1. Introduction
At harvest, whole-plant corn (WPC) is typically processed using an on-board kernel processor featuring a pair of closely spaced toothed rolls operating at differential speeds. The main goal of processing in this fashion is to size reduce the grain fraction, hence the term “kernel processor”. The corn kernel pericarp protects the endosperm, and the pericarp is highly resistant to rumen microbial attachment and enzymatic digestion if it is left intact [
1]. Processing breaks the seed coat, creating greater starch surface area, and ruminant starch digestion is enhanced [
2]. The fraction of total starch that passes through a 4.75 mm sieve is defined as the Corn Silage Processing Score (CSPS), with an optimal score of at least 70% [
3]. The efficacy of current kernel processing as quantified by the CSPS is often variable, influenced by both crop factors and harvester configuration. Salvati et al. [
4] reported that 38% of United States Midwest producers surveyed were not achieving the optimum CSPS score.
Although processing WPC with a kernel processor improves starch utilization, its use has shown to have variable impact on the digestibility of the fiber fraction [
5,
6,
7,
8]. Research has shown that fiber digestibility was not significantly improved or even decreased when WPC was processed with conventional kernel processors [
9,
10]. Corn stalks are structurally strong [
11] with high lignin content, and thus, processing by shredding them with a conventional kernel processor may not create enough improvement in the specific surface area to affect fiber digestion [
6]. One potential way to improve the utilization of the fiber fraction of WPC is through new processing mechanisms that dramatically change the physical form of not only the grain fraction but also the non-grain fractions of WPC. This is the focus of this research.
Any new mechanism to change the WPC physical properties should increase the specific surface area of the non-grain fractions without excessive particle size reduction of the fiber fraction. Physically effective NDF (peNDF) is the fraction of fiber that stimulates chewing activity. It is primarily related to particle size and promotes rumination and saliva production [
12]. The most effective way to increase WPC peNDF using current technology is to increase the theoretical length of the cut at harvest, but this can lead to reduced CSPS [
7], reduced harvester throughput and shortened processor roll life. Alternatives to the conventional roll processors should be explored that produce greater WPC digestion, maintain fiber length, and consistently provide optimal CSPS.
This work focused on a new method of improving WPC digestion by a novel mechanical processing technique using impact and shredding. Our first hypothesis was that processing by impact and shredding would substantially alter the physical properties of not only the grain fraction of WPC, but also the fiber fraction. An additional hypothesis was that these physical changes would improve in situ DM digestion in ruminant dairy cows. The specific objectives were to: (a) modify a hammermill to process WPC through a combination of impact and shredding; (b) quantify the physical properties of processed WPC as affected by crop maturity, number of processing operations, processor configuration, and process timing; and (c) quantify the compositional, fermentation, and in situ digestion of WPC silage that was processed prior to ensiling.
2. Materials and Methods
2.1. Impact–Shredding Processor
Greater physical disruption of forage crops was obtained through a combination of impact and shredding than by shredding alone [
13]. Therefore, to process WPC by both impact and shredding, a screenless hammermill was developed (
Figure 1). Disruption of the plants’ physical structure occurred by impact with the high-speed hammers with some additional attrition by shredding as the material was dragged along the roughened surface of the scroll. The experimental impact–shredding processor had a 50 cm wide rotor featuring three rows of hammers each with 22 free swinging hammers that were 4 mm thick and spaced 19 mm apart. The traced radius of the hammers was 25 cm, and the radial clearance between the scroll and the hammers was 10 mm. The peripheral speed of the hammers was generally 80 m·s
−1, except for experiments where rotational speed of the rotor was varied (see
Section 2.7). A scroll without openings replaced the typical hammermill screen. Input flow of chopped material occurred tangentially into the path of the hammers where, after impact, it was dragged along the scroll through an arc of 180 degrees before exiting tangentially (
Figure 1). To facilitate shredding, the scroll featured a roughened diamond plate surface (part number 3DRW1, Grainger, Chicago, IL, USA). The rotor was powered by a John Deere (Moline, IL, USA) model 7235R tractor through a belt drive that increased rotor speed to a maximum of 3056 rev·min
−1 when the tractor PTO was operated at 1100 rev·min
−1. Material recirculation was not observed, and thus, the time to traverse the 0.785 m arc from the input to the exit was less than 0.01 s at the hammer tip speed of 80 m·s
−1. The mechanism was stationary, and material was brought to it for processing.
