Plant material and soil
Soil was collected (0–15 cm) from a subalpine Eucalyptus pauciflora Sieber ex Spreng. woodland in the Snowy Mountains of Australia (36°06′S; 148°32′E; 1500 m altitude). The soil is classified as a humic umbrosol (World Reference Base) or chernic tenosol (Isbell, 2002) and has been described previously (Warren, 2009b; Warren & Taranto, 2010). The soil is a well-drained sandy loam without coarse fragments > 2 mm, pH (H2O) is 4.5, organic C (Walkley and Black method) is 12–17%, and total N is 0.2–0.3%. Seeds of E. pauciflora (seedlot 19626; Australian Tree Seed Centre, ACT, Canberra, Australia) were sown into soil, stratified at 4°C for 4 wk and then germinated in a fully sunlit glasshouse at the University of Sydney (Camperdown, NSW, Australia). Germinants were transferred to individual 210-ml plastic tubes filled with the same soil and grown for 1 yr before being re-potted into 1.89-l glass preserving jars (wide-mouth preserving jar; Ball Corporation, Broomfield, CO, USA) filled with c. 1.5 l of soil packed to field density. Measurements of 15N uptake and 13C evolution were made when the seedlings were 18 months old and weighed c. 12 g each. The mean temperature inside the glasshouse during the period of plant growth was 22.1°C with an absolute maximum of 35.8°C and minimum of 11.7°C. Average daily photosynthetically active radiation inside the glasshouse was 472 μmol m−2 s−1 (18.8 mol m−2 d−1) with an absolute maximum of 1701 μmol m−2 s−1.
Gas exchange system for measuring fluxes of 12CO2 and 13CO2
To determine if added isotope label was subsequently respired as 13CO2, fluxes of 12CO2 and 13CO2 from leaves and soil were quantified. Measurements were made inside the laboratory in a temperature-controlled incubator fitted with two LED arrays and two fluorescent tubes that provided c. 150–300 μmol photosynthetically active radiation (PAR) m−2 s−1 at plant height for a 10–11-h photoperiod. Air (and soil) temperatures during measurements were 24–27°C. 12CO2 and 13CO2 exchange by soil and leaves was determined with a tunable diode laser (TGA100a; Campbell Scientific, Logan, UT, USA) from continuous measurements of 12CO2 and 13CO2 from the soil headspace and one leaf per plant (Fig. 1). To permit measurements of 12CO2 and 13CO2 exchange from the soil headspace, inlet and outlet quick-connect bulkhead fittings were fitted to the lids of the glass preserving jars, as described previously (Anonymous, 2009). To accommodate the stem of a seedling, a 10-mm-diameter hole was drilled in the centre of the lid, and then an 8–10-mm-wide removable tongue was cut from the centre hole to the periphery. The stem was positioned in the centre of the lid and sealed with plastic reusable adhesive (Blu-Tak; Bostik, Kings Park, NSW, Australia), and the 8–10-mm-wide tongue was replaced and sealed with cloth tape (cloth gaffa tape, 3M; Pymble, NSW, Australia) and plastic reusable adhesive (Blu-Tak). The screw-on sealing ring was placed over the top of the seedling and screwed onto the jar. For measurements of leaf gas exchange I used a custom-built 18-cm2 chamber covered with transparent Propafilm connected to an open gas exchange system (Li-6400; Li-Cor, Lincoln, NE, USA) and the tunable diode laser, as described previously (Douthe et al., 2011; Warren et al., 2011). When a leaf was placed in the chamber it was kept in its natural orientation and received illumination from the LED arrays and fluorescent tubes of the refrigerated incubator.
