Clone-Specific Response in Leaf Nitrate Reductase Activity among Unrelated Hybrid Poplars in relation to Soil Nitrate Availability

1 Fiducie de Recherche sur la Forêt des Cantons-de-l’Est, Eastern Townships Forest Research Trust, 1 Rue Principale, St-Benoı̂t-du-Lac, QC, Canada J0B 2M0 2 Centre d’Étude de la Forêt (CEF), Université du Québec à Montréal, C.P. 8888, Succursale Centre-Ville, Montréal, QC, Canada H3C 3P8 3 Department of Biology, University of Regina, 3737 Wascana Parkway, Regina, SK, Canada S4S 0A2 4 Département des Sciences Biologiques, Université du Québec à Montréal, C.P. 8888, Succursale Centre-Ville, Montréal, QC, Canada H3C 3P8

Because they can be clonally propagated with ease, poplars from the Tacamahaca and the Aigeiros sections and their hybrids form the basis of most poplar breeding programs worldwide [10].Although they are all pioneer species that mainly occur in coastal, riparian, alluvial, and bottomland environments, poplars from these two sections differ widely in their natural distributions, as they are adapted to different soil and climatic conditions [11].Poplars from the Tacamahaca section are mostly associated with riparian or wetland habitats [11].They are widely distributed in the northern latitudes, with some species growing to the latitudinal or altitudinal limits of trees [11].Poplars from the Aigeiros section are better adapted to riparian soils in the bottomlands of temperate and arid regions [11,12].
Poplars from the Tacamahaca and the Aigeiros sections also show marked differences in their N-form preferences 2 International Journal of Forestry Research [13,14].This is because organic matter mineralization processes are strongly influenced by habitat characteristics such as climate (temperature and precipitation), soil pH, and water table depth [15][16][17].For example, balsam poplar (Populus balsamifera), growing as far north as 69 • latitude in Alaska [11], is able to assimilate directly both NH 4 + and amino acids, with no apparent preference [18], and its physiological capacity to assimilate NH 4 + is greater than for NO 3 − [13].Fertilisation trials also show that P. balsamifera and poplar hybrids with one parental species related to the Tacamahaca section, tended to grow best with NH 4 + fertilisation over NO 3 − fertilisation [19].Conversely, a high NO 3 − : NH 4 + ratio in the soil solution strongly stimulates root development in Eastern cottonwood (P.deltoides) [20].
Nitrogen form preferences have been shown to be closely linked to the ability of tree species to reduce NO 3 − from the soil solution [21][22][23].Because nitrate reductase (NR) is a substrate-induced enzyme [24], in vivo nitrate reductase activity (NRA) in the leaves and in roots has proven to be a useful indicator of NO 3 − assimilation in a wide range of species, management practices, and environmental conditions [23,[25][26][27][28][29][30][31].
In poplars, Dykstra [32] detected important differences in leaf NRA between hybrid poplar clones P. tristis x balsamifera and P. deltoides x nigra.In free-growing populations, similar observations were reported by Al Gharbi andHipkin [25] when P. alba, P. deltoides x nigra, and P. tremula were compared.More recently, Black et al. [33] reported that NRA in P. tremula x alba was at least 10-fold greater in leaves than in stems or in roots at all nitrate availabilities.These authors concluded that most nitrate assimilation occurs in poplar leaves, a finding that was later corroborated by Rosenstiel et al. [34] in Eastern cottonwood (P.deltoides).Balsam poplar also showed slightly higher NRA in leaves than in roots when substrate was not limiting [29].
Relationships between soil N availability and NRA in poplars have also been documented.Min et al. [21] showed that NRA in roots and in leaves of trembling aspen (P.tremuloides) is rapidly induced following NO 3 − exposure, with leaves having the greatest activity.Higher NRA was also observed in the N fertilisation treatment for P. deltoides x P. nigra hybrid [35].Nitrate reductase activity in leaves and roots was also greater when P. tremula x alba was grown in the highest external NO 3 − concentration [33].In this field study, we use in vivo NRA activity in hybrid poplar leaves as an indicator of NO 3 − assimilation [29] in five unrelated hybrid poplar clones: (1) Populus trichocarpa x P. deltoides (TxD-3230), (2) P. deltoides x P. nigra (DxN-3570), (3) P. x canadensis x P. maximowiczii (DNxM-915508), (4) P. nigra x P. maximowiczii (NxM-3729), and (5) P. maximowiczii x P. balsamifera (MxB-915311).We hypothesize that the intrasectional hybrid from the Aigeiros section (DxN hybrid) should exhibit a higher NRA than the intersectional hybrids (TxD, NxM, and DNxM hybrids) and the intrasectional hybrid from the Tacamahaca section (MxB hybrid).This hypothesis should be supported because parental species of the DxN hybrid are adapted to temperate floodplain environments, where NO 3 − is the dominant N-form [36], while parental species of the MxB hybrid are adapted to riparian habitats and wetland ecotones of colder climates (Alaska, northern Canada, Siberia) [11], where NH 4 + is the dominant N-form in soils [37], although hydrologically driven NO 3 − input occurs periodically [29].In this study, we also examine if leaf NRA of these unrelated hybrid poplar clones is influenced to the same extent by different levels of soil NO 3 − availability within two riparian agroforestry systems located in pastures.