2.2. Experiments Conducted
A total of seven experiments related to processing performance were conducted (
Table 1). These experiments were conducted to test the hypothesis that processing by impact and shredding changed important physical properties of both the grain and fiber fraction of WPC. These experiments determined how processing level was affected by crop maturity, processor configuration, and process timing (i.e., pre- or post-storage). An additional experiment was conducted to examine the hypothesis that impact–shredding processing changed the in situ DM digestion of WPC in ruminant dairy cows.
Four treatments were investigated in most experiments: chopped but unprocessed (UP), and UP material that was subsequently processed once or twice with the experimental processor (1X and 2X, respectively). The fourth treatment, which served as the control, was chopped and processed with the harvester’s on-board kernel processor (KP) (see
Section 2.4). In all experiments, there were three replicates per treatment, and treatments were created in random order.
2.2.1. Impact of Crop Maturity
Experiments 1–4 were conducted to investigate the effect of using the experimental processor across different WPC maturities. This was accomplished by harvesting and processing in a similar fashion but on four different days over a 20-day period.
2.2.2. Specific Energy Requirements and Rotor Speed
Experiments 5 and 6 were conducted to quantify the specific energy requirements of processing. In the latter experiment, three different processor peripheral speeds were used (51, 65 and 80 m·s
−1) (see
Section 2.7).
2.2.3. Chop Length
It was observed that processing with the experimental processor considerably reduced the material particle size. Therefore, Experiment 7 was conducted using 100 mm theoretical length of cut (chop length) to determine if the final particle size of the processed whole plant could be increased by doubling the initial chop length (50 mm was used in Experiments 1–6) of the UP material used to create the 1X and 2X treatments.
2.3. Additional Investigations
2.3.1. Process Timing
Processing by impact and shredding was considered as an alternative to the kernel processor currently used on forage harvesters. However, processing with the experimental processor could alternatively occur after ensiling and just prior to feeding. This alternative process timing was investigated using material harvested during Experiment 1. To create fermented material for post-storage processing, three additional replicates of UP material were placed into 19 L plastic containers, compacted using the procedure described in
Section 2.5, and then sealed. This material was stored indoors for 81 days. After storage, the fermented contents of the three replicate containers were removed, consolidated, and homogenized by hand mixing. The homogenized material was then halved by mass and further subdivided into three replicates per treatment, which were then processed in the experimental processor either once or twice (1X or 2X).
2.3.2. Processing of Plants without Ears
Processing as investigated here changed the physical properties of both the kernel and non-grain fractions of the plant. To investigate the impact of processing on just the stalk and leaves, additional crop treatments were created during Experiments 4 and 7. These were created by removing the ears by hand prior to chopping. Using this material, additional UP, KP, 1X, and 2X treatments were created as described above.
2.4. Harvest Procedure
Details of the WPC crop used in all experiments is provided in
Table 1. For all experiments, WPC was harvested using a New Idea (Coldwater, OH, USA) model 6200 forage harvester. Average stubble height was 27 cm. Except where noted, the unprocessed WPC that was subsequently processed in the experimental processor was chopped at 50 mm chop length. For the KP treatment, WPC was chopped at 25 mm chop length and then processed with the forage harvesters on-board roll-type kernel processor operating at 15% speed differential with 2 mm roll gap. Except when power requirements were measured (see
Section 2.7), the stationary processor was fed with a 28 cm wide by 5.5 m long conveyor. Typical mass-flow rate into the processor is provided in
Table 1.
2.5. Properties Quantified
Each replicate for all treatments and experiments generated approximately 20 kg wet matter (WM) of material from which sub-samples were randomly collected to quantify various material properties. For all experiments, two 400 g WM sub-samples per replicate were collected by hand to determine DM content by oven drying at 105 °C for 24 h in accordance with ASABE Standard S358.3 [
14]. An additional sub-sample per replicate of approximately 6 L was collected by hand to determine whole-plant geometric mean particle size using procedures described in ASABE Standard S424.1 [
15].
