Journal of Experimental Botany, Vol. 49, No. 318, pp. 59–68, January 1998 Ontogenic changes in the construction cost of leaves, stems, fruits, and roots of tomato plants Christian Gary1,5, Jacques Le Bot2, Jean-Sylvain Frossard3 and Jerônimo Luiz Andriolo4 1 Institut National de la Recherche Agronomique, Unité de Bioclimatologie, Domaine St-Paul, Site Agroparc, F-84914 Avignon Cedex 9, France 2 Institut National de la Recherche Agronomique, Unité de Recherches en Ecophysiologie et Horticulture, Domaine St-Paul, Site Agroparc, F-84914 Avignon Cedex 9, France 3 Institut National de la Recherche Agronomique, Unité Associée Bioclimatologie-PIAF, Site de Crouël, 234 avenue de Brézet, F-63039 Clermont-Ferrand Cedex 2, France 4 Universidade Federal de Santa Maria, Centro de Ciências Rurais, Departamento de Fitotecnia, 97119–900 Santa Maria, RS, Brasil Received 31 January 1997; Accepted 3 September 1997 Abstract The construction cost of a plant tissue, i.e. the amount of photoassimilates used in the synthesis of a unit weight, varies with its biochemical composition. Crop modellers use standard values published for a few groups of cultivated species. Yet, there are also intraspecific variations in the construction cost in relation with the development of the plant or organ. This research aimed at analysing the ontogenic changes in the construction cost of leaves, stems, roots, and fruits of tomato plants and the specific contribution of the mineral content to these changes. For that purpose, samples were harvested from the vegetative phase to the beginning of fruit production. The estimation of the construction cost was based on the contents of carbon, nitrogen and ash. In leaves, the construction cost decreased with the physiological age whereas, in stem internodes, it varied with the sympod number. These ontogenic changes could partly be explained by different accumulations of minerals. In contrast, the construction cost and the mineral content of fruits and roots remained fairly stable. On a whole plant basis, the construction cost of the bulk of each category of organs varied much less. Most of the increase in the mean construction cost of the whole plant during the experiment was due to changes in the allocation ratio between the vegetative parts and the fruits. Attention of crop modellers is drawn to the importance of a precise estimation of the construction cost and to the existence of ontogenic changes at the whole plant and organ levels. Key words: Lycopersicon esculentum Mill., construction cost, mineral content, ontogeny, carbon content. Introduction In crop models, the net production of assimilates is converted into an increment of dry matter through a parameter C named ‘construction cost’ and generally expressed in grams equivalent glucose per gram dry matter, or through a parameter Y named ‘growth yield’ g that is the inverse of the construction cost (for an inventory of the terminology used in this field, see Gary et al., 1995). The construction cost varies with the composition of the synthesized plant material. For example, a unit weight of lipids is made from about 2.5 times more glucose than a unit weight of carbohydrates as an extra amount of glucose has to be metabolized to produce the higher amounts of reducing power (NADH ) and energy (ATP) that are involved in the synthesis of the former. Tables of values of the construction cost are available in the literature for a limited number of species. For vegetative organs ( leaves, stems), typical values of construction cost have been proposed by Penning de Vries et al. (1989) for the bulk of three groups of species: leguminous crops, rice crops and ‘non leguminous except rice’ crops. For storage organs, as there is more variation in their bio- 5 To whom correspondence should be addressed. Fax: +33 4 90 89 98 10. E-mail: [email protected] © Oxford University Press 1998 60 Gary et al. chemical composition, Penning de Vries et al. (1983) calculated median construction costs for 23 species on the basis of proximal analyses found in the literature. Information on the construction cost of tomato tissues is still scarce. The values presently used in tomato crop models (Bertin and Heuvelink, 1993) have generally been considered as close to the mean value for ‘non-leguminous except rice’ species for the vegetative parts (1.46, 1.51 and 1.44 g g−1 for leaves, stems and roots, respectively) and to the estimation of Penning de Vries et al. (1983) for fruits that is based on a reference of chemical composition for mature fruits (1.42 g g−1). Recent estimations (Gijzen, 1994; Gary et al., 1998) showed that the construction cost of tomato tissues are actually lower than these standard values. For tomato vegetative tissues, this is due to a high mineral content, at least as high than those observed in rice crops (0.15 g g−1 in Penning de Vries et al., 1989), and in the case of tomato fruits, it is due to an overestimation of the content in energy-rich compounds ( lignin, estimated from