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* University of Hohenheim, Institute of Animal Nutrition (450), Emil-Wolff-Str. 10, 70599 Stuttgart, Germany
Department of Agricultural, Food and Nutritional Science, University of Alberta, Edmonton, Alberta, Canada T6G 2P5
2 Corresponding author: zebeli{at}uni-hohenheim.de
| ABSTRACT |
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Key Words: particle length enzyme activity rumen fermentation dairy cow
| INTRODUCTION |
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Although the effects of PL of CS on digestive processes in high-yielding dairy cows have been extensively investigated (e.g., Bal et al., 2000; Yang and Beauchemin, 2005, 2006a), results obtained from these studies have not been conclusive. For example, some studies found that PL of CS had no effect on chewing activity (Kononoff et al., 2003a) or ruminal pH (Bal et al., 2000; Beauchemin and Yang, 2005; Yang and Beauchemin, 2006a), and other reports suggested that decreasing PL of CS can compromise chewing activity (Beauchemin and Yang, 2005; Yang and Beauchemin, 2006a) or fiber digestion (Bal et al., 2000; Yang and Beauchemin, 2005). However, most of the studies conducted to investigate effects of PL of CS on digestive parameters in dairy cows used CS as a single forage source with a high concentrate level (>45%), and hence the content of dietary fiber in these studies was maintained at a relatively low level (23 to 32% NDF on DM basis). In a recent meta-analysis, Tafaj et al. (2007) concluded that digestive effects of PL of CS, contrary to effects of PL of grass silage, should be considered in relationship with dietary NDF and particularly forage NDF proportion in the diet. We hypothesized that decreasing PL of CS may still exert positive effects on fermentation and fibrolytic activity in the rumen of high-producing dairy cows fed diets that contain also a small portion of fiber-rich hay (i.e., 33 to 35% dietary NDF on DM basis), regardless of a high dietary concentrate level (50% on DM basis).
The main objective of this study was to evaluate effects of PL of CS on feed intake patterns, sorting consumption, fermentation profile, and activities of non-starch polysaccharide (NSP)-degrading enzymes in the rumen of lactating Holstein cows. Another objective was to examine if certain measures of particle fractions, determined by Penn State Particle Separator (PSPS), are useful in predicting the effect that PL of CS had on digestive parameters measured.
| MATERIALS AND METHODS |
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Cows were fed 1 of 3 diets as TMR containing 40% CS, 10% coarsely chopped grass hay (PL = 30 mm), and 50% concentrate (Table 2
). The inclusion of 10% fiber-rich grass hay in TMR aimed at obtaining a "marginal" NDF content for a diet containing 50% concentrates. Diets were chemically similar, but differed only in the PL of CS (i.e., long, medium, and short). Each experimental period lasted 23 d with the first 11 d used for adaptation to the diet. To protect silage from aerobic deterioration, only 1 silo bag per 23-d period was opened, and 3 treatments were sequentially and randomly allocated to the cows in 4 experimental periods.
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Particle Size Distribution and Physically Effective Fiber of Diets
Samples of TMR, CS, and feed refusals were collected on 8 occasions during each period and used for particle size distribution analysis and determination of physically effective NDF (peNDF) contents. The new compact, manually operated PSPS with 3 sieves and a solid bottom pan (model C24682N, Nasco, Fort Atkinson, WI) was used as described by Kononoff et al. (2003b). The material remaining on each sieve and pan was removed, weighed, and oven-dried at 60°C to determine the distribution of feed DM retained on each sieve and on the pan. The peNDF was determined either as the sum of DM proportion retained on sieves of 19- and 8-mm of PSPS multiplied by the NDF content of the diet (peNDF>8), or as the sum of particles retained on sieves of 19-, 8-, and 1.18-mm multiplied by the NDF content of the diet (peNDF>1.18) multiplied by the NDF content of the diets (Kononoff et al., 2003b). For particles retained on the 19- and 8-mm sieves (i.e., >8 mm), the NDF content was also determined, and this proportion of peNDF contained in particles >8 mm was defined as peNDF>8-NDF.
