Results Directory UMM :Data Elmu:jurnal:L:Livestock Production Science:Vol68.Issue1.Jan2001:

44 F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 model included feeding level and CP content and their interaction as sources of variation. This was carried out on the data of groups A to F i.e., all the supplemented groups. This data was also subjected to regression analysis using the PROC GLM state- ment of the Statistical Analysis Systems SAS Institute to test the linear and quadratic effects of hay allowance on all digestibility coefficients. Data from the seventh group G who were fed 800 g d of hay unsupplemented with any protein 42 g CP kg DM Fig. 1. In-sacco analysis of untreated hay. were then combined with the other two groups who received 800 g d of hay, group E 110 g CP kg DM and group F 200 g CP kg DM. These data were is potentially degradable in the rumen Fig. 1. Using analysed as a completely randomised design using the method of Weisbjerg et al. 1990 291.1 g kg the PROC GLM statement of the SAS Institute DM of the hay was soluble in water. 1985. The model included CP content i.e., treat- Where digestibility coefficients for groups A to F ment as the source of variation. The mean di- were compared in the factorial analysis, no signifi- gestibility coefficient for OMD, True OMD 1 and cant interaction of protein content and hay intake True OMD 2 for all animals were also compared level was found. With regard to the effect of protein using the PROC GLM statement of SAS in order to content, the digestibility of the hay in the 182 g compare the two methods of measuring true di- CP kg DM diets was found to be significantly higher gestibility and the estimates of apparent OMD. For P , 0.05 than the digestibility of hay in the 103 g the in-sacco analysis, parameters were estimated CP kg DM diets for all digestibility coefficients using the PROC NLIN statement of the SAS Institute except NDFD and GED Table 3. 1985. Table 3 a Effect of dietary CP content on digestibility coefficients g kg

3. Results

Groups S.E.M. P The urea supplementation resulted in dietary CP A, C and E B, D and F concentrations of 103 and 182 g kg DM for the low CP g kg DM 103 182 and high levels of urea, respectively Table 2. DMD 594.6 622.2 7.84 0.026 OMD 604.2 632.8 8.01 0.021 Furthermore the use of the urea solutions did not CPD 610.4 780.5 4.60 0.001 affect the other chemical components of the hay to NDFD 563.6 591.1 11.4 0.106 any great extent Table 2. From the in-sacco analy- ADFD 520.3 555.5 10.70 0.032 sis, the rapidly soluble DM or the so called ‘a’ GED 571.5 593.6 8.07 0.069 fraction of the hay equates to 358.2 g kg DM, while True OMD 1 694.1 720.6 7.90 0.030 True OMD 2 681.0 711.8 7.90 0.010 the slowly degradable DM or the ‘b’ fraction is a 452.4 g kg DM and this fraction degrades at a rate c D, Denotes digestibility coefficients for that nutrient. S.E.M., value of 3.19 h. Thus 810.6 g kg DM of the hay Standard error of the mean. Table 2 Chemical composition of the supplemented and unsupplemented hay g kg DM, except DM, g kg and GE, MJ kg DM Hay treatment DM OM CP Ash NDF ADF ADL GE Hay only 896 850 42 46 678 406 50 17.64 Low urea 884 830 103 54 668 390 50 17.89 High urea 890 839 182 51 652 385 51 17.63 F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 45 Table 5 The pattern of actual DM intakes DMI closely Effect of dietary CP content on digestibility coefficients g kg for reflected that of the fresh hay allowances because 1 all groups fed 800 g d of hay there was little feed refusal. The dry matter intakes Group S.E.M. P obtained, together with the GE content and the GED for the hay used means that the feeding levels of the G E F animals were 0.64, 0.76 and 0.88 3 maintenance CP g kg DM 42 103 182 using metabolisable energy 5 digestible energy 3 DMI g 711.8 697.5 705.8 a ab b DMD 589.5 605.9 629.3 7.71 0.081 0.82 for groups, A and B, C and D and E, F and G, a ab b OMD 603.3 614.4 639.8 8.03 0.119 respectively Robinson et al., 1980. No significant a b c CPD 8.1 611.6 775.4 6.48 0.001 effect of hay allowance on digestibility was observed NDFD 563.2 574.9 599.5 12.12 0.353 in the factorial analysis. In general, digestibility ADFD 542.8 537.5 568.2 10.84 0.361 a ab b tended to increase as intake level increased and a GED 562.6 587.5 605.9 8.14 0.072 True OMD 1 689.3 702.0 726.3 8.51 0.141 significant linear effect of