Annals of Botany 77 : 179–185, 1996 Resource Capture by Localized Root Proliferation : Why Do Plants Bother ? DAVID ROBINSON Cellular and Enironmental Physiology Department, Scottish Crop Research Institute, Dundee DD2 5DA, UK Received : 7 July 1995 Accepted : 6 October 1995 Using data from a well-known, published experiment [Drew (1975) The New Phytologist 75 : 479–490], the potential exploitation of locally available nutrients by barley roots is calculated. Local proliferation of lateral roots does not necessarily achieve significantly greater exploitation of mobile soil resources like nitrate, but it does for less mobile ones such as phosphate. Despite this, the magnitude of the proliferative response is as great to locally available nitrate as it is to phosphate. This implies an ‘ over-production ’ of roots in response to localized nitrate availability, prompting a re-evaluation of the nature and implications of the response mechanism(s) of roots to soil heterogeneity. # 1996 Annals of Botany Company Key words : Hordeum ulgare, barley, carbon, heterogeneity, lateral root, nitrate, localized nutrient supply, phosphate, proliferation, root. INTRODUCTION The responses of plant roots to the localized availability of soil resources are widely documented. They are a central feature of current thinking about how plants cope with environmental heterogeneity (Caldwell and Pearcy, 1994 ; Hutchings and de Kroon, 1994). Species’ responses to locally available nutrients can differ quantitatively. But, typically, roots proliferate in regions where nutrients are most concentrated and avoid those where nutrients are in short supply (Robinson, 1994 a). The same is true for water (Gallardo, Turner and Ludwig, 1994). This is regarded as an obvious mechanism whereby plants compensate for the variability of soil. At the same time, plants have been considered by many authors (e.g. Givnish, 1986 ; Robinson, 1986 ; KastnerMaresch and Mooney, 1994) to partition their captured resources (including carbon) optimally, achieving maximal returns at minimal cost. Plants less adept than others in this resource balancing act are presumed to be at greater risk of elimination by natural selection. Although never tested experimentally, this remains an implicit justification for many mathematical probings in plant ecophysiology (see Gleeson and Tilman, 1992). If this presumption is correct, plants should respond to locally available nutrients only as long as they obtain a net benefit from so doing. Otherwise, they would be wasteful, partitioning resources nonoptimally : ‘‘… viewing the plant as an ‘ optimal forager ’ can lead to the prediction that in nature plants should vary in physiology and morphology so as to avoid excess foraging for a nonlimiting resource and to maximize effort expended in the acquisition of a limiting resource … The most efficient allocation of foraging effort and thus the greatest fitness for an individual plant result in a morphology and physiology for which no resource is taken up in excess …’’ (Gleeson and Tilman, 1992). To test this idea, I have analysed data obtained in a well0305-7364}96}02017907 $12.00}0 known, published experiment on barley (Drew, 1975). In addition, data collated by Robinson (1994 a) have been further analysed to examine the generality of the conclusions reached from the barley experiment. EXPERIMENTAL METHODS Full details and data are given by Drew (1975). Briefly, barley (Hordeum ulgare cv. Proctor) seedlings were grown in pots of irrigated sand. The pots were divided into three hydraulically isolated compartments, top (A), middle (B) and bottom (C). The compartments were separated by wax membranes through which the five seminal axes of each plant could grow, but not laterals. The top two compartments were 4 cm deep, the bottom, 30 cm. Each pot was 6±8 cm in diameter. The top two compartments each had a volume of 145 cm$. Each compartment was irrigated separately with a nutrient solution at a rate of about 2 cm$ min−". Two treatments will be considered here. In the controls, all three compartments received the full nutrient solution. In the localized nutrient treatment, only the middle compartment, B, received the full solution. The top and bottom compartments, A and C, were supplied with a solution containing one nutrient (P, NO−, NH+ or K) much $ % more dilute than the rest. This had the effect of localizing each nutrient to compartment B. Plants were grown for 21 d, when they were harvested. Dry weights of shoots and roots were measured, as were the