The effect of type of additive on rumen fermentation and digestion of grass silage in cattle Aila Vanhatalo, Tuomo Varvikko and IlmoAronen Vanhatalo, A., Varvikko, T. & Aronen, I. 1992.The effect of type of additive on rumen fermentation and digestion of grass silage in cattle. Agric. Sci. Finl. 1:163- 175. (Agric. Res. Centre of Finland, Inst. Anim. Prod., SF-31600 Jokioinen,Finland.) Four grass silages made from a second cut cocksfoot-timothy grass were ensiled with the application of water, i. e., without additive (NA), formic acid (FA), lignosulfonate + formic acid + acetic acid (LFA) and cellulase + glucose oxidase enzymes (E), The silages were fed at maintenance level to four dry cows, which had been equipped with a rumen cannula and a simple T-shaped duodenal cannula, in a digestibility experiment designed as a 4x4 latin square. The silages and a mixture of barley and oats (1:1) were given at a ratio of 70:30 on a dry matter basis. All the silages were well preserved, but fermentation in the silo was more restricted in silages ensiled with acid-based additives. The enzyme treatmentresulted in reduced levels of cell wall contents compared to the other silages. The apparent digestibilities oforganic matter (OM) and neutral detergent fibre with E silage were higher (P<0.05) than with the other silages. The microbial N flow at the duodenum was significantly higher (PcO.OOl) with the LFA diet compared to the other diets (NA 52; FA 53; LFA 66 and E 47 g N/d) and the efficiency of microbial protein synthesis tended to be lower with the E diet compared to the other diets (NA 31; FA 31; LFA 38 and E 20 g N/OM apparently digested in the rumen). The molar proportion of acetate in the rumen was significantly higher (PcO.OOl) and the proportion of propionate significantly lower (PcO.OOl) with acid silages than with E and NA silages. The proportion of butyrate was significantly higher with E silage compared to the others. Key words: enzymes, acids, microbial protein, rumen degradation,mobile bag Introduction Ensiling grass into silage aims at maintaining the high nutritional value of original grass. This can be done using acids to create an environment with a sufficiently low pH within a shortperiod of time to stagnate the biological activities in the grass. Alter- natives to acid additives include so-called biologi- cal additives, e.g. lactic acid bacteria or fibre de- grading enzymes, which develop an acidic environ- ment through fermentation during the ensiling. In Finland acid-based additives have been pre- dominantly used during the past few decades in silage making to ensure sufficiently good grass silage for high-quality milk products, even for cheese making. However, as acid additives are corrosive to machinery and not user-safe, there is an increasing tendency to reduce the use of acids in silage making by replacing them with biological additives. Thus, a number of trials have been carried out to study theresponse ofcattle to grass silages preserv- 163 Agric. Sei. Fint. 1 (1992) https://www.c-info.fi/en/info/?token=M93C6TyY3ov9Sj8w.DBW426uhWXT-zuRMHZ-Prg.ngvifmhtlWT2mdnmNscQho_M_a-qwnu5YnYLd9yyfSOnej9O8F2CEonAW8sBwe2J18MbbnUb8i0Zay6ejal4uvwDf6ZWWv0Wpmtw1IYM5DkkgInMEP2E34cHqQoDXo3nTgSKHQ57lRXxpTM1pDJ5_XrtgV8Rf9-tS1d8mKvf6Zt58_AR06CPmb_TMYKswkhSfXqpduxKqy9VRIINcSVRdVq7PSNB5gG0SOH7veh5isFHSJ4qtGSQ4R7utxXx5iBP95UDiZcXTalN_ybAW6F6ufkN8gh62WladnAdDpSbdI7O39TzEA ed using biological or acid-based additives (e.g. Gordon 1989,Heikkilä et al. 1989,Jaakkola and Huhtanen 1990, Jaakkola et ai. 1990, Kennedy 1990, Heikkilä et ai. 1991). However, there are only few reports (Jaakkola et al. 1991,Jacobs and MeAllan 1991, van Vuuren et al. 1991) compar- ing the digestibility and rumen fermentation pat- terns of grass silage preserved with acid and bio- logical additives. The purpose of the present expe- riment was to compare digestibility, rumen fermen- tation, and ruminal and intestinal degradability of grass silages preserved withacid or biological addi- tives. Material and methods Experimental silages The experimental silages were prepared from a second cut cocksfoot (Dactylis glomerata)-timothy (Phleum pratense) grass by a flail harvester using: no additive (NA) AIV-2 (Valio Finnish Co-operative Dairies' Association) 5.5 1/t, containing 80 % (w/w) formic acid and 2 % orthophosphoric acid (FA) - Farmi-solution (Farmos-Group Ltd.) 5,6 1/t, containing 50 % lignosulphonate, 25 % formic acid and 25 % acetic acid (LFA) - Clampzyme (Finnish Sugar Ltd.) 0.2 1/t, con- taining cellulase and glucose oxidase enzymes (E) All the