Additional sub-samples of approximately 850 g WM per replicate were collected by hand to quantify kernel particle size. These sub-samples were oven dried for 12 h at 55 °C, and then, the kernel fraction was separated from the non-grain material by a water separation procedure described in [
16]. Savoie et al. [
16] reported that more than 92% of kernels were separated from the stover using this technique. After separation, the kernels were oven dried for 24 h at 55 °C and then fractionated by size using a cascade of screens in a Ro-Tap screener (W.S. Tyler; Mentor, OH, USA). The screener was configured with eight screens (9.53, 6.35, 4.75, 3.35, 2.36, 1.70, 1.19, and 0.59 mm) and a bottom pan. After operating the screener for 2 min, the contents of each screen and the pan were weighed to the nearest 0.001 g. The kernel particle size was determined using equations found in ASABE Standard S319.4 [
17].
From the approximate 20 kg WM generated per replicate, approximately 9.0 kg WM was used to quantify compacted density. Material was placed into a plastic tube (25 cm inside diameter, 62 cm height, 30 L volume) and compressed with a hydraulic cylinder, which applied force to a 25 cm diameter platen. Pressure applied by the platen on the face of the material was 140 kPa, controlled by a relief valve in the hydraulic circuit. Cylinder extension was halted automatically when relief valve actuation occurred. With the hydraulic cylinder stationary in the final position, the height of the compacted material was measured by hand to the nearest 1 cm so that the volume and density could be calculated.
Leachate conductivity (LC) was used to quantify the level of crop processing using a procedure first developed by Kraus et al. [
18]. The first step to determine LC involved using a microwave oven to determine DM content using procedures described in ASABE Standard S358.3 [
14]. The DM was then used to determine the wet mass needed to create 5 g DM sub-samples from each replicate. Each sub-sample was individually placed in a 600 mL glass container and 300 mL of distilled water added. An orbital shaker table operated at 180 cycles·min
−1 was used to mix the material for 1 min. After mixing, the contents were then filtered through two layers of cheesecloth and the conductivity of the leachate immediately measured using a Thomas Scientific (Swedesboro, NJ, USA) model 4366 conductivity meter. To maintain balance on the shaker, two duplicate samples per replicate were simultaneously analyzed in this manner. A normalizing treatment defined as the ultimate possible level of mechanical processing, and hence the maximum LC, was used the compare processing across treatments and experiments. To create this treatment, the shaking step was replaced by processing the mixture in a model KB64 Vanaheim blender (City of Industry, CA, USA) for 1 min at no-load speed of 28,000 rev·min
−1. The LC was then measured as described above. Four blender replicates were created during each experiment. The ratio of the treatment LC
tr to the blender (i.e., “ultimate”) treatment LC
bl, expressed as a percent, was defined as the processing level index (PLI):
2.6. Kernel Leachate Conductivity
Initial results had shown that processing with the experimental processor increased the LC and PLI and decreased both the whole-plant and kernel particle size. Greater release of ions into the leachate could have been the result of greater surface area of the kernel or the non-grain fractions of the plant. To quantify the effect of kernel particle size on LC, additional procedures were carried out on extra 1X material created during Experiment 4. The kernel and stover fractions were separated by differences in terminal velocity using a vertical tube air separation device [
19]. This technique was used rather than water separation described in
Section 2.5 so that the subsequent LC would not be affected by the loss of water-soluble constituents to the effluent during separation. The separated kernel fraction was then classified by size using the screening process described in
Section 2.5. This process resulted in the following classifications: material from the (a) 6.54 mm screen; (b) 4.75 and 3.35 mm screens; (c) 2.36 and 1.70 mm screens; and (d) the remaining screens and pan. The LC of 5 g DM of each of these four classifications was then determined for eight replicates per size classification using techniques described in
Section 2.5.
2.7. Specific Energy Requirements
Experiment 5 was conducted to quantify the power required for processing 1X or 2X when processor speed was 80 m·s−1. Experiment 6 was conducted to investigate the power required for processing 1X but at 51, 65 and 80 m·s−1. These processor speeds were attained by varying input PTO speed at 700, 900 and 1100 rev·min−1. A self-unloading forage wagon was used to collect UP material chopped at 50 mm chop length. After chopping, material was deposited from the forage wagon into a silo blower, which fed the processor. The mass processed per replicate was determined using load cells on the forage wagon. Typical mass processed per test was 450 kg WM, and each treatment was replicated three times. The rate of fuel use was recorded during each replicate test from the tractor’s controller area network (CAN) bus with a USB to CAN adapter (ECOM, EControls, San Antonio, TX, USA) connected to the tractor’s diagnostic CAN terminal. The fuel message (PGN 65203, J1939) was sampled at 10 Hz, decoded, and exported to an Excel spreadsheet by EControls (San Antonio, TX, USA) CANCapture Version 3.5 software. Prior to these experiments, engine fuel use was recorded in this manner at PTO speeds of 700, 900, and 1100 rev·min−1, while the tractor’s PTO was loaded from 11 to 130 kW in nine equal increments using a PTO dynamometer (model NEB400, AW Dynamometer, Pontiac, IL, USA). Using these data, linear equations were developed to predict tractor PTO power from CAN fuel rate (R2 = 0.99) at each PTO speed. The mass processed per test divided by processing time was used to calculate the mass-flow. Dividing the PTO power by mass-flow rate provided the specific energy required.