Study Sites.
In May 2003, two multiclonal hybrid poplar riparian buffers were planted along headwater streams in the Eastern Townships region of southern Quebec, Canada.The buffer had cumulated five years of growth in 2007, the year of the study.The two riparian buffer study sites (Bromptonville: 45 • 29 N; 71 • 59 W; Magog: 45 • 14 N; 72 • 07 W) are located in pastures of the regional landscape unit of Sherbrooke [38].This landscape unit is characterised by gentle slopes, a continental subhumid moderate climate, a growing season of 180-190 days, and a precipitation regime of 1000-1100 mm/year [39].Cattle densities at the two pasture sites are 0.6 cow ha −1 at Bromptonville and 0.2 cow ha −1 at Magog.The Bromptonville site is fertilized each year with cow manure, while the Magog site receives no fertilisation.The soil of the Bromptonville site developed on glacial outwash, deposited over lacustrine clay [40].It is well-drained and named "Sheldon sandy loam" [40].The soil of the Magog site developed on glacial till.It is imperfectly drained and named "Magog stony loam" [40].Much higher aboveground biomass (including leaves) have also been measured at the fertile site of Bromptonville, one year following this study (6th growing season) [1].Site and soil characteristics are presented in Table 1.Additional site and soil characteristics are available in other related studies [1,7,41].

Experimental Design.
A randomized block design was used at each of the two sites, with 4 blocks (replicates) and 5 hybrid poplar clones (treatments) for a total of 40 experimental plots.Each block contains 5 experimental plots (one clone per plot).Plots are 4.5 m wide and 9 m long (40.5 m 2 ).Each plot contains 9 trees from a single clone (3 rows, 3 trees/row).Each tree is spaced 3 m on the row and the rows are 1.5 m apart.Tree rows were planted parallel to stream bank.A total of 180 hybrid poplars where planted at each site (36 trees of each clone) for a total of 360 hybrid poplars, two blocks on each side of the stream.This design allowed us to test 5 poplar clones in two different riparian environments simultaneously, a common procedure in crop cultivar trials [43].

Soil Nutrient Availability.
Nutrient availability in the hybrid poplar buffers was determined using Plant Root Simulator (PRS-Probes) technology from Western Ag Innovations Inc., Saskatoon, Canada.The PRS-probes consist of an ion exchange membrane encapsulated in a thin plastic probe, which is inserted into the ground with little disturbance of soil structure.Nutrient availability predicted with this method is generally significantly correlated with conventional soil extraction methods over a wide range of soil types [44].Three pairs of probes (an anion and a cation probe in each pair) were buried along the middle row (of 3 rows parallel to stream bank) of poplars in each experimental plot (40 plots).At each site, burial length was 15 days, starting in mid-August 2007.After removal, probes were washed in the field with deionised water and returned to Western Ag Labs for analysis (NO 3 − , NH 4 + , P, K, Ca, Mg, and Mn).Composites were made by combining the three pairs of probes in each experimental plot.Probe supply rates are reported as µmol of nutrient 10 cm −2 15 days −1 and are presented in Table 1.