additives were applied by a pressure pump at cutting using the application rates recom- mended by the manufacturers. The silages were ensiled in fibreglass silos of 3 m 3 for seven months. Animals and their feeding The four non-pregnant and non-lactating cows (live weight 550 kg) of Finnish Ayrshire breed used in the experiment were equipped with a rumen can- nula and a simple T-piece duodenal cannula. The animals were fed in a balanced 4x4 latin square close to maintenance level (Salo et al. 1982), the diets consisting of experimental grass silages supplemented with a mixture of barley and oats (1:1). The ratio of forage to concentrate was 70:30 on a dry matter (DM) basis. The animals were fed twice daily in equal amounts at 12 h intervals. A commercial mineral supplement was included in the diet and water was freely available. Experimental procedures The length of each experimental period was 28 days with a 10-day adaptation period. Representa- tive samples of the grass silages and concentrate mix were obtainedfrom each experimental period. The flow of nutrients to the small intestine was estimated using the graphic alternative (McAllan and Smith 1983) of the double-marker method (Faichney 1975). Cr-mordanted straw and LiCo- EDTA prepared as describedby Udén et al. (1980) were used as a marker for the solid and liquid phase ofdigesta. Cr-mordanted straw was administered to the rumen from day 8 twice a day (2 x 7.5 g) and LiCo-EDTA (sg/d) was infused continuously into the rumen from day 9 onwards. Duodenal digesta was spot-sampled on days 17, 18 and 19. Samples (150 ml) were collected at three hours' intervals, four times a day, starting at 8, 9 and 10 o'clock on consecutive collection days. The spot samples ofeach animal were pooled to provide one composite unrepresentative digesta sample. One half of this sample was centrifuged (700 x g/ 10 min) to separate the particulate and liquid phases. The particulate phase and the other half of the digesta sample were dried at 60 °C and milled to pass a 1 mm screen. The liquid phase was stored at -20 °C before analysis. In order to determine the overall digestibility of nutrients using acid-insoluble ash as a natural marker, faecal grab samples were taken twice a day from day 14 to day 18 when feeding the animals. To estimate the rumen liquid outflow rate, a single dose of LiCo-EDTA (8 g) was infused into the rumen during one feeding interval. The infusion was started at evening feeding on day 19 and con- tinued till the next morning feeding. On day 20, the ruminal and duodenal digesta samples were col- lected before morning feeding and at 1.5 hours' 164 Agric. Sei. Finl. 1 (1992) intervals thereafter during the daytime feeding cycle. The liquid phase of the samples was separ- ated and stored as described above. Nitrogen of microbial origin in duodenal N was measured using purine bases ofnucleic acids as mar- kers (Zinn and Owens 1986). The contents of the purine bases in the microbial mass were analyzed from the rumen samples collected on day 21 imme- diately before morning feeding and four hours the- reafter. The microbial mass was isolated by separa- ting the rumen liquid as described earlier and by furt- her centrifuging (26000 x g/20 min) the supernatant. To measure rumen fermentation, samples of rumen fluid were collected on day 21 right before feeding and 0.5, 1,2, 3,4, 6, 8 and 10 h after feed- ing. The ammonia-N and pH of the digesta were measured immediately, and samples for the mea- surement of volatile fatty acids (VFA) were stora- ged withAg20 in a refrigerator for later analysis. To determine the rumen degradability and subse- quent intestinal degradability of the experimental silages, nylon bag techniques were used. Each experimental silage was incubated in the animal fed with that particular silage diet. Five nylon bags (60 x 120 mm) made of polyester (PES 41 pm/33 %, Polymon, Switzerland) containing fresh, chopped (< 10 mm) silage (2.5 g DM) were inserted into the rumen on day 14 and incubatedfor periods of 2,4, 8, 16, 24, 48, 72 and 96 h. After removal, the bags were machine-washed and dried at 60 °C in a forced-draught oven. Fifteen mobile bags (35 x 50 mm, PES 10 pm/2 %/C) per experimental silage were introduced into the duodenumfrom day 14 onwards. Each bag con- tained 0.8 g DM freeze-dried or rumen-incubated (30 h) silage, that was milledthrough a 2 mm mesh. One animal received a maximum of20 mobile bags per day. Subsequently, the bags were collected from the faeces and machine-washed (40 °C) and dried at 60 °C. Chemical analyses The DM content