Journal of Experimental Botany, Vol. 55, No. 396, pp. 525±534, February 2004 DOI: 10.1093/jxb/erh049 RESEARCH PAPER Impact of temperature on the arbuscular mycorrhizal (AM) symbiosis: growth responses of the host plant and its AM fungal partner A. Heinemeyer* and A. H. Fitter Department of Biology, University of York, PO Box 373, York YO10 5YW, UK Received 22 September 2003; Accepted 21 October 2003 Abstract The growth response of the hyphae of mycorrhizal fungi has been determined, both when plant and fungus together and when only the fungus was exposed to a temperature change. Two host plant species, Plantago lanceolata and Holcus lanatus, were grown separately in pots inoculated with the mycorrhizal fungus Glomus mosseae at 20/18 °C (day/night); half of the pots were then transferred to 12/10 °C. Plant and fungal growth were determined at six sequential destructive harvests. A second experiment investigated the direct effect of temperature on the length of the extra-radical mycelium (ERM) of three mycorrhizal fungal species. Growth boxes were divided in two equal compartments by a 20 mm mesh, allowing only the ERM and not roots to grow into a fungal compartment, which was either heated (+8 °C) or kept at ambient temperature. ERM length (LERM) was determined on ®ve sampling dates. Growth of H. lanatus was little affected by temperature, whereas growth of P. lanceolata increased with temperature, and both speci®c leaf area (SLA) and speci®c root length (SRL) increased independently of plant size. Percentage of colonized root (LRC) and LERM were positively correlated with temperature when in symbiosis with P. lanceolata, but differences in LRC were a function of plant biomass. Colonization was very low in H. lanatus roots and there was no signi®cant temperature effect. In the fungal compartment LERM increased over time and was greatest for Glomus mosseae. Heating the fungal compartment signi®cantly increased LERM in two of the three species but did not affect LRC. However, it signi®cantly increased SRL of roots in the plant compartment, suggesting that the fungus plays a regulatory role in the growth dynamics of the symbiosis. These temperature responses have implications for modelling carbon dynamics under global climate change. Key words: Acaulospora, arbuscular mycorrhiza, belowground carbon allocation, compartment experiment, extraradical mycelium, global climate change, Glomus, niche separation, soil warming. Introduction Arbuscular mycorrhizal (AM) fungi, all members of the Glomales (Glomeromycota), form a symbiosis with about two-thirds of plant species (Fitter and Moyersoen, 1996) and occur in almost all terrestrial ecosystems (Trappe, 1987; Tinker, 1975). However, only some 150 AM fungal species have been described so far (Redecker et al., 2000), in contrast to the over 250 000 known plant species. Yet typically 20±30 species of AM fungi occur in most plant communities, so that AM fungal a-diversity seems to be quite similar to that of plants in the same community (Fitter, 2001). Niche separation between AM fungal taxa might therefore be expected (Bever et al., 2001), yet almost nothing is known about their response to different environmental conditions, which would be required for an evaluation of such an hypothesis. The role of AM fungi in nutrient uptake (Clark and Zeto, 2000) and carbon cycling (Smith and Read, 1997) has been widely recognized. Potential host plants differ in their dependency on the AM fungus, most likely due to their different root system architecture (Newsham et al., 1995; Hetrick et al., 1991) and thus different ability to acquire highly insoluble nutrients such as phosphate (Koide, * To whom correspondence should be addressed. Fax: +44 (0)1904 43 2898. E-mail: [email protected] Journal of Experimental Botany, Vol. 55, No. 396, ã Society for Experimental Biology 2004; all rights reserved 526 Heinemeyer and Fitter 1991). However, as obligate symbionts, all AM fungi rely on host plant carbon (Smith and Read, 1997) and mycorrhizal colonization increases sink strength of the root (Harris and Paul, 1987; Wright et al., 1998). Any impact on plant carbon ®xation and growth might have direct impacts on this carbon allocation to the rootcolonizing AM fungi (Same et al., 1983), with a consequent feedback on the host plant due to changes in fungal functions such as nutrient uptake or other bene®ts (Fitter et al., 2000). On the other hand the fungus itself might respond to any environmental changes directly, independently of any effect on the host plant (Fitter et al., 2000) and, consequently, might also affect host root morphology (Hooker et al., 1992). Global climate is predicted to change dramatically over the next century (Houghton et al., 2001). The effect of elevated CO2 on plant growth has been studied in detail, and current evidence suggests that impacts on AM fungi are likely to be indirect responses, mediated via changes in plant growth (Staddon and Fitter, 1998). There is less certainty about potential temperature impacts on plant communities, despite a predicted rise in global mean temperature of about 3 °C over the next century (Houghton et al., 1995). Due to acclimation responses to temperature, root growth seems to be more affected by PAR (photosynthetically active radiation) than by temperature (Aguirrezabal et al., 1994; Fitter et al., 1999). Temperature responses of AM fungi have not been investigated intensively if compared to studies on elevated CO2. The mycelium of an AM fungus in effect comprises two linked mycelia, the internal root-colonizing hyphae and the extra-radical mycelium (ERM): the ERM is likely to experience the wider variation in soil parameters such as pH and nutrient levels, exploring soil pores inaccessible to roots (Smith and Read, 1997) and nutrient patches in the upper organic-rich soil horizons (Tibbett, 2000; Hodge et al., 2001) where there are higher temperature ¯uctuations than in deeper soil horizons. Apart from work on spore germination (Daniels Hetrick, 1984) and internal colonization (Jakobsen, 1986), the few studies of temperature response to date were not designed to separate effects on the fungus from those on the plant (Fitter et al., 2000). More recently, compartment studies have been used to investigate differences in nutrient uptake of the ERM among AM fungal species (Jakobsen et al., 1992). This approach has not previously been used to detect direct temperature effects on the ERM. Successful prediction of impacts of global climate change on ecosystem functioning must take into account the AM symbiosis and, in particular, the ERM, which links above- and below-ground carbon cycling (Smith and Read, 1997) and will be crucial in supplying the possible higher nutrient demands of the host plant under a changing climate (Fitter et al., 2000). In order to determine the responsiveness of AM fungi to temperature, three hypotheses were tested: (1) a species more heavily colonized by mycorrhizal fungi (here Plantago lanceolata) will respond more to temperature and shading treatments than one less colonized (Holcus lanatus); (2) when plant and fungus are exposed to different temperatures, changes in plant growth will mainly determine any fungal response; (3) warming the extra-radical mycelium stimulates its growth independently of stimulated plant growth. Two experiments were carried out: one in pots where plant and fungus experienced the same temperature, was designed to test hypothesis 1; the other was a compartment study, where fungal temperature was varied independently of the plant and tested hypotheses 2 and 3. Materials and methods Experiment 1 Experimental design: Eighty 10 cm pots were each planted with two seeds (Emorsgate Seeds, Norfolk, UK) of either Plantago lanceolata L. or Holcus lanatus L. and kept for 28 and 26 d, respectively, in a growth chamber (Percival A32L, Percival Scienti®c Inc., Iowa, USA). Conditions in the growth chamber were 20/18 °C (day/night), 60±80% RH and a mean photosynthetically active photon ¯ux density (PPFD) of 250 mmol m±2 s±1 at plant level for 16 h d±1. Pots were thinned to one seedling after 2 weeks. The growth medium consisted of 380 g (dry weight) of a 1:1 mixture (v/v) of coarse builders' dried silica sand and terragreenâ (an attapulgite clay soil conditioner, Turfpro Ltd, Staines, UK). This was evenly inoculated (40 g kg±1 growth medium) with dried fungal inoculum of Glomus mosseae (Nicol. & Gerd.) Gerd. & Trappe (isolate UY282), consisting of c. 1 cm pieces of maize roots in the same medium. Although this medium does not re¯ect natural soil it enabled a more uniform nutrient supply and was necessary to measure hyphal length accurately. The measurement of hyphal length is very dif®cult in soils with organic matter, since hyphae penetrate and bind together the particles. Plants were re-randomized weekly inside the chambers and watered daily with tap water. Half-strength Rorison's nutrient solution (Hewitt, 1966) containing only 1/20 of the normal concentration of phosphate was given weekly (2.5 ml per pot) from day 21. Temperature was recorded every 30 min (averaged 5 min readings) with thermistor probes at 1 cm depth (Grant Instruments Ltd, Shepreth, UK) and PAR ¯ux measured weekly at plant level using a light meter (SKD210, Skye Instruments Ltd, Powys, UK). There were six sequential destructive harvests and four replicates. After the ®rst harvest, which was at 26 and 28 d after planting (dap) for Holcus and Plantago, respectively, half of the pots of each plant species were transferred to an identical growth chamber under the same growth conditions, but with a temperature of 12/10 °C (day/ night). P. lanceolata harvests occurred at 28, 52, 59, 66, 73, and 80 dap and H. lanatus at 26, 33, 40, 47, 59, and 82 dap. Plant measurements At harvest, plants were extracted from