Nitrogen Mineralization Rate.
A sequential coring technique was used to measure nitrification and ammonification rates at the two riparian sites [45].In each experimental plot, two pairs of hard PVC tubes (20 cm in length and 5.5 cm in diameter) were inserted 15 cm vertically into the soil.The first pair of tubes and their soil content were immediately removed and placed in a portable ice box and transported to the lab for extraction with 2 M KCl [46] within 24 h.The content of each pair of tubes was mixed thoroughly and duplicate extractions were made for each composite.During the following days, the concentration of NO 3 − and NH 4 + were determined using a Tecator FIAstar continuous flow analyzer.
The second pair of tubes remained in the soil for a 24 day period (from 17 July to 9 August 2007).They were capped with tape to prevent N loss from leaching by rain.A small hole was pierced laterally on each tube (1 cm from the top) to allow aeration.After 24 days, tubes were removed from the soil and the same procedure (as for initial tubes) was used in order to determine concentrations of N-forms.Nitrification was calculated as the NO 3 − concentration of the soil at the end of the incubation period minus the NO 3 − concentration at the beginning.Ammonification was calculated the same way.
Measurement of the in vivo NRA in poplar leaves was done according to the method developed by Jaworski [47] and optimized for broadleaf tree species [30].In early summer (June 29, 2007), leaves from the upper shoots were taken at noon at the Bromptonville site.For each of the two clones, a composite sample was made by combining two leaves from two different trees.The plastochron index was used to select fully expanded leaves at the same developmental stage [48].Leaf plastochron index 7 (LPI 7) was selected for all samples.Samples were put in a plastic bag and immediately placed in a portable icebox (4 • C).The sampling operations were always done within 1 h and plant material was brought back to the lab within 30 min after sampling.
At the lab, the leaves from each sample were cut into small pieces (2 × 2 mm) and 0.1 g of fresh tissue, in duplicate for each composite sample, was placed in a test tube containing 5 mL of incubating solution (pH 7.5), containing 100 mM phosphate buffer, 1.5% 1-propanol, and the different KNO 3 concentrations.Tissues samples and solutions were vortexed for 2 min to enhance infiltration of the assay medium.Each test tube was sealed and incubated in the dark for 1 h at 30 • C. A blank was done for each composite sample.The enzymatic reaction was stopped by immersing the tubes in boiling water over five minutes.The colorimetric determination of the reaction was achieved by mixing 1 mL of incubation solution with 1 mL of 0.02% NED and 1 mL of sulphanilamide.After 30 min, the samples were centrifuged at 2000 ×g for 5 min and the supernatant was read in a spectrophotometer at 540 nm.Nitrate reductase activity is expressed as the amount of NO 2 − measured in the test tube after the 1 h incubation period, calculated for 1 g of dry leaf tissue.

Effect of Leaf Age on Hybrid Poplar NRA.
The effect of leaf age on NRA was assessed for the five hybrid poplar clones.The same procedure as the one described above was employed, except that leaf samples from LPI 3 to LPI 9 were collected from the five clones at the Bromptonville site (July 2-3, 2007).Based on the enzymatic kinetics assay, we used a substrate (KNO 3 ) concentration of 40 mM.

Determination of Hybrid Poplar NRA at the Two
Riparian Buffer Sites.In mid July (July 10 and 11, 2007) and late August (August 28 and 29, 2007), NRA assays were performed with plant material from the two riparian buffer sites (Bromptonville and Magog).In each experimental plot (n of plots = 40), a composite sample was made by combining two leaves from two different trees of a single clone (one clone per plot).Leaf samples were collected in the same manner as in the previous assays and the same procedure was used for NRA determination.Based on the observations concerning the effect of leaf age on NRA, plant material corresponding to LPI 6 was used for all clones in this assay.
2.6.Statistical Analysis.ANOVA tables were constructed in accordance with Peterson [49], and degrees of freedom, sum of squares, mean squares, and F values were computed.When a factor was declared statistically significant (Sites, Clones and Sites x Clones interaction), the standard error of the mean (SE) was used to evaluate differences between means for four levels of significance (P < 0.1, P < 0.05, P < 0.01, and P < 0.001).All of the ANOVAs were run with the complete set of data (2 sites, 5 clones, and 4 blocks = 40 experimental plots).Results of enzymatic kinetics and effect of leaf age on NRA are presented as means with standard deviations (SD).

