|
|
||||||||


* Agriculture and Agri-Food Canada, Soils and Crops Research and Development Centre, Québec, Québec, Canada G1V 2J3
Department of Grassland Science, College of Animal Science and Technology, China Agricultural University, Beijing, P. R. China, 100094
Université Laval, Québec, Québec, Canada G1K 7P4
1 Corresponding author: tremblaygf{at}agr.gc.ca
| ABSTRACT |
|---|
|
|
|---|
Key Words: Phleum pratense milk fever hypomagnesemia near-infrared reflectance spectroscopy
| INTRODUCTION |
|---|
|
|
|---|
![]() |
![]() |
![]() |
![]() |
The DCAD1 formula is widely used in applied dairy cattle nutrition because it is well correlated with urinary pH and is predictive of clinical milk fever. DeGaris and Lean (2008) suggested that DCAD1 was the most effective formula for predicting the risk of milk fever, based on the simplified strong ion model and the meta-analysis of Lean et al. (2006). However, Charbonneau et al. (2006) reported that DCAD3 was most highly associated with milk fever (R2 = 0.44) and urinary pH (R2 = 0.85) according to their meta-analysis of 22 published studies.
To prevent milk fever, dairy cows should be fed a ration with a DCAD1, DCAD2, and DCAD3 of approximately –50, 150, and –42 mmolc/kg of DM, respectively, beginning from 3 to 4 wk before calving (Goff and Horst, 2003; Pelletier et al., 2008). The respective DCAD1 and DCAD3 values of forages should be no more than 250 and 290 mmolc/kg of DM to avoid adding excessive amounts of anionic salts, such as those based on CaCl2 or MgCl2, which reduce DMI (Horst et al., 1997; Pelletier et al., 2008). The occurrence of grass tetany is greatly increased for cattle grazing forages with a GT index higher than 2.2 (Jefferson et al., 2001).
Timothy (Phleum pratense L.) is the dominant perennial forage grass species grown in eastern Canada (Bélanger et al., 2001). Several studies have reported lower values of K concentration, the DCAD, or the GT index for timothy compared with other forage grasses such as orchardgrass (Dactylis glomerata L.) or phalaris (Phalaris aquatica L.; Thomas et al., 1998; Tremblay et al., 2006; Pelletier et al., 2008). Timothy is therefore a forage species well suited to decrease risks of milk fever and grass tetany. Data on the DCAD and the GT index of timothy and other forage species are commonly obtained after chemical determinations of several minerals, rendering the acquisition of these indices time-consuming and expensive.
Near-infrared reflectance spectroscopy (NIRS) has been widely used as a fast and cost-effective method for determining forage nutritive value (Shenk and Westerhaus, 1994). The ability of NIRS to predict forage nutritive value and many other organic substances is based on the rotational or vibrational energies of hydrogen bonds. Although minerals theoretically do not absorb energy in the near-infrared spectrum, some of the inorganic minerals in forages can be predicted by NIRS (Clark et al., 1987, 1989; Halgerson et al., 2004) through their association with organic molecules. The NIRS prediction of minerals has produced many inconsistent results in forage analyses. Clark et al. (1987) reported that NIRS calibrations for the macrominerals Ca, P, Mg, and K were useful in crested wheatgrass [Agropyron cristatum (L.) Gaertn.] and alfalfa (Medicago sativa L.). Halgerson et al. (2004) obtained similar results, in which concentrations of Ca, P, and K were accurately predicted in leaves and stems of alfalfa hay, whereas predictions of Mg and S were less consistent and prediction of Na failed. In contrast, Stoltz (1990) reported that calibrations for Ca, K, P, and Mg in alfalfa and white clover (Trifolium angustifolium L.) were unsuccessful, and in other studies, difficulties were also found in obtaining accurate NIRS predictions for minerals (Redshaw et al., 1986; Saiga et al., 1989). Based on reported successful NIRS predictions for some minerals needed in calculation of the DCAD and the GT index, we hypothesized that predicting the DCAD and the GT index is possible. To our knowledge, information on the possibility of predicting the DCAD and the GT index of timothy with NIRS is limited. The objective of this study was to evaluate the feasibility of using NIRS to predict Na, K, Ca, Mg, Cl, S, and P concentrations, as well as the DCAD and the GT index in timothy.
