NITRATE REDUCTASE ACTIVITY IN LEAVES AND STEMS OF TANNER GRASS ( Brachiaria radicans Napper )

Tanner grass (Brachiaria radicans Napper) is a forage plant that is adapted to well-drained soils or wetlands, and responds well to nitrogen (N) fertilization. The assimilation of N involves the nitrate reductase (NR) enzyme, and its activity seems to be dependent on N supply. Molybdenum (Mo) is also important because it is a cofactor of NR. In this study, the variables of an in vivo assay were optimized for measuring nitrate reductase activity (NRA) in the leaves and stem tissues. This method was used to evaluate NO 3 metabolism in plants fertilized with NaNO 3 , NH 4 Cl or urea, in association with or without application of H 2 MoO 4 , aiming to provide guidelines for N management of this species. The best conditions to determine NRA involved the incubation of 300 mg of tissues in a medium composed of 200 mmol dm phosphate buffer (pH 7.4), 60 mmol dm KNO 3 , 10 cm dm n-butanol, 0.1 cm dm detergent (triton-X-100), under vacuum and in the dark for a period of 60 to 100 minutes. Leaves showed NRA levels two to three times higher than stems. Although there were some interactions between treatments, stem fresh weight and NRA were not affected by N sources. Plants fertilized with NaNO 3 showed the best growth and NRA values when compared with NH 4 Cl and urea, which had, respectively, the lowest and intermediate scores. The application of Mo in the absence of N improved NRA and did not affect leaf and stalk growth. In the presence of N, the Mo levels applied limited leaf NRA and plant development.


INTRODUCTION
Tanner grass is the common name for Brachiaria radicans Napper (Skerman & Riveros, 1990), lately described as Brachiaria arrecta (Souza, 1999).This forage grass is very competitive when compared with other forage species, and grows well under tropical conditions (Mitidieri, 1983;Skerman & Riveros, 1990).As in the majority of crops, nitrogen (N) is one of the most important nutrients in grasses.To improve the efficiency of N fertilization, more information on the processes of N utilization is required for each plant species (Baer & Collet, 1981).There is evidence suggesting that nitrate reductase activity (NRA) is the main limiting step in N assimilation in most plants (Srivastava, 1990;Lea, 1997).Leaf NRA seems to be dependent on the source of N (Roberts & Menary, 1994), and on a continuous supply of nitrate (NO 3 Sci.Agric.(Piracicaba, Braz.), v.61, n.6, p.640-648, Nov./Dec.2004 tions between the effects of N sources and Mo fertilization on NRA have been reported (Dordas et al., 2001).The NRA levels in a plant are of help in the study of plant metabolism and its complex relationship with the environment (Muller & Janieshch, 1993;Faleiros & Cazetta, 1996;Viégas et al., 1999;Stolz & Bazu, 2002), and one of the challenges of research in N metabolism is to develop approaches to analyze this complex interaction (Stitt et al., 2002).
NRA can be measured by either an in vivo or in vitro assay (Viégas et al., 1999).The in vitro assay is accomplished by extracting the enzymatic fraction from the tissue (Lillo, 1983;Viégas et al., 1999), and by measuring the reaction in an appropriate buffered medium (Aslam et al., 1984;Lillo, 1983).On the other hand, the in vivo assay can be carried out easily, without enzyme extraction, by incubating tissue samples in a buffered medium containing NO 3 -, solvent and/or detergent, and by measuring NO 2 -produced during an adequate period of time, in the dark (Jaworski, 1971;Jones & Sheard, 1977;Harper, 1981).Nitrite production in the in vivo assay depends on the diffusion of NO 3 -into the tissue, to reach the cytoplasm of cells where the enzyme is located.Therein, nitrate reductase catalyses the conversion of NO 3 -to NO 2 -, by using the reducing power of NADH (Nicotinamide Adenine Dinucleotide, reduced form) coming from the respiratory oxidative pathways.Under normal conditions, NO 2 -produced in green tissues is transported into chloroplasts and reduced to ammonia, using the reducing power of reduced ferredoxin, derived from photosynthetic electron transport (Lea, 1997).However, during the in vivo assay procedure, the tissue is kept in the dark, which inhibits NO 2 -reduction.This leads to NO 2 -accumulation, which drives its diffusion from the tissue toward the incubation medium, where it is measured as the product of NR activity.Thus, NO 2 -present in the medium not only depends on the NRA, but also on the diffusion processes.
Although NR always catalyzes the same reaction, its location within tissues, structure, and regulatory mechanisms are organism-dependent (Stolz & Bazu, 2002).Due to differences between species, or even between various plant parts, it is best to optimize the conditions for the in vivo assay, before NRA determinations are made (Lin & Kao, 1980;Faleiros & Cazetta, 1996).Therefore, the first objective of this research was to establish the optimum conditions for tanner grass leaf and stem NRA determinations, using the in vivo assay method.The second objective was to evaluate NRA in leaves and stems of tanner grass plants fertilized with NaNO 3 , NH 4 Cl, or urea, with or without Mo, for the purpose of providing guidelines for N management of this species in the future.

