control -C i Deradicate Defoliate Derc and d cote iliate Low nutrient Heated glasshouse Figure 3. The effect of treatments upon root: shoot ratios of dry weight (C) and total phosphorus (P) in flowering plants (calculated excluding weights of excised tissue). DISCUSSION The treatments applied to S. olusatmm in these experiments were severe, either major surgical removal of tissues, severely limiting nutrient supplies or the continued maintenance of higher temperatures and longer day lengths than would ever be experienced by the plant in the field. The surgical treatments mimicked very severe damage by, for example, defoliating insects or the activities of root pathogens or predators. Nevertheless, very few plants died: two of them under the low nutrient regime (which much reduced the growth of survivors) and five that had been both deradicated and defoliated; these died after the onset of flowering. Five of the 15 control plants had not flowered at the time of Harvest 2 and the same proportion of deradicated plants failed to flower. A slightly greater proportion of plants failed to flower after defoliation (with or without deradication), low nutrient or heated glasshouse treatments. The variation from plant to plant in the ability to flower in the second year of growth would not be surprising if it was clearly effected by treatments, yet the effect of the most severe treatments, which reduced dry weight at flowering by 80% only slightly reduced the probability of flowering. It may be that there is genetic variation within J. LOVETT DOUST 162 Table 3. Mean phosphorus concentrations (mg P/g) (+ S.E.) in selected tissues (at H2 (second harvest); all data are for plants that flowered and set seed unless described otherwise) Dead basal leaves Control Deradicated Defoliated Deradicated and Defoliated H2 reproductive plants H2 vegetative plants HI vegetative plants H2 reproductive plants H2 vegetative plants 0.96 (0.07) 0.64 (0.02) 1.76 (0.26) 3.07 (0.17) 1.17 (0.07) 2.33 (0.12) 0.99 (0.09) I .02 (0.06) I .69 (0.07) 1.75 (0.36) 1.72 (0.19) 3.34 (0.16) 3.29 (0.031 I .03 (0.06) I .03 (0.05) 0.70 (0.05) 1.87 (0.03) 2.68 10.03) HI Low nutrient Heated glasshouse 1.39 0.99 2.0 I 2.34 (0.08) 2.19 (0.23) 4.11 (0.10) (0.18) (0.11) (0.08) 1.51 (0.07) 1.61 (0.09) 4.3 1 (0.17) 2.84 (0.18) 2.17 (0.23) (0.11) 2.85 (0.13) 2.82 3.25 3.05 (0.18) (0.11) (0.10) 1.74 (0.I I ) (0.17) 0.36 (0.03) 2.40 (0.371 4.40 (0.39) 2.87 (0.19) 0.91 (0.031 I .03 (0.06) 4.32 (0.24) 4.07 (0.13) 1.26 (0.06) 3.55 (0.14) (0.10) 0.40 (0.04) 3.25 (0.31 ) 4.46 (0.27) 3.89 (0.16) 2.56 (0.07) Rays (tertiary) 2.05 (0.09) 1.35 (0.22) 4.53 (0.35) 7.88 (0.19) 5.49 (0.29) 5.54 (0.3 I ) Fruit (tertiary) 4.07 (0.21) 3.45 10.13) (0.15) 4.53 (0.221 4.41 (0.5 1 ) 2.83 (0.04) Tuberous root vegetative plants Stem 0.71 (0.08) Dcad caulinc leaves Peduncles I .23 cn.11) 0.93 3.75 3.75 3.62 populations affecting the propensity to flower in the second year of growth. Variation in the length of the vegetative growth phase in so-called ‘biennials’ has been observed by other authors e.g., in Daucus carota (Holt, 19721, Dipsacus fullonum (Werner, 1975a) and Digitalis purpurea (Oxley, in Harper, 1977). Werner (1975a, b) has shown that in field populations of Dipsacus the probability that an individual will die, remain vegetative or flower is correlated with the size attained by the vegetative rosette at the end of the preceding growing season. Flowering occurs only after the rosette has attained a critical size or weight. No such lower limit of plant weight appears to be critical for flowering in Smyrnium. The mean weight of control plants that remained vegetative was considerably greater in the second year than that of plants that had flowered. The ability of vegetative plants to continue to grow was reduced by the removal of half the root system at the end of the first year, but this same deradication had very little if any effect on the weight achieved by those plants that did flower. I t was as if, for plants that flowered, half the root system and the reserves accumulated in it during the first growing season represented luxury RESOURCE ALLOCATION IN SMYRNIUM OLIISATRUM 1 h3 growth and storage. All other treatments greatly reduced the dry weight of flowering plants at Harvest 2. The performance of plants under the heated glasshouse regime was particularly interesting because they maintained a high rate of leaf production but the rate of leaf death was also high; the effect of the “favoured” environmental conditions was to increase the flux or turnover of leaves without increasing the dry weight achieved by the flowering plants. Very few experimental studies have been made to compare the effects of defoliation and deradication but two studies are relevant to the interpretation of the present experiments. Maggs (1964) studied the growth of young apple trees after (a) removing half the foliage; (b) removing half the root system; and (c) treatments (a) plus (b). His most striking result was the failure of severe root pruning to reduce growth. Humphries ( 1 958a, b) examined the growth of barley after very severe root pruning and he also found no reduction in shoot growth. In his experiment with the apple Maggs (1964) found that removal of half the foliage reduced total growth much more than did root pruning. His period of observation was shorter than in the present study of S . olusatrum. Deradication of S . olusatrum in addition to defoliation, had only marginally more affect on plant biomass at Harvest 2 than did defoliation