lengths of axes and lateral roots in each compartment. Localizing the supplies of P, NO− or NH+ to the middle $ % compartment resulted in proliferations of lateral roots in that compartment, and their suppression in compartments A and C, relative to the controls [see fig. 4 in Drew (1975) ; Table 1]. No proliferation or suppression was caused by supplying K locally. Analysis of variance of Drew’s data showed that there were no significant differences between # 1996 Annals of Botany Company 180 Robinson—Localized Resource Capture T 1. Root length (m per plant) of barley grown for 21 d with uniformly aailable nutrients (control ) or with P or NO− $ supplied only to roots in compartment B, as described in the Experimental Methods section. Data are deried from Table 3 of Drew (1975) and M. C. Drew (pers. comm., 1988). Data for first and second order laterals are combined Locally supplied Root type Axis Lateral Axislateral Pot compartment A B C Total A B C Total A B C Total Control P NO− 0±2 0±2 1±5 1±9 18±5 22±1 16±2 56±8 18±7 22±3 17±7 58±7 0±2 0±2 1±7 2±1 2±2 37±1 7±3 46±6 2±4 37±3 9±0 48±7 0±2 0±2 1±8 2±2 1±4 40±0 2±4 43±8 1±6 40±2 4±2 46±0 $ the relative responses of roots to localized P or NO−. Plants $ grown with locally supplied P had the same total dry weight as the controls ; those in the other treatments were only 71–85 % as heavy. THEORETICAL METHODS General The purpose of this section is to calculate the extent to which roots in the middle compartment in Drew’s (1975) experiment could have exploited the locally available nutrients P and NO−. This was done using the data for root $ growth reported by Drew and by assuming reasonable diffusivities of P and NO−. Theoretically, all ions have $ similar diffusivities in saturated sand (as used in Drew’s experiment), although no experimental evidence for this appears to exist. In soil, however, ion diffusivities are very different, and it is when these differences in mobility among ions occur that the localized growth responses of roots are most likely to be important in nutrient capture. NO− is $ relatively mobile in moist soil ; P, because of its exchange reactions with charged surfaces, diffuses more slowly (Clarke and Barley, 1968 ; Nye and Tinker, 1977, p. 71). The other ions that Drew studied, NH+ and K, are of intermediate % mobility. The analysis presented here, therefore, examines the consequences of the responses measured by Drew had they occurred in soil rather than irrigated sand. Exploitation was estimated as the fraction of the locally supplied volume (compartment B of Drew’s pots) from which roots could have withdrawn P or NO−, following $ Fitter (1987) and Berntson (1994). This fraction is the sum of the volumes of the concentration depletion zones around the roots (Nye and Tinker, 1977, p. 130) and those of the roots themselves, divided by the volume of space in which those roots were growing. When the ‘ exploited ’ volume equals the volume of space containing the roots, any further root growth would give the plant access to relatively little more nutrient. This does not imply that the roots would necessarily have absorbed all the nutrients available to them, only that they would have the potential to do so. This analysis was done in four steps. (1) Calculate the lengths of seminal axes and laterals on day 21 of Drew’s experiment. (2) Calculate root growth rates in compartment B between days 0 and 21, assuming linear and exponential rates of change in the lengths of axes and laterals, respectively. (3) Calculate root radii from Drew’s measurements of root dry weight and the lengths calculated in (1). (4) Calculate the volumes of the depletion zones of P and NO− around the roots in compartment B of locally supplied $ plants. Steps 1–3 were done for control and locally supplied plants ; step 4, for locally supplied plants only. Details of these procedures now follow so that the route from Drew’s original data to the quantities derived from them is as transparent as possible. All symbols are defined in the Appendix. Root lengths at day 21 Seminal axes. Drew reported the length of each root axis, a (cm). The total length of root axis per plant, A, is simply A ¯ na (1) where n is the number of axes per plant (five). It is assumed that axes grow vertically downward. Consequently, the maximum length of an axis in compartments A or B is the depth of that compartment, z (4 cm) and is given by (2) AA,B ¯ nz The length of axis in compartment C is then found by difference : (3) Ac ¯ A®2AA,B Laterals. Drew reported values of Ii, the lengths of laterals (first plus second order) per cm of seminal axis in each compartment, i, of the pot. Thus, the total length of laterals, Li, in patient i is the product of I and the length of axis per compartment : Li ¯ Ii Ai (4) Equations (1)–(4) were used to derive the data shown in Table 1 on which subsequent calculations were based. Root growth rates Seminal axes. It is assumed that axes extend at a constant, linear rate, R (cm d−"). At any time, t (d), therefore, the length of axis per plant is given by A(t) ¯ Rt (5) Values of A measured on day 21 (Table 1) were used to find 181 Robinson—Localized Resource Capture T 2. Parameter alues obtained as described in the Theoretical Methods section Locally supplied Parameter Symbol Rate of change of axis length R Time for axes to enter compartment B Rate of change of lateral length in B Specific root length Mean root radius Ion diffusion coefficient tB r λ o D per plant per axis large small R for control and locally supplied plants (Table 2). These values seem reasonable. Rose (1983) quoted 2 cm d−" per axis of barley in nutrient solution. The time, tB, at which the axes entered compartment B is given by (6) tB ¯ zInR Laterals. It is assumed that the length of laterals in compartment B, LB, increased exponentially from the moment that axes entered from compartment A. An equation that describes this behaviour is LB(t) ¯ exp[r(t®tB)]®1 (7) d−"). where r is the rate of change in lateral length (cm [The ®1 in eqn (7) ensures that at t®tB ¯ 0, L ¯ 0 also.] Equation (7) implies a linear increase in the logarithm of root length. Robinson and Rorison (1983) found such an increase for the roots of three grass species receiving localized supplies of N in nutrient solution. The dry weight of barley roots supplied locally with P showed the same trend (Drew and Saker, 1978). As before, r was found using values of LB measured on day 21 (Table 1) ; these are given in Table 2. Total root length in compartment B. Total root length in compartment B at any time, t, is the sum of the lengths of axes and laterals in that compartment : TB(t) ¯ AB(t)LB(t) (8) Equation (8) was used to generate daily cohorts of root length from which ion depletion zones were calculated (see below). The total length of roots in a cohort produced in compartment B on day t is the difference between the lengths on successive days, i.e. χB(t) ¯ TB(t)®TB(t®1) (9) Root radii Drew did not report root radii. As a best approximation, mean radii, o (cm), were calculated from cylindrical geometry and Drew’s measurements of root dry weight and length by (10) o ¯ 1}oπλφρ where λ is the ratio of root length (cm) and dry weight (g), the specific root length, in other words (Table 2). ρ is the Units Control P NO− cm d−" cm d−" d cm d−" cm g−" cm cm# s−" cm# d−" cm# s−" cm# d−" 9±05 1±81 2±21 0±410 0±044 0±008 9±86 1±97 2±03 0±433 0±055 0±008 5¬10−) 0±004 5¬10−* 0±0004 10±22 2±04 1±96 0±435 0±040 0±009 5¬10−' 0±432 5¬10−( 0±043 $ specific gravity of root tissue (assumed to be 1 g cm−$), and φ is the dry weight : fresh weight ratio of root tissue (assumed to be 0±1). Values of o produced by eqn (10) are shown in Table 2 ; these varied little among treatments. Ion depletion zones The radius of the notional outer boundary of a depletion zone, x (cm), of an ion diffusing to a cylindrical sink, the root, in a porous medium can be approximated by (Nye and Tinker, 1977, p. 231) : x(τ) ¯ o2oDτ (11) τ is the time (d) since the cohort of roots was produced, and since they started exploiting nutrients, and distinct from t, the time since the start of the experiment. In other words, τ is t®t where t is the time when the roots were produced. ! ! Equation (11) calculates the root-mean-square displacement of a diffusing substance (Nye and Tinker, 1977, p. 136). Statistically, some of the substance will have moved from a distance greater than x cm after τ s. So, eqn (11) calculates an ‘ average ’ radius of depletion. Moreover, eqn (11) applies strictly to diffusion to a planar sink rather than to a cylinder. Comparing eqn (11) with a more exact equation published recently by Syring and Claassen (1995) gave, however, a mean discrepancy between the two of only ³16 %, depending on time and diffusivity. D is the ion’s diffusion coefficient in soil (cm# d−"), assumed constant. Rather than assume a single value, it was felt safer to assume a large and small D for each ion. This allowed upper and lower limits to be put on the volumes exploited. For NO−, Clarke and Barley (1968) reported D in $ a moist sandy soil of 5¬10−' cm# s−". When diffusion was impeded by drying, D fell to one tenth of this value. These were taken to be the large and small values of D for NO−. $ For simplicity, I assumed that P diffused two to three orders − of magnitude more slowly than NO in the same system, i.e. $ values of D of 5¬10−* to 5¬10−) cm# s−" were assumed for P. This is a generous assumption, as the diffusivity of P in soil has been measured to range from 10−"% to 4¬10−* cm# s−" (data compiled by Fitter and Hay, 1987, p. 85). Equation (11) assumes that ions are absorbed as soon as roots are produced. It also assumes that roots suffer no physiological impairment or developmental change that 182 Robinson—Localized Resource Capture (t) ¯ π[x(τ)]#χB(t) (12) Therefore, the total volume, V(t) (cm$), of the depletion zone up to time t is the sum of the volumes around each cohort produced up to that time : t V(t) ¯ 3 (t) (13) tB Values of V(t) were calculated until V " 145 cm$, the volume of compartment B, or until t " 21 d, the duration of the experiment. RESULTS The time-courses of exploitation of the middle compartment, B, in Drew’s (1975) experiment are shown in Fig. 1. For NO−, full exploitation occurred after only 4±5–11±5 d, $ depending on the mobility of the ion. Full exploitation of P was also probable after 18 d, but only if a large diffusion Fractional exploitation 1 0.8 0.6 0.4 0.2 0 3 6 9 12 Time (days) 15 18 1 Fractional exploitation might limit absorption. This is a reasonable assumption for the time-scale of Drew’s experiment and for the young cereal plants he used. Equation (11) also implies no overlap of adjacent depletion zones until the soil becomes fully exploited. Overlap could be included only with a more sophisticated mathematical description of the growth of the root system. That of Rose (1983) would be particularly useful as it was based partly on data obtained for barley root systems, but ones grown in nutrionally uniform nutrient solution rather than non-uniform sand. Different forms of the equations used here would generate different timecourses of exploitation. This is a point of detail that would require even more assumptions (both conceptual and numerical) that Drew’s (1975) data cannot (and were not designed to) support. The volume, (t) (cm$), of the depletion zone formed around each cohort of roots in compartment B at any time since the cohort was produced is : 0.8 0.6 0.4 0.2 0 3 6 9 12 Time (days) 15 18 21 F. 2. As for Fig. 1, but assuming that root growth in response to locally available NO− or P was the same as in control plants receiving $ uniformly concentrated supplies of nutrients. coefficient was assumed. With the smaller value of D, only 33 % of full exploitation of P was possible by the end of the experiment. We now ask : what would have happened had no proliferation greater than that in the control occurred in the middle compartment ? This question was addressed by replacing LB in eqn (8), for both P and NO−, with the length $ of laterals measured in compartment B of the controls. This generated the same, smaller value of r for both treatments (Table 2). The result is in Fig. 2. The time-courses of exploitation of NO− would have barely differed from those $ in Fig. 1. Full exploitation of NO− would have been delayed $ by only 0±5 d compared with Fig. 1. That of P would have been delayed by up to 1 d. With the smaller D, only 21 % of full exploitation would have been possible after 21 d without the localized proliferation of roots. Taking this line of thought to its logical conclusion we can now ask, What would have happened had no laterals been produced in compartment B ? The plant would then have had to exploit the nutrients in the middle compartment via only its five seminal axes. This question was addressed by simply assigning a value of zero to LB in eqn (8). This biologically improbable event would have had no effect on the exploitation of NO− if D was large (Fig. 3). Full $ exploitation would have been delayed by up to 3 d, compared with Fig. 1, with a small diffusivity. For P, however, the complete absence of laterals would have been disastrous, with hardly any exploitation possible, whatever value of D was assumed. Only a maximum of 13 % of full exploitation would have been possible with a large D, and one-tenth of this with the smaller D. 21 F. 1. The fraction of the locally available nutrient exploited by barley roots in Drew’s (1975) experiment, calculated using eqn (1), as described in the text. (——) NO− ; (– – – – – –) P. The upper curve for $ each nutrient is calculated using the larger diffusivity given in the text and Table 2 ; the lower with the smaller diffusivity. The time axis refers to the number of days’ growth of the barley seedlings. DISCUSSION The impact of localized root proliferation on local exploitation of P and NO− $ The necessity for the production of extra lateral roots to exploit supplies of locally available P is clear from Fig. 1. Robinson—Localized Resource Capture obtained from data collated by Robinson (1994 a). These data were from many published experiments in which control plants received uniformly enriched supplies in nutrients, as in Drew (1975). On average, therefore, roots do not respond morphologically any less to locally available NO− than they do to P. This, and the results shown in Figs $ 1–3, suggests that responses to locally available NO− are $ likely to be superfluous for effecting the capture of that − NO . $ What is the reason for this ? Without firm details of the underlying physiological mechanisms, the best answer one can give is to offer arguments for various possible explanations in the hope that they stimulate deeper inquiries. Fractional exploitation 1 0.8 0.6 0.4 0.2 0 3 6 9 12 Time (days) 15 18 21 F. 3. As for Fig. 1, but assuming no production of lateral roots in either treatment. T 3. The size, as a percentage of that in uniformly supplied controls, of roots locally supplied with or depried of NO− or P. Data are from Tables 2 and 3 (for NO− and P) and $ $ Figs 2 and 3 (for P only) of Drew (1975) for barley, and compiled from numerous original sources by Robinson (1994a) Reference Drew (1975) Robinson (1994 a) 183 Nutrient NO− $ P P NO− $ P P Roots supplied with nutrient Roots deprived of nutrient 135 181 0±11, n.s. 158 198 0±28, n.s. 49 58 0±84, n.s. 61 65 0±65, n.s. ‘ Size ’ was measured as dry weight, length or number. Statistics were derived from a single factor analysis of variance on log-transformed data ; n ¯ 3 for NO− and 7 for P (Drew, 1975) ; n ¯ 64 for NO− and 72 $ $ for P (Robinson, 1994 a). After 21 d, root proliferation exploited up to 57 % more P compared with the control (33 % of full exploitation in Fig. 1 ; 21 % in Fig. 2). The effect was greatest at small diffusivities and diminished as D increased. Such a necessity for the proliferation of lateral roots is less obvious for the exploitation of locally available NO−. The necessity for any $ laterals to exploit NO− is similarly obscure (Fig. 3). What is $ clear is that axes alone are quite inadequate for effective exploitation of P. It takes no great insight to reach these conclusions, predictable qualitatively since Bray (1954), so they are hardly new findings. But from Fig. 1 and the ‘ optimality ’ principle outlined in the Introduction, one might be tempted to predict that the response of roots to locally available NO− $ would be smaller than that to P. This prediction does not accord with the evidence. Table 3 shows that there was no difference between the root responses of barley to the localized P and NO− $ treatments in Drew’s (1975) experiment. Statistics similar to these are also presented in Table 3 for other species, The response is non-specific The first possibility is that the mechanisms whereby plants detect and respond morphologically to significant variations in nutrient availability may not be subtle enough to discriminate one ion from another. Any ionic imbalance, provided that it is large enough and the plant’s demand for the ion is big enough, may trigger effectively the same ‘ allor-nothing ’ response. That happened in Drew’s (1975) experiment. Both NO− and P elicited an ‘ all ’ response, and $ K nothing, at least in terms of localized root growth. Once initiated, perhaps the proliferative response continues as a developmental ‘ cascade ’, similar to that which leads to the hairy root syndrome when roots are infected with the Ri plasmid from Agrobacterium rhizogenes. What then could switch off the cascade ? Drew (1975) suggested that the eventual exhaustion of a locally available nutrient signals the end of further proliferation. Another way of putting this is that proliferation stops when the spatial imbalance in ionic activity among the regions containing the root system is reduced below a certain threshold. The design of Drew’s pots, with the continual renewal of nutrient supplies, prevented this from happening. This would also apply to the vast majority of similar experiments, done in replenished nutrient solutions (see Robinson, 1994 a). But in soil, a localized supply of nutrients will eventually be exhausted by the roots, microbes, or chemical and physical processes and could, therefore, switch off the proliferative response. However, there is evidence that root proliferation in soil continues after a locally available source of nutrients is exhausted. Van Vuuren, Robinson and Griffiths (1995) grew wheat roots through a layer of rapidly decomposing organic matter in otherwise N-deficient soil. Root proliferation occurred most markedly during the last third of the experiment. Then, only negligible amounts of NO− and NH+ were available to those roots and differed $ % little from the concentrations of these ions in bulk soil. If the morphological response of roots to a locally available supply of nutrients is so non-specific, and if it is to ever genuinely benefit a plant expressing it, the response must be capable of improving the exploitation of the least mobile nutrients in soil. Then, the exploitation of more mobile nutrients by a response of that magnitude would be inevitable but inefficient as more roots would be produced than would be needed. This seems to be what happens in barley. The evolution of a non-specific response system 184 Robinson—Localized Resource Capture sufficient to exploit only mobile resources would be useless for the capture of less mobile ones. Such non-specificity in response to variations in nutrient supply does not apply to processes involved in transporting ions into root cells. When a nutrient is localized, or withheld for a time then re-supplied, its rate of uptake per unit of root is stimulated (see Robinson, 1994 a, b). This effect is generally restricted to the nutrient whose supply has been varied ; the uptake of other, uniformly available, nutrients is unaffected (Drew and Saker, 1978 ; Lee, 1982 ; Jager, 1985 ; Robinson, Linehan and Gordon, 1994). Roots operate in a multi-ion enironment In soil solution, the concentrations of individual ions are coupled electrochemically to those of all the others. Large changes in concentration of one ion may cause simultaneous changes in the concentration of another ion. For example, additions of NH NO to soil releases K and P from % $ exchange sites, transiently increasing the concentrations of these ions in the soil solution (Yanai et al., 1996). If a root meets a localized concentration of an ion that is otherwise sparsely available, it is likely that it will meet an improved availability of other ions, too. A morphological response capable of opportunistically exploiting such localized variations in availability would, as discussed above, have to be capable of capturing the least mobile nutrients to be effective. Roots eoled in a competitie enironment An individual may gain as much by reducing the resource capture by a neighbour as it would by maximizing its own capture of the resource. Then, the speed of full exploitation would be an important factor, rather then the physiological efficiency with which exploitation is achieved. If effective, such mechanisms might be expected to evolve in many taxa because those that did not express the response would be more likely to be evolutionarily disadvantaged. In my survey of 41 species (Robinson, 1994 a), all expressed some growth (or suppression of growth) response in their roots to locally available nutrients. Roots do not operate independently of shoots Jager (1985) found a close association between the concentrations of P and N in maize shoots and the growth stimulation of roots locally supplied with P or NO−. When $ the concentrations of P and N were restored to, respectively, 70 and 90 % of those in uniformly supplied control plants, root proliferation in the nutrient-rich zone was suppressed. This did not happen when K or Ca were supplied locally. Jager found responses similar to those of maize in Plantago major and P. lanceolata, but not P. media, when they were supplied locally with P. Internal controls, related to the shoot concentration of, or sink strength for, some locally supplied nutrients may exert as strong an influence on root development as do external factors such as ion concentration and distribution. Shoots may also influence roots through the supply of carbon. Modifications to the rooting medium affect, by unknown mechanisms (Jackson, 1993), stomatal conductances, rates of leaf expansion, and therefore, rates of carbon gain by the plant. Localization of nutrients seems to have a transient effect on shoot growth, but one that is felt long after the initial response to the localization. The