the pots, collecting as much growth medium as possible for fungal measurements (see below), and were then divided into root and shoot fractions. Total fresh weight (FW) of leaves and roots and leaf area (AL) were recorded after cleaning of remaining growth medium. Dead leaves were removed beforehand, dried, and later added to the total plant weight (WRS). Roots were chopped into c. 1 cm pieces in a 500 ml beaker Mycelial growth, mycorrhizas, temperature, and light ®lled with 400 ml water and mixed with a glass rod. Four subsamples were taken from this pool twice at random, one for measurement of root length (LR) and subsequently root dry weight (WR) and another for root length colonization (LRC). Fresh weight of shoots and of the root subsamples were re-measured, then shoot material and root subsamples were dried at 70 °C for 3 d and their dry weight (WS and WR) recorded. Leaf area and LR were calculated using a ¯at bed scanner (Hewlett Packard, USA) and images were later analysed with the program Winrhizoâ (ReÂgent Instruments, Quebec, CAN). Speci®c leaf area (SLA) and speci®c root length (SRL) were both calculated. Remaining growth medium was kept overnight at 8 °C for extraction of fungal hyphae the following day. Fungal measurements The four root subsamples for mycorrhizal assessment were pooled. Roots were cleared at room temperature in 20% KOH (2 d), acidi®ed in HCl (30 min), stained with 0.1% acid fuchsin (3 d) (as in Kormanik and McGraw (1982) but omitting phenol), and were left in a destain solution for a further 3 d. Mycorrhizal colonization was assessed under a compound microscope (Optiphot-2, Nikon Inc., Melville, U.S.A.) at 3200 magni®cation using epi¯uorescence (Merryweather and Fitter, 1991). Scoring followed McGonigle et al. (1990) with a minimum of 100 intersections. The percentage of intercepts where hyphae are present is termed root length colonized (LRC). In addition, intercepts where arbuscules (LRCarb) or vesicles (LRCves) were visible were scored separately. From each growth medium sample, three subsamples were taken and their FW obtained, one for oven-drying to calculate the FW:DW ratio of the medium and two for extraction of extra-radical mycelium (ERM). A modi®ed membrane ®lter technique (based primarily on Abbott et al., 1984; Jakobsen et al., 1992; Sylvia, 1992) was used for the extraction. The growth medium sample was made up to 500 ml with tap water, then stirred full speed with a magnetic stirrer (Voss Instruments Ltd, Maldon, Essex, UK) for 4 min. Before settlement, 200 ml were quickly transferred to a tall beaker stirred at full speed then at 40% of full speed, allowing larger particles to sediment. After stirring, two 5 ml samples were quickly taken with a syringe, centrally, about 1 cm from the surface. Each sample was placed in a ®lter funnel (diameter 19 mm) ®tted with a 0.45 mm mesh nylon membrane (MSI, Westboro, MA, USA), attached to a vacuum pump (N740.3FT.18, KNF, Germany). When the ®lter was totally dry, the funnel was removed and a few drops of the staining solution were applied to the ®lter. After a short drying period the ®lter was removed from the ®lter-holder and placed in the dark. After about 1 h the ®lter was rinsed and dried under vacuum, then mounted on a labelled slide in destaining solution under a coverslip. Four ®lters were thus obtained from each pot. Assessment of ERM length (LERM) per ®lter was carried out by the gridline intercept method (Miller and Jastrow, 1992) for a minimum of 50 ®elds of view at 3125 magni®cation (Jenamed 2, Zeiss, Leipzig, Germany) using a 10310 grid of 1 cm side length (Graticules Ltd, UK). The hyphal lengths per ®lter were then converted to hyphal densities (m g±1 DW growth medium), assuming all hyphae to be mycorrhizal (pots without inoculum revealed no colonization). For subsequent analysis, the mean value for the four ®lters obtained per plant was used. Experiment 2 Experimental design: Twelve open-top Perspex boxes (233233 10 cm) were divided into halves using a Perspex plate (3 mm). These halves were then each further divided into two compartments (A and B) with nylon mesh (pore size diameter 20 mm, Staniar P/No. 25T1120), allowing passage only of extra-radical hyphae and not roots into fungal compartment B. The entire box was ®lled with a dried silica sand and terragreenâ growth medium (as above) and vertically inserted loops of a soil-warming cable (Macpennyâ Cameron, East 527 Riding Horticulture, Sutton-on-Derwent, UK) were inserted vertically in the fungal compartment B at a 7.5 cm distance from the mesh. After germination on moist ®lter paper (Whatmanâ No. 1) for 2 d (20 °C in the dark) two P. lanceolata seedlings (supplier as in Experiment 1) were planted in the middle of each compartment A, 3.5 cm from the mesh, and thinned to one seedling per compartment after 2 weeks. The 24 compartments A were evenly inoculated (50 g kg±1 growth medium) with dried fungal inoculum of one of three AM fungi contrasting in the amount of ERM produced: (a) G. mosseae ((Nicol. & Gerd.) Gerd. & Trappe, isolate UY 282, ex P. Bonfante, Torino-Trotta, I.), (b) Glomus hoi (Berch & Trappe; isolate UY 110, Welburn, GB) and (c) Acaulospora sp. (isolate UY 991, Elphin, GB, ex C Walker, likely to be A. laevis) (all provided by J Merryweather, University of York, UK) and consisting of c. 1 cm pieces of a P. lanceolata, Trifolium pratense L., and Sorghum sp. (Sudan grass) root mixture within the same growth medium). Although the three AM fungal species originated from various places in Europe, all species have been cultivated for many years under similar growth conditions at the University of York collection. Boxes were placed in walk-in chambers (Southern & Redfern Ltd., Bradford, UK) over the ®rst 3 weeks at 20/17 °C (day/night), 60±80% RH, and a mean PPFD of 350 mmol m±2 s±1 at plant level for 16 h d±1. Over 125 d on ®ve occasions growth medium samples with four replicates each (one from each replicate hyphal compartment) were taken for each fungal species and temperature treatment combination. Temperature was recorded in the growth medium for both compartments (in four boxes per temperature treatment) at similar distances from the mesh every 10 min. (averaged 30 s readings) with thermistor probes (as in Experiment 1) and PPFD measured weekly at plant level. Compartments A and B were watered daily with tap water. From week three onwards a half-strength Rorison's nutrient solution (Hewitt, 1966) was given weekly (12.5 ml) to compartment A (containing 1/20 phosphate) and B (containing 1/10 phosphate), except within 1 cm of the mesh. For this procedure plant compartment A was always watered ®rst; all compartments were subsequently watered with tap water to remove nutrient solution from the leaves. The ®rst sampling after 20 dap represents the beginning of the treatment and over the following 15 weeks the temperature in the growth chamber was maintained at 12/10 °C (day/night). Over this period one end of the fungal compartment B was either kept at ambient temperature or heated (giving each four replicates per treatment) to approximately 8 °C above ambient temperature at sampling position for each fungal species. Heating fungal compartment B did not affect the temperature of the plant compartment A (Fig. 1). Any moisture differences between heated and unheated compartments B were limited by manually watering all the compartments at least three times per day. Plant measurements On the last sampling day, plants were extracted from compartment A and divided into root and shoot fractions. Analysis followed as described for Experiment 1. Fungal measurements On each sampling day a growth medium core (9 cm depth 3 1.5 cm in diameter) was taken from compartment B, but in a random location along an arc 8.5 cm from each shoot base, at approximately 4.5 cm distance from the mesh. Samples were taken at identical positions in compartments B and used for ERM extraction (as described for Experiment 1); the sample area was then re®lled with the same growth medium, gently compressed and watered with nutrient solution. Root samples were stained and investigated for LRC as described in Experiment 1. In this study both clearing (10 min) and staining (35 min) were conducted in a waterbath 528 Heinemeyer and Fitter Fig. 1. Experimental design for the compartment experiment. The entire box was divided into two equal halves by a 20 mm mesh (M). Plant position (PP), sample area position (SP), and heating cable position (HC) are indicated with arrows. Data are means (bars indicate minima and maxima) of the medians of the four replicates per temperature treatment (open symbols: ambient; ®lled symbols: heated) measured in the growth medium at different distances from the mesh in either plant compartment (A) or fungal compartment (B) after heating was switched on (different distances between thermistor probes of ambient and heated treatments were due to number of probes available and box position determining cable length). The lines shown are best ®t polynomials (dashed line: ambient, R2=0.87; solid line: heated, R2=0.94). (80 °C). To improve staining results, samples were acidi®ed and stained twice. The percentage of LRC and also LRCarb and LRCves were scored (see above). Statistical analysis Analysis was performed in SPSS v6.1 (Norusis, 1994). All data were checked and transformed appropriately (e.g. arcsine transformation for percentage values and mostly log or square root transformation for other parameters, however, data were presented as back transformed data in most tables and ®gures) to normalize skewed distributions before statistical analysis and data were also checked for equality of variance (Levene's test in SPSS); no cases were encountered where data could not be made suitable for ANOVA. In Experiments 1 and 2 plant growth data were