alone. One may infer some fitness value in the ability of plants to continue life and to flower and set ripe seed after deradication or continued defoliation. Natural selection by predators or pathogens may have set the level at which resources are accumulated and stored well above the minimum required for flowering and seed set in a hazard-free environment. There is of course no reason to suppose that evolution optimizes function at the level of the individual. The process of natural selection is the result of variations in individual fitness, i.e., increase in the number of descendants that are left by an individual relative to its neighbours. ‘Over-consumption’ or ‘over-production’ may increase an organism’s fitness so long as this activity deprives neighbours of needed resources. In these experiments 68 to 74% of plant phosphorus was ultimately found in reproductive tissues both in control and deradicated plants. There are few reported studies of phosphorus allocation between plant parts. A study by Williams (1948) showed that in Awena satiwa (an annual) growing at low and medium phosphorus levels, 72 to 78% of accumulated phosphorus was eventually allocated to the inflorescence. In the annual Senecio syluaticus, Van Andel 8c Vera (1977) found that 35 to 57% of accumulated phosphorus was ultimately allocated to reproductive organs by plants grown at the low and medium nutrient levels. They found that the growth of the perennial, Chamaenerion angustfolium was less responsive to nutrient level than S. syluaticus and the allocation of phosphorus to reproductive activities in C. angustfolium was only 15 to 18%. In a study of phosphate allocation in the banana (a perennial) which did not take allocation to roots into account, Twyford 8c Walmsley (1974) found 26% of plant phosphorus was allocated to reproductive organs. The proportion of phosphorus allocated to reproductive organs in the biennial S. olusatrum was therefore considerably higher than that reported for perennials and closer to the values reported in annuals. It was not surprising that higher proportions of plant phosphorus than of total biomass are allocated to reproduction bearing in mind that a large fraction of biomass is represented by non- translocatable structural carbohydrate, whereas phosphorus is one of the elements that remains relatively mobile within plant tissues. 164 J . LOVETT DOUST Only control plants and deradicated plants contained significantly more phosphorus at the fruiting stage than they did at Harvest 1. It is therefore presumed that the defoliated plants (with or without deradication), those grown at low nutrients and those grown in the heated glasshouse, rovided all or most of the phsophorus for their reproductive organs by redistri ! k ution of phosphate already taken up in the first ten months of growth. Figures 1 and 2 illustrate by menas of pie diagrams the proportionate allocation of biomass and of phosphorus among the organs of flowering plants at maturity. Deradication slightly increased the proportion of phosphorus allocated to reproductive structures but defoliation reduced, and deradication with defoliation, the low nutrient treatment and the heated glasshouse treatment, all greatly reduced the proportion of total phosphorus allocated to reproductive structures. In the two defoliated regimes and in the low nutrient regime a very much greater proportion of the phosphorus was retained in the tuberous root system; and under heated glasshouse conditions a large fraction of plant phosphorus was lost in the dead leaves that were accumulated as a result of the very high birth and death rates of leaves on plants growing in this regime. The amounts of phosphorus present in different plant organs reflect in part the different allocations of biomass (dry weight) to the different categories of organ. Measures of the concentration of phosphorus within various organs give a different picture, perhaps more indicative of the extent to which particular structures may be depleted of phosphorus during the process of reallocation at fruit formation. The concentrations of phosphorus in fruits (Table 3) varied only slightly between treatments (between 3.5 and 4.5 mg P/g dry weight) except that under heated glasshouse conditions fruits of low phosphate content were formed. In the control and deradicated plants phosphorus concentrations fell to very low levels in the stem, rays and peduncles but in plants receiving the other treatments, all of which greatly reduced total growth, the concentrations of phosphorus in these organs remained high. This suggests that internal phosphorus concentrations were perhaps limiting during fruit formation in those plants that had grown large and that consequently, during fruit ripening, more completely drained the rays and peduncles of phosphate content than was the case in plants that had made less growth and in which internal phosphate levels might not have been limiting. Phosphate concentration in the tuberous root also declined sharply in control and deradicated plants that flowered, again suggesting that it was in the plants that had grown most vigorously that the vegetative organs were most depleted of phosphate when it was required for ripening of the large amount of fruit formed under these conditions. In marked contrast, the phosphate concentration in the root system did not fall significant?, and in some cases actually increased, in plants that were grown under con itions that greatly reduced plant biomass. Lovett Doust & Harper ( 1980) reported