the fibre content). In their estimations of the construction cost of plant tissues, crop modellers have focused on interspecific variations although there is some evidence that intraspecific variation is not negligible. It can be linked either to environmental factors (Griffin, 1994; Poorter, 1994) or to the development of the crop or organ. At the whole plant level, Stahl and McCree (1988) clearly gave evidence of an increase of the growth yield throughout the development cycle of a grain sorghum crop. They concluded that this was the result of changes in the allocation ratios between various organs: during the crop cycle, there is a shift from the synthesis of leaves and roots to the synthesis of stems, sheaths and grains. The first are richer in proteins and their construction cost is higher. This hypothesis was integrated in a sorghum crop model (McCree, 1988). The use of specific construction costs for each class of organs enabled a better simulation of experimental data than the use of a single constant construction cost. At the organ level, there are also ontogenic variations in the biochemical composition (cf. for example the studies of Merino et al., 1984, on leaves of chaparral shrubs and Walton and de Jong, 1990, on kiwifruit berries) that induce changes in their construction cost. Changes in mineral content also need to be accounted for: VarletGrancher (1982) carried out a comprehensive study of the time-course of the heat of combustion and of the ash content of the various organs of maize plants. He observed a simultaneous decrease in the ash-free heat of combustion and in the ash content during the development of ears and leaf blades and sheaths. The decrease in the dilution of organic biomass by minerals compensated for the decrease in the energy content of organic biomass, which explained a fairly stable construction cost of the biomass. The estimations of the construction cost of tomato tissues published in Gijzen (1994) and Gary et al. (1998) were obtained on plants in production, i.e. composed of a set of about eight sympodial units with leaves, stem internodes and fruits of different physiological ages. Even though organs of different age classes were present on the plants, the question of the ontogenic changes of the construction cost at the scale of the whole plant was not fully addressed by these authors. In the present study, samples of leaves, stems, fruits and roots were analysed five times during the 2 months from the end of the vegetative phase until the beginning of harvest of tomato plants in order to (1) be able to observe possible ontogenic changes in the construction cost during the development of several sympodial units and (2) analyse the contribution of the mineral content in these changes. These observations were carried out during the time when the plant experienced major changes in the pattern of dry matter allocation. It must be stressed that the expected information was not the construction cost of new biomass at specific points of time that is needed in crop models. It was the energy value (in equivalent glucose) of the biomass accumulated since the appearance of the analysed organs, i.e. the cost of synthesizing biomass possibly altered by subsequent changes (e.g. storage, translocation, turn-over of some compounds). Such estimations of the construction cost were based on the contents in carbon, nitrogen and ash, an approach proposed by Vertregt and Penning de Vries (1987) and modified by Walton et al. (1990), Poorter (1994) and Gary et al. (1995). Ontogenic changes in the construction cost of organs could be observed, particularly in leaves where they could be associated with the accumulation of minerals. At the whole plant level, ontogenic changes of the construction cost could be linked to changes in the allocation ratio of biomass among vegetative and generative organs. Because of the sensitivity of the dry matter production to the construction cost in crop models, the importance of estimating its actual value and possible sources of variation is stressed. Materials and methods Cultivation of plants and preparation of samples Tomato seeds (Lycopersicon esculentum Mill. cv. Rondello) were sown in small rockwoll cylinders on 5 February 1993. After three leaves had appeared, the seedlings were transplanted under a greenhouse located in southern France (INRA, Avignon). The plants grew in a recirculating hydroponic system made of series of 10 l pots linked with a 2 m3 reservoir and in which the nutrient solution continuously circulated. The composition in the major elements of the nutrient solution was 4.0 mol m−3 KNO , 0.9 mol m−3 K SO , 1.5 mol m−3 KH PO , 3 2 4 2 4 3.75 mol m−3 Ca(NO ) , and 1.0 mol m−3 MgSO . pH was 3 2 4 checked daily and controlled to 5.5–6.0 using HNO . The 3 composition of the nutrient solution in the major cations and anions was determined twice a week by atomic absorption spectrophotometry and HPLC in order to identify the drifts in the mineral balance. Temperature