| MATERIALS AND METHODS |
|---|
|
|
|---|
A sample of approximately 500 g was taken from each plot, weighed, dried at 55°C in a forced-draft oven for 3 d, and then ground using a Wiley mill (Standard model 3, Arthur H. Thomas Co., Philadelphia, PA) to pass through a 1-mm screen. All dried and ground timothy samples (n = 1,108) were stored in plastic containers at room temperature in a dark room. Samples were scanned between July 7 and 19, 2006, at 2-nm intervals from 400 to 2,498 nm using a Foss NIRSystems 6500 monochromator (Foss, Silver Spring, MD) and spinning (ring) cups. Instrument performance was checked daily by running a performance test and analyzing the check cell. For each spectrum, principal components analysis scores were calculated by the H distance using the SCORES program of WinISI III software (version 1.61, Infrasoft International LLC, Silver Spring, MD). Based on the SELECT algorithm of the WinISI software, 240 timothy samples were then selected to form a calibration set, and the remaining 868 samples formed the validation set.
Chemical Analyses and NIRS Calibration
All timothy samples were analyzed for Na, K, Ca, Mg, Cl, S, and P concentrations as described by Pelletier et al. (2007, 2008). In brief, S was extracted by a method adapted from Mills and Jones (1996). Sodium and Ca were extracted by dry ashing (Miller, 1998) and K, Mg, and P were extracted using a method adapted from Isaac and Johnson (1976) and then analyzed with a Perkin-Elmer 3300 atomic absorption spectrometer (Perkin-Elmer, Überlingen, Germany) by flame emission for K and atomic absorption for Ca, Mg, and Na. Phosphorus and S were analyzed using an automated continuous-flow injection analyzer (QuikChem 8000 Lachat autoanalyzer, Zellweger Analytics Inc., Lachat Instruments, Milwaukee, WI). Chloride was extracted using a method adapted from Liu (1998) and measured with a Dionex DX 500 chromatograph equipped with an ASII HC column (Dionex Corporation, Sunnyvale, CA). For each mineral, 66 samples were randomly selected and analyzed in duplicate to determine the standard error of laboratory (SEL). The DCAD1, DCAD2, and DCAD3 were calculated with 3 different formulas (equations [1], [2], and [3]) and the GT index was calculated with equation [4], with each mineral expressed in millimoles of charge per kilogram of DM (g/kg of DM x 1,000 x valence/atomic weight; 1 mmolc/kg of DM = 1 mEq/kg of DM).
The regression method chosen to develop calibration equations for the DCAD, the GT index, and all related minerals was modified partial least squares (Shenk and Westerhaus, 1991). A repeatability file (n = 85) was created by collecting, during the scanning time, 5 spectra per sample using independently filled cups for 17 randomly selected samples, and this file was applied in every calibration process to account for possible operator errors (Nie et al., 2009a). To improve the calibration models, 20 spectral pretreatments were tested (WinISI III software, version 1.61, Infrasoft International LLC). The correction of the scatter effect was done using standard normal variate and detrending mathematical procedures were applied (Barnes et al., 1989). Several derivative pretreatments were evaluated: the derivatives used a 4-digit notation, in which the first digit was the number of the derivative, the second was the gap over which the derivative was calculated, the third was the number of data points in a running average or smoothing, and the fourth was the second smoothing. Two criteria were used to select the best spectral pretreatment parameters: simultaneous low standard errors (SECV) and high coefficient of determination (1 – VR) in cross-validation (Table 1). The best spectral pretreatment parameters were (1, 4, 4, 1) for Ca and Cl, (1, 10, 10, 1) for DCAD1, DCAD2, DCAD3, and the GT index, and (2, 5, 5, 2) for Na, K, Mg, S, and P. When developing the NIRS equations, 4 cross-validation groups were selected to choose the optimal number of terms and avoid overfitting (Shenk and Westerhaus, 1994).
