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* Abbotsford Veterinary Clinic, 200-33648 McDougall Avenue, Abbotsford, British Columbia, Canada V2S 5Z5
Pacific Agri-Food Research Centre, Agriculture and Agri-Food Canada, Box 1000 Agassiz, British Columbia, Canada V0M 1A0
1 Corresponding author: pacificagri{at}shaw.ca
| ABSTRACT |
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Key Words: fertilizer macromineral cation-anion difference grass
| INTRODUCTION |
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Grass-based feeding programs can present unique challenges to the successful implementation of the DCAD concept. The high concentrations of K that can be found in grass herbage (Fisher and Bates, 1986; Moore et al., 2000; Roche et al., 2002) necessitate feeding large amounts of anionic salts, which can decrease the palatability of the diet (Oetzel and Barmore, 1993). In some cases, decreasing the DCAD of grass-based diets to negative values, as recommended in the literature (NRC, 2001), is impractical.
The scientific literature contains several reports on the success of breeding forage grasses to increase the concentrations of Mg to alleviate hypomagnesemia, commonly known as grass tetany (Moseley and Baker, 1991; Wilkinson and Mayland, 1997; Crawford et al., 1998). In the studies reported by Wilkinson and Mayland (1997) and Sabreen et al. (2003), the concentrations of K were reduced in the grasses bred to contain higher concentrations of Mg. In addition, the concentrations of Ca and Mg were increased, which resulted in a lower grass tetany ratio, defined as the ratio of K to the sum of Ca and Mg (Smith et al., 1999).
Pehrson et al. (1999), investigating the effect of applying different formulations and amounts of K fertilizers on DCAD levels in primary and first-regrowth harvests of grass, reported that KCl fertilizer had the greatest effect on DCAD because it doubled the concentrations of Cl in the herbage. In contrast, Roche et al. (2002) reported that, although addition of KCl fertilizer increased K concentrations in pastures, there was no consistent effect on DCAD balance because of a concomitant decrease in Na and increase in Cl concentrations. Calcium and Mg were not affected by the K fertilizer treatment (Roche et al., 2002). This study investigated the feasibility of altering DCAD in grass forages by altering the amount and formulation of K and Mg fertilizer applied to 2 tall fescue varieties, one selected for high Mg concentration.
| MATERIALS AND METHODS |
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To ascertain the effect of the type of K fertilizer, a second experiment was conducted with 2 treatments (each replicated 4 times) of HiMag tall fescue fertilized with zero or soil test-based rates. Application rates were 125 kg/ha of K as KCl or as K2SO4. Nitrogen, Mg, and P fertilization was as described for experiment 1.
Harvesting
Five harvests of grass were done on May 8 (first), June 16 (second), July 21 (third), August 20 (fourth), and October 6 (fifth) in 1997. The fresh weight of harvested material from each plot was recorded in the field, and subsamples were retained for DM determinations and chemical analyses.
Chemical Analysis
Subsamples were dried in a forced-air oven at 60°C to constant weight and then ground to pass through a 1-mm screen. Samples from 3 of the 4 replicates were submitted to a commercial laboratory (Griffin Laboratories, Kelowna, British Columbia, Canada) for quantification of Ca, P, Mg, K, Na, and S using inductively coupled plasma optical emission spectroscopy after perchloric-nitric acid digestion. Ten milliliters of a perchloric-nitric acid mixture (3 vol of 72% perchloric and 7 vol of concentrated nitric) was combined with 0.5 g of ground plant material and allowed to stand overnight before gradual heating to 70°C over 1 h and then increasing to 203°C over 4 h (John, 1972). After cooling, 2.5 mL of 1 N hydrochloric acid was added, and the solution was made up to 12.5 mL in preparation for inductively coupled plasma analyses. Chloride was first extracted from the samples using nitric acid (0.25-g sample in 25 mL of 0.5 M nitric acid) and then measured using a Cl selective electrode.