set-points were 20 °C during Ontogenic changes in construction cost the day and 16 °C at night. The development of plants was sympodial and indeterminate. All axillary buds were removed so that sympodial units made of three leaves and one inflorescence (or truss) appeared successively, once every 8–10 d, along the single stem. The pruning policy was to keep four fruits per truss and remove all axillary buds. Three plants were harvested every 2 weeks from flowering until harvest of the first inflorescence (or truss), i.e. from the end of the vegetative phase until the beginning of the production period. At the end of the experiment, the tenth truss (on top of the canopy) was setting fruits while fruits on the first truss (in the bottom of the canopy) were maturing. In each sympodial unit, all fruits were pooled in one ‘fruit’ sample, all leaf blades in one ‘leaf ’ sample and all stems and petioles in one ‘stem’ sample. The first sympodial unit was split in two fractions: the first truss with the surrounding leaves (two under and one above the truss) and the corresponding internodes belonged to sympod unit 1 and all the leaves and internodes appeared before belonged to sympod unit 0. The physiological age of the sympodial units was expressed in number of trusses from the truss that was setting fruits at the moment of plant harvest. All samples were dried in an air-forced oven at 70 °C during 72 h, except the fruits which were dried for up to a week. They were subsequently ground to about 60 mm. Determination of the carbon, nitrogen and mineral content Carbon and nitrogen contents were determined on the three replicas wheareas mineral content was on one only. Total carbon and nitrogen contents were measured directly on plant samples using an automatic elemental analyser (Carlo-Erba model 1500, Milan, Italy). The analysis was performed on 4 mg aliquots after a flash combustion at 1030 °C in a pure oxygen atmosphere. After reduction of all carbon and nitrogen oxides by copper at 750 °C, carbon dioxide and free nitrogen gas were separated by gas chromatography and analysed by thermal conductivity. A residual moisture determination was carried out on aliquots (24 h at 105 °C ) to enable the carbon and nitrogen results to be converted to a 100% dry matter basis. Nitrate concentration in the plant tissues was measured on water-extracted samples using an automatic chemical analyser (Quanta, Nice, France) based on the principle of reduction of NO− into NO− by a mixture of copper/hydrazine sulphate, 3 2 and subsequent reaction with sulphanilamide and NNED to form a coloured compound absorbing light at 520 gm. Cation concentration determinations ( K, Ca, Mg) in the plant tissues were carried out on 500 mg aliquots after dry combustion in a muffle furnace for 12 h at 420 °C, dissolution of the ashes in 0.1 N HNO and dilution to 50 ml in volu3 metric flasks. The determination was performed on an atomic absorption spectrophotometer (Perkin-Elmer 2100, Uberlinger, Germany). The ash content was measured by weighing the whitish-grey ashes remaining from this dry combustion. It gave a biased estimation of the mineral content. In these experimental conditions, there was certainly no more organic material after combustion: Gurakan et al. (1990) showed that samples of microbial biomass burnt over 450 °C contain no more carbon, hydrogen and nitrogen. Yet organic acids can be transformed in carbonates and some elements like sodium, chloride or sulphur may volatilize at high temperatures (Masle et al., 1992). To estimate the mineral content from the ash content, several corrections have been suggested in the literature. Vertregt and Penning de Vries (1987) proposed an approximation of the mineral content based on the hypothesis that inorganic ions and organic anions would have the same weight and that the latter would be transformed into carbonates during ashing with 61 a weight reduction of 50%; consequently, the weight of minerals would be 2/3 of the weight of ashes. Poorter and Bergkotte (1992) subtracted to the ash content a value (in g g−1) equal to 30 times the ash alkalinity (in meq g−1) to correct for oxides. When using the latter method, Gijzen (1994) obtained the mineral content by reducing the ash content by 2% (in stem tissues) to 18% (in leaf tissues). Masle et al. (1992) compared the ash content of plant material to the sum of the concentrations of all mineral elements above trace level measured by X-ray spectrometry. On wheat leaves, the ash content overestimated the mineral content by about 20% yet large variations were observed among genotypes. On tomato tissues, Gary et al. (1998) compared the ash content to the complement of the fraction of organic material (carbon+hydrogen+oxygen+ nitrogen contents). If the ash content overestimated the mineral content by about 15% in leaves, it was similar to it in stems and underestimated it in fruits. On the basis of the present uncertainty about the proper correction to apply to the ash