Nitrogen Supply Rate, Soil N Concentration, and N
Mineralization.Nitrate supply rate was approximately three times higher at the Bromptonville site compared to the Magog site, while NH 4 + supply rate was approximately 50% higher at the Magog site (Table 1).This resulted in very contrasting molar ratios of NO 3 − : NH 4 + availability (1.8 at Bromptonville versus 0.4 at Magog) (Table 1).
Initial NO 3 − concentration measured at the beginning of the mineralization study was approximately 60% higher at the Bromptonville site, while initial NH 4 + concentration was more than twice higher at the Magog site (Table 3).After the incubation period (24 days), a three-fold increase in NO 3 − concentration occurred at Bromptonville, while only a two-fold increase was observed at Magog.This resulted in a higher nitrification rate at Bromptonville.At both sites, NH 4 + concentration in soil showed a decrease after the incubation period because of high nitrification rates.Because nitrification rate was higher at Bromtptonville, the decrease in NH 4 + concentration was also higher, although ammonification rates were not statistically different between the two sites.
Strong positive linear relationships were obtained between NO 3 − supply rate measured during a 15 day period with ion exchange membrane (PRS-probes) and initial NO 3 − concentration in soil tube soils prior to incubation (Figure 1(a)), final NO 3 − concentration in soil tube soils following a 24 day incubation period (Figure 1(b)) and nitrification rate in soil tube soils during a 24 day incubation period (Figure 1(c)).

Nitrate Reductase Activity .
The enzymatic kinetics assay revealed that leaf NRA was much higher for clone DxN-3570 than for clone MxB-915311 at any substrate concentration (Figure 2).Results also show that both of these clones had their highest leaf NRA at a substrate concentration of 20 mM NO 3 − .In fact, for both of these clones a similar pattern of NR induction was observed.For substrate concentrations lower than 20 mM NO 3 − , leaf NRA increased very rapidly in relation to substrate availability and afterwards decreased slightly at higher NO 3 − concentrations (Figure 2).The effect of leaf age (developmental stage) on NRA was different from one clone to another (Figure 3).At all developmental stages, leaf NRA of clone DxN-3570 was higher than any other clones and showed a rapid decrease from LPI3 to LPI9.In younger leaves, clone NxM-3729 had a higher leaf NRA value than clones TxD-3230, MxB-915311, and DNxM-915508, at most developmental stages.For the three other clones (TxD-3230, MxB-915311, and DNxM-915508), leaf NRA was equal or below 1 µmol NO 2 − g dw −1 h −1 , with a maximum value observed at LPI 3 (Figure 3).At almost all leaf developmental stages, clone DNxM-915508 had the lowest NRA.
For the two NRA assays at the two riparian sites (July 10-11 and August 28-29 2009), a significant Site x Clone interaction was detected by the ANOVA (Figure 4).During the July assay, NRA of clone DxN-3570 was statistically higher than any other clones at both sites.However, during   the August assay, only NRA of clone DxN-3570 at the Bromptonville site was statistically higher than any other clones at both sites.During both assays, clone DxN-3570 had a significantly higher NRA at the Bromptonville site than at the Magog site, while NRA of the four other clones was generally higher at the Magog site or equivalent to what was observed at the Bromptonville site.The NRA of clone DxN-3570 at Bromptonville was almost twice as high in the August assay as in the July assay, while little difference in NRA was observed at the Magog site between the two assay dates.In fact, at the Bromptonville site, NRA of all clones was generally higher in the August assay compared to the July assay.This trend was not observed at the Magog site.

Nitrate Reductase Activity in Relation to Soil Nitrate
Concentration.Significant relationships between NO 3 − concentration observed following a 24 day incubation period in riparian soils and nitrate reductase activity (NRA) were only observed for two of the studied clones: DxN-3570 (R 2 = 0.39, P < 0.1) and MxB-915311 (R 2 = 0.63, P < 0.05) (Figure 5).A positive relationship (power function) between NO 3 − and NRA was observed for clone DxN-3570, while a negative relationship (power function) between those two variables was observed for clone MxB-915311.