Calculation of DCAD
The DCAD index was calculated according to the equation of Ender et al. (1971) as presented in NRC (2001), in which the milliequivalents of the anions Cl and S are subtracted from the milliequivalents of the cations Na and K:
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Statistical Analysis
Concentrations of Mg, Ca, Na, K, Cl, and S are expressed as grams per kilogram of DM, DCAD as milli-equivalents per kilogram of DM, and DM yield as kilograms per hectare. Data from both experiments were analyzed in a similar manner using the mixed-models procedure (Littell et al., 1996). In experiment 1, data analysis investigated main effects, namely, block, harvest, grass variety, and K and Mg fertilizer treatments, and the following interactions: harvest x variety, harvest x K fertilizer, harvest x Mg fertilizer, harvest x variety x K fertilizer, harvest x variety x Mg fertilizer, harvest x variety x K fertilizer x Mg fertilizer, harvest x K fertilizer x Mg fertilizer, variety x K fertilizer, variety x Mg fertilizer, variety x K fertilizer x Mg fertilizer, and K fertilizer x Mg fertilizer. Harvests were considered repeated measurements on each experimental block and were analyzed using the repeated statement with a compound symmetry covariance structure. The critical level of significance was set a priori at P < 0.05. Block and harvest x variety x Mg fertilizer, harvest x variety x K fertilizer x Mg fertilizer, harvest x K fertilizer x Mg fertilizer, variety x K fertilizer x Mg fertilizer, and K fertilizer x Mg fertilizer interactions were not significant and are not reported. In experiment 2, the data analysis investigated the main effects of block, harvest, and type of K fertilizer and the interaction of harvest x type of K fertilizer. Harvests were considered as repeated measures and were analyzed as in experiment 1.
Ration Evaluation
To evaluate the effect of using a grass bred for mineral concentration in transition diets, rations were formulated using the CPM-Dairy nutrition model (Version 3.06; Cornell-Penn-Miner; Cornell University, Ithaca, NY). Diets were balanced to provide 10.5 kg of DM using 9.1 kg of corn silage, 13.6 kg of grass silage, and a grain mix consisting of 2.1 kg of ground barley, 0.42 kg of canola meal, 0.42 kg of corn distillers grains, 0.21 kg of limestone, 0.21 kg of a vitamin-mineral premix, and 0.08 kg of MgO. Nutrient values for all ingredients were taken from the feed tables within CPM-Dairy except for grass silage, for which nutrient values of HiMag or Barcel tall fescue (Table 1
, first-harvest data) were used.
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| RESULTS AND DISCUSSION |
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Experiment 1
Varietal Effects.
There was no difference (P = 0.681) in the concentrations of Mg between the 2 varieties of tall fescue (Table 1
). This observation does not agree with work previously published for HiMag tall fescue (Crawford et al., 1998; Sabreen et al., 2003; Shewmaker et al., 2004). Crawford et al. (1998) reported an increase (22%) in the concentration of Mg when HiMag was compared with other tall fescue varieties. The current study is the first to evaluate HiMag tall fescue in a system in which K fertilization approximated that applied through the spring application of manure and in which multiple harvests (>2) are taken each crop year.
The concentrations of Ca were higher in HiMag than in Barcel tall fescue, with the magnitude of the difference increasing from 0.36 to 1.10 g/kg from the first to last harvest (Table 2
). Crawford et al. (1998) reported an increase of 18.5% in Ca concentration of HiMag vs. other tall fescue varieties. Other studies (Moseley and Baker, 1991; Wilkinson and Mayland, 1997; Shewmaker et al., 2004) also reported increased Ca concentrations in grass bred for a higher Mg concentration.
The HiMag tall fescue contained lower concentrations of K than did Barcel in the first (P = 0.024), second (P = 0.001), and third (P = 0.006) harvests, with no difference in the fourth (P = 0.107) and fifth harvests (P = 0.517; Table 2
). Previous reports detailing K concentrations of HiMag, as compared with other varieties of tall fescue, have been inconsistent. Crawford et al. (1998) found no difference in K concentrations of 4 varieties of tall fescue, including HiMag. Sabreen et al. (2003) conducted 3 growth-chamber experiments comparing HiMag with 2 other varieties of tall fescue. Potassium concentrations were lower in shoots of HiMag in 2 of the 3 experiments reported. Whitehead (2000) reported that K competes with Ca, Mg, and Na for uptake by the plant and that some grass species have a greater tendency for uptake of divalent cations relative to monovalent cations depending on the cation exchange capacity of their root system. In particular, tall fescue is reported to have higher concentrations of Ca and Mg but lower K, compared with orchardgrass (Dactylis glomerata L.) and reed canary grass (Phalaris arundinacea L.; Odom et al., 1980).
In general, HiMag tall fescue contained less Na than did Barcel, but the magnitude of difference in Na concentrations between the 2 varieties was affected by K and Mg fertilization (Table 3
). Application of K fertilizer decreased Na concentrations in Barcel (P = 0.001) but not in HiMag (P = 0.173) tall fescue (Table 3
). Similarly, application of Mg fertilizer decreased Na concentrations in Barcel (P = 0.001) but not in HiMag (P = 0.677) tall fescue (Table 3
). Previous publications detailing the mineral composition of HiMag relative to other varieties of tall fescue have not reported Na concentration data (Wilkinson and Mayland, 1997; Crawford et al., 1998; Sabreen et al., 2003). Moseley and Baker (1991) reported a decrease in the Na concentration of a high-Mg ryegrass as compared with a standard ryegrass variety but did not attempt to explain the reported difference. Adams (1973) reported a decrease in Na concentration in response to K fertilization in 22 out of 30 harvests of grass harvested over 3 yr. Likewise, Reith et al. (1964) reported that increasing K fertilization from none to 412 kg/ha decreased the Na concentration of grass. The low Na accumulation in HiMag may be of importance on soils with higher Na concentrations.
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Chloride concentrations were not different (P = 0.594) between HiMag and Barcel tall fescue (Table 1
). Previous reports detailing the macromineral concentration of HiMag tall fescue in comparison with other varieties of tall fescue have not discussed Cl. Whitehead (2000) reported that differences in Cl concentration among cool-season grass species are small.
The increase in DCAD attributable to K fertilizer application was less in HiMag (82 mEq/kg) than in Barcel tall fescue (130 mEq/kg; Table 3
). This was in large part due to the lower concentrations of K noted for HiMag vs. Barcel. Although lower in HiMag than in Barcel tall fescue, the concentrations of Na were too low in our trial to have a notable effect on DCAD.
K Fertilizer
In general, application of K fertilizer decreased concentrations of Mg in tall fescue, but the magnitude of the decrease was not consistent across the 5 harvests, resulting in a harvest x K fertilizer interaction (P = 0.001; Table 1
). Brown and Sleper (1980) reported a decrease in Mg concentration in 2 varieties of tall fescue when 50, 150, or 250 mg/kg of K were applied to the soil. Roche et al. (2002) reported no decrease in Mg concentrations with increasing K fertilizer application rates up to 225 kg/ha. The inconsistent response of Mg concentrations in grass forages in response to K fertilization has been noted in the literature, as reviewed by Whitehead (2000), and may be explained by the rate of K fertilizer application in relation to the requirement. Application of K fertilizer in amounts greater than required for maximum yield decreased the Mg concentration in the forage (Whitehead, 2000). This would suggest that experimental treatments in this study provided excess K in terms of that required for maximum yield, and that the magnitude of this excess was greatest for the fourth harvest, which showed the greatest magnitude of decrease (0.7 g/kg) in Mg concentration (Table 2
).
Application of K fertilizer decreased Ca concentrations in the first (P = 0.001), fourth (P = 0.001), and fifth harvests (P = 0.001), with no difference noted in the second (P = 0.748) and third (P = 0.200) harvests (Table 2
). Roche et al. (2002) reported a linear decrease in Ca concentrations with increasing levels of K fertilizer application up to 225 kg/ha. However, when the experiment was repeated, there was no response in Ca concentration to increased rates of K fertilizer application. Reith et al. (1964) illustrated a consistent depressing effect of K fertilizer on Ca concentration in the presence of N fertilization. In a summary of data from 3 harvests in each of 16 trials conducted over 3 yr, Adams (1973) found that K fertilizer application resulted in numerically lower Ca concentrations in 10 of the harvests, numerically higher concentrations in 34 of the harvests, and only significant (level of significance not given) decreases in 4 of the 48 harvests.
Application of K fertilizer increased the K concentration across all 5 harvests, but the magnitude of the increase ranged from 2.1 g/kg (first harvest) to 8.1 g/kg in the second harvest (Table 2
). Increasing K concentrations in grass in response to increasing K fertilizer has been shown in many studies (Adams, 1973; Dampney, 1992; Whitehead, 2000). Application of K fertilizer increased K concentrations in HiMag (P = 0.001) and Barcel (P = 0.001), but the increase was smaller in magnitude in HiMag (4.7 g/kg) than in Barcel (6.5 g/kg) tall fescue (Table 3
).
With the exception of grass harvested on October 6 (fifth harvest), K fertilization did not affect the Na concentration of grass (Table 1
). Grass harvested on October 6 receiving no K fertilization contained greater (P = 0.001) concentrations of Na than did grass receiving K fertilization (Table 2
). Pehrson et al. (1999) reported no effect of increasing the application rate of KCl fertilizer on Na concentration in first and second harvests of grass herbage. Application rates of K fertilizer were notably lower (7, 44, and 56 kg/ha) than used in the current study.
The response in S concentrations to K fertilizer was not consistent across harvests (Table 2
). Application of K fertilizer decreased (P = 0.025) S concentrations in first-harvest grass, increased S concentrations in second- and third-harvest grasses (P = 0.014 and 0.008, respectively), and had no effect on S concentrations in fourth- and fifth-harvest grasses (P = 0.351 and 0.122, respectively). McLaren (1976) reported that regardless of harvest, the application of 78 or 314 kg/ha of KCl fertilizer reduced S concentrations in grass, and hypothesized this was attributable to dilution with increasing yield or, second, that S uptake was reduced because of competition for uptake with Cl in the K fertilizer. Roche et al. (2002) found that increasing KCl fertilizer application from 0 to 225 kg/ha of K did not affect the S concentration of pastures in either of 2 experiments.
In this study, KCl fertilizer application inherently increased application of Cl, which increased the Cl concentration of tall fescue, although the magnitude of the response was not consistent across harvests (Table 2
). This observation is similar to the reports of Whitehead (2000) and Roche et al. (2002). Application of Mg fertilizer had no effect (P = 0.478) on Cl concentrations (Table 1
).
Application of K fertilizer did not affect (P = 0.221) the DCAD value of grass harvest on May 8 (first harvest) but did increase DCAD values by 157, 142, 158, and 58 mEq/kg of grass harvested for the second, third, fourth, and fifth harvests, respectively (Table 2
). Roche et al. (2002) reported higher DCAD values when the rate of K fertilizer applied to pasture was increased from 0 to 225 kg/ha.
Mg Fertilizer
Application of Mg fertilizer increased (P = 0.597) Mg concentrations in HiMag and Barcel tall fescue, but the increase was not consistent across the 5 harvests of grass, resulting in a harvest x Mg fertilizer interaction (P = 0.001; Table 1
). As shown in Table 2
, the increase in Mg concentrations attributable to Mg fertilizer application ranged from 0.16 to 0.80 g/kg in the first and fourth harvests, respectively.
Application of Mg fertilizer decreased Ca concentrations in HiMag and Barcel tall fescue, but the magnitude of the decrease was much greater in HiMag than in Barcel (0.34 vs. 0.09 g/kg; Table 3
). Previous studies comparing HiMag to other varieties of tall fescue did not include Mg fertilizer as an experimental variable (Wilkinson and Mayland, 1997; Crawford et al., 1998). Application of Mg fertilizer decreased (P = 0.002) the concentration of S regardless of variety or harvest (Table 1
).
Experiment 2
Harvest date affected DM yield (P = 0.001) and concentrations of K (P = 0.008), Na (P = 0.001), Cl (P = 0.013), and the DCAD (P = 0.009) but had no effect on S concentrations (P = 0.063) in HiMag tall fescue (Table 4
). The effects of K fertilizer formulation (KCl vs. K2SO4) on DM yield, concentrations of K, Na, Cl, and S (g/kg of DM), and the DCAD (mEq/kg of DM) in HiMag tall fescue are presented in Table 4
. Application of K fertilizer as K2SO4 increased (P = 0.011) the yield over that realized with K fertilizer applied as KCl.
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The DCAD was lower (P = 0.001) in grass fertilized with K2SO4 compared with that fertilized with KCl. This finding is in contrast with the results of Pehrson et al. (1999), who reported that the DCAD was decreased with the application of KCl fertilizer, and attributed this result to the increased Cl concentration in the grass. In the current study, the application of K fertilizer as KCl did not elicit the magnitude of positive response in Cl concentration reported by Pehrson et al. (1999). The average response in this study was 81%, in comparison with the 100% reported by Pehrson et al. (1999). The largest difference between the 2 studies was in the response of S concentrations in grass fertilized with KCl vs. K2SO4. In the current study, K2SO4 fertilizer application supported a mean increase in S concentration of 51%, whereas Pehrson et al. (1999) reported a small increase of 8% in S concentration for first-harvest grass. This can be explained by the difference in fertilizer regimens between the 2 studies. In the current study, the amount of KCl or K2SO4 fertilizer applied was based on K application, whereas in the study by Pehrson et al. (1999), the amounts and types of fertilizer applied were based on N application. Therefore, in the current study plots fertilized with KCl received no supplemental form of S, whereas in the study by Pehrson et al. (1999) grass fertilized with KCl also received S in the form of ammonium sulfate. The large increase in S concentrations in grass fertilized with K2SO4 noted in the current study, coupled with the numerically lower K concentration, resulted in a lower DCAD for HiMag tall fescue fertilized with K2SO4 compared with that fertilized with KCl.
Implications for Feed Formulation
Grass silage is often not included in the diets for transition (21-d prepartum) dry cows in the south coastal region of British Columbia because of its high K concentration and the subsequent need for anionic salts or products containing HCl to be included in the diet. To evaluate the effect of grass bred for mineral concentration in transition diets, rations were formulated using HiMag or Barcel tall fescue.
Diets containing HiMag had a calculated DCAD index of 26 vs. 28 for the diet containing Barcel tall fescue. To decrease the DCAD to a value of 50 mEq/kg (Goff, 2004), NutriChlor 18-8 (Nutritech Solutions, Abbotsford, British Columbia, Canada) was added to the diet at the expense of barley, canola, and corn distillers grains. Amounts of limestone and MgO were adjusted to account for the Ca and Mg concentration of NutriChlor 18-8. The diet containing HiMag required approximately 8% less NutriChlor 18-8 (1,361 vs. 1,474 g, respectively) than the diet containing Barcel tall fescue.
A duplicate exercise to evaluate the effect of fertilizer formulation was evaluated using nutrient values for HiMag tall fescue fertilized with KCl or K2SO4 (Table 2
, harvest 1). The diet containing HiMag fertilized with K2SO4 required approximately 10% less NutriChlor 18-8 to be added to the ration to achieve a DCAD value of 50 mEq/kg (1,600 vs. 1,450 g).
| CONCLUSIONS |
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| ACKNOWLEDGEMENTS |
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Received for publication July 11, 2005. Accepted for publication September 14, 2006.
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