hay allowance was ob- a ab b True OMD 2 676.8 692.1 721.4 8.17 0.062 served on GED P 5 0.05. In addition the linear 1 abc effect of hay allowance on ADFD approached sig- , Values within a row with different superscripts differ significantly P , 0.05. S.E.M., Standard error of the mean. DMI, nificance P 5 0.099. With the exception of CPD, Dry matter intakes. D, Denotes digestibility coefficients for that there was no significant quadratic effect of hay nutrient. allowance Table 4. Where groups E and F were re-analysed with average digestibility coefficients over the seven group G as a completely randomised experiment treatment groups were 704.8, 693.6 and 616.3 g kg i.e., all groups fed 800 g d of hay, dietary protein S.E.M. 5.81 for True OMD 1, True OMD 2 and content significantly affected P , 0.05 the diges- apparent OMD, respectively. The difference between tibility coefficients determined for the hay in the case the two estimates of true digestibility was not of DMD, OMD, CPD, GED and True OMD 2 Table significant with both estimates of true digestibility 5. However, the differences were only significant being significantly higher P , 0.05 than the appar- between the lowest 42 g CP kg DM, group G and ent OMD. The mean difference between the average the highest CP content diets 182 g CP kg DM, of both true digestibility estimates and the apparent group F for DMD, OMD, GED and True OMD 2. OMD was 82.9 g kg. When the data for all animals was analysed, the Significant differences P , 0.05 were apparent in Table 4 a Effect of hay allowance on DM intakes g d and digestibility coefficients g kg Groups S.E.M. Linear A and B C and D E and F Allowance g d 600 700 800 DM allowance g d 538 627 717 DMI g d 535 614 702 DMI range 526–538 556–627 675–715 DMD 596.8 610.8 617.6 9.13 0.122 OMD 608.0 620.4 627.1 9.32 0.163 CPD 686.4 706.4 693.5 5.49 0.368 NDFD 562.9 582.0 587.2 13.25 0.208 ADFD 522.4 538.5 552.9 12.45 0.099 GED 569.0 582.0 596.7 9.38 0.050 True OMD 1 697.3 710.5 714.2 9.19 0.209 True OMD 2 687.7 694.8 706.8 8.84 0.143 a DMI, Dry matter intakes. D, Denotes digestibility coefficients for that nutrient. S.E.M., Standard error of the mean. , Indicates a significant quadratic effect P , 0.05. 46 F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 Table 6 1 Effect of feeding level and dietary CP content on the quantitative classification of faecal N as a proportion of faecal DM g kg DM Groups DMI Total N Feed N Microbial and Microbial and 2 g endogenous N endogenous ab a A and B 534.5 16.01 4.04 11.97 74.77 a a C and D 613.8 15.63 4.03 11.60 74.22 b b E and F 701.8 16.60 3.88 12.78 76.99 S.E.M. 0.307 0.103 0.262 CP g kg DM a a A, C and E 103 15.56 4.10 11.46 73.65 b b B, D and F 182 16.65 3.87 12.78 76.76 S.E.M. 0.251 0.084 0.214 1 ab , Values within a column with different superscripts differ significantly P , 0.05. 2 Indicates the of total faecal N that microbial and endogenous faecal N is. the output of microbial and endogenous faecal 4. Discussion nitrogen as a proportion of faecal DM due to dietary CP content using groups A to F and groups E, F and 4.1. Hay quality G Tables 6 and 7. However, for the comparison of groups E, F and G, the differences only reached In terms of the quality of the hay used, the low CP significance P , 0.05 between group F 182 g CP content 42 g kg DM and the high fibre content kg DM and the other two groups with no significant NDF: 678 and ADF: 406 g kg DM indicate that difference arising between groups G and E. The the hay used was mature, low-quality material Table output of microbial and endogenous faecal N was 2. Jarrige 1989 reports a range of CP values for also significantly higher for the highest hay allow- perennial ryegrass hays extending from 81 to 119 ance groups groups E and F: 800 g d than for the g kg DM. The CP content of the hay used in this two lower hay allowance groups groups A and B: experiment is well below the minimum of this range. 