Herbage nutritive value of binary- and multi-species swards relative to single-species swards in intensive silage systems

Moloney, T.; Sheridan, H; Grant, J.; O’Riordan, E.G.; O’Kiely, P.

doi:10.15212/ijafr-2020-0109

Introduction

Sown grassland swards containing species of grasses, legumes and herbs can, if appropriately formulated and managed, produce greater and less variable yields than monocultures of their constituent species (Lüscher et al., 2008; Nyfeler et al., 2009; Finn et al., 2013). Much of the potential yield advantage of these multi-species swards is derived from factors such as biological N fixation by rhizobia in legume root nodules and functional differences between species which can facilitate increased light- and nutrient-use efficiency (Cardinale et al., 2007; Temperton et al., 2007).

Differences in chemical composition between the three functional groups grass, legume and herb, and also the corresponding differences between and within species of each functional group, would be expected to be manifested in indices of nutritive value such as dry matter digestibility (DMD) and crude protein (CP) content (Fraser & Rowarth, 1996; Li & Kemp, 2005; Brink et al., 2015). Thus, for example, grasses such as timothy (Phleum pratense L.) can have a greater DMD than Italian ryegrass (Lolium multiflorum L.) at the same date during the primary growth (King et al., 2012), while temperate legumes typically have a greater CP content than temperate grasses (Phelan et al., 2015). Herb species such as ribwort plantain (Plantago lanceolata L.) and chicory (Cichorium intybus L.) can have similar DMD to perennial ryegrass when in the vegetative growth stage and are also rich in minerals (Sanderson et al., 2003; Pirhofer-Walzl et al., 2011), while some legume and herb species have relatively high concentrations of condensed tannins which can have implications for animal performance (Barry & McNabb, 1999). In addition, the rate of DMD decline as plants advance from vegetative through inflorescence growth stages is lower for legumes such as red clover (RC) (Trifolium pratense L.) and white clover (Trifolium repens L.) than for perennial ryegrass (Dewhurst et al., 2009) and this has significant implications for the timing of silage harvest. Differences in the temporal growth patterns and thus the timing of peak nutritive value of grasses, legumes and herbs (Sanderson, 2010) may also offer potential to extend the period in which high-quality home-produced forage is available.

On many commercial farms the primary management strategy for increasing herbage yield is to apply inorganic fertiliser N while ensuring that soil fertility, that is, pH and contents of phosphorus (P) and potassium (K), is not limiting the herbage growth. Such applications of inorganic nitrogen (N) can impact the herbage nutritive value, for example, directly by increasing the CP content in grass and herb species (Keating & O’Kiely, 2000b; Martin et al., 2017) or indirectly by altering sward botanical composition (Hopkins et al., 1990; Sanderson, 2010).

This study is part of a larger project undertaken under a four-cut silage production regime, the yield and botanical composition components of which have been reported by Moloney et al. (2020). The objectives of this study were to quantify the effects on the herbage nutritive value of (1) three common temperate grass swards receiving inorganic N or grown in binary mixtures with RC, (2) a perennial ryegrass sward compared to a perennial ryegrass/RC binary mixture or to two multi-species swards, each grown with zero inorganic N input, and (3) the response of a perennial ryegrass sward compared with two multi-species mixtures to receiving increasing rates of inorganic N (0–360 kg N/ha per year). As the timing of the harvest of the primary growth of herbage can have an important impact on the nutritive value of both the first and second cuts for silage production (Gilliland et al., 1995), and as these impacts may differ with sward type, the effects of harvest schedule (specifically the timing of the primary growth harvest) were also investigated. The latter would also allow elucidation of the rates of change in chemical composition traits at the time of the first cut.