content, it was decided to present the results on the basis of the measured ash content and to discuss when needed the consequences of the subsequent ovestimation of the mineral content on these results. Calculation of the construction cost The construction cost C (g g−1) was calculated from the heat of combustion DH (kJ g−1) ( Williams et al., 1987), here c estimated from the carbon content c∞ (mol g−1), and the nitrogen content n∞ (mol g−1): A B 180.15 1 1 DH + kn∞ (1) c E 15.65 24 G E is the growth efficiency, i.e. the fraction of the energy G retained in the products during the biosyntheses of the various compounds of the biomass. Its mean value was estimated to be 0.88 by McDermitt and Loomis (1981). k is the valence of nitrogen in the substrates used for biosyntheses; it was set here to −3 as ammonium was considered to be the only source of nitrogen. Coefficients 15.65 and 180.15 are the heat of combustion (kJ g−1) and the molar mass (g mol−1) of glucose, respectively, and 24 is the number of electrons involved in the oxidation of one mole glucose. The heat of combustion of the organic matter can be estimated from its carbon content with the linear relation retained for tomato tissues in Gary et al. (1998) and recalculated from Walton et al. (1990); for dry matter (organic matter+minerals), this relation becomes: C= DH =(1−A)[648.5c∞/(1−A)−7.333] (2) c where A (g g−1) is the mineral content. This method of estimating the construction cost is based on the approach proposed by Vertregt and Penning de Vries (1987) to which a correction for the reduction status of nitrogen was added, as suggested by Poorter (1994) and Gary et al. (1995). For this correction, only the organic nitrogen (total N minus nitrate N ) values presented in Andriolo (1995) were considered. Results Dry matter partitioning From the flowering of the first truss to the beginning of harvest, the growth of the tomato plants presented a fairly classical pattern. In 8 weeks, i.e. from the first to the fifth plant harvest, the ratio of dry matter allocation 62 Gary et al. increased from 0 to 41% for fruits and decreased from 41% to 25% for leaves and from 40% to 25% for stems. In the meanwhile, the ratio of dry matter allocation to roots decreased from 18% to 8% with a decrease in dry weight during the last 2 weeks. Mineral content The ash content was lower in fruits (the mean value was 0.10 g g−1) than in vegetative organs (in leaves, stems and roots, the mean values were 0.22, 0.17 and 0.17 g g−1, respectively). It varied more in leaves than in stems, roots and fruits. In leaves and on all sympodial units, there was an accumulation of minerals with time, at least until 6 May as the profiles of ash content were fairly similar on 6 and 18 May ( Fig. 1A). In contrast, the ash content of stems varied less with time (except between 25 March and 8 April ), but remained higher in the first sympods than in the others ( Fig. 1B). In fruits, the ash content did not vary either with the physiological age of the organ or with its position on the plant (Fig. 1C ). The root system presented a high content in minerals all along the experiment ( Fig. 2). Despite the ontogenic increase in ash content of leaves, the mean ash content per plant did not vary more in leaves than in the other organs during the experiment ( Fig. 2). The cumulated content of K, Ca and Mg represented about half the ash content in all the samples. Mg content was lower than 0.01 g g−1 whereas K and Ca contents attained 0.09 g g−1 in stems and 0.08 g g−1 in roots, respectively. In leaves, Ca content increased with the ash content and was higher than K content whereas in stems and roots K content increased with the ash content and was higher than Ca content ( Fig. 3). In fruits, K content was much higher than Ca content. Carbon content The carbon content was higher in fruits (the mean value was 0.44 g g−1) than in vegetative organs (in leaves, stems and roots, the mean values were 0.38, 0.36 and 0.37 g g−1, respectively). In leaves and on all sympods, the carbon content decreased with time until 6 May and then stabilized (Fig. 4A). In stems, the carbon content was lower in the first sympods than in the others ( Fig. 4B). In fruits ( Fig. 4C ) and roots ( Fig. 2), it remained fairly stable all along the experiment. There was clearly a relation between the variations in ash and carbon content. When expressed per unit organic biomass (dry matter minus ashes), the carbon content presented less changes either with the physiological age or with the position of the organ: the standard deviation lowered from 2.6 to 1.5 g g−1 in leaves, from 2.7 to 2.1 g g−1 in stems and increased slightly in fruits, from 1.0 to 1.4 g g−1. Similarly, when expressed per unit organic biomass, the carbon content presented Fig. 1. Ash content in leaves (A), stems (B) and fruits (C ) of tomato plants. Sympods 1 to 10 include two leaves under and one leaf above the truss and the corresponding stem internodes; sympod 0 includes all the leaves