Discussion
In this study, leaf NRA differences of more than one order of magnitude were observed between the hybrid poplar clones, a clear indication of their different abilities to reduce NO 3 − in leaves.Clone DxN-3570 had the greatest leaf NRA (1) during the enzyme kinetic assays at different substrate concentrations (Figure 2), (2) in leaves of different developmental stages (Figure 3), and (3) during both assays under field conditions in two contrasted sites in terms of soil NO 3 availability (Figure 3).Large differences in leaf NRA have also been reported in other species of Populus [25,32].
In addition, large differences in nitrification rate and soil NO 3 − availability across the two riparian sites (Tables 1  and 3) induced a clone-specific response in leaf NRA.This resulted in a significant Site x Clone interaction during the mid July and late August assays, with clone DxN-3570 having a significantly higher leaf NRA at the Bromptonville site, where NO 3 − availability is high, compared to the Magog site (Figure 4).Conversely, leaf NRA of the four other clones (TxD-3230, MxN-3729, MxB-915311, and DNxM-915508) was generally much lower and similar between clones and between sites (Figure 2).This suggests that clone DxN-3570 has a particular ability to activate the NO 3 − reduction process in its leaves in response to a higher NO 3 − availability in the soil.
Based on previous findings, higher leaf NRA from all clones could be expected at Bromptonville given the higher soil NO 3 − availability at this site.As reported by Black et al. [33] and Rosenstiel et al. [34], higher leaf NRA values were found in poplars grown on soils with higher external NO 3 measured across the two sites and leaf NRA for this clone (R 2 = 0.39, P < 0.1) (Figure 5), a positive relationship that was not observed for the other clones.It could also be argued that the NO 3 − reduction process in hybrid poplars grown at the Bromptonville site was diluted in a much larger biomass compared to the Magog site (Table 1).An inverse relationship between dry biomass and NRA was also reported in Robinia pseudoacacia [50].However, this dilution effect was not observed for clone DxN-3570 in this study.
As proposed earlier by Dykstra [32], we suggest that important leaf NRA differences among unrelated hybrid poplars reflect the genetic assemblage, or parentage, of the five clones studied.The parental species of clone DxN-3570 (P.deltoides and P. nigra) are typical colonisers of floodplain habitats of temperate and arid climates, where best growth occurs on sandy loam soils [11].In those habitats, the predominant N-form in soils is generally NO 3 − because of the warm climate and good soil drainage (water table below 30 cm of soil surface) [17,36].
Studies on Eastern cottonwood (P.deltoides) also suggests that a 60-80% NO 3 − (balanced with NH 4 + ) solution optimizes whole-plant growth [14].Moreover, Woolfolk and Friend [20] found that greatest total root length, specific root length, and N concentration of roots in enriched patches occurred at the 80 : 20 NO 3 − : NH 4 + ratio.These observations are consistent with the particular ability of the clone DxN-3570 to increase its NRA in riparian environments with high NO 3 − availability, as observed at Bromptonville (Tables 1 and 3, Figure 4).High leaf NRA in response to a high NO 3 − : NH 4 + ratio in soils has also been reported in red ash (Fraxinus pennsylvanica), a common early succession species of rich alluvial bottomlands [23].
The relatively low leaf NRA in hybrid poplar clones that have a Tacamahaca section genetic contribution may be related to the soil N-form preferences of these clones.It is well known that boreal species, such as balsam poplar, show a marked preference for the uptake of NH 4 + over NO 3 − , as observed for other species growing in cold climates [13].In addition, south of the boreal forest, balsam poplar typically colonises wet soils found at the edges of streams and lakes, in swamps and depressions [11].In those habitats, where the water table is near the soil surface, ammonification is generally the dominant N-mineralization process and NH 4 + generally accumulates in the top soil [17].During fertilisation trials, DesRochers et al. [19] also pointed out that P. balsamifera and two other clones related to the Tacamahaca section were better adapted for NH 4 + uptake rather than that of NO 3 − .Furthermore, balsam poplar and other poplars related to the Tacamahaca section are known to have high concentrations of tannins and other phenolic compounds in their leaves and fine roots [51,52].Once entered into the soil system through litter fall and fine root decomposition, these secondary compounds have a major effect on the Ncycle, including a decrease in N-fixation from competitive species such as alder (Alnus), an increase in N immobilisation and a decrease in nitrification [51,52].Consequently, the physiological traits of low leaf NRA in clones related to the Tacamahaca section (Figures 2, 3 and 4) is consistent with the ability of poplars from this section to modify the environment, in order to reduce NO 3 availability, at their own advantage.
Our observations also suggest a negative relationship between leaf NRA and soil NO 3 − concentration (R 2 = 0.63, P < 0.05) for the Tacamahaca intrasectional hybrid (MxB) (Figure 5).This is potentially the sign of a negative feedback of prolonged exposure to high soil NO 3 − concentrations on leaf NRA.   and 4) had the lowest biomass growth and N accumulation among the five clones studied [1,41].In a greenhouse study with 12 week-old trees originating from cuttings, Dykstra [32] also reported that leaf NRA was not an index of N assimilation in hybrid poplars.But, this author observed that the poplar clone with the highest NRA had a significantly higher dry stem weight, dry leaf weight, and height growth.This was not the case in our field study during the fifth growing season.However, further research is needed to determine if NRA might be a good indicator of growth among hybrid poplar clones of the same parentage.
Finally, a clearer portrait of NRA in the set of clones studied here may have been obtained if NRA in roots had been tested in parallel to leaf NRA.Given that very low NRA was found in the leaves of some clones (DNxM-915508 and MxB-915311), it could also be suggested that NO 3 − assimilation is relatively important in the roots of some clones and hybrid types, as shown in trembling aspen and balsam poplar [21,29].Given the high genetic variability in physiological traits of poplar species, generalities such as that nitrate assimilation is almost entirely restricted to leaves in poplars [33], should be made with caution.
Although different poplar species and hybrids may have soil N-form preferences, trees from the genus Populus are considered generalist pioneer species, capable of thriving on low and high NO 3 − or NH 4 + sites [67].Still, future research is needed to clearly understand soil N-form preferences among unrelated hybrid poplar clones and its potential relationship with NRA.If this relationship is proven, NRA could provide interesting information on the suitability and adaptability of different hybrid poplar clones to different fertilisation treatments [36] or to various plantation environments (clearcut forests, cultivated fields, abandoned farmland, riparian buffers, contaminated sites, etc.).In that context, it may be important to understand which N-form is preferred by different parental species from both Tacamahaca and Aigeiros sections, and how hybridization between and within those two sections influences N-form preferences and mechanisms of N assimilation.