Feed Intake and Sorting Index
Feed intake was recorded for each cow after the adaptation period for 6 d of each period. The TMR was offered in intake control feeders (WestfaliaSurge GmbH, Bönen, Germany). Each feeder was equipped with an access gate that was programmed to allow a specific cow to access a feed bin, and 2 infrared sensors that recorded the presence of the cow in the feeder. A computer connected to the feeder recorded time at the start and end of each visit of the cows continuously over 24 h. Start and stop times were recorded to the nearest 1 s and bin weights to the nearest 0.05 kg of feed. Therefore, the time spent eating was calculated based on the time the cows were present in the feeders and at least 0.05 kg of feed was consumed. The feed refusals were collected daily at 0700 h.
To evaluate the selective feed consumption for particular fractions of particles retained on the screens of PSPS, a sorting index was calculated based on the differences in particle size distribution between the offered TMR and feed refusals as described by Silveira et al. (2007). A sorting index of 1 indicated no sorting, whereas a sorting index of <1 indicated sorting against, and >1 indicated sorting in favor of particles retained on a particular screen of PSPS.
Chemical Analyses and In Vitro Degradation Kinetics
Samples of CS were taken on 4 occasions from each silo, isolated in plastic bags, immediately frozen at –20°C, and analyzed for fermentation parameters using the method of von Lengerken and Zimmermann (1991). The degradation characteristics of CS were determined based on cumulative in vitro gas production (incubation time of 72 h) using the Hohenheim Gas method (Menke and Steingass, 1988). Rumen fluid for incubation was collected from 2 cows 1 h before morning feeding. Degradation kinetics were defined by fitting the exponential equation: p = a + b(1 – e–ct), where p is gas production at time t, a + b is the potential gas production, and c is the fractional rate of gas production used as an index for fractional DM degradation rate (Zebeli et al., 2008a).
Samples of CS, TMR, and orts were collected daily during each collection period and used for DM determination, and 4 composite samples were stored for proximate analysis. Dried, composite samples were ground to pass a 1-mm screen using a lab mill (SM 100, Retsch, Haan, Germany). Dry matter content and the chemical composition of feeds and orts were determined according to official analytical methods of the Union of German Agricultural Research Stations (VDLUFA; DM: section 3.1; OM: section 8.1; ether extract: section 5.1.1; CP: section 4.1.1; Naumann and Basler, 1997). The methods described by Van Soest et al. (1991) were used in analyses of NDF and ADF including the use of amylase and sodium sulfite in the NDF procedure.
Parameters of Ruminal Fermentation
Fermentation profile was investigated in 2 ruminal phases (i.e., particle-associated rumen liquid, PARL; and free rumen liquid, FRL) to test separate responses to PL within the rumen. A sample of approximately 250 mL of FRL was collected from the ventral rumen sac using a vacuum pump (VT 4.2, Becker, Wuppertal, Germany) and filtered through 4 layers of cheesecloth, as used in the Hohenheim Gas technique (Menke and Steingass, 1988). Collection of PARL was as described previously (Zebeli et al., 2008a). The sampling of digesta was carried out at 0700, 1000, 1500, and 1800 h on d 18 of each experimental period.
The pH value was measured immediately after sampling using a pH electrode (InLab 412, Mettler-Toledo, Greifensee, Switzerland). Approximately 100 mL of fluid was centrifuged at 2,010 x g for 20 min. Two replicates (5 mL each) of supernatant were frozen at –30°C for determination of VFA concentrations as described by Zebeli et al. (2008a).
Enzyme Activities
The activities of selected NSP-degrading enzymes were measured in supernatants obtained from PARL or FRL using an agar diffusion assay. Digesta samples were collected on d 21 of each period at 2 sampling times (i.e., 0700 and 1100 h). Sampling of digesta was the same as described above, and the procedure for obtaining the supernatants from PARL and FRL for agar diffusion assay was described by Ölschläger (2007). Briefly, 4 g of homogenate of digesta was mixed with 4 mL of protease inhibitor (Sigma-Aldrich, Schnelldorf, Germany) and centrifuged (Megafuge 2.0, Heraeus, Hanau, Germany) for 10 min at 1,800 x g at 4°C. The supernatants were collected and recentrifuged (Biofuge fresco, Heraeus) for 20 min in 13,000 x g at 4°C. The obtained supernatants were collected using a 10-mL sterile syringe (Becton Dickinson, Franklin Lakes, NJ) and sterile-filtered through a cellulose-acetate-filter (FP 030/3, 0.2 µm, Rotrand, Schleicher and Schuell, Dassel-Rellinhausen, Germany).