2.8. Fermentation Properties
In Experiments 1–4, an additional sample of approximately 230 g DM per replicate was used to fill polyethylene vacuum pouches and the air evacuated using a vacuum sealer (Minipak, Friulmed, Monfalcone, Italy). This material was removed from storage after 96, 90, 81 and 75 days in storage. The 12 total vacuum bags per treatment (4 experiments × 3 replicates) were combined and homogenized. Five replicate sub-samples of approximately 385 g DM each were then created for each treatment. These samples were subsequently analyzed for crude protein (CP), neutral detergent fiber (NDF), and starch (using NIRS techniques) and pH, fermentation products, and CSPS (using wet laboratory techniques). All analyses were performed by Rock River Laboratories (Watertown, WI, USA) using their standard methodology.
2.9. Rumen Degradation
Rumen DM degradation characteristics of the KP, 1X, and 2X treatments were quantified using the remaining homogenized material described in
Section 2.8. An in situ technique was used that preserved the physical form of the samples, i.e., samples were placed in the rumen bags in their “as-fed” physical form, not dried and ground as typically used for in situ digestion research. This technique was successfully used by Johnson et al. [
10]. Individual samples of wet material equaling 9.0 g DM were weighed into mesh bags (25 × 35 cm, 50 μm pore size). A total of 225 samples (3 treatments × 5 replicates × 3 cows × 5 time points) were prepared. Each time point (3, 7, 16, 24, and 120 h) was incubated separately because the large size of samples limited the ability to run all time points concurrently. At each time point, fifteen samples (3 treatments × 5 replicates per treatment) were placed into each of three separate mesh laundry bags, which were individually placed in three different lactating dairy cows with rumen cannulas. After incubation, the residues from the three cows were combined prior to analyses to mitigate cow-to-cow variation. The cows were milked twice daily and fed a diet consisting of corn silage, alfalfa haylage, and concentrate.
At the appropriate time intervals, sample bags were removed from the rumen and immediately placed in ice water to terminate microbial activity. The samples were then rinsed in a commercial washing machine using two 5 min rinse cycles. Washed samples were then dried in a forced-air oven for 24 h at 60 °C and weighed to determine DM disappearance. An additional set of 15 samples was prepared, as described above, to determine 0 h digestibility (i.e., the rapidly soluble fraction). These samples were soaked in warm water (approximately 40 °C) for 20 min and then rinsed, dried, and weighed as described above. Ruminal disappearance of DM was expressed as a fraction of the original sample DM amount:
where M
t was the dry mass at any time point t, M
res was residual dry mass at 120 h, and M
tot was the total initial dry mass.
2.10. Statistical Analysis
Factorial analysis using the Standard Least Squares option in the Fit Model platform of JMP Pro (ver. 15, SAS Institute Inc., Cary, NC, USA) was used to conduct the statistical analysis. The investigations of processing treatment effect on processing level (PLI); whole-plant and kernel particle size; energy requirements; fermentation properties; and in situ DM disappearance at each of the six time points were all analyzed as separate one-way ANOVAs. The one-way ANOVAs were analyzed using the model:
where µ is the overall mean, T
i is the processing treatment (UP, KP, 1X, or 2X), and E
ij is the residual error.
The investigation of differences due to processing treatment and harvest date (see
Section 2.2.1) were analyzed using a two-way ANOVA. The investigation of processing occurring either pre- or post-ensiling (see
Section 2.3.1) was also analyzed using a two-way ANOVA. The two-way ANOVAs were analyzed using the models:
where µ is the overall mean, T
i is the processing treatment (UP, KP, 1X, or 2X), D
j is the harvest date, P
j is when processing took place (i.e., pre- or post-ensiling), (T × D)
ij is the interaction between processing treatment and harvest date, (T × P)
ij is the interaction between processing treatment and process timing, and E
ijk is the residual error.
All least square means were compared using Tukey’s test or Student’s t test as appropriate. Significant differences were declared at p ≤ 0.05, and tendencies were considered at 0.05 ≤ p ≤ 0.10.
4. Discussion
The physical effect of processing WPC is often only quantified by whole-plant particle size or Corn Silage Processing Score (CSPS). Neither metric adequately describes the physical effect of processing on the fiber fraction. Because of the absence of grain, the particle size of the plants without ears was two to three times larger than the whole-plant particle size (
Table 3). This shows that whole-plant particle size as determined by screening does not adequately describe the fiber fraction. The processing level index (PLI) as used here was a better way to quantify the physical disruption caused by processing. For instance, there was only a 4 mm difference in average whole-plant particle size between the KP and 1X treatments (
Table 3), yet the PLI was 19 percentage points greater for the latter treatment (
Table 2). This was due to the increased surface area and cell rupture caused by impact–shredding processing. By contrast, the average whole-plant particle size was 18 mm smaller for the KP treatment compared to the UP treatment, but here, the PLI was only 5 percentage points greater. These results show that unlike impact–shredding processing, conventional roll processing as currently practiced does little to change the physical form of the fiber fraction and that that the PLI does a better job of quantifying plant physical disruption than particle size alone. Future research on processing WPC should include the processing level index, or a similar metric, as a means to quantify the physical effect of processing on both the grain and fiber fractions.
Dairy cattle diets containing of finely chopped forages and high levels of grain may not contain adequate particle size to maintain proper rumen function and prevent certain metabolic disorders [
22]. It has been suggested that the fraction of total screened material residing on or above an 8 mm screen is a useful metric to describe the physical effectiveness of the fiber and the rumination potential of that feed [
22]. The average particle size of the plants processed without ears was 26, 22, and 11 mm for the KP, 1X, and 2X treatments and the fraction of mass on or above the 6.4 mm screen was 60%, 51%, and 34%, respectively (
Table 3). Although the particle size metrics of the KP and 1X treatments were similar, the latter treatment had greater rapidly soluble fraction and greater DM disappearance through the first 7 h of incubation (
Figure 5 and
Table 8). This can be attributed to the physical disruption of the grain and fiber fractions caused by impact–shredding processing as quantified by the PLI (36% KP vs. 54% 1X). The 2X treatment produced the best in situ digestion performance, but the particle size and fraction on or above the 6.4 mm screen were much smaller than the control KP treatment. Increasing the chop length from 50 to 100 mm (Exp. 7) did little to improve the whole-plant particle size (
Table 3). Whether these particle size concerns translate into rumination or metabolic issues is an important next step for future research into animal response to WPC subjected to intensive mechanical processing.
It was observed that processing shredded the stalk into strands of fibers and destroyed the tubular structure of the stalk (
Figure 2). This subsequently made the bulk material more compliant, which resulted in a greater compacted density (
Figure 4). The 1X and 2X treatments had significantly smaller whole-plant and kernel particle size (
Table 3 and
Table 4), which also contributed to improved void reduction and consolidation. Muck and Holmes [
23] suggested that the compacted dry basis density in bunk or bag silos should be at least 240 kg·m
−3 to minimize DM losses in bunk or bag silos. Only the 1X or 2X treatments were able to achieve this target density at the pressures applied. Grass or alfalfa silage processed by shredding had greater density in laboratory-scale silos [
24] or wrapped bales [
25], but to date, there has been no published results on how intensive processing affects silage density in a bag or bunk silos. When a chop length of 100 mm was used prior to processing (Exp. 7), the compact density was 9% to 13% greater compared to KP material using a 25 mm chop length. This suggests that chopping using a very long chop length prior to processing with the impact–shredding processor may not have a detrimental effect on silage density. Further research is needed to determine if WPC processed with the impact–shredding processor will result in greater density in bag or bunk silos.