Conclusion
This study has shown large variation in leaf NRA among hybrid poplars, with NRA differences of more than one order of magnitude for the hybrids studied (DxN, TxD, NxM, DNxM, and MxB).Clone DxN-3570, an Aigeiros International Journal of Forestry Research intrasectional hybrid, always had the highest leaf NRA during the assays under field conditions.Across the two riparian sites, this clone was also the only one to increase its leaf NRA with increasing NO 3 − soil availability, which resulted in a significant Site x Clone interaction, but also a positive relationship between soil NO 3 − concentration and NRA.All four other clones studied had one or both parental species from the Tacamahaca section.They also had relatively low leaf NRA and they did not increase their leaf NRA when grown on the NO 3 − rich site, which sharply contrasts with the physiological response observed for the DxN hybrid in terms of leaf NRA.These results suggest that NO 3 − assimilation in leaves varies widely among hybrid poplars of different parentages suggesting potential soil N-forms preferences under genetic control.

Figure 1 :
Figure 1: Linear relationships between soil NO 3 − supply rate and soil tube in situ incubations in riparian soils for 3 variables: (a) initial NO 3− concentration in soil tube soils prior to incubation, (b) final NO 3 − concentration in soil tube soils following a 24 day incubation period, and (c) nitrification rate in soil tube soils during a 24 day incubation period.All relationships are significant at P < 0.001.

−Figure 2 :Figure 3 :
Figure 2: Effect of substrate concentration on nitrate reductase activity (NRA) of clone DxN-3570 and clone MxB-915311.All data points are means of duplicate samples and vertical bars represent SD of the means.

Figure 4 :
Figure 4: Nitrate reductase activity (NRA) of the five hybrid poplar clones at the two riparian buffer sites.On the left (a), the NRA assay was done in mid-July (July 10 and 11, 2007) and Site x Clone interaction is significant at P < 0.05.On the right (b), NRA assay was done in late August (August 28 and 29, 2007) and Site x Clone interaction is significant at P < 0.01.Vertical bars represent SE of the means.

Table 1 :
Site and soil characteristics at the two riparian sites: elevation, mean aboveground poplar dry biomass (including leaves), soil drainage class, pH, and nutrient supply rate (µg 10 cm −2 15 d −1 ).The NO 3 − : NH 4 + nutrient supply rate molar ratio is also indicated.For nutrient supply rate, PRS-Probes were buried during a 15 day period in late August 2007.
[40]lar aboveground biomass per tree data and pH data were taken from Fortier et al.[1].2Soildrainageclasses were obtained from Cann and Lajoie[40].

Table 2 :
Name, parentage, section, and origin of the five hybrid poplar clones.

Table 3 :
Nitrification and ammonification rates measured during a 24 days period at the two riparian sites (July 17-August 9, 2007).Nitrate and ammonium concentrations at the beginning (initial) and at the end (final) of the in situ incubation period are also presented.