of the grass silages was deter- mined by oven-drying (105 °C), correcting the values for volatile losses according to Huida et al. (1986). Organic matter (OM) content was measu- red by ashing at 500 °C for 2 h and total N by the Kjeldahl method. Determinations of neutral deter- gent fibre (NDF) and acid detergent fibre (ADF) were made according to Van Soest (1963) and Van Soest and Wine (1967), calculating the con- tent of hemicellulose as the difference between NDF and ADF and the content of lignin as the dif- ference between ADF and cellulose. Experimental silages as well as rumen liquor and the liquid phase of duodenal digesta were analyzed for ammonia-N (McCullough 1967). Silages and rumen liquor were further analyzed for VFAs (Huida 1973). Also the lactic acid concentration (Barker and Summerson 1941)and water soluble carbohydrates (WSC) (Somogyi 1945) in the silages were measu- red. Nucleic acids in the microbial fraction and duodenal digesta were determined according to Zinn and Owens (1986). Chromium and cobalt concentrations in faecal and digesta samples were determined by atomic absorption spectrophoto- metry (Williams et al. 1962).Faecal samples were analyzed also for acid-insoluble ash (Van Keulen and Young 1977). Calculations and statistical analysis The duodenal flow of nutrients was calculated based on the amounts of Co and Cr excreted in faeces. The liquid outflow rate from the rumen was calculated as the slope of theregression of the natu- ral logarithm ofthe Co concentration against time. The total outflow of liquid at the duodenum was calculated as the difference between total digesta flow and DM flow. The estimate of rumen volume was calculated as total outflow (l)/[liquid dilution rate (1/h) x 24 (h)]. The rumen degradability of feed N in vivo was estimatedby assuming an endogenous N flow of 15 % of the duodenal N flow (Tamminga et al. 1989). To characterize the rumen degradability of the experimental silages, their degradability values were fitted in to the following equations (McDo- nald 1981): 165 Agric. Sei. Finl. 1 (1992) p=a' up to time t o p 2=a+b{ l-c*) from timeto onwards, where a 1 represents the rapidly degradable fraction of the feed during the washing ('0 h wash'), p 2 is the proportionate disappearance of feed after time t (h) (t>t o ) and a, b and c are the constants for the in- stantly degradable and slowly degradable fraction of the feed and rate ofdegradation of the latter from time t onwards. The lag time, t o, was calculated as: t=Mc In\h/(a+h-a)\. The values obtained for N were corrected for microbial contamination as suggested by Lindberg (1988). The total tract degradability (TTD) of the feeds was calculated as a sum of the 30-h ruminal degra- dation and the subsequent intestinal degradation of the undegraded feed residue. The standard analysis of variance appropriate to the latin square design was applied to digestibility and nylon bag data using the Tukey's test for treat- ment comparisons. Rumen fluid data was analyzed by analyses of variance using the following model: = H-+ Ai +PJ +Tk + eijk +H I + AH i, + PHji + + eijklm’ where A, P, T and H stand for the effects ofanimal, period, treatment and sampling time, respectively, and e.... the residual error term. e... was used as anijkltn ijk error term for testing the main effects A, P and T. Dilution rate data were analyzed using the same model as withrumen fluid data, with the exception that the effect of sampling site replaced sampling time in the model. Tukey's test was used for the comparison of the treatments. Table 2. The fermentation characteristics of the silages pre- served with different additives. Silage additive Grass NA FA LFA E pH 4.1 4.2 4.1 4.1 In dry matter (g/kg dry matter) WSC 18 89 18 24 91 Lactic acid 92 11 60 86 Acetic acid 14 7 20 10 Formic acid - 21 8 Total acids 106 39 88 96 Ethanol 5 11 19 8 Lactic/Acetic 6.9 1.7 3.1 8.6 In total N (g/kg) Ammonia N 47 18 45 55 Soluble N 541 432 467 499 22 For silage additives, see text. WSC, water soluble carbohydrates. None of the silages contained propionic or butyric acid. Table 1.The chemical composition (g/kg dry matter) of the silages, grass and concentrate. Silage additive Grass Concen- NÄ FA LFA E trate Dry matter, g/kg 177 196 175 187 173 888 Ash 100 93 99 95 95 28 Nitrogen 28 28 29 28 27 19 NDF 531 541 541 508 589 269 ADF 320 319 319 299 305 90 Cellulose 280 280 279 260 262 70 Hemicellulose 211 221 221 207 284 179 Lignin 40 39 40 40 43 20 For silage additives, see text. NDF, neutral detergent fibre; ADF, acid detergent fibre. 