MATERIAL AND METHODS
Plants were collected in Brazil (21º15'17''S and 48º19'20''W), in December of 2002, and separated into leaf blades and stems (stalk plus leaf sheath adhering to the stalk).The central portion of leaves was cut into discs with a diameter of 1.0 cm.The stems were cut transversally into 2 mm long pieces.Both tissues were assayed for their in vivo NRA.The basal assay procedure used was a modification of the Jaworski (1971) method, described by Faleiros & Cazetta (1996), based on the incubation of fresh tissue (300 mg) in 10.0 cm 3 of a medium containing 25 mmol dm -3 phosphate buffer (pH 7.2), 25 mmol dm -3 KNO 3 , 30 cm 3 dm -3 n-propanol, and 30 cm 3 dm -3 of triton X-100 ® (t-octyl-phenoxypolyethoxy-ethanol, Rohm & Haas Co: U.S.A.).In order to induce anaerobic conditions in the incubation medium, the system was subjected to vacuum infiltration three times, as recommended by Klepper et al. (1971) to remove air from the tissue.The medium was maintained in the dark at 30 o C for 60 minutes.
The NO 2 -produced by action of the NR enzyme was determined by drawing an 0.5 cm 3 aliquot of the incubation medium, and treating this sample with 0.5 cm 3 of 10 g dm -3 sulfanilamide in 3 mol dm -3 HCl and 0.5 cm 3 of 0.2 g dm -3 N-(1-naphtyl)-ethylenediamine dihydrochloride.After 20 minutes, the solution was diluted to 4.5 cm 3 with deionized water, and the absorbance (540 nm) was measured using an Ultrospec 2000 ® spectrophotometer (Pharmacia Biotech: England).In order to calculate the amount of NO 2 -contained in the sample, a standard curve was prepared in the same way as the sample, but using aliquots of 0.5 cm 3 of NaNO 2 standard solutions (containing from 0 to 140 µmol dm -3 NO 2 -).
The optimization of the NRA assay was developed by evaluating the best incubation time (ranging from 20 to 120 minutes), pH level (6.0 to 8.0), surfactant compounds (solvents: ethanol, n-propanol, n-butanol, ketone, ethyl acetate; and detergents: triton X-100 ® or tween 80 ® (poly-oxy-ethylene sorbitan monooleate, Atlas Chemie: Germany), as well as the best concentration for phosphate (ranging from 0 to 400 mmol dm -3 ), NO 3 -(0 to 100 mmol dm -3 ), solvent (0 to 100 cm 3 dm -3 ), and surfactant (0 to 100 g dm -3 ), for the incubation medium.The effect of vacuum infiltration on the performance of the assay was also studied.The NO 2 -diffusion results were expressed as micromoles of NO 2 -per gram of fresh tissue, after a given incubation time, and NRA results were expressed as micromoles of NO 2 -produced per g of fresh tissue per hour (µmol g -1 h -1 NO 2 -).The optimized NRA method was applied to study NO 3 -assimilation in stems and leaves of tanner grass plants fertilized with different sources of N, and varying levels of Mo.This experiment was carried out using a Sci.Agric.(Piracicaba, Braz.), v.61, n.6, p.640-648, Nov./Dec.2004 medium-textured Typic Hapludox, collected from a field previously cultivated with corn (Zea mays L.).The initial soil properties were: pH in 0.01 mol L -3 CaCl 2 solution = 4.7; organic matter = 12 g dm -3 ; P = 11.0 mg dm -3 ; K = 1.5 mmol c dm -3 ; Ca = 16.0 mmol c dm -3 ; Mg = 5.0 mmol c dm -3 ; H + +Al 3+ = 37.0 mmol c dm -3 , cation exchange capacity (CEC) = 59.5, and base saturation = 37.8%.To reduce acidity, CaO was added and blended into the soil at a rate necessary to obtain a base saturation of 60%.The mixture was kept moist, and let stand for 15 days.The soil was then fertilized with Ca(H 2 PO 4 ) 2 , K 2 SO 4 , and Mg(SO 4 ) 2 , at levels corresponding to 80 kg ha -1 P 2 O 5 , 60 kg ha -1 K 2 O, and 30 kg ha -1 Mg, respectively, and then transferred to 5 dm 3 pots.Rooted sprouts of tanner grass of similar size were collected from the field, and individually planted in 32 pots.
The eight treatments consisted of three sources of N: NaNO 3 , NH 4 Cl, and urea.All N sources were applied at a rate corresponding to 300 kg N ha -1 , combined with two levels of Mo fertilization (0 and 20 kg Mo ha -1 , as H 2 MoO 4 ), plus two control treatments: no N or Mo fertilization, and fertilization with Mo, applied without N.The Mo fertilizer was added to appropriate treatments before planting.The different sources of N were applied with the irrigation water, divided into four weekly applications, which were started 10 days after planting.
The experiment was organized as a completely randomized design, with eight treatments and four replications, where each 5 dm 3 pot containing one plant comprised an individual experimental unit.Plants were maintained in a growth chamber with a photoperiod of 16 h (176 µmol PPFD m -2 s -1 ) provided by incandescent and fluorescent bulbs.The temperature was maintained between 20 and 35ºC (night and day, respectively) and the experiment was conducted for 40 days after planting.Plants were then harvested and separated into stems (stalk plus sheath adhering to stalk) and leaf blades and weighed, and NRA determinations were made according to the method previously described.
A factorial design (three N sources × two Mo levels, plus two controls), with four replications, was used for statistical analysis in this study.The F test was applied to detect main and interaction effects, and means were compared using Tukey test (P < 0.05).Analyses of variance and factorial analyses were performed using SAS ® (SAS version 6.11 software package, Statistical Analysis System Institute: U.S.A).