The energy requirements for processing with the impact–shredding processor was greater than that reported for conventional roll-type kernel processors. Energy requirements for processing WPC chopped at 19 mm chop length and processed with a conventional set of kernel processing rolls was between 0.6 and 1.1 kW-h·Mg
−1 [
26]. Energy requirements for shredding unchopped corn using a pair of kernel processing rolls ranged from 0.9 to 1.9 kW-h·Mg
−1 and averaged 1.3 kW-h·Mg
−1 [
27]. Because a harvester’s overall energy requirements impact its throughput capacity, energy requirement, and machine cost, the energy requirements of processing are an important factor in the cost–benefit consideration of the impact–shredding process. When the processor was operated at 51 and 65 m·s
−1, the resulting PLI were statistically similar, but the energy requirements were 32% less at the slower rotor speed (
Table 5). Processing with the experimental processor produced numerically similar physical properties when processing material chopped at either 50 or 100 mm chop length (
Table 2,
Table 3 and
Table 4). Chopping at longer chop length would save energy expended at the harvester’s cutterhead, partially offsetting the added power requirement of the impact–shredding processor. Previous work has established that increasing the chop length for WPC from 9.5 to 19 mm reduced the whole-machine energy requirements by 20% to 44% [
26,
28]. Further research is needed to understand the impact of processing longer material and to parse the energy requirements of chopping and processing on a forage harvester that combines conventional chopping and processing with an impact–shredding processor.
An alternative to processing WPC at harvest is to process post-ensiling. Processing by impact and shredding was effective at altering WPC physical properties when applied either pre- or post-ensiling (
Table 6). Due to high energy requirements, processing in this manner at harvest might reduce achievable harvest rates or necessitate a more powerful engine to maintain current harvest rates. If processing took place post-ensiling, it could diminish the required severity of kernel processing at harvest as currently practiced using conventional kernel processors, increasing harvest productivity and timeliness. However, post-ensiling processing would eliminate the potential benefits from greater storage density and require an added step during feed preparation.
Processing WPC with conventional kernel processors has consistently shown to improve ruminant starch digestion [
2,
29], but achieving optimum CSPS of 70% is challenging [
3,
30]. The reported impact of processing on WPC fiber digestion has been variable, with both declines [
5,
9,
10] and increases reported [
8]. Compared to conventional kernel processing, Jančík et al. [
31] reported more intensive processing with an on-board kernel processor increased 12 h DM disappearance, but the difference was only 2 percentage points. WPC processed with a conventional kernel processor had more rapid attachment and heavier colonization of rumen bacteria compared with the unprocessed silage, which enhanced ruminal digestion and fermentation [
32]. However, the effect was more pronounced for the kernels than for the stems. Processing with a conventional kernel processor improved the rapidly soluble DM by 3.9 percentage points and the 8 h in situ DM disappearance by 2.1 percentage points [
10]. By contrast, in this research the rapidly soluble DM increased by 10.2 percentage points and the 7 h in situ DM disappearance was 5.0 percentage points greater for the 2X treatment than for the KP treatment (
Table 8). Processing WPC with a screenless hammermill as investigated here produced material that was highly fiberized (
Figure 2), resulting in consistently greater processing level index (
Table 2), which was the result of greater specific surface area and cell rupture of the fiber fraction. Processing pulverized the kernel fraction such that CSPS was 86% and 95% for the 1X and 2X treatments, respectively (
Table 7). Although there were some differences in composition and fermentation properties (
Table 7), these differences were small and not likely to be biologically significant. Therefore, it can be concluded that the quantified physical differences were responsible for the observed increase in rapidly soluble DM and DM disappearance for the impact-shredded treatments.
Improved DM disappearance was likely the result of greater processing of both the fiber and starch fractions, but the DM disappearance of these fractions was not observed separately in this work. Previous research has shown that greater CSPS increased starch digestion [
3]. The high CSPS of the 1X and 2X treatments (
Table 7) may have led to greater starch digestion than the KP treatment. There has been no published research covering the digestion of highly fiberized corn plants as produced in this research. Because decreased fiber digestibility has been linked to greater starch digestibility [
5,
33], new research is needed to draw conclusions regarding how processing WPC by impact–shredding affects the relative changes in digestion of the starch and fiber fractions. An equally important next step is to determine how feeding WPC processed by impact and shredding affects dairy cattle lactation performance.
Based on an exhaustive review of the literature, it has been suggested that further technological improvement of processors is warranted to allow for more consistent processing of WPC [
34]. The results of this research show that processing by impact and shredding is a new approach to change the physical form of both the grain and fiber fraction of WPC.