|
|
|
![]() |
The calibration monitoring procedure implemented in the WinISI III software (version 1.61, Infrasoft International LLC) was used for validation of the equations. This procedure calculates 2 control limits: the bias control limits (BCL
0.6 SECV) and unexplained error control limits (UCL
1.3 SECV). These limits were respected except for Na (UCL = 1.5 SECV) and Cl (UCL = 1.35 SECV). The NIRS prediction performance was evaluated by several statistical criteria reported in Table 2. Generally, the coefficients of determination of prediction
and the ratio of prediction to deviation [RPD = SD of the reference data in the validation set/standard errors of prediction corrected for bias, SEP(C)] are considered for evaluating the accuracy of NIRS prediction (Williams, 2001; Nie et al., 2009a). The SEP(C) is calculated using the following formula (Naes et al., 2002):
|
|
|
|
|
The SECV is calculated in the same way as SEP(C) but is based on data from cross-validation. High
and RPD and low SEP(C) indicate good NIRS performance; a prediction with an
>0.90 and RPD >3.0 is usually classified as successful. The slope of the regression between predicted and measured values of each constituent for the validation set is also considered. As suggested by Williams (2001), a deviation of less than 0.05 from the slope value of 1.0 indicates successful NIRS equations.
Because low concentrations and a narrow range are generally observed for mineral concentrations, which could render R2 values misleading (Clark et al., 1989; Murray and Cowe, 2004; Nie et al., 2009b), some authors suggest evaluating the NIRS prediction of minerals by using the coefficient of variation rather than R2. As proposed by Clark et al. (1989), the coefficient of variation of prediction {CVP = [SEP(C)/mean] x 100} between chemically analyzed and NIRS-predicted values is considered a useful tool in evaluating NIRS performance across minerals. Clark et al. (1987, 1989) reported useful NIRS mineral equations with coefficients of variation ranging from 11 to 28% across 3 forage data sets, and Halgerson et al. (2004) accurately predicted several minerals by NIRS in alfalfa with coefficients of variation
20% and 1-VR
0.60. In the present study, the NIRS prediction performance was considered successful when RPD
3, CVP
20%, and
0.60 for minerals, and when RPD
3, CVP
20%, and
0.90 for DCAD and the GT index.
| RESULTS AND DISCUSSION |
|---|
|
|
|---|
Among the 3 DCAD, DCAD3 showed the highest mean value of 267.0 mmolc/kg of DM in the calibration set (Table 1); however, the mean values of all 3 were lower than the acceptable maximum for forage (Goff and Horst, 2003; Pelletier et al., 2008). The mean values of all 3 DCAD were approximately 12 mmolc/kg of DM lower in the validation (Table 2) than in the calibration set (Table 1) but the ranges of values were all extended to varying degrees in the validation set, possibly because of a larger number of samples. The sample statistics of the GT index were similar between the calibration and validation sets, and their mean values of 1.64 and 1.61 were much lower than the acceptable maximum value of 2.2 (Jefferson et al., 2001) for rations (Tables 1 and 2).
NIRS Calibration and Validation for Mineral Concentrations
All selected NIRS predictions of mineral concentrations used to calculate the DCAD and the GT index were cross-validated with 1-VR >0.60 (Table 1). The best prediction was observed for Cl concentration, with 1-VR of 0.96 and SECV of 0.82 g/kg of DM, and it was followed by predictions for K, Ca, and Mg, with slightly lower 1-VR values of 0.92, 0.91, and 0.86, respectively. The NIRS predictive accuracy for Na, S, and P was relatively low, with 1-VR of 0.66, 0.61, and 0.69 and SECV of 0.024, 0.25, and 0.23 g/kg of DM, respectively (Table 1).
Based on the criteria of CVP <20% and
>0.60 (Clark et al., 1987, 1989; Halgerson et al., 2004), the NIRS predictions for K, Ca, Mg, Cl, and P concentrations were successful, with CVP ranging from 6.6 to 11.4%, and
from 0.69 to 0.92, whereas those of S and Na were unsuccessful, with low
of 0.53 and 0.58 and a much higher CVP of 82.2% for Na (Table 2). The statistic of RPD was calculated as a secondary criterion for the prediction of mineral concentrations (Table 2). All successful equations classified by the criteria of CVP and
had RPD values higher than 3.0 except for P, with an RPD of 1.8 (Table 2). Meanwhile, the unsuccessful equations for Na and S both had a low RPD of 1.5 (Table 2). The NIRS predictions of K, Ca, Mg, Cl, and P concentrations, which were classified as successful based on the criteria of CVP and
all showed deviations of less than 0.05 from the slope value of 1.0 (Williams, 2001), with the slope values ranging from 0.97 to 1.01 (Table 2) in the validation sample set. The Na and S concentrations were predicted unsuccessfully, with slope values of 1.30 and 0.90 (Table 2), respectively; these values were not within the acceptable range (Williams, 2001).