RESULTS AND DISCUSSION
Results obtained for the standard curve (Figure 1) showed high correlation (r 2 = 0.999) between absorbance at 540 nm and [NO 2 -].This indicates that the assay model was reliable to determine NO 2 -with good precision.
Stem NRA showed some variations within the first 60 minutes of incubation, but tended to be stable from 60 to 120 minutes (Figure 2), and exhibited an activity of about 20% of that observed for leaves.
NRA results for leaves revealed an increase (P < 0.05) during incubation times from 20 to 120 minutes (Figure 2).The behavior of NRA during incubation was reported to increase (Jaworski, 1971;Streeter & Bosler, 1972;Blondel & Blanc, 1975;Lin & Kao, 1980;Faleiros & Cazetta, 1996), to remain constant up to 120 minutes (Brunnetti & Hageman, 1976, Heuer & Plaut, 1978), to decrease during the first 60 minutes (Streeter & Bosler, 1972), or to decrease after 60 minutes (Klepper et al., 1971), indicating that it is dependent upon the species or tissue under study.In order to be reduced to NO 2 in the in vivo assay, NO 3 -has to diffuse into the tissue Phosphate buffer, pH 7.2, 25 mmol dm -3 KNO 3 , 30 cm 3 dm -3 n-propanol and 30 cm 3 dm -3 triton-X-100 ® , at 30 o C after vacuum infiltration), as well as nitrate reductase activity for leaf (NRA LEAF) and stem (NRA STEM), obtained after different incubation time periods.Means (obtained from triplicates and represented as points on the graph) for a given line with the same letter are not different (Tukey test, P < 0.05).
Figure 1-Standard curve obtained by reacting 0.5 cm 3 of NaNO 2 standard solutions (containing 0 to 140 µmole NO 2 -dm -3 ) with 0.5 cm 3 of 10 cm 3 dm -3 sulfanilamide in 3 mol dm -3 HCl, and 0.5 cm 3 of 0.2 cm 3 dm -3 N-(1-naphtyl)ethylenediamine dihydrocloride, and after 20 minutes diluted to 4.5 cm 3 with deionized water.Each point in the graph refers to means obtained from triplicates.and the NO 2 -produced has to diffuse into the incubation medium in order to be measured.Thus, since induced NRA is not expected to increase during incubation, increases suggest that variations may rely on diffusion processes.This possibility reinforced the need for solvents and surfactants as medium components.
The inclusion of n-butanol or n-propanol in the leaf incubation medium promoted higher NRA, when compared to the addition of ethanol.Acetone and ethyl acetate suggested intermediate promotion (Figure 3).Among the surfactants, triton-X-100 ® improved NRA, in comparison to tween-80 ® (Figure 3).When these same chemicals were included in the incubation medium for stem tissue, no differences (P > 0.05) were observed (Figure 3).The inclusion of solvents in the incubation medium was intended to increase membrane permeability.This would facilitate the influx of NO 3 -into tissue cells, and NO 2 -efflux into the medium.For triticale (Triticosecale Wittmack) propanol was more effective than butanol (Lin & Kao, 1980), but for tanner grass similar results were obtained for both alcohols (Figure 3).Butanol was chosen because of its supposedly lower toxicity and higher water solubility, compared to propanol (Jaworski, 1971).
The presence of a detergent in the medium is important in order to minimize liquid surface tensions, and improve contact of the tissue with the medium.However, our data indicated that NRA decreased when triton-X-100 ® was added to the medium (Figure 4).By increasing the concentrations of the triton-X-100 ® detergent from 0 to 100 cm 3 dm -3 in the incubation medium, leaf NRA decreased by an average of 5.8 % for each 10 cm 3 dm -3 increment of triton-X-100 ® added.Stem tissue NRA decreased by an average of 47% when the triton-X-100 ® concentration in the medium was increased from 0 cm 3 dm -3 to 30 cm 3 dm -3 .Higher concentrations tended to in-duce further reductions, but at much smaller rates (Figure 4).These results suggest that triton-X-100 ® could be excluded from the incubation medium for both tissues.Nevertheless, considering that the concentration required to reduce liquid tension is very low (about 0.1 cm 3 dm -3 ), and also that a mixture of surfactants tend to induce a synergistic effect (Streeter & Bosler, 1972;Tingey et al., 1974;Lawrence & Herrick, 1982;Faleiros & Cazetta, 1996), it would be advisable to include 0.1 cm 3 dm -3 triton-X-100 ® .
After choosing n-butanol as the solvent to be used, the effect of different concentrations in the medium was observed.Increasing the concentration from 0 cm 3 dm -3 to 10 cm 3 dm -3 increased NRA by an average of 5 % for leaf, and 18% for stem tissue, while concentrations higher than 10 cm 3 dm -3 decreased NRA.The inhibitory effect was proportional to the concentration of butanol, chiefly in the range from 10 cm 3 dm -3 to 70 cm 3 dm -3 for leaf, and from 10 cm 3 dm -3 to 30 cm 3 dm -3 for stem tissues.Comparing the results of butanol at 10 cm 3 dm -3 with butanol at 100 cm 3 dm -3 , NRA was reduced by 93% and 89% for leaf and stem tissues, respectively (Figure 5).
In spite of the fact that data from the different tests were obtained on different dates, and with the use of different plants, it becomes clear that when the average values for NRA are compared, the lower activities observed in the first tests (Figure 2, 3) were mainly due to the use of excessive concentrations of surfactants (30 cm 3 dm -3 ).The best butanol concentration (30 cm 3 dm -3 ) for Cajanus cajan (Faleiros & Cazetta, 1996) promoted a significant inhibitory effect when applied to tanner grass.