all analysed with a twoway ANOVA (temperature and harvest or temperature and fungal species as factors); species differences in Experiment 2 were also named by Bonferroni's multiple comparisons test. The F-ratio method was used to test for signi®cant difference of ®tted regression lines (Sokal and Rohlf, 1981) if data were plotted against plant biomass. Data for ERM growth in Experiment 2 were tested for any treatment effects with the repeated measurement design of the general linear model (GLM), with species and temperature as between-subject factors. These data were also tested with a one-way ANOVA, with treatment as the only factor, in order to detect signi®cant treatment effects for individual species at particular harvests. Since the ERM of Acaulospora sp. was very low (<0.2 m g±1 DW growth medium), apart from the last sampling time, these data were excluded from the GLM-analysis. Furthermore, in one compartment of each Glomus species and in two different treatments of Acaulospora sp. roots had grown through the mesh into the fungal compartment B; these data were also excluded from further analysis. Results Temperature impact in experiment 1 Growth of H. lanatus was only slightly affected by temperature over the experimental period of 56 d. Only leaf area (AL) and root length (LR) were signi®cantly higher at 20 °C than at 12 °C (Table 1), although the mean plant dry weight (WSR) was 40% greater in the 20 °C treatment. Length of colonized root (LRC) and of extraradical mycelium (LERM) were both very low, did not differ between temperature treatments, and declined after initially peaking between 33 and 40 dap (<10% and <0.8 m g±1, data not shown) to less than 2% and 0.5 m g±1 at the last harvest (Table 1); the root length colonized by arbuscules (LRCarb), was always very low (Fig. 2A). Total LRC was nearly three times higher in the 20 °C treatment (Table 1). Growth of P. lanceolata was greater at the higher temperature after 52 d (Table 1). Similar differences were observed for AL and LR (Table 1). Colonization of roots was 25±30% by the end of the experiment. Both LRC and LERM increased over time and total LRC was nearly three times and LERM almost twice as large under the higher temperature (Table 1). The percentage LRCarb increased over time to about 25% (Fig. 2A) and was signi®cantly higher in the 20 °C than in the 12 °C treatment (P <0.05). Percentage LRCves also showed a signi®cant treatment effect during an initial peak between 28 and 52 dap with values of 2% and 5% for the 12 °C and 20 °C treatments, respectively, but thereafter declined to about 1% in both treatments (Fig. 2B). There were signi®cant differences in the morphology of P. lanceolata as measured by increased SLA and SRL (Table 1) and these were direct responses to increased temperature. Even though both SRL and SLA showed a pronounced ontogenetic drift, the effect of temperature was independent of plant biomass as shown by analysis of covariance. There was a signi®cant difference in the ®tted regression lines of both SRL and SLA on ln biomass between the temperature treatments (Fig. 3). The same analysis revealed that LERM was greater at 20 °C than at 12 °C at a given plant biomass (Fig. 4A), but there was Mycelial growth, mycorrhizas, temperature, and light 529 Table 1. Temperature effects on plant growth and colonization of roots (LRC) and extra-radical mycelium length (LERM) of Glomus mosseae grown in symbiosis with either Holcus lanatus or Plantago lanceolata in the pot experiment Data are the means 6 SE at the last harvest for plant biomass (WRS), leaf area (AL), speci®c leaf area (SLA), root length (LR) and speci®c root length (SRL), LRC, total LRC, LERM, and LERM per pot per unit LR (LERM/LR) or unit total LRC (LERM/total LRC) for either at 12 °C or 20 °C grown H. lanatus or P. lanceolata plants, respectively. Signi®cances between temperature treatments are based on a two-way ANOVA. n.s., not signi®cant, *P <0.05, **P <0.01, ***P <0.001. WRS (g) AL (cm2) 2 ±1 SLA (cm g ) LR (m) SRL (m g±1) Temperature Plant growth (n=4) °C H. lanatus 12 20 12 20 12 20 12 20 12 20 0.960.3 n.s. 1.360.3 45.360.3* 82.9611.2 200.1613.0 n.s. 220.5627.2 162.4646.5* 216.4627.0 323.6612.1 n.s 319.6615.9 Fungal growth (Glomus mosseae) (n=4) P. lanceolata * 0.460.0 0.560.1 19.261.7** 37.964.5 105.562.7* 171.321.3 23.663.2** 49.469.6 0.4611.6** 0.568.4 H. lanatus Total LRC (m) LRC (%) ±1 LERM (m g soil) LERM/LR (m m±1) LERM/total LRC (m m±1) P. lanceolata * 1.360.6 3.661.3 1.060.4 n.s. 1.560.5 0.460.1 n.s 0.560.0 1.160.4 n.s. 0.960.1 81.8610 n.s. 74.5617.8 5.560.5* 14.563.9 24.463.5 29.564.6 1.160.2 2.160.1*** 18.262.9 n.s 17.663.0 80.9618.6 n.s. 71.2621.4 P = 0.086 Fig. 2. Effects of temperature on mean percentage of root colonization of (A) arbuscules (LRCarb) or (B) vesicles (LRCves) in either Plantago lanceolata (diamonds) or Holcus lanatus (triangles) roots at the six harvests (days