Air from outside the laboratory was drawn at 2.5 l min−1 into a 10-l buffer volume and humidified to a dew-point of 15°C (Li-610 dew-point generator; Li-Cor) (Fig. 1). Air from the dew-point generator was split into four streams: soil headspace, leaf gas exchange system, ‘reference gas’ entering the soil chamber, and a vent to avoid over-pressurizing the soil headspace or leaf gas exchange system. Samples of air from the soil headspace, and reference and sample gas from the leaf gas exchange chamber were continuously drawn into the manifold system of the tunable diode laser at 200 ml min−1. The tunable diode laser was programmed to measure13CO2 and 12CO2 of, in turn, the two calibration gases, and the four intakes (air entering and exiting the soil and leaf chambers). Each intake was measured for 45 s, but the first 15 s was ignored to minimize carryover and enable stabilization between intakes. Calibration of the tunable diode laser was a two-step process with an initial linear interpolation between two calibration cylinders, and then a minor recalculation to account for some nonlinearity and permit extrapolation beyond the range of the two calibration cylinders (Douthe et al., 2011). In brief, the initial (‘working’) calibration used two calibration cylinders with absolute concentrations of 12CO2 and 13CO2 of 414.5 and 4.49 μmol mol−1 for cylinder 1 and 286.9 and 3.10 μmol mol−1 for cylinder 2, respectively. Recalculating data required knowledge of the deviation between the carbon isotope ratio (δ13C) estimated with the linear interpolation and actual δ13C. To determine this deviation, an 8-g cartridge of pure CO2 (soda charger; iSi, Vienna, Austria) was diluted with the gas mixer of an Li-6400 to create CO2 mole fractions from 200 to 2000 μmol mol−1 with the same δ13C. The Li-6400 was plumbed to the tunable diode laser and replicated measurements were made at a range of CO2 concentrations. The tunable diode laser was highly linear across the entire range of measured 12CO2 and 13CO2, with the highest concentrations of 12CO2 and 13CO2 differing from actual concentrations by < 0.5%. There was an offset of < 3‰ in calculated δ13C at the largest CO2 concentrations measured in this experiment. The relationship between measured (with linear interpolation) and actual δ13C was used to recalculate data. The precision of the measurement of δ13C was determined by substituting the source of external air with a cylinder of CO2 in air (12CO2 = 405.5 μmol mol−1 and 13CO2 = 4.54 μmol mol−1), and then measuring δ13C of each of the four intakes (i.e. air entering and exiting empty soil and leaf chambers). The precision of each of the four intakes was better than 0.06‰ (SD; n = 10).
Rates of soil respiration were calculated separately for 12CO2 and 13CO2 based on tunable diode laser measurements of (dry) concentrations of 12CO2 and 13CO2, and flow measured within the manifold system:
(Eqn 1)
where flow is the molar flow of air through the soil headspace, and CO2s and CO2r are concentrations of 12CO2 or 13CO2 measured in the sample and reference air, respectively. Carbon isotope discrimination by leaves (Δ) was determined as described previously (Farquhar et al., 1982; Evans et al., 1986):
(Eqn 2)
where δο and δe are the carbon isotope composition (13C/12C) of air exiting the chamber (δο) or entering the chamber (δe). Carbon isotope composition was expressed against the carbon isotopic composition of the Pee Dee Belemnite formation (PDB), where δ = 1000 [((13Csample/12Csample)/(13CPDB/12CPDB)) – 1]. ξ = uCe/(sA) where u is the molar flow rate through the chamber, Ce is the concentration of CO2 entering the chamber, A is the rate of photosynthesis and s the projected leaf area. To determine if 13C-labelled amino acids were being metabolized and 13CO2‘lost’ within leaves, it was necessary to fit data to the model of leaf-level carbon isotope discrimination (Farquhar et al., 1982; Evans et al., 1986). The discrimination of carbon isotopes during photosynthesis and respiration is a function of the different diffusivities of 13CO2 and 12CO2 and fractionation by enzymes (Farquhar et al., 1982; Evans et al., 1986):
(Eqn 3)
where Δ = Ra/Rp– 1 and Ra and Rp are the molar ratios of 13CO2 : 12CO2 in the air and the photosynthetic product, respectively. In this model, discrimination is a function of the concentrations of CO2 in air (Ca), at the leaf surface (Cs), in the intercellular air spaces (Ci) and in the chloroplast (Cc); and fractionations resulting from diffusion through the boundary layer (ab, 2.9 ‰), diffusion through stomata (a, 4.4 ‰), and diffusion and dissolution of CO2 into water (ai, 1.8 ‰); net fractionation by Rubisco and PEP carboxylase (b, 28 ‰); fractionation resulting from mitochondrial respiration (e); and fractionation resulting from photorespiration (f). k is the carboxylation efficiency computed as (Farquhar et al., 1982) k = (A + Rd)/(Ci – Γ*), where Γ* is the CO2 photocompensation point (38 μmol mol−1 for a variety of Eucalyptus spp.; C. Warren unpublished). Fractionation caused by the boundary layer was negligible with our well-mixed leaf chamber and thus was omitted from the model. Rd, Ca and Ci were provided by the Li-6400. Cc was estimated based on the known relationship between net photosynthesis (A) and mesophyll conductance (gm = max {0.05, 0.019 A}) and then by calculating Cc (Cc = Ci–A/gm)( Warren, 2008; Douthe et al., 2011; Warren et al., 2011). f was assumed to be 11‰ (Lanigan et al., 2009). The model was solved for e for groups of five data points by using the Solver add-in of Microsoft Excel to find the value of e that provided the best fit to measured Δ. The carbon isotope composition of the respiratory substrate was then determined as described previously (Wingate et al., 2007).