600 g d; and groups C and D: 700 g d. The ADF content of the hay used 406 g kg DM is The mean output of microbial and endogenous also higher than the maximum ADF value of 397 faecal N for all groups was 5.24 g kg DMI, while g kg DM reported by Jarrige 1989 for perennial the output of microbial and endogenous faecal OM ryegrass hay. using methods True OMD 1 and True OMD 2 was With regard to the degradability characteristics of 7.33 and 8.24 g 100 g DMI, respectively Table 8. the hay, the observed ‘a’ value 358.2 g kg DM is Table 7 Effect of dietary protein content on the quantitative classification of faecal N as a proportion of faecal DM g kg DM for all groups fed 800 1 g d of hay Group CP Total N Feed N Microbial and Microbial 2 g kg DM endogenous N and endogenous a a G 42 14.80 3.82 10.98 74.19 a a E 103 15.94 3.92 12.02 75.41 b b F 182 17.40 3.85 13.55 77.87 S.E.M. 0.453 0.137 0.403 1 ab , Values within a column with different superscripts differ significantly P , 0.05. 2 Indicates the of total faecal N that microbial and endogenous faecal N is. F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 47 Table 8 TDN in digitigrass hay fed to sheep after supple- Estimates of faecal microbial and endogenous OM excretion mentation with soyabean meal at levels of 0 and g 100 g DMI using methods True OMD 1 and True OMD 2 and 0.17 of body weight and by Krishna Mohan et al. of microbial and endogenous faecal N excretion g kg DMI for 1987. However, larger responses have been re- all treatment groups ported. Cronin 1996 reported particularly large Group True OMD 1 True OMD 2 Microbial and increases of 135 g kg for OMD and 157 g kg for endogenous N NDFD for the digestibility of hay fed to sheep by A 7.47 8.44 5.34 increasing CP contents using soyabean meal from B 7.65 8.14 5.46 56 g kg DM up to 202 g kg DM. This report is at C 7.00 8.36 5.00 D 7.11 8.39 5.07 odds with all others cited and the results presented E 7.36 8.08 5.26 here. F 7.74 8.10 5.53 It could be argued that a certain degree of G 7.01 8.20 5.01 solubilisation of the hay cell wall had occurred by using urea, thus leading to the observed increase in Mean 7.33 8.24 5.24 C.V. 4.133 1.803 4.153 digestibility. The hay being fed however was sprayed with urea just prior to feeding. For solubilisation of the cell wall to result in digestibility advantages, a O period of 4 days at 80 8C or 3 weeks at 30 C would quite high when compared to the maximum ‘a’ value be appropriate using 30 g NH kg DM Ballet et al., 3 of 247 g kg DM reported for six hays by ADAS 1997. Thus if the hay was quite readily consumed, 1989. However, the relatively large ‘a’ value is the time available for any cell wall solubilisation was supported by the large soluble DM component probably too short. 291.1 g kg DM determined using the method of When the three groups fed 800 g d of hay at Weisbjerg et al. 1990. It is possible that the dietary CP contents of 42, 103 and 182 g CP kg of difference between both values is due to particle loss DM i.e., groups E, F and G are compared, the from the nylon bags at washing. Smith et al. 1972 effect of increasing the protein content from 103 to also report large soluble DM components for a range 182 g CP kg DM gave responses similar in mag- of mature grasses ranging from 290 g kg DM for the nitude to those obtained when the 6 treatment groups Pennlate variety of Orchardgrass to 460 g kg DM in the factorial experiment were compared. What is for common wheat. of interest in the comparison of groups E, F and G is the effect of giving no supplementary protein at all. 4.2. Dietary protein level and digestibility This gave the lowest digestibility coefficients but they were not substantially lower than the other two The results obtained in the factorial analysis treatments OMD; 639.8, 614.4 and 603.3 g kg for Table 3, groups A to F differ somewhat from groups fed 182, 103 and 42 g CP kg DM, respective- previous reports Satter and Roffler, 1977; NRC, ly. Given that a response to protein supplementation 1984; Boggs et al., 1987; Willms et al., 1991 which when going from 103 to 182 g CP kg DM was found suggest that dietary CP contents in the region of 100 in the factorial experiment, one could reasonably to 120 g kg are adequate for optimum digestibility. expect a larger response when a very low protein diet In this experiment, digestibility increased when the was supplemented. The absence of such an effect dietary CP content was increased from 103 to 182 indicates that ruminants fed a maintenance diet have g kg DM. However, the magnitude of the increase is the ability to recycle sufficient nitrogen to compen- small in biological terms 28.6 g kg in OMD and is sate for very low protein levels in the diet. Kennedy not much greater than the normal variation associ- and Milligan 1980 stated that 23–92 