To determine the activities of NSP-degrading enzymes, digesta supernatants were assayed in specific agar substrates including 1.3–1.4-β-glucan (medium viscosity barley), carboxymethyl-cellulose (CMC)-4M, galactan (potato), arabinoxylan (medium viscosity wheat), polygalacturonic acid (orange), and 1.4-β-mannan (medium viscosity guar). With exception of polygalacturonic acid that was purchased from Sigma-Aldrich (Schnelldorf, Germany), all other specific substrates were purchased from Megazyme International Ltd. (Wicklow, Ireland). The resulting enzymatic degradation of specific agar substrates was used as an indication of the activities of NSP-degrading enzymes, respectively, of 1.3–1.4-β-glucanase, carboxymethylcellulase (CMCase), galactanase, xylanase, polygalacturonase, and mannanase.
The agar diffusion assay used in this study to measure the enzyme activities was the same as described by Vahjen et al. (1997) with minor modifications. Briefly, after dissolving each substrate in 20 mM Bis/ Tris at pH 6.3 (Sigma-Aldrich), the solution was boiled for 10 min in a microwave oven (600 W). Subsequently, Gelrite (Roth, Karlsruhe, Germany) was added as solidifier and boiled again until all particles were dissolved. After this, the hot solution was cooled to 60°C and uniformly poured into 25- x 25-cm polycarbonate Petri dishes (Nunc, Wiesbaden-Schierstein, Germany) and allowed to solidify at room temperature to obtain the specific agar substrates. The measurement of enzymatic degradation of substrates in agar plates in form of lysis zones was also described previously (Vahjen et al., 1997). The procedure for determination of enzymatic degradation of substrates in agar plates and quantification of lysis zones through a computer-assisted evaluation system (Raytest, Straubenhardt, Germany) are described in details by Vahjen et al. (1997).
In Sacco and Total-Tract Apparent Digestibility
To investigate the effect of PL of CS on DM and NDF degradation in the rumen, in situ bags made of Dacron polyester cloth (5 x 10 cm) with pore size of 52 ± 5 µm (mean ± SD) were used. In each period, 3 replicates of TMR (
5 g of sample each) identical to that fed to the animals (i.e., not dried or ground samples) were weighed into bags and soaked in warm water for 10 min to simulate the addition of saliva before insertion into the rumen for 24 h. Bags were dried at 60°C for 48 h and ruminal DM and NDF degradability were measured by difference.
Apparent digestibility of nutrients in the total digestive tract was determined using TiO2 as an external marker (40 g per animal per day was mixed with 500 g of concentrate and fed for 10 d twice daily in 2 equal meals, shortly after milking). Fecal samples (
200 g, wet weight) were collected during the last 7 d of marker feeding, every 8 h from rectum, and were pooled and stored at 4°C. After mixing, subsamples were dried at 65°C and ground in a Retsch mill to pass a 1-mm screen and stored for chemical analysis. Apparent nutrient digestibility in the total tract was calculated as described by Zebeli et al. (2007a).
Statistical Analyses
All data were analyzed using PROC MIXED of SAS (SAS Institute, 2003). The model included the random cow effect and the fixed effect of PL. In addition, period was considered as a random effect, and lactation day of the cows was used as a covariate in the analysis of covariance (Mielenz et al., 2006) to account for the error term related to differences among periods.