166 Agric. Sei. Finl. 1 (1992) Results Chemical composition and fermentation of the silages The chemical composition (Table 1) and fermenta- tion (Table 2) of the silages were clearly affected by the additive used. The DM content was highest in FA silage, and E silage had the lowest contents ofcell walls. Compared withE and NA silages, fer- mentation was restricted during ensiling by the acid-based additives, particularly FA. The content of WSC in FA silage was close to that in original grass, and ammonia-N and total acid content was low compared with the other silages. Intake and digestion of organic matter and fibre There was no difference (P>0.05) in OM intake or in faecal OM between the silages (Table 3). How- ever, compared with the other silages, the amount of OM entering the duodenum was lower (P<0.01) in E silage and the microbial OM higher (PO.OOl) in LFA silage. Digestibility of OM in the rumen, disappearance of digestible OM before the intes- Table 3. The effect ofsilage additive on organic matter (OM) and cell wall digestion. Statistical Silage additive... NA FA LFA E SEM significance ofadditive Organic matter (g/24h) In feed 4633 4714 4886 4746 67.9 NS At duodenum 2907 b 2994 b 3101 b 2339 a 80.7 ** Microbial OM§ 580 a 590 a 729 b 520 a 18.3 *** In faeces 1040 1078 1127 978 31.9 NS Digestibility in the rumen Apparent 0.370 a 0.366 a 0.364 a 0.510 b 0.0227 ** Truet 0.496 a 0.493 a 0.512 a 0.619 b 0.0213 * Disappearance of digestible OM before intestine Apparent 0.477 a 0.476 a 0.473 a 0.642 b 0.0293 * True 0.640 a 0.640 a 0.666 ab 0.779 b 0.0275 * Apparent digestibility 0.774 0.771 0.769 0.794 0.0052 * Neutral detergent fibre (g/24h) In feed 2253 ab 2329 ab 2441 b 2230 a 41.9 * At duodenum 675 697 711 561 32.8 NS In faeces 586 595 615 516 23.4 NS Digestibility Rumen 0.699 0.699 0.708 0.750 0.0109 * Total 0.738 0.743 0.747 0.769 0.0093 NS Total digestibility Hemicellulose 0.709 0.717 0.710 0.741 0.0101 NS Cellulose 0.799 0.798 0.815 0.823 0.0100 NS For silage additives, see text. § Assuming a N:OM ratio ofmicrobial matter 0.09 (Czerkawski 1986). t Corrected according to microbial organic matter. a,b Means in the same row with different superscripts were significantly different (P<0.05). NS, not significant; *, P<0.05; �*, P<0.01; ***, P0.05) for all the diets (Table 4). Non-ammonia-N (NAN) and feed N entering the small intestine were lower (P<0.05) for E treat- ment as compared with the others, while microbial N was highest (PO.OOl) and microbial N synthesis most efficient (P<0.05) for LEA treatment. Silage- N degradability was lowest in FA silage. Ruminal and intestinal degradability of silages Except for the potential degradability (a+h) of cell walls (P<0.05), no statistically significant differ- ences were found between the silages in the con- stants describing the degradability of OM, NDF or N in the rumen. However, there was a tendency towards lower a and higher b values, and effective protein degradability (EPD) was always lower for silages ensiled with acid-based additives (Table 5). The correction of EPD values for microbial protein according to Lindberg (1988) increased all the values notably, the EPD for FA silage being signi- ficantly (P<0.001) lower than that of the other si- lages. No statistically significant differences (P>0.05) were found in lag time, 30-h rumen degradation, intestinal degradation, or total degradation of the nutrients between the silages. Table 4. The effect ofsilage additive on N intake, flow ofN to the duodenum and efficiencies ofmicrobial protein synthesis. Statistical Silage additive... NA FA LFA E SEM significance ofadditive Nitrogen (g/24h) In feed 127 129 138 132 2.6 NS At duodenum Total-N 174b 179 b 188 b 138 a 5.1 ** Ammonia-N 4 5 6 3 0.5 NS NAN 169b 174 b 182 b 135 a 5.0 ** Microbial N 52 a 53 a 66 b 47 a 1.7 *** FeedN§ 91b 94 b 89 b 67 a 4.5 * In faeces 30 32 32 30 1.3 NS Apparent digestibility 0.762 0.753 0.765 0.772 0.0090 NS Silage-N degradability 0.284 0.271 0.353 0.492 0.0050 * NAN at duodenum/N intake 1.34 b 1.35 b 1.32 b 1.02 a 0.005 * Microbial N g/kg OMADRt 31 ab 31 ab 38 b 20 a 2.5 * Microbial N g/kg OMTDR} 23 b 23 b 26 b 16 a 1.3 ** Microbial N g/kg DCHO/ 19 b 19b 23 c 16 a 0.5 *** For silage additives, see text. § assuming endogenous flow ofN to be 15 % of duodenal N flow (Tamminga et. al. 1989). f Organic matter apparently digested in the rumen. { Organic matter truly digested in the rumen. / Digestible carbohydrates. a,b Means in the same row with different superscripts were significantly different (P<0.05). NS, not significant; *, P<0.05; **, P<0.01; ***, P