under sympod 1. (&) 25 March; (%) 8 April; (+) 22 April; (6) 6 May; ($) 18 May. Ontogenic changes in construction cost Fig. 2. Time-course of the ash (closed symbols) and carbon (open symbols) contents of the bulk of leaves (+), stems (&), roots (2) and fruits ($) between the end of the vegetative phase and the beginning of harvest of tomato plants. Carbon content=mean±95% confidence interval. Fig. 3. Relations between the ash content and the contents in K (closed symbols) and Ca (open symbols) in leaves (+), stems (&), roots (2) and fruits ($). less differences among organs (the mean values were 0.49 g g−1 in fruits and leaves and 0.44 and 0.45 g g−1 in stems and roots, respectively). Because of the relative stability of the carbon content in the organic biomass and of the mean ash content at the whole plant scale, the mean carbon content of the bulk of leaves, stems and fruits varied by less than 0.03 g g−1 (Fig. 2). Fig. 4. Carbon content in leaves (A), stems (B) and fruits (C ) of tomato plants. Sympodial units 1 to 10 include two leaves under and one leaf above the truss and the corresponding stem internodes; sympodial unit 0 includes all the leaves under sympodial unit 1. Each value is the mean of three replicates. (&) 25 March; (%) 8 April; (+) 22 April; (6) 6 May; ($) 18 May. 63 64 Gary et al. Construction cost The measurements of carbon, nitrogen and ash content enabled the calculation of the construction cost for the various tissues. The content in reduced nitrogen in the organic biomass decreased with the physiological age of the organ in leaves (from 0.06 to 0.04 g g−1) and stems (from 0.03 to 0.02 g g−1) and remained constant in fruits (0.03 g g−1) and roots (0.04 g g−1). The construction cost of leaves decreased significantly (P<0.05) with their ageing whereas it remained fairly constant in stems (Fig. 5) and roots ( Fig. 7) and slightly increased in fruits ( Fig. 5). These trends were linked to the different dynamics of mineral accumulation in the various groups of organs. More generally, the differences in construction cost among organs, age classes and sympodial units could partly be explained by differences in ash content ( Fig. 6). When expressed on an ash-free basis, the construction cost of leaves increased significantly (P<0.05) with ageing. This trend actually depended on the method of calculating the mineral content from the ash content. When the rule proposed by Vertregt and Penning de Vries (1987) was adopted (mineral content= 2/3 ash content), there was no ontogenic variation in the construction cost of the organic fraction of the leaf biomass (Fig. 5). At the scale of the whole plant, the ontogenic changes in the construction cost were buffered (Fig. 7). During the time of the experiment, the construction cost of the bulk of leaves decreased as the number of aged leaves increased and the construction cost of the whole stem increased as the ash content of the last internodes decreased. But the mean construction cost of the whole plant increased more because of the increasing generative/ vegetative weight ratio than because of the ontogenic changes observed in each group of organs. This is proved by the comparison with the time-course of the construction cost of the whole plant that is calculated from constant values (mean of the five plant harvests) of the construction cost of each group of organs and from the allocation ratios of biomass ( Fig. 7). Discussion Ontogenic changes in construction cost at the organ and whole plant levels This study has verified that the construction cost of the vegetative organs of tomato plants is fairly low, compared to other species. On plants in production (harvested at a later development stage than in the present study), Gijzen (1994) found mean values of the construction cost of 1.16, 1.10 and 1.57 g g−1 for leaves, stems and mature fruits, respectively whereas Gary et al. (1997) estimated these mean values to be 1.05, 1.02 and 1.27 g g−1 for leaves, stems and fruits, respectively. In both publications, the estimation of the construction cost was based on the carbon content. Gijzen (1994) applied Vertregt and Penning de Vries’ method (1987) designed for high carbon content tissues instead of that of Walton et al. (1989) better adapted to low carbon content tissues, which certainly led to an overestimation of the construction cost (by 0 to 7%) and the mean values reported here from his work do not take into account the relative weight of the various age classes of organs in the whole plant. The construction cost of the vegetative organs of tomato plants is in the lower 10% of the data compiled from a large number of sources by Poorter (1994) for leaves, stems, roots, and seeds/fruits of herbaceous and woody species (for comparison, our data were recalculated with NO− as the N-source, i.e. k=+5 in Equation 1) whereas 3 the construction cost of fruits is among the upper 10%. Ontogenic changes in the construction cost appeared clearly at the scale of the organ. In the