Feed intake and eating patterns were analyzed by considering the measurements in 6 d and 24 h, respectively, as longitudinal repeated measures using a first-order autoregressive covariance structure, which assumes that the covariance of measurements at the same animal i decays with time t[cov (eit, eit') =
2
|t-t'|, where 0

1; Littell et al., 1998]. For the analysis of ruminal fermentation and enzyme activities, the measurements of the same animal at different sampling sites and times were considered as time repeated measures and were analyzed using a compound symmetry and unstructured covariance structure (Littell et al., 1998). Data of particle size distribution of diets and orts were averaged 4 times per period and analyzed by considering the fixed effect of PL and the random effect of replication within treatment. To test a linear or quadratic effect of PL on response parameters, the orthogonal contrasts were performed using the CONTRAST statement of SAS (SAS Institute, 2003). The LSM and the respective pooled SEM were computed. The degrees-of-freedom were adjusted with the Satterthwaite method. Significance was declared at P
0.05 and a tendency was considered if 0.05 < P
0.10.
| RESULTS AND DISCUSSION |
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The results in Table 1
showed that CS did not differ in chemical composition, concentrations of VFA and lactate, as well as pH and in vitro degradation characteristics, excluding an effect of PL on the quality of CS.
Particle Size Distribution and Contents of Physically Effective Fiber
Proportions of particles retained on different screens of PSPS and the contents of peNDF in TMR are shown in Table 2
. As expected, proportion of DM retained on 19- and 8-mm screens of PSPS linearly decreased (P < 0.01) as the PL of CS decreased, and this was reflected in a significant decrease in peNDF>8 and peNDF>8-NDF. These results are in agreement with other studies that used the new PSPS to measure particle size distribution of CS-based TMR (Kononoff et al., 2003a; Yang and Beauchemin, 2006a). Decreasing PL of CS at harvesting from 28.6 (long) to 15.9 (medium) and then to 4.8 (short) mm, Yang and Beauchemin (2006a) reported significant decreases of dietary peNDF>8 or peNDF>8-NDF from 17.6 to 14.8 and then to 10% or from 22.2 to 18.8 and then to 11.9%, respectively. The lower contents of peNDF>8 compared with peNDF>8-NDF in the diets can be attributed to the fact that the method of peNDF>8 underestimates the NDF content of the fraction of particles >8 mm by assuming uniform NDF content of all particle fractions. However, given that both these methods gave similar rankings of the dietary peNDF contents, and that the measurement of peNDF>8 is a more practical and less costly procedure than the measurement of peNDF>8-NDF, the first method would be more applicable on the farm.
In contrast, the peNDF>1.18 contents of the diets were not different among treatments (P > 0.10; Table 2
). This is in agreement with Yang and Beauchemin (2006a), who also did not find any differences in the content of dietary peNDF>1.18 (28.3, 26.6, and 26.5% for long, medium, and short, respectively). In both studies, the differences in peNDF>1.18 content among treatments were leveled out because of a significant increase (i.e., from 42.0 to 50.0 and then to 57.8% in present study and from 33.8 to 38.6 and then to 52.8% in the study of Yang and Beauchemin, 2006a) of the fraction of particles retained between the 1.18- and 8-mm sieves with decreasing PL of CS.
Eating and Sorting Patterns
Results of feed intake and sorting index are given in Table 3
, whereas data of eating patterns and time are shown in Figure 1
. Cows linearly decreased sorting in favor of the particle fraction retained between 1.18- and 8-mm and fine particles (i.e., particles passing through the 1.18-mm screen; P < 0.01) as well as against peNDF>1.18 content of TMR (P = 0.04) as PL of CS was decreased. Decreased sorting activity in favor of fine particles with decreasing PL of CS in TMR was also reported by Kononoff et al. (2003a). In contrast, sorting against long particles (i.e., >19 or 8 mm) and against the contents of peNDF>8 or peNDF>8-NDF of TMR was not affected by treatment in this study (Table 3
). In addition, decreasing PL of CS linearly increased DMI of particles retained between the 1.18- and 8-mm sieves, which led to a quadratic increase of peNDF>1.18 intake (P < 0.01; Table 3
). In contrast, intakes of DM retained on 19-and 8-mm screens of PSPS and peNDF>8 or peNDF>8-NDF were significantly decreased with decreasing PL of CS.