of plasma ated with carefully controlled digestibility trials urea may be recycled with the higher value associ- which amounts to a minimum of 20 g kg Van Soest, ated with low protein diets. Thus on low protein 1994. A similarly small effect was reported by diets, recycling of urea may avoid severe depressions Moore et al. 1997 for total digestible nutrients in digestibility provided the extent of protein under- 48 F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 nutrition with regard to the microbes is not greater 1982 also noticed a lesser effect of feeding level on than the recycling capacity. The small difference in the digestibility of both forages and concentrates on digestibility coefficients between group G 42 g high forage diets than on low forage diets. CP kg DM and group F 182 g CP kg DM may Digestibility depressions in response to increased indicate that the recycling of nitrogen did decrease level of intake have largely been implicated with the protein under-nutrition of the rumen microbes to increased rates of passage Owens and Goetsch, a large extent, although not eliminating it entirely. 1986. However, in comparison to concentrate feed It should be noted that where the digestibility of particles, forage feed particles are relatively insensi- the exact same batch of hay was measured when fed tive to feeding level in terms of rumen outflow rate. with soyabean meal at CP contents of 100 g kg DM This is clearly demonstrated in the data of Colucci et in two separate digestibility trials Mulligan, 1997, al. 1982 where the fractional rumen outflow rate the digestibility coefficients OMD: 590 and 606 for concentrates increased by a much greater amount g kg were similar to those obtained in this experi- than the fractional rumen outflow rate for forages ment. Thus, there appears to be no effect of protein due to increasing feeding level for dairy cows fed source on digestibility, and no detrimental effect of both high 83 and low 32 forage diets. Varga the urea levels used on rumen fermentation. and Prigge 1982 and Blaxter et al. 1956 also observed no significant effect of level of intake on 4.3. Level of intake and digestibility the rumen outflow rate of alfalfa and orchardgrass, and long hay, respectively with increasing levels of It has been reported Tyrrell and Moe, 1975; intake when fed to sheep. It may be the case Colucci et al., 1982; Robinson et al., 1987; Edionwe therefore that forage will remain in the rumen until it and Owen, 1989; Zinn et al., 1994; Woods et al., has been sufficiently degraded to pass out. Bruinning 1999 that as intake increases, the digestibility of et al. 1998 clearly demonstrated that rumen outflow feeds decreases. However increasing hay intake level rate increases for grass silage, maize silage and in this trial had no detrimental effect on the di- alfalfa silage particles after particle size reduction. gestibility both true and apparent of hay. Indeed This theory was also supported by Van Soest 1985 hay digestibility increased with increasing hay allow- who stated that retention time in the rumen is ance and this effect was significantly linear for GED regulated by rumination that is required to commi- P 5 0.05. Many of the reports which exist con- nute lignified fibrous particles i.e., digestibility and cerning digestibility depressions as level of intake particle breakdown control the intake and rate of increases relate to diets containing large amounts of passage of forages to a greater extent than vice concentrates Robinson et al., 1987; Edionwe and versa. Owen, 1989; Zinn et al., 1994; Woods et al., 1999. The observed trend of increasing digestibility with However level of intake effects on the digestibility of increased feeding level was unexpected. Increases in predominantly forage diets are less common, or are digestibility in response to increased feeding level not of the same scale as those which accrue on have been previously reported by Ortigues et al. concentrate diets. Galyean and Owens 1991 in a 1993 who also conceded that such responses were review, stated that increasing intake has greater contradictory to most other reports. Attempts to effects on the site and extent of digestion with explain this phenomenon in the current work are high-concentrate and mixed diets than with all- based on the observed pattern of consumption of roughage diets. This