Materials and methods

Field plots

Details of the layout and management of field plots established in September 2012 have been reported by Moloney et al. (2020). Briefly, in each of four replicate blocks, treatments were allocated in a split-plot design. The main plots involved the primary growth harvest of a four cut per year schedule being on 12–13 May (Early), 26–27 May (Middle) or 9–10 June (Late). Cuts 2 and 3 were harvested 7 and 14 wk after their primary growth harvest, while Cut 4 for all treatments was on 10 and 24 November in successive years. The sub-plots involved 18 treatments differing in herbage species and inorganic N input (Table 1). Details of the species and varieties used have been reported by Moloney et al. (2020). During 2013 all plots were fertilised and harvested as per the two following experimental years (Years 1 and 2 of results), but no data recording took place. Inorganic N was applied as calcium ammonium nitrate (CAN; 275 g N/kg), with 0.333, 0.278, 0.222 and 0.167 of the annual allocation being applied at the commencement of the growths that culminated in Cuts 1–4, respectively. Herbage was harvested using a Haldrup forage plot harvester (J. Haldrup, Løgstør, Denmark) to an approximate stubble height of 6 cm before being chopped and sampled. Samples (ca. 2 kg) were stored at −18°C prior to chemical analysis. The plot management regime of Years 1 and 2 was maintained through 2016 (Year 3) when single samples of timothy, RC, white clover, ribwort plantain and chicory were obtained from either the Mix 1/120N or Mix 2/120N plots in each replicate block at Cuts 1–3 of the Early, Middle and Late harvest schedules, and these were stored at −18°C prior to chemical analysis. Sward botanical composition and prevailing meteorological conditions have previously been reported by Moloney et al. (2020).

Table 1:

Sward types and the associated species included, their rates of seed sown and the rates of inorganic N applied

Sward	Species included	Seed rate¹	N²
TIM/360N	Timothy	15	360
IRG/360N	Italian ryegrass	42	360
PRG/0-360N	Perennial ryegrass	32	0, 120, 240, 360
RC	Red clover	15	0
TIM/RC	Timothy, red clover	6, 9	0
IRG/RC	Italian ryegrass, red clover	16.8, 9	0
PRG/RC	Perennial ryegrass, red clover	12.8, 9	0
Mix 1/0-360	Timothy, perennial ryegrass, red clover, white clover	3, 6.4, 5.25, 3	0, 120, 240, 360
Mix 2/0-360	Timothy, perennial ryegrass, red clover, ribwort plantain, chicory	3, 6.4, 5.25, 1.5, 0.63	0, 120, 240, 360

¹kg seed/ha (values correspond in order with species in the preceding column).

²Inorganic N input (kg N/ha per year).

Prior to each harvest during Years 1 and 2, the herbage growth stage was determined according to Moore et al. (1991) for grass and Ohlsson & Wedin (1989) for RC. For white clover, ribwort plantain and chicory, a growth stage index was devised based on an adaptation of the index developed by Ohlsson & Wedin (1989) for RC, for which the numeric values and the corresponding criteria are described in Table 2.

Table 2:

Modified growth stage index for white clover, ribwort plantain and chicory

Growth stage number	Description
1	Vegetative
1.5	Stem appearance
2	Stem visible; early elongation
2.5	Late elongation
3	Early reproductive phase; buds visible
3.5	Reproductive phase; flowers visible
4	Late reproductive phase; seeds developing
5	Seed pods visible

Chemical analysis

Herbage dry matter (DM) content was estimated following drying in a forced-air circulation oven at 98°C for 16 h. Replicate samples dried at 60°C for 48 h were milled through a 1-mm aperture sieve (Wiley mill, 1 mm screen) and used for the determination of chemical composition. In vitro DMD was determined using the method of Tilley & Terry (1963) with the modification that the final residue was isolated by filtration (Whatman GF/A 55 mm, pore size 1.6 μm; Whatman International, Maidstone, UK) rather than by centrifugation. Water-soluble carbohydrate (WSC) content was measured using the anthrone method (Thomas, 1977) on an Autoanalyser 3 (Bran and Leubbe GmbH, Norderstedt, Germany), while ash was determined by complete combustion in a muffle furnace at 550°C for 5 h. The CP content (N × 6.25) was determined using an LECO FP 428 N analyser (Leco Instruments, St. Joseph, MI, USA) based on method 990-03 of Association of Analytical Chemists (AOAC, 1990). The content of WSC was not measured in Cut 4 samples.

Statistical analysis

The 18 sub-plot treatments within the main plots (three levels of harvest schedule) of this split-plot design, which had four replicate blocks, had a number of subsets with factorial structure and associated controls. The nested model, or elaborate contrasts, required to incorporate the controls and the multiple factorial sets of treatments resulted in undue complexity and, to avoid this, the sub-plot treatments were arranged into three groups for statistical analysis. The treatment contrasts within these groups addressed the three objectives identified at the end of the Introduction, and this is the same approach as used by Moloney et al. (2020).