15N uptake and fluxes of 12CO2 and 13CO2 after adding glycine or glutamine to soil
Eight seedlings of similar size were used in this experiment. Three seedlings received glutamine, with one seedling harvested at each of 60, 120 and 360 min. Five seedlings received glycine with one seedling harvested at each of 60, 360 and 5760 min, while two seedlings were harvested at 120 min. Collection of root and xylem sap samples involved termination of the experiment and 12CO2 and 13CO2 measurements, whereas leaf samples could be collected nondestructively and thus were collected at each time-point (until roots and xylem sap were collected). Leaf samples were collected 30, 60, 120 and 360 min after addition of amino acids. It was not possible to obtain replicate measurements of root and xylem sap for each time-point because of the large amount of expensive 13C- and 15N-labelled amino acid required to label the soil.
Plants were installed in the gas exchange system and fluxes of 12CO2 and 13CO2 from leaves and soil were recorded for at least 12 h before addition of 50.0 ml of 250 μg N ml−1 (equivalent to 17.86 mM of N) U-13C,15N glycine or glutamine (99 atom %; Isotec Inc., Miamisburg, OH, USA). This amount of added amino acid N is proportional to what was used in previous experiments with E. pauciflora growing in the same soil (Warren, 2009a,b) after scaling for differences in mass of soil between studies. Seedlings were not watered for 1 d before solutions were injected into the soil. This let the soil dry to 50–100 ml below field capacity, thereby avoiding the risk of waterlogging. Solutions were injected into the soil 90–120 min after lights were turned on (i.e. while plants were actively photosynthesizing and transpiring). A total of 50 ml of solution was injected into the soil in five 10-ml aliquots using a 4-sideport Cass needle (18 gauge × 150 mm long; Victor-G & Company, Kanpur, India). It was not necessary to irrigate plants harvested within 360 min of amino acid addition, whereas the seedling harvested at 5760 min received c. 40 ml of water each day to replace what was lost via evaporation and transpiration (determined gravimetrically by weighing jars). To disentangle evaporation from soil from transpiration, I determined the rate of water loss of soil-filled jars without seedlings.
Collection of leaves, roots and xylem sap
Uptake of 15N, 13C and labelled amino acids was traced into roots, leaves and xylem sap. Leaf samples were collected from the leaves closest to the leaf enclosed in the chamber by punching 4–6 leaf discs (0.56 cm2 each) into a 2-ml microfuge tube (Safe-Lock tube 2.0 ml; Eppendorf AG, Hamburg, Germany), immediately freezing in liquid N and subsequently storing at − 80°C. Following termination of 12CO2 and 13CO2 measurements, xylem sap was collected by cutting off a 10–15-cm length of shoot with at least five attached leaves, placing the shoot in a Scholander pressure chamber and exuding xylem sap by applying a slight over-pressure (0.05–0.1 MPa above the balancing pressure). The xylem sap was collected from the cut end of the shoot with a Pasteur pipette, transferred into a 2-ml microfuge tube, frozen in liquid nitrogen and stored at − 80°C. Roots were collected by transferring the entire jar of soil plus roots into a 1-mm sieve and rapidly separating roots from soil. A random subsample of roots (of all diameters) was washed three times with 50 mmol l−1 KCl and three times with ultra-pure water, patted dry, placed into a 2-ml microfuge tube, frozen in liquid nitrogen and stored at − 80°C.
Measurement of amino acids in leaves, roots and xylem sap
Leaf and root samples were extracted with methanol:chloroform:water and analysed by GC-MS of tert-butyldimethylsilyl derivatives as described previously (Warren, 2009b), except that acetonitrile replaced dimethylformamide as the derivatisation solvent. Amino acids were identified based on retention indices and mass spectra of authentic standards run under the same conditions. 14N,12C glycine was quantified from m/z 246; U-13C,15N glycine was quantified from m/z 249; 14N,12C glutamine was quantified from m/z 431; and U-13C,15N glutamine was quantified from m/z 438. Natural isotopes of the unlabelled amino acid did not contribute to peak area for the labelled amino acid. Each sample was analysed twice and the duplicate measurements were averaged. The flux of isotope labelled amino acids in the xylem was calculated by multiplying the measured concentration of amino acid in xylem sap (in nmol 15N ml−1 xylem sap) by the transpirational flux of water (in ml h−1) and then dividing by the dry mass of leaves. The cumulative amount of labelled amino acids delivered to leaves via the xylem was determined at 60, 120 and 360 min after isotope addition.