the pattern of resource allocation to stamens, pistils, petals and stylopodia in these plants and showed it to be very fixed in nature. Stebbins (1950) has argued that characters formed by long periods of meristematic activity (for instance total plant size, o r leaf number) will be more subject to environmental influences and are likely to be more plastic than characters formed relatively rapidly (such as floral organs). Clear plasticities in reproductive allocation are known to exist, e.g. in iteroparous plants there may be whole years in which vegetative growth occurs and no flowers are RESOURCE ALLOCATION IN SMYRNIUM OLUSATRUM 165 produced, and Hickman (1975; 1977) has shown that there is some plasticity in the allocation of biomass to reproductive organs in species of Polygonum. The present study indicates that the homeostatic processes in S. olusatrum maintain patterns ofallocation in whole plants only within wide limits ofvariation. Reproduction is a lethal activity in Smyrnium olusatrum. At the time ot fruit formation biomass becomes concentrated in the fruits, and phosphorus more strikingly so. I t is as if demands made on limited resources by the process of fruit filling deplete the plant of resources that might otherwise be used in continued vegetative growth and perennation. Only in those flowering plants that were inhibited in growth by defoliation, mineral deficiency, or the high leaf death rate in the heated glasshouse were relatively high phosphate levels maintained in vegetative structures at the time of flowering. I t might be suggested that internal phosphorus resources were adequate to supply the limited number of fruits formed under these conditions without drawing on the reserves in other tissues. In general those plants that failed to flower and persisted in a vegetative condition also maintained high phosphate concentrations in the vegetative organs. The pattern of resource allocation in S. olusatrum a 'biennial' semelparous species with lethal reproduction, is very similar to that described for the oat (Williams, 1948). The contrast with the perennial iteroparous Chamaenerion angustfolium is striking (Van Andel 8c Vera, 1977). In Chamaenerion a low proportion of phosphorus was allocated to fruits and phosphate concentrations remained high in other tissues. Sufficient resources were left within the plant after flowering to permit renewed vegetative growth and activity in subsequent years. This suggests that the death of monocarpic plants after seed set may be a direct consequence of the depletion of resource levels in the vegetative tissues below that necessary to sustain future meristematic growth. ACKNOWLEDGEMENTS I am grateful to ProfessorJ. L. Harper and Drs L. M. Lovett Doust, P. B. Cavers and M. A. Maun for their helpful suggestions and comments. REFERENCES ALLEN, S. E. (Ed.), 1974.Chemical Analysis ofEcologica1Materials. Oxford: Blackwell Scientific Publications. GREGORY, F. G., 1953.The control of growth and reproduction by external factors. Report of 13th International Horticultural Congress: 96-105. London: Royal Horticultural Society. HARPER, J. L., 1967.A Darwinian approach to plant ecology.Journal cfEcology, 5 j : 247-270. HARPER, J . L., 1977.Population Biology ofPlants. London: Academic Press. HICKMAN, J. C., 1975. Environmental unpredictability and lastic energy allocation strategies in the annual Polygonum cascadense (Polygonaceae).Journal ofEcology, 63: 68f-701. HICKMAN, J. C., 1977. Energy allocation and niche differentiation in four co-existing annual species of Polygonum in western North America. Journal ofEcology, 65:3 11-326. HOLT, B. R., 1972. Effect'of arrival time o n recruitment, mortality, and reproduction in successional plant populations. Ecology, 53: 668-673. HUMPHRIES, E. C., 1958a. The effect of removal of the root-system of barley o n the production of ears. Annals @Botany, NS 22:4 17-422. HUMPHRIES, E. C., 1958b. Effect of removal of a part of the root system o n the subsequent growth of the root and the shoot. Annals ofBotany, NS 22:251-257. LOVEIT DOUST, J. N., 1980. A comparative study of- life history and resource allocation in selected Umbelliterae. BiologicalJoumal ofthe Linnean Society, 13: 139- 154. LOVEIT DOUST, J . N. & HARPER, J. L., 1980.The resource costs of gender and maternal support in an andromonoecious umbellifer, Smyrnium olwatrum L. New Phytologitt. In press. 8 166 J . LOVETT DOUST MAGGS, D. H., 1964. Growth rates in relation to assimilate supply and demand. 1. Leaves and roots as limiting regions. Journal ofExperimenta1 Botany, 1 5 : 574-583. STEBBINS, G . L., 1950. Val.iationandEuolutioninPlantr. Columbia University Press. TWYFORD, 1. T . & WALMSLEY, D., 1974. The mineral composition of the Robusta banana plant. 3. Uptake and distributionofmineralconstituents. PlantandSoil41:47 1-491. VAN ANDEL, J. & VERA, F., 1977. Reproductive allocation in Senecio syluaficus and Chamaernerion angustifohm in relation to mineral nutrition.Journa1 ofEcology, 65: 747-758. WERNER, P. A,, 1975a. Predictions of fate from rosette size in Teasel (Dipsacus fullonum L.) Oecologk 20: 197-201. WERNER, P. A,, 1975b. The biology of Canadian weeds. 12. Dipsacus syluestris Huds. Canadian Journal of Planf Scienre, 5 5 : 783-794. WILLIAMS, R. F., 1948. The effects of phosphorus supply o n the rates of intake ofphosphorus and nitrogen and upon rertain aspects of phosphorus metabolism in gramineous plants. Australian Journal of Scienttfrr Herearch. (81,I: 333-361.
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