after planting, dap) 6SE (standard error, n=4). Temperature treatments were either 12 °C (open symbols) or 20 °C (®lled symbols) and started after the ®rst harvest. Signi®cances between treatments based on a two-way ANOVA differed only for P. lanceolata and were as following: (A) harvest: F5,36=3.14, P=0.019; temperature: F1,36=4.42, P=0.043; (B) harvest: F5,36=5.96, P <0.001; temperature: F1,36=5.91, P=0.020; there were no other signi®cant differences for either treatment or interaction terms. no temperature effect on LERM if it was expressed per unit LR or LRC (Table 1). Even though %LRC did not differ signi®cantly between treatments (P=0.086) (Table 1), the large difference in total LRC was still evident when plotted as a function of plant biomass (Fig. 4B), with similar-sized plants having greater total LRC at 20 °C than at 12 °C, indicating a direct response to increased temperature. Effect of temperature in the compartment experiment 2 Heating the fungal compartment B did not affect growth of P. lanceolata, although it did alter root morphology: SRL was higher for plants grown with hyphae connected to a heated fungal compartment (Table 2). However, plant growth did respond to the fungal species. Overall plants had the highest biomass if grown with Acaulospora sp. (Table 2). Percentage LRC and %LRCarb declined in the order G. mosseae >G. hoi >Acaulospora sp., but heating the fungal compartment B had no effect on any measure of colonization in the root compartment A (Table 2). LERM increased progressively during the experiment (Fig. 5) with a lag phase prior to colonization of the fungal compartment B, that differed in duration among the species, followed by a phase of more or less exponential increase. At all times hyphal length differed between species (GLM, P <0.001) and in the order G. mosseae >G. hoi >Acaulospora sp. Further, LERM was signi®cantly 530 Heinemeyer and Fitter Fig. 3. Effects of temperature on (A) speci®c root length (SRL) or (B) speci®c leaf area (SLA) of Plantago lanceolata at all harvests against ln plant biomass. Temperature treatments were either 12 °C (open symbols and dashed line) or 20 °C (®lled symbols and line). The lines shown are best ®t regression lines with (A) y (12 °C)= ±83.8x+8.4, r2=86%; y (20 °C)= ±54.2x+96.6, r2=66%; (B) y (12 °C)= ±93.7x+20.3, r2=93%; y (20°C)= ±72.5x+102.6, r2=93%. Signi®cances between temperature treatments based on the F-ratio method (Potvin et al., 1990) comparing the two ®tted lines were as following: (A) F2,44=25.30, P <0.001; (B) F2,44=8.28, P <0.001. Fig. 4. Effects of temperature on (A) extra-radical mycelium (ERM) length g±1 growth medium or (B) total length of colonized roots (total LRC) of Glomus mosseae grown in symbiosis with Plantago lanceolata at all harvests against (A) ln plant biomass and (B) plant biomass. Temperature treatments were either 12 °C (open symbols and dashed line) or 20 °C (®lled symbols and line). The lines shown are best ®t regression lines with (A) y (12 °C)=0.29x+1.45, r2=42%; y (20 °C)=0.45x+2.19, r2=64%; (B) y (12 °C)=11.39x+0.49, r2=60%; y (20 °C)=23.29x±0.13, r2=65%. Signi®cances between temperature treatments based on the F-ratio method (Potvin et al., 1990) comparing the two ®tted lines were as following: (A) F2,44=6.87, P <0.001; (B) F2,44=6.83, P <0.001. (GLM, P <0.001) greater in the heated fungal compartments B (Fig. 5), but for each species this difference was transient: the effect of heating was signi®cant for G. mosseae and G. hoi at harvest three and four (Fig. 5). On the last sampling day, however, there was no longer a temperature effect on the ERM of either Glomus spp., whereas it became more evident (though not yet signi®cant) for Acaulospora sp. (Fig. 5). Discussion Higher temperature enhanced the growth of both the internal and external mycelium of AM fungi in P. lanceolata. Enhanced growth responses of AM fungi to higher temperature have been reported earlier (Furlan and Fortin, 1973; Graham and Leonard, 1982); however, the few experiments either exposed the symbiosis to the different temperatures right from the germination stage, which leads to differences in spore germination (Daniels Hetrick, 1984) and growth of infection units (Tinker, 1975), or were single harvest experiments. Single harvest experiments must be interpreted with great caution because they may involve comparisons of individuals that have grown at different rates and therefore are at different developmental stages (Staddon et al., 1998, 1999). Treatments were applied for shorter periods in this Mycelial growth, mycorrhizas, temperature, and light 531 Table 2. Treatment effects on plant growth and colonization of roots (LRC) by Glomus mosseae (GM), G. hoi (GH) and Acaulospora sp. (A sp.) grown in symbiosis with Plantago lanceolata in the compartment experiment Data are the means 6 SE at the last harvest for plant biomass (WRS), speci®c root length (SRL), total