Nitrate reductase activity was enhanced by increases in NO 3 -supply from 0 mmol dm -3 to 33 mmol dm -3 , while no further effect was observed for [NO 3 -] higher than 33 mmol dm -3 , for either leaf or stem tissues, indicating that the optimum concentration should be between 17 mmol dm -3 and 33 mmol dm -3 (Figure 6).Media containing [NO 3 -] higher than 83 mmol dm -3 promoted a decreased NRA in stem tissue.These findings agree with data from previous studies (Nicholas et al., 1976;Watanabe et al., 1985;Faleiros & Cazetta, 1996), which showed that high [NO 3 -] could decrease enzyme activity.However, in this research, leaves did not exhibit a decrease in NRA, even when [NO 3 -] was increased to 100 mmol dm -3 .This suggests that tanner grass leaves tolerated a wider range of [NO 3 -] than did other plants (Nicholas et al., 1976;Faleiros & Cazetta, 1996).These results confirm that the addition of exogenous NO 3 -(60 mmol dm -3 ) is necessary in order to ensure maximum NRA during an in vivo assay of tanner grass tissues.This also indicates that concentrations of about 60 mmol dm -3 are sufficient to saturate the enzyme in in vivo assays for both tissues analyzed.
The highest values were obtained when leaf and stem tissues were incubated in media containing phosphate buffer at concentrations of 200 mmol dm -3 and 300 mmol dm -3 , respectively (Figure 7).A significant (P < 0.05) effect of the [PO 4 -3 ] concentration in the medium on NRA was observed for tanner grass, but not for other species (Jones & Sheard, 1977;Nicholas et al., 1976;Streeter & Bosler, 1972).
Leaf NRA was enhanced when pH increased from 6.0 to 7.6, but dropped when pH further increased from 7.6 to 8.0.Nitrate reductase activity for pH 7.2 and 7.6 did not differ (P > 0.05), indicating that the optimum pH for the incubation medium may be between those values.For stems, probably due to the low levels of NRA in this tissue, no difference (P > 0.05) was detected for pH ranging from 6.8 to 8.0 (Figure 8), even though the behavior of NRA as a function of pH was similar to that observed for leaves.These results show similar patterns to those found for soybean (Glycine max L. Merril), beans (Phaseolus vulgaris L.), and pigeon pea (Cajanus cajan L. Millsp) (Jaworski, 1971;Nicholas et al., 1976;Puranik & Srivastava, 1983;Faleiros & Cazetta, 1996), while different values were observed for triticale (Triticosecale Wittmack) (Lin & Kao, 1980).
Figure 5 -Nitrate reductase activity (NRA) determined in leaf and stem tissues of Brachiaria radicans incubated for 80 minutes in media (25 mmol dm -3 Phosphate buffer, pH 7.2; 25 mmol dm -3 KNO 3 , 0.1 cm 3 dm -3 triton-X-100 ® , at 30 o C under vacuum), with different butanol concentrations (cm 3 dm -3 ).Means (obtained from triplicates and represented as points on the graph) for a given line with the same letter are not different (Tukey test, P < 0.05).Both pH and buffer isotonic strength are important variables in NRA determinations (Figures 7 and 8).Despite the stems having much lower levels of NRA compared to those of leaves, the stem tissue showed the highest activity at a lower pH and higher [PO 4 -3 ], and exhibited tolerance to a wider range of both pH or buffer strength.
The incubation of tissues under vacuum conditions enhanced (P < 0.05) NRA for leaves and stems by an average of 21% and 15%, respectively, compared to the procedure without vacuum infiltration and incubation under room pressure (Figure 9).The assay showed a better performance after vacuum infiltration, with incubation maintained under vacuum conditions.Faleiros & Cazetta (1996) suggested that this is probably due to the elimination of inter-cellular gases from the tissue, which improves the contact between solution and tissue.This causes the tissue to submerge into the medium.The removal of O 2 from the tissue also reduces the possibility of NO 2 -reduction to NH 4 + in the cells, maintaining its diffusion towards the medium.Based on these results, the best in vivo assay to determine Brachiaria radicans NRA is the incubation of tissues in a medium composed of 200 mmol dm -3 phosphate buffer pH 7.4, 60 mmol dm -3 KNO 3 , 10 cm 3 dm -3 n-butanol, and 0.1 cm 3 dm -3 triton-X-100 ® .This should be done under vacuum and in the dark for a period of time between 60 and 100 minutes.
When tanner grass was grown in pots, it produced 1.5 to 2.5 times more stem than leaf fresh weight (Table 1).However, the average NRA per unit of fresh weight was higher (from 4.6 to 10.5 fold) in leaves, compared to the stem tissue.When NRA in the whole plant was calculated, leaf tissue had an activity from 2.1 to 6.8 times greater than stem tissue.
The treatments did affect plant development and NRA of tanner grass tissues (Table 2).Except for leaf fresh weight and NRA per unit of stem fresh weight, there were no significant N source x Mo level interactions (Table 2), indicating that N sources and levels of Mo, under this soil and experimental conditions, tended to play independent roles.
Plants fertilized with NaNO 3 and urea produced more leaf fresh weight than those fertilized with NH 4 Cl (Table 3).No differences, however, were observed for N sources on stem fresh weight.Nitrate fertilizer tended to