theory is substantiated by the urea treated hay. The sheep fed 600 g d of hay results of Blaxter et al. 1956, Ulyatt et al. 1983 tended to eat their allowances much quicker than and Mbwile and Uden 1997 who report no di- those fed the 700 g d or the 800 g d treatments, gestibility decline due to increased level of intake for with the sheep fed the 800 g d treatment almost fresh grass or hay when fed to sheep in the case of consuming some of their allowance in each hour of both Blaxter et al. 1956 and Ulyatt et al. 1983 the day. This was most likely due to a pungent and dairy cows in the case of Mbwile and Uden ammonia-like odour, which seemed to effect the 1997. Tyrrell and Moe 1975 and Colucci et al. palatability of the urea treated hay. This frequent F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 49 feeding behaviour of livestock fed non protein a proportion of faecal DM Table 6 for animals fed nitrogen has previously been reported by Owens and the highest hay allowance i.e., groups E and F is Bergen 1983 who suggest that such behaviour may possibly due to a more viable rumen microbial improve the energetic efficiency of rumen-microbes. population associated with the observed diet con- It has also been reported Ulyatt et al., 1983 that sumption pattern. With regard to the effect of CP frequent feeding behaviour results in greater N content on this parameter, the level of microbial and retention. Both these factors may have combined to endogenous faecal N as a proportion of faecal DM result in a more viable rumen microbial population, excreted by the animals on the 182 g CP kg DM diet with a resulting trend of higher digestibility values at was significantly higher than the amount excreted on the higher feeding levels. Other possible explana- the 103 g CP kg DM diet Table 6. This observa- tions are a that some solubilisation of the hay cell tion was also noted in the comparison of treatments wall fraction occurred in the extended period prior to E, F and G Table 7 where the proportion of faecal consumption in the case of the higher feeding level DM that is microbial and endogenous faecal N is treatments and b it could possibly be argued that significantly lower for the 42 and 103 g CP kg DM the frequent feeding behaviour decreased rates of diets than for the 182 g CP kg DM diets. The higher passage and thus increased digestibility. microbial and endogenous faecal N output on the The significant quadratic effect P , 0.05 of hay 182 g CP kg DM diets may have been due to allowance on CPD is unusual. Of particular interest enhanced microbial production in the rumen, as is is the lower digestibility coefficient for animals fed suggested by the higher digestibility coefficient for 800 g d of hay compared to animals fed 700 g d of this group. hay. The significantly higher amount of microbial The proportion of total faecal N that is microbial and endogenous faecal nitrogen excreted by the and endogenous is in the region of 73–78. Mason animals fed 800 g d of hay may be the only cause of 1968 demonstrated that in the case of diets which this anomaly. had highly available sources of protein, that almost all of the faecal N was extracted by NDR i.e., was 4.4. Estimation of true digestibility mostly microbial and endogenous. Van Soest 1994 stated that there was no evidence of potentially Both methods for estimating true digestibility are digestible feed protein in normal faeces. However a based on the use of neutral detergent reagent NDR. certain amount of N in forages ca. 7 has been Neutral detergent reagent has also been used for this implicated as being unavailable due to its association purpose by Robertson and Van Soest 1975, Deinum with lignin Van Soest, 1994. This N may account et al. 1984, Uden 1984 and Woodward and Reed for some of the feed N present in the faeces not 1995. digested by the animal and not soluble in NDR in the When used as suggested by Van Soest 1994, the faeces. It is also possible that bacterial cell walls in two estimates of true digestibility are quite compar- the faeces posses a certain resistance to NDR able, with no significant difference P . 0.05 occur- Mason, 1968, and thus the proportion of total ring between the means of both estimates. Similar faecal N that is microbial and endogenous may have differences to that observed in this experiment been underestimated. 