data of Drew and Saker (1978), for example, suggest an interruption in the dry weight gain of barley shoots after P was supplied locally to the root system. The interruption must have occurred within 3±4 d of the P being localized (3±4 d being the time between the start of localization and the first harvest). Relative growth rates of shoot dry weight were subsequently similar to those of control plants (0±18 d−" in controls and 0±17 d−" in locally supplied plants). But shoot dry weights of locally supplied plants were ultimately (after 29 d growth) only 81 % of those of controls. Shoots of locally supplied plants may be smaller than those of controls, therefore, whereas total dry weights of root systems may be similar (Drew, 1975 ; Drew and Saker, 1978). If so, net rates of carbon export from shoots must be greater per unit shoot dry weight in locally supplied plants than in controls. Carbon export may also be greater per plant, as Lambers et al. (1982) found for wheat supplied locally with NO−. The likelihood is, therefore, of the $ concentration (or flux density) of soluble carbon being greater in the phloem of locally supplied roots than in control roots. This, together with the external signal of the locally available nutrients, may trigger (and sustain ?) lateral root proliferation near unloading regions (cf. Oparka, Prior and Wright, 1995). Many models of shoot–root relationships assume that carbon can be used as a notional currency with which to assess the value to the plant of alternative physiological traits (e.g. Givnish, 1986 ; Fitter, 1991). For anything to be a currency, it must be in relatively short supply and difficult for many individuals to secure in great quantity. The notion that carbon meets these requirements in autotrophic plants has recently been challenged by Thomas (1994). He put forward the provocative view that most terrestrial plants exist in a surfeit of fixed carbon, a legacy of the assimilatory systems that evolved before the colonization of land. Once on land, plants were able to capture far more carbon than could be used to combine with the relatively meagre supplies of N, P and other nutrients available to them from soil. Processes that removed excess carbon from taking part in further assimilatory activities might, therefore, occur with little detriment to the plant’s chances of survival. ‘ Looked at this way ’, wrote Thomas, ‘ even roots invite reinterpretation. What better way of disposing of fixed carbon than by burying it where it cannot make more assimilatory biomass ’ ! If Thomas is right, the use of carbon in producing apparently superfluous roots may, despite prevailing views of the physiological costs involved, carry only a negligible cost evolutionarily. 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Van Vuuren MMI, Robinson D, Griffiths BS. 1995. Nutrient inflow and root proliferation during the exploitation of a temporally and spatially discrete source of nitrogen in soil. Plant and Soil (in press). Yanai J, Linehan DJ, Robinson D, Young IM, Hackett CA, Kyuma K, Kosaki T. 1996. Effects of inorganic nitrogen application on the dynamics of the soil solution composition in the root zone of maize in a Scottish soil. Plant and Soil (in press). APPENDIX Symbol φ ρ A a A, B, C χ D λ L I n o R r T t τ tB t ! V x z Definition Dry weight : fresh weight ratio of root tissue Specific gravity of root tissue Length of root axes per plant Length of each root axis Subscripts, refer to compartments A, B and C of the pots used by Drew (1975) Total length of axes and laterals in a cohort of roots produced on a particular day Ion diffusion coefficient in the rooting medium Specific root length Length of lateral roots per plant Length of lateral roots per unit length of root axis Number of root axes per plant Mean root radius Rate of change of axis length Rate of change of lateral length in compartment B Total length of axes and lateral roots per plant Time since the start of the experiment Time since a given cohort of roots was produced Time for axes to enter compartment B Time when a certain cohort of roots is produced Volume of the ion depletion zone around a particular cohort of roots Total volume of the ion depletion zone around all cohorts of roots at a certain time Radial distance (from the centre of the root) of the notional outer boundary of the ion depletion zone Depth of compartments A and B Units g cm−$ cm cm cm cm# s−" cm g−" cm cm cm−" cm cm d−" cm d−" cm d d d d cm$ cm$ cm cm
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