STEM
Table 1 -Fresh weight (FW) and nitrate reductase activity (NRA) in leaf and stem fresh tissues of Brachiaria radicans fertilized with 300 kg ha -1 N as NaNO 3 , NH 4 Cl, or urea, without Mo application or fertilized with 20 kg ha -1 Mo (as H 2 Mo 2 O 4 ), plus two controls (no fertilization, and Mo only).The NRA determinations were carried out by incubating 200 mg tissues for 80 minutes in medium containing 200 mmol dm -3 phosphate buffer pH 7.5, 60 mmol dm -3 KNO 3 , 10 cm 3 dm -3 n-butanol, and 0.1 cm 3 dm -3 triton-X-100 ® , at 30 o C, under vacuum (85kPa) following vacuum infiltration.The means in the table were obtained from three replications, and are accompanied by their standard deviation.
Plants fertilized with urea tended to show intermediate growth and NRA values, despite visual similarities between NaNO 3 or NH 4 Cl fertilized plants (Table 3).Despite the fact that urea is a source of NH 4 + , not all of it is immediately available, but is slowly released during its hydrolysis in the soil.The rate of urea hydrolysis in soils containing low levels of organic matter (like the one used in this research) tends to be low (Reynolds et al., 1985).Thus, NH 4 + is released at such a rate that the plant can absorb NH 4 + with little risk of toxicity.Also, in the moisture and oxidizing conditions under which the soil was maintained in this study, NH 4 + was probably slowly oxidized to NO 3 - (Malavolta, 1981), providing a NO 3 -supply just enough to induce a slight NRA increase (Kawachi et al., 2002).

Causes of Variations
Leaves Stems

Degrees of freedom
Fresh weight NRA Fresh weight NRA Source of nitrogen When Mo was added, plant development (leaf and stem fresh weight) was partially suppressed, as well as total NRA in leaf tissue.NRA in stem tissue showed no differences (P < 0.05), but data suggested a similar pattern as that observed for leaves (Tables 1, 2, and 3).The growth suppression imposed by Mo application may be due to partial toxicity.No injury symptoms were observed in the plants used in this study, although Gupta (2001) stated that symptoms become apparent only under very high Mo levels.
When Mo was applied in the absence of N (control), it improved NRA, but stalk development tended to be suppressed (Tables 2 and 3).Leaf fresh weigh tended to show similar results, although the differences did not reach significant levels (P < 0.05) (Tables 2 and 3).It seems that Mo improved NRA because it is a NR cofactor; however, the rate of Mo applied to the soil in this research probably was too high for this species, and may explain the partial suppression of plant development.
The addition of Mo tended to reduce leaf fresh weight of plants under NaNO 3 and urea fertilization (Tables 2 and 4).Also, urea promoted better leaf growth than NH 4 Cl when Mo was not applied, but did not differ under Mo fertilization (Table 4).Sources of N did not affect stem NRA when plants were grown without Mo fertilization (Table 5).However, for Mo fertilized plants, NaNO 3 induced higher NRA when compared to NH 4 Cl, while urea produced intermediate values.On the other hand, the effect on NRA was increased by NaNO 3 , decreased by NH 4 Cl, and was not altered by urea under Mo fertilization.
These findings together suggest that in this research the limitation imposed by Mo application would not be directly related to NR, but involved toxicity in other ways.
In summary, the objective of the NRA assay optimization was met.Tanner grass plants produced much more stem fresh weight than leaf fresh weight, with most NRA found in the leaves.Although it would be expected that, to some extent, tanner grass plants could avoid NO 3 reduction by absorbing reduced N directly from fertilizers, NH 4 Cl and urea induced less plant development when compared to NaNO 3 , showing that this species has a lower tolerance to these sources of N, mainly NH 4 Cl.The application of 20 kg ha -1 of Mo as H 2 Mo 2 O 4 to the soil under the conditions used in this research, affected plant development and NRA to some extent; however, it seems that the reduced plant growth observed did not directly involve NRA.
Further research is needed to unveil the plant toxicity mechanism triggered by high levels of Mo in the soil, and how it effects N utilization.Experiments consisting of combinations of different NO 3 -and Mo levels might help clarify and better understand this matter.
Table 4 -Effects of the interaction between sources of N and levels of Mo on leaf fresh weight (g plant -1 ) of Brachiaria radicans fertilized with 300 kg ha -1 of N as NaNO 3 , NH 4 Cl, or urea, without Mo application or fertilized with 20 kg ha -1 Mo (as H 2 Mo 2 O 4 ), obtained from a factorial statistical analysis.

Figure 2 -
Figure 2 -Nitrite diffused from leaf (DIF.LEAF) and stem (DIF.STEM) tissues of Brachiaria radicans into incubation medium (25 mmol dm -3 Phosphate buffer, pH 7.2, 25 mmol dm -3 KNO 3 , 30 cm 3 dm -3 n-propanol and 30 cm 3 dm -3 triton-X-100 ® , at 30 o C after vacuum infiltration), as well as nitrate reductase activity for leaf (NRA LEAF) and stem (NRA STEM), obtained after different incubation time periods.Means (obtained from triplicates and represented as points on the graph) for a given line with the same letter are not different (Tukey test, P < 0.05).

Figure 6 -Figure 7 -Figure 8 -
Figure 6 -Nitrate reductase activity (NRA) determined in leaf and stem tissues of Brachiaria radicans incubated for 80 minutes in media (200 mmol dm -3 phosphate buffer pH 7.4; 10 cm 3 dm -3 n-butanol and 0.1 cm 3 dm -3 triton-X-100 ® , at 30 o C under vacuum) with different NO 3 concentrations.Means (obtained from triplicates and represented as points on the graph) for a given line with the same letter are not different (Tukey test, P < 0.05).

Figure 9 -
Figure 9 -Nitrate activity (NRA) determined in leaf and stem tissues of Brachiaria radicans incubated for 80 minutes (200 mmol dm -3 phosphate buffer pH 7.5, 60 mmol dm -3 KNO 3 , 10 cm 3 dm -3 n-butanol and 0.1 cm 3 dm -3 triton-X-100 ® , at 30 o C) under vacuum (85kPa) after vacuum infiltration or at room pressure without previous vacuum infiltration.Means (obtained from triplicate samples and represented as bars on the graph) from a given tissue with the same letter are not different (Tukey test, P < 0.05).
56 ab B 11.43 b *Capital letters compare means within each column and small letters within each line.Means followed by the same letter are not different (Tukey test, P > 0.05).*Capitalletters compare means within each column and small letters within each line.Means followed by at least one identical letter are not different (Tukey test, P > 0.05).

Table 2 -
Analysis of variance and F test results obtained for fresh weight and nitrate reductase activity (NRA) in leaf and stem fresh weight (FW) tissues of Brachiaria radicans fertilized with 300 kg ha -1 N as NaNO 3 , NH 4 Cl, or urea, without Mo application or fertilized with 20 kg ha -1 Mo (as H 2 Mo 2 O 4 ), plus two controls (No fertilization, and Mo only).

Table 3 -
Main effects of sources of nitrogen, levels of Mo, and controls on the fresh weight (FW) and nitrate reductase activity (NRA) of leaf and stem tissues of Brachiaria radicans fertilized with 300 kg ha -1 of N as NaNO 3 , NH 4 Cl, or urea, without Mo application or fertilized with 20 kg ha -1 Mo (as H 2 Mo 2 O 4 ), plus two controls (No fertilization, and Mo only), obtained from a factorial statistical analysis.
# Values were obtained from three replications.Means followed by the same letter within each factor and variable are not different (Tukey test, P > 0.05).

Table 5 -
Effects of the interaction between sources of N and levels of Mo on stem nitrate reductase activity (µmole h -1 gFW -1 NO 2