13.45 between true average of True OMD 1 and The excretion of microbial and endogenous faecal True OMD 2 and apparent digestibility have been N averaged 5.24 g kg DMI Table 8. This was the previously reported. Woodward and Reed 1995 average of a range of values extending from 4.72 to reported a difference of 15 in the true and apparent 5.99 g kg DMI. These values agree well with results digestibility of diets composed of East African previously reported by Robertson and Van Soest browses and vetch straw when fed to sheep and 1975, Paquay et al. 1972 and Petit et al. 1985 goats. where microbial and endogenous faecal nitrogen The significantly higher P , 0.05 level of micro- excretion was estimated to be 5.8, 4.96 and 5.74 bial and endogenous faecal N output calculated as g kg DMI, respectively. Mason and Frederiksen the difference in total faecal N and faecal NDF N as 1979 agree well with these estimates and report an 50 F .J. Mulligan et al. Livestock Production Science 68 2001 41 –52 overall mean of 6.0 g of microbial and endogenous consumption patterns have been cited as two possible faecal nitrogen per kg DMI, but their actual values reasons for this largely unexplained effect. The ranged from 3.6 to 8.0 g per kg DMI. The similarity determination of true digestibility values provided of the results of this trial and those reported by other little extra information on the effect of both vari- authors suggests that quite an accurate estimation of ables. However the true digestibility estimates pro- microbial and endogenous faecal N excretion was duced differences in true and apparent digestibility, made. which were consistent with other reports. The pro- Microbial and endogenous OM excretion has been cedures used for true digestibility determination were reported to be 12 of DMI by Robertson and Van quite easy to apply and may be useful in further Soest 1975. The mean percentage of DMI that investigation of the inherent inaccuracies of apparent microbial and endogenous OM excretion comprises digestibility values. It is important to note that these for the two methods is 7.33 and 8.24 for the True inaccuracies may not be of similar magnitude in all OMD 1 and the True OMD 2 methods, respectively cases. Table 8. The discrepancy between the observed values and those of Robertson and Van Soest 1975 may indicate that microbial and endogenous organic Acknowledgements matter excretion is not a constant across all feeding situations. However, the small range in values Table This project was co-funded by the European 8 obtained by both methods of true digestibility Union from structural funds. The technical assistance determination indicate that microbial and endogen- of Mr. J. Callan and Ms. B. Flynn was essential to ous organic matter excretion is quite similar regard- the completion of this work and is greatly ap- less of intake level or dietary protein content, at least preciated. when a similar basal diet in this case low-quality hay is fed. The difference in true and apparent digestibility References however, is unlikely to be constant for all feeding situations as the range in microbial and endogenous ADAS, 1989. ADAS Feed Evaluation Unit Tables of Rumen faecal N excretion 3.6 to 8 g kg DMI reported by Degradability Values For Ruminant Feedstuffs. ADAS Feed Evaluation Unit, Stratford On Avon. Mason and Frederiksen 1979 for 47 feeds or feed AOAC, 1980. Official Methods of Analysis, 13th Edition. As- mixes suggests. Such a range will result in large sociation of Official Analytical Chemists, Washington, DC. differences in microbial and endogenous OM excre- Ballet, N., Besle, J.M., Demarquilly, C., 1997. Effect of ammonia tion when multiplied by an appropriate conversion and urea treatments on digestibility and nitrogen content of factor in this case 1 0.07 was used. Thus a case dehydrated lucerne. Anim. Feed Sci. Technol. 67, 69–82. Blaxter, K.L., Graham, M.C., Wainman, F.W., 1956. Some ob- exists for further investigation of the microbial and servations on the digestibility of food by sheep and on related endogenous distortion of apparent digestibility values problems. Br. J. Nutr. 10, 69–91. across different feeds. Boggs, D.L., Bergen, W.G., Hawkins, D.R., 1987. Effect of tallow supplementation and protein withdrawal on rumen fermen- tation, microbial synthesis and site of digestion. J. Anim. Sci. 64, 907–914.

5. Conclusions