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Ruminal Fermentation
Ruminal pH and VFA concentration were not affected by treatment in this study (Table 4
). This result agrees with other studies (Kononoff et al., 2003a; Beauchemin and Yang, 2005; Yang and Beauchemin, 2006a), which similarly reported unchanged ruminal pH independent of dietary differences (i.e., differences in PL of CS at harvesting, fractions of particles >8 mm or contents in peNDF>8 and peNDF>8-NDF). However, although the contents of peNDF>8 or peNDF>8-NDF in TMR were reduced in response to a decreasing PL of CS, the fraction of particles retained between the 1.18- and 8-mm screens was increased such that the difference in peNDF>1.18 content among diets was minimized (Table 2
). The greater fraction of particles retained between the 1.18- and 8-mm screens with decreasing PL of CS may have balanced the lower content in particles >8 mm, and hence contributed to leveling out the differences in ruminal pH and VFA concentration among treatments. In addition, the inclusion of the fiber-rich hay resulted in increased NDF and peNDF contents (e.g., peNDF>1.18 exceeded 28% on a DM basis) in TMR, which in turn might have lowered the influence of PL of CS on ruminal pH.
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Because no interaction was observed between sampling site (i.e., FRL vs. PARL) and dietary PL (P > 0.10; i.e., the response of fermentation parameters followed similar trends in FRL and PARL), only data of ruminal fermentation for FRL are presented. The only difference between PARL and FRL was that FRL had higher pH (0.49 ± 0.06 pH units; P < 0.01) and lower VFA concentrations (39.1 ± 4.12 mM; P < 0.01) compared with PARL, in agreement with our previous observations (Zebeli et al., 2008a). The lowest pH (nadir) measured was achieved at 1500 and 1800 h (i.e., 7 to 10 h after the feeding; result not shown), which corresponded to the greatest concentrations of VFA. The nadir was achieved near the range of Nordlund and Garrett (1994), who proposed to sample 4 to 8 h postfeeding in TMR-fed herds to measure ruminal pH near the nadir.
Enzyme Activities
The activities of NSP-degrading enzymes are in Table 5
, which also are shown only for FRL, because no interaction was observed between sampling site (i.e., FRL vs. PARL) and dietary PL (P > 0.10; result not shown). In general, decreasing PL of CS linearly or quadratically (i.e., activity of mannanase) increased the lysis zone of almost all specific agar substrates investigated in this study (Table 5
). A greater fibrolytic activity of rumen digesta with decreasing PL agrees with results of Zebeli et al. (2008a), who reported similar results using in vitro trials.
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5.8 throughout this study (result not shown). The latter indicates that cows of this study apparently were not at risk of subacute ruminal acidosis (Beauchemin et al., 2003; Zebeli et al., 2008b), and hence the likelihood that diet may adversely affect the counts of fibro-lytic microbiota in the rumen is very low (Zebeli et al., 2008b). In addition, these results suggest that if dairy cows are fed diets that do not present any apparent risk of subacute ruminal acidosis (as in this study), lowering of the PL of CS may be beneficial due to increasing fiber degradation in the rumen, particularly by stimulating the activities of NSP-degrading enzymes.
In Situ and Total-Tract Digestibility
In situ and total-tract digestibilities of DM and nutrients are given in Table 6
. Decreasing the PL of CS in the diet tended to increase in situ 24-h NDF disappearance (P = 0.07), which was also reflected in a quadratically increased total-tract NDF digestibility (P = 0.02). The results of in situ NDF digestibility are generally in agreement with activities of NSP-degrading enzymes in the rumen. Thus, the quadratic increase of in situ NDF digestibility with decreasing PL of CS can be explained by a greater activity of NSP-degrading enzymes of rumen microbiota. However, in terms of maximization of feed efficiency, only the moderate reduction of PL of CS was shown to be beneficial. Although DMI was similar for all diets, the medium PL had the greatest NDF and NFC digestibility. A further decrease in PL to a fine particle size decreased both NDF and NFC digestibility, which is undesirable in terms of maximizing energy efficiency.
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| CONCLUSIONS |
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| ACKNOWLEDGEMENTS |
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| FOOTNOTES |
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Received for publication October 30, 2007. Accepted for publication February 15, 2008.
| REFERENCES |
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