Group 1 used seven of the 18 sub-plot treatments (PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC) to give a (3 × 2) +1 arrangement, with the +1 (i.e. RC) being a control. A nested linear model was used to accommodate this structure. For Group 2 the four sub-plot treatments PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N formed a simple four treatment contrast and in Group 3, 12 of the 18 sub-plot treatments (PRG/0-360N, Mix 1/0-360N and Mix 2/0-360N) provided a 3 × 4 factorial arrangement.

All analyses of these groups incorporated year, replicate blocks and harvest schedule as the main plot factors. In the first instance, harvest schedule was included in the analyses as a factor and then, with equally spaced time intervals, the analyses were repeated with schedule included as a covariate in an analysis of covariance, to identify trends over time. All interactions were tested and, in the analysis of covariance, linear and quadratic terms and their interactions were included. A similar analysis of covariance was used for inorganic N application rates in Group 3.

Residuals from all analysis models were checked to ensure that the assumptions of the analyses were met. Contrasts between means were specified for significant effects in the analyses and allowance for multiplicity effects used Tukey’s adjustments to P-values.

All data were analysed using the GLIMMIX and MIXED procedures of SAS 9.3 (SAS, 2013).

Results

The corresponding values for the Early and Late harvest schedules are presented in Appendix Tables A1 and A2.

Tables of mean values for each sward species × inorganic N treatment within each level of harvest schedule, and of corresponding standard errors of the mean and P-values for the three groups of treatment contrasts, are presented for DMD (Tables 3 and 4), WSC (Tables 5 and 6) and CP (Tables 7 and 8). Appendix Tables A3 (means) and A4 (standard errors of the mean and P-values) provide DM content values and Appendix Tables A5 and A6 provide the corresponding values for ash.

Table 3:

Mean in vitro dry matter digestibility (g/kg) at each cut, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Cut		1			2			3			4
Schedule¹	E	M	L	E	M	L	E	M	L	E	M	L
Sward²
IRG/360N	757	723	654	674	655	663	689	738	765	700	761	784
TIM/360N	775	733	673	714	669	718	769	764	762	748	774	782
RC	756	746	703	723	693	686	721	768	763	732	761	739
IRG/RC	772	741	688	717	638	670	718	768	765	741	749	791
TIM/RC	787	740	689	720	672	705	728	761	762	717	761	774
PRG/RC	795	744	696	742	695	721	722	758	765	706	764	787
PRG/0N	816	747	687	790	763	784	814	798	787	740	778	793
PRG/120N	794	736	662	781	757	766	786	805	779	714	783	804
PRG/240N	784	720	635	764	733	766	793	794	786	718	732	792
PRG/360N	784	739	631	749	738	777	789	803	803	684	752	789
Mix 1/0N	796	752	684	739	719	734	745	783	795	744	767	784
Mix 1/120N	785	739	686	753	711	677	762	800	800	730	779	776
Mix 1/240N	767	728	688	736	697	736	762	788	793	735	744	808
Mix 1/360N	775	720	662	733	702	740	765	781	805	719	781	776
Mix 2/0N	776	736	705	722	692	701	725	766	782	767	758	761
Mix 2/120N	773	738	674	727	693	714	727	759	779	734	756	773
Mix 2/240N	782	722	658	716	701	729	739	776	787	725	757	770
Mix 2/360N	771	744	668	726	703	723	753	768	793	738	766	797

¹Harvest schedule: E = Early, M = Middle, L = Late.

²Sward species × inorganic N treatment.

Table 4:

Standard errors of the mean (SEM) and P-values for in vitro dry matter digestibility (g/kg) at each cut, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Group¹		1				2		3

Effect		Species²	Source²	Species × Source	Species × Source × Schedule	Species³	Species × Schedule	Species⁴	N rate	Species × N rate	Species × N rate × Schedule
Cut 1	SEM	4.7	4.4	5.5	9.4	7	12.1	4.6	4.8	6.2	10.5
Cut 1	P	0.018	<0.001	0.134	0.032	0.55	0.091	0.465	<0.001	0.106	0.032
Cut 2	SEM	3.5	3	4.5	7.8	4.6	8	3.6	4	6.9	11.6
Cut 2	P	<0.001	0.011	<0.001	0.041	<0.001	0.681	<0.001	0.463	0.051	0.428
Cut 3	SEM	5.3	4.8	6.5	11.3	7.1	11.9	3.4	3.8	6.1	10.2
Cut 3	P	<0.001	0.001	<0.001	0.131	<0.001	0.009	<0.001	0.377	0.277	0.759
Cut 4	SEM	6.1	5.4	7.8	0.2	7.3	13	5.2	5.7	9.2	15.5
Cut 4	P	0.16	0.762	0.052	12.93	0.021	0.001	0.669	0.257	0.253	0.677

¹Group 1 = PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC (the SEMs for Species were calculated for the 3 × 2 interaction but were also used when comparing RC to any of the 3 × 2 treatments); Group 2 = PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N; Group 3 = PRG/0-360N, Mix 1/0-360N and Mix 2/0-360N.

²Within Group 1, Species is IRG, PRG or TIM and Source is either grass + 360 kg N/ha per year or grass + red clover.

³Within Group 2, Species is PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N.

⁴Within Group 3, Species is PRG, Mix 1 and Mix 2. Schedule = Harvest schedule.

Table 5:

Mean water-soluble carbohydrate content (g/kg DM) at Cuts 1–3, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Cut		1			2			3
Schedule¹	E	M	L	E	M	L	E	M	L
Sward
IRG/360N	231	179	141	124	138	143	135	120	130
TIM/360N	80	63	73	52	70	75	69	56	60
RC	83	61	67	56	73	79	71	80	57
IRG/RC	263	196	162	121	153	151	130	93	99
TIM/RC	95	79	77	67	77	86	67	66	52
PRG/RC	158	115	100	67	84	103	69	67	68
PRG/0N	248	197	119	178	186	172	151	132	157
PRG/120N	207	168	121	187	194	160	175	174	159
PRG/240N	173	130	102	156	135	120	153	148	137
PRG/360N	149	138	114	106	109	104	120	110	121
Mix 1/0N	132	97	126	60	85	90	68	59	67
Mix 1/120N	137	109	116	92	98	79	85	77	79
Mix 1/240N	106	97	104	77	88	80	85	84	91
Mix 1/360N	102	98	111	71	74	73	74	72	83
Mix 2/0N	135	108	106	63	83	78	80	63	58
Mix 2/120N	130	94	114	73	91	81	74	78	81
Mix 2/240N	116	94	86	65	78	80	84	83	95
Mix 2/360N	103	83	86	70	74	73	76	70	76

¹See footnotes beneath Table 3.

Table 6:

Standard errors of the mean (SEM) and P-values for water-soluble carbohydrate content (g/kg DM) at Cuts 1–3, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Group¹		1				2		3

Effect		Species	Source	Species × Source	Species × Source × Schedule	Species	Species × Schedule	Species	N rate	Species × N rate	Species × N rate × Schedule
Cut 1	SEM	4.4	3.6	6.2	10.7	6.1	10.5	3.5	3.8	5.8	10.1
Cut 1	P	<0.001	0.093	0.032	0.854	<0.001	<0.001	<0.001	<0.001	0.003	0.069
Cut 2	SEM	4.1	3.7	5.5	9.6	4.7	8.1	2.4	2.7	4.1	7
Cut 2	P	<0.001	0.784	0.006	0.487	<0.001	0.177	<0.001	<0.001	<0.001	0.44
Cut 3	SEM	4.2	3.9	5.1	8.9	6.1	10.5	2.8	3	4.3	7.5
Cut 3	P	<0.001	<0.001	<0.001	0.449	<0.001	0.597	<0.001	<0.001	<0.001	0.194

¹See footnotes beneath Table 4.

Table 7:

Mean crude protein content (g/kg DM) at each cut, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Cut		1			2			3			4
Schedule¹	E	M	L	E	M	L	E	M	L	E	M	L
Sward
IRG/360N	129	105	86	120	103	107	131	152	174	200	251	296
TIM/360N	157	131	94	127	115	136	172	175	188	215	285	314
RC	223	185	144	183	175	158	181	219	263	264	290	316
IRG/RC	101	93	85	126	88	94	130	177	187	198	229	250
TIM/RC	175	139	102	144	143	153	191	208	220	247	282	295
PRG/RC	154	133	85	151	147	144	163	206	219	229	248	270
PRG/0