case of tomato leaves, the decrease of the construction cost with the physiological age was mainly linked to the accumulation of minerals. Such an approach of the time-course of the energetic value of each organ class on a plant is probably original. Merino et al. (1984) measured the biochemical composition and estimated from it the construction cost of five age classes of leaves on three chaparral shrubs. In two species, they observed an ontogenic decrease of the construction cost of leaves. They could show that, on this plant material, such a decrease was explained both by an accumulation of minerals and by a shift from the synthesis of costly compounds ( lipids) to the synthesis of cheap structural compounds (cellulose and hemicellulose). Walton et al. (1990) carried out a similar approach on kiwifruit berries and showed that the construction cost decreased when organic acids accumulated then increased during the formation of the seeds and the synthesis of their lipid reserves without any significant contribution of the ash content that remained low. These examples show that the analysis of the ontogenic changes in the construction cost of organs cannot be done without a clear separation of the respective effects of changes in the mineral content and of changes in the composition of the organic fraction. The present uncertainty in the estimation of the mineral content from the ash content does not facilitate such an analysis. At the scale of the whole plant, the changes in the Fig. 5. Ontogenic changes in the construction cost of leaves (A), stems (B) and fruits (C ) of tomato plants, calculated on a dry weight basis (closed symbols) or on an organic basis (open symbols). In the latter case, the mineral content was calculated as 2/3 of the ash content ( Vertregt and Penning de Vries, 1987). The physiological age was calculated as the number of trusses from the truss setting fruits (which is aged 0). Mean±95% confidence interval. Ontogenic changes in construction cost 65 66 Gary et al. (1982) observed on whole maize plants that variations in the heat of combustion depended either on changes in the allocation of biomass (when grain formation started ) or on changes in the ash content (during the panicle differentiation). Then the patterns of ontogenic changes in the construction cost of the whole plant and the contribution of the mineral content vary among species. Dilution of the organic matter by the accumulation of minerals in greenhouse tomato crops Fig. 6. Relation between the ash content and the construction cost of leaves (6), stems (%), roots (1), and fruits (#). Full line: regression for leaf samples ( y=−0.85×+1.24, R2=0.66). Dotted line: regression for stem samples ( y=−2.05×+1.34, R2=0.72). Fig. 7. Time-course of the mean construction cost of the bulk of leaves (+), stems (&), roots (2) and fruits ($) and of the whole plant (bold line) between the end of the vegetative phase and the beginning of the production period of tomato plants. The dotted line is the construction cost of the whole plant calculated from the mean construction cost of each group of organs (on the five plant harvests) and from the allocation ratios of biomass. construction cost of tomato plants were mainly attributed to the time-course of the allocation ratio of dry matter. This pattern could be observed in our experiment as the plants transited from the vegetative phase to the beginning of fruit production. Later in the crop cycle, when the plants are maintained in a steady-state with the development of new trusses and leaves compensated by the harvest of mature fruits and the pruning of old leaves, there should be no more changes in the construction cost of the whole plant. Similarly, Stahl and McCree (1988) attributed ontogenic variations in the construction cost of grain sorghum plants to changes in the allocation ratio of dry matter among organs. But Varlet-Grancher et al. This study confirms that high amounts of minerals accumulate in tomato, and particularly in the vegetative organs. Such a feature has been observed on other greenhouse crops such as cucumber (Challa, 1976; Marcelis and Baan Hofman-Eijer, 1995; Schapendonk and Challa, 1981), sweet pepper and eggplant (Gijzen, 1994) yet it is fairly unusual among plant tissues. The values published (Gijzen, 1994; Gary et al., 1998) or measured in this study for tomato organs are close or belong to the upper 10% of the compilation of data published by Poorter (1994). The highest value measured on shoots of 24 wild species by Poorter and Bergkotte (1992) was 0.16 g g−1. Masle et al. (1992) measured on leaves of field crops maximal values of 0.11 g g−1 in sunflower, 0.09 g g−1 in wheat and 0.15 g g−1 in tobacco. In their study, the mineral contents varied by 18–35% among genotypes and by 10% or less under environmental changes (vapour pressure deficit and nutrient availability). The reasons why tomato plants, and other greenhouse crops, accumulate relatively larger quantities of minerals in