LRC, LRC, arbuscular LRC (LRCarb), and vesicular LRC (LRCves) for P. lanceolata plants at either ambient (A) or heated (+8 °C, H) temperature grown in symbiosis with one of the three AM fungi. Signi®cances between temperature treatments are based on a two-way ANOVA; there were no signi®cant interactions. Note that number of replicates (n=4) was reduced to n=3 in ambient treatments of GH and A sp. and in heated treatments of GM and A sp. n.s., not signi®cant, *P <0.05, **P <0.01, ***P <0.001; different letters indicate signi®cant differences between species according to multiple comparison by Bonferroni. Temperature WRS (g) SRL (m g±1) Total LRC (m) LRC(%) LRCarb (%) LRCves (%) A H A H A H A H A H A H Plantago lanceolata Species Warming GM GH A sp. d.f.=2 P-value d.f. = 1 P-value 6.760.6 b 7.161.1 90.867.8 101.6611.1 137.9618.0 a 151.569.2 41.165.0 a 39.567.1 21.862.8 a 16.962.6 0.960.4 a 3.361.6 6.862.0 b 6.061.1 90.769.4 103.465.1 42.6624.2 b 80.769.9 10.464.2 b 20.162.4 6.063.7 b 13.461.2 0.060.0 b 0.060.0 11.061.0 a 9.260.7 80.3610.1 103.364.2 27.768.3 b 47.762.3 5.261.3 b 6.062.0 3.261.0 b 3.661.5 0.760.3 a 0.960.5 * n.s n.s. * ** n.s. *** n.s. ** n.s. ** n.s. Fig. 5. Temperature effects on log transformed data of the extraradical mycelium (ERM) length g±1 growth medium of Glomus mosseae (GM, diamonds), G. hoi (GH, triangles), and Acaulospora sp. (circles) grown in symbiosis with Plantago lanceolata in either ambient (open symbols) or heated (+8 °C, ®lled symbols) fungal compartments over 126 d after planting (dap). Signi®cances between temperature treatments based on a one-way ANOVA at a particular harvest differed as following: (GM) harvest 3: F1,5=17.67, P=0.008; harvest 4: F1,5=8.99, P=0.030; (GH) harvest 3: F1,5=6.60, P=0.050; harvest 4: F1,5=8.64, P=0.032. There was no signi®cant difference for the Acaulospora sp. at any one harvest. study and the effects were followed over several harvests, so that it was possible to allow for such developmental effects. When both plant and fungus were warmed, an enhanced growth response of the ERM to temperature was demonstrated that was independent of plant biomass (Fig. 4A), but not of LR (Table 1), because of a temperature-induced increase in SRL. In other words, the ratio of LERM to root length remained constant, even though variation was considerable; this is in agreement with model ®ndings by Fitter (1991) that there is an optimal number of entry points per unit LR at low phosphate concentrations. Although the ratio was greater in P. lanceolata than in H. lanatus, the much lower colonization intensity in H. lanatus, which was expected for this fast growing, ®nerooted species under the relatively low irradiance provided, resulted in LERM per unit root length colonized (LRC) being very similar at 71±82 m m±1, within the range reported by Sanders et al. (1977) for another Glomus sp. The constancy of this ratio suggests regulation of the amount of ERM attached to a given amount of internal fungal biomass, and might indicate that the host plant controls carbon allocation to the fungal partner (Graham et al., 1997). Although the pot experiment could not determine whether the ERM responded directly to temperature, independently of the host plant, the compartment experiment clearly showed such a direct temperature response of the ERM. The length of ERM produced differed among AM species (Fig. 5) as reported in other studies (Sylvia, 1992; Jakobsen et al., 1992), but at about 6 m g±1 growth medium was in the range of other studies (Boddington et al., 1999) and differences re¯ected different degrees of internal colonization (Table 2). Further, sampling 4.5 cm from the mesh might have underestimated the overall amount of ERM of the less colonized species as the rate of development of the front of mycelium growth also differs among AM fungal species (Dodd, 1994). Differences in 532 Heinemeyer and Fitter LERM might re¯ect different functions (Dodd, 1994; Dodd et al., 2000) and might also be an important reason for possible niche separation of AM fungi based on speciesspeci®c differences in ERM production (Fitter et al., 2000). It may be signi®cant that the most responsive (and fastest-growing) isolate, G. mosseae, came originally from Italy, where it would have experienced a greater mean soil temperature. Only P. lanceolata had a clear growth response to temperature in the pot experiment (Table 1); both SLA and SRL declined over time, but also increased under higher temperature. These temperature-induced changes were independent of plant biomass which suggests that they may have been mediated by a direct fungal response to temperature. Biomass of P. lanceolata was very different between the pot and the compartment experiment, possibly due to differences in length of the growing periods or pot sizes. However, in both cases SRL was greater if connected to a heated mycelium. A reduction in SRL due to AM colonization has been reported (Torrisi et al., 1999; Atkinson et al., 1994), but the ®nding that changing the environment of an AM fungus can affect plant morphology with no change in the plant's environment is novel. This result suggests that the causation is fungus to plant: enhanced fungal growth causes changes in plant growth that stabilizes colonization density. The different LRC patterns in the pot experiment re¯ected the expected different degrees of mycorrhizal colonization in the two host plants (cf. Gange and West, 1994; Abbott et al., 1977; Fitter, 1996; Eissenstat et al., 2000). Colonization was lower than in some studies, but not untypical. The higher LRC together with an increase in LERM in the warmer environment might increase the competitiveness of P. lanceolata due to increased phosphate uptake (Smith et al., 2000) or enhancement of other bene®ts (Dodd et al., 2000) compared with H. lanatus, which often co-occurs with P. lanceolata in the ®eld. These results support Tinker's view (Tinker, 1975) that the total LRC is ecologically more important than its percentage, although to test such an hypothesis would require the comparison of a greater number of plant species. The positive growth response of the AM symbiosis to a warmer environment might have important implications for nutrient uptake and carbon cycling. Although the temperature difference in this study (8 °C) was large, temperature changes approaching this might occur in topsoils if global mean temperature rises by 3 °C over the next century (Houghton et al., 1995). Host plant photosynthesis is expected to increase under the predicted changes (Saxe et al., 2001; Grace and Rayment, 2000), and plants will therefore need an increased nutrient supply to maintain higher growth rates (Ceulemans et al., 1999), which could possibly be supplied by the response of the ERM. However, viability of the ERM was not measured and its turnover time may be as short as 5±6 d (Staddon et al., 2003). Differences in viable LERM might have been smaller. All three AM fungal species in the compartment experiment showed an enhanced ERM production in the warmer environment, yet the response time differed according to the overall amount of ERM and signi®cant differences for two of the three species tested were transient (Fig. 5). The transience of the temperature effects in G. mosseae and G. hoi might have been due to the mycelial front passing the sampling points at different rates. The increased ERM growth might also lead to a higher carbon input to the soil as AM hyphae have high concentrations of both chitin (and chitosan) and excrete large amounts of glomalin (Grif®n, 1994; Wright and Upadhyaya, 1996), both very stable in soil (Rillig et al., 2001). Increased ERM growth might therefore lead to accumulation of these compounds, possibly increasing carbon sequestration (Fitter et al., 2000). Both increased temperature and elevated CO2 (Treseder and Allen, 2000) may increase external mycelium growth. The interaction between temperature and elevated CO2 might be rather complex as little is known about either plant growth responses in the natural environment or effects on other soil microorganisms, which are closely linked to the ERM (Mar Vazquez et al., 2000), for example, grazing by collembola on the ERM (Warnock et al., 1982; Klironomos et al., 1999; Gange, 2000). Despite frequent watering, possible moisture differences in fungal compartments which could have resulted in osmotic effects (i.e. a nutrient gradient towards the heating cable position) cannot be ruled out completely; possibly affecting ERM growth into the fungal compartment. Although controlled conditions can never re¯ect natural conditions, these ®ndings clearly indicate the need for future experiments examining any temperature impacts under ®eld conditions; molecular techniques in combination with staining techniques might offer a very valuable tool for this approach (Redecker, 2000). In conclusion, ®rst, when plant and fungus were both subject to varying temperatures, the impact on the internal and external part of the AM fungus was related to different biomass or root growth dynamics, respectively; and second, when only the ERM was subject to a different temperature, increased ERM growth was independent of plant growth but increased SRL. This implies that both plant and fungus can regulate the symbiosis, resulting in stable colonization densities. These ®ndings underline the important role of the AM fungal symbionts in global carbon cycling, but leave unanswered key questions about the responsiveness of different mycorrhizal symbioses to temperature. Land plants in nearly all ecosystems around the world interact closely with AM fungi and a more mycocentric point of view is needed in the development of predictions of impacts of a rising global temperature on ecosystem functioning. 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