The predictions of P and S were diversely classified as successful and unsuccessful according to their respective
values of 0.69 and 0.53. Other performance criteria for the prediction of those 2 elements, however, were close to each other, as shown by CVP of 8.2 and 12.9 g/kg of DM and RPD of 1.8 and 1.5 for P and S, respectively (Table 2). We suggest that the successful prediction of P should be used with caution because the
of 0.69 is close to the lower limit of a successful equation (0.60). On the other hand, the unsuccessful prediction of S could possibly be useful as a broad first approximation for selecting samples for more accurate analyses.
As explained by Clark et al. (1987) and Vazquez de Aldana et al. (1995), the successful prediction of mineral concentrations relies on their association with organic and hydrated inorganic molecules. Potassium, Ca, and Mg were found to be predictable by spectral peaks of their corresponding organic acid salts (Clark et al., 1989); the wavelength used for detecting Mg was also similar to the peaks from the chlorophyll spectrum. Other factors that influence the accuracy of NIRS equations are the average concentration and the range for each constituent (Murray and Cowe, 2004; Nie et al., 2008). The successful predictions of K, Ca, and Cl in the present study were mainly explained by their higher concentrations and ranges. For example, our prediction of Cl concentration was better than that reported by Halgerson et al. (2004) for oven-dried alfalfa stems (n = 58; SECV = 0.69 g/kg; 1-VR = 0.84); this can be explained by higher concentrations (mean = 8.39 g/kg of DM) and a greater variation in Cl concentrations (SD = 4.45 g/kg of DM) in the present study (Table 1) compared with those (mean = 3.85 g/kg of DM; SD = 1.71 g/kg of DM) reported by Halgerson et al. (2004). Our higher concentrations and greater variation in Cl concentrations were partly caused by the application of different amounts of Cl fertilizers, including CaCl2 and NH4Cl.
The concentrations and range of values of Mg were relatively low compared with K, Ca, and Cl, but prediction of Mg was more successful than that of P and S, which had similar concentrations and ranges of values (Tables 1 and 2). This result could possibly be attributed to its better detectability in the near-infrared spectral region.
Previous analyses suggest that P and S exist in forms detectable by NIRS in some forages (Saiga et al., 1989; Cozzolino and Moron, 2004). Both P and S in plants exist in multiple valences and in different organic forms, such as phytate, phospholipids, and nucleic acids for P, and the proportion of total P and S in different forms varies seasonally or among species and genera. This attribute may lead to unstable NIRS calibrations and inconsistent prediction results. Prediction of P in our study, however, was comparable with that reported by Clark et al. (1987) in 100 crested wheatgrass samples (SEP = 0.20 g/kg, R2 = 0.84), by Halgerson et al. (2004) in oven-dried alfalfa leaves (SECV = 0.20 g/kg, 1-VR = 0.74) and stems (SECV = 0.22 g/kg, 1-VR = 0.63), and by Vazquez de Aldana et al. (1995) in 75 samples of natural grasslands (SEP = 0.22,
= 0.73). Prediction of S failed in our study and variable results were reported by Clark et al. (1989) in crested wheatgrass (SEP = 0.16 g/kg, R2 = 0.61), by Halgerson et al. (2004) in oven-dried alfalfa leaves (SECV = 0.43 g/kg, 1-VR = 0.12) and stems (SECV = 0.10 g/kg, 1-VR = 0.74), and by Cozzolino and Moron (2004) in legumes (SEP = 5.5 g/kg and
= 0.70). In our study, the prediction performance of P and S was restricted by their low concentrations and ranges of values. However, because P mean concentrations and range values (2.58 and 2.32 g/kg of DM in the calibration set, and 2.61 and 3.34 g/kg of DM in the validation set, respectively) were slightly higher than those of S (2.09 and 2.13 g/kg of DM in the calibration set, and 2.05 and 2.02 g/kg of DM in the validation set, respectively), we obtained a better prediction performance for P, with
of 0.69, CVP of 8.2%, and RPD of 1.8, which was classified successful, whereas S was predicted with
of 0.53, CVP of 12.9%, and RPD of 1.5 (Table 2).