their tissues than plants grown in the soil, still remain unclear. The mineral content in the plant results from the balance between the demand of the growing organs and the ability of the root system to absorb nutrients. In the present study, plants were grown in a hydroponic system on a nutrient solution with a composition close to those encountered in commercial greenhouses, i.e. with concentrations in elements generally higher than the standard Hoagland solution. There is a relation between the availability of nutrients in the root medium and their concentration in plant tissues (shoots and roots of various species in Pitman, 1988; tomato leaves in Seresinhe and Oertli, 1989). The range of concentrations of K and Ca we observed fits with the values reported by Pitman (1988) for the highest concentrations of these elements in the nutrient solution. The accumulation of minerals in ageing leaves indicates that the balance between import from the xylem, growth and export to the phloem changed with ontogenesis. But, at present, no rationale can be proposed to explain and, further, model the dynamics of accumulation of minerals in the various organs of tomato plants. Such high mineral contents dilute the organic matter and lead to the observed low construction costs. There is indeed a negative correlation between the ash content Ontogenic changes in construction cost and the energy content of biomass; the ash content is even used as a predictor of the heat of combustion of biomass in fuel engineering (Jenkins, 1989). Which coefficients of construction cost should be used in tomato crop models? The discrepancy between the few estimations of the construction cost of tomato organs (this paper, Gijzen, 1994; Gary et al., 1998) and the standard values that have been used until now by tomato crop modellers (Bertin and Heuvelink, 1993) questions the use of standard values when starting on a new species. Furthermore, interspecific variations can be significant, because of changes either in the biochemical composition and/or in the mineral content of organs. Various methods are available for the estimation of the construction cost; on the same samples, they produce values that may differ by up to 10% ( Walton et al., 1990). Any error in the estimation of the construction cost will have direct consequences in crop models on the calculation of the dry matter production from the net assimilation rate of CO . 2 The process of conversion of photoassimilates into biomass is quite fundamental and deserves at least as much attention and experimental effort as the other processes (such as photosynthesis and dry matter partitioning) during the calibration of a crop model. In this study, the analysis of the ontogenic changes in the construction cost differed at the organ and whole plant levels. If a tomato crop model aims at simulating the growth of the bulk of a category of organs (vegetative and generative organs or leaves, stems, roots and fruits), using a mean construction cost for each category is possible. It provided in the present study a satisfactory estimation of the construction cost of the whole plant ( Fig. 7). At the scale of the organ, ontogenic changes in the construction cost of leaves were observed. If a tomato crop model is designed to simulate the growth of individual organs or sympodial units, then it should take into account these ontogenic changes. In that case, two difficulties have to be overcome. First, the estimations of the construction cost are based on the analysis of tissues that are the result of the integration of growth during a period of time, whereas the crop model needs at each time step a conversion factor for the increment of biomass. Such a conversion factor should integrate possible changes in the composition of the organic fraction of the new biomass (it has been shown that they are fairly limited, Fig. 5) and in the accumulation of minerals (information on its dynamics is still scarce and descriptive). Second, changes in the composition of an organ may be due to the remobilization of some compounds from other organs and their synthesis should not be accounted for twice (Stahl and McCree, 1988). The present status of our knowledge in this field limits the ability of crop models to simulate small units within the plant. 67 Acknowledgements We are grateful to Claude Sarrouy for building the experimental set-up, to Béatrice Brunel for growing plants and preparing samples and to Monique Bonafous, Magali Augé and Laurent Gomez for analysing them carefully. During this research, Jerônimo Andriolo received a Brazilian CAPES fellowship. Nadia Bertin is acknowledged for her critical reading of the manuscript. References Andriolo JL. 1995. Analyse des flux de NO− , H O et CO au 3 2 2 cours de la culture et du nycthémère chez la tomate (Lycopersicon esculentum Mill.) adulte en hors-sol. Thèse de Doctorat, Université de Montpellier II, 101. Bertin N, Heuvelink E. 1993. 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