The unsuccessful prediction of Na concentration in timothy was mainly attributed to its low concentration, with an average value of 0.042 g/kg of DM (Table 1), which is well below the lowest recommended limit of NIRS analysis (1 g/kg), and to its narrow range of 0.002 to 0.422 g/kg of DM in all timothy samples. The excellent precision of Na determinations, as indicated by an SEL of 0.003 g/kg of DM and a CVR of 7.5% (Table 1), was not sufficient to compensate for the low values and narrow range. Even with greater concentrations of Na (2.3 g/kg of DM) and S (30 g/kg of DM), and wider ranges of concentrations of Na (0.2 to 6.8 g/kg of DM) and S (20 to 72 g/kg of DM) than in our study, Cozzolino and Moron (2004) reported NIRS predictions of Na (SEP = 1.2 g/kg of DM;
= 0.61) and S (SEP = 5.5 g/kg of DM;
= 0.70) in legumes that were not much better than in our study.
NIRS Calibration and Validation of DCAD and the GT Index
Calibration and cross-validation showed that NIRS predictions for all the DCAD and the GT indices were qualified, with 1-VR
0.90, SECV of 35.2 to 37.0 mmolc/kg of DM for the DCAD, and 0.21 for the GT index (Table 1). Based on the validation set, NIRS predictions were successful for DCAD1, DCAD2, and DCAD3, with
of 0.92, 0.90, and 0.92, and RPD values of 3.4, 3.2, and 3.5, respectively (Table 2). The CVP values of 17.9% for DCAD1, 19.1% for DCAD2, and 13.9% for DCAD3 (Table 2) were all lower than the value of 20% suggested as the maximum for successful predictions of mineral concentrations. Based on
RPD, and CVP, DCAD3 was predicted with the best accuracy, followed by DCAD1 and then by DCAD2. The slope values, ranging from 0.99 to 1.00 (Table 2), also indicate that all 3 DCAD were predicted with good accuracy (Williams, 2001).
The predictions of all 3 DCAD were successful even though Na and S concentrations, which are used in the calculation of all 3 DCAD, were both predicted unsuccessfully by NIRS. This result could be explained by the minor influence of these 2 minerals on DCAD values; Na and S were among the lowest concentrations as compared with other minerals, especially K and Cl. The better NIRS prediction of DCAD3 than DCAD1 can be explained by the influence of unsuccessful prediction of S concentration, which was weakened by adding a coefficient of 0.6 for S in the DCAD3 calculation. The slightly lower prediction accuracy for DCAD2 than for the 2 other DCAD predictions can be attributed, in part, to the fact that the calculation of DCAD2 involves more minerals (Ca, Mg, and P); these minerals would introduce their own laboratory errors into the calculated values of DCAD2.
The best NIRS prediction for the GT index had a 1-VR value of 0.91 and an SECV of 0.21 (Table 1), and the statistics for the validation set
= 0.93, RPD = 3.7, CVP = 11.6%, and slope = 0.97; Table 2) confirmed that this equation was successful. Good NIRS prediction of the GT index reflects the fact that concentrations of K, Ca, and Mg were successfully predicted (Tables 1 and 2).
This study focused on a single grass species, and we have demonstrated the possibility of predicting the DCAD and the GT index of timothy. Most forage grown in eastern Canada, however, is based on several species, including both legumes and grasses, within the same field. Applying these NIRS equations to other plant species or mixtures of different species should be done with great caution. To develop more robust and practical NIRS predictions for rapid analyses of minerals, DCAD, and GT indices, further research is required in which the NIRS prediction of samples of multiple forage species would be studied.
| CONCLUSIONS |
|---|
|
|
|---|
| ACKNOWLEDGMENTS |
|---|
|
|
|---|
Received for publication December 12, 2008. Accepted for publication May 6, 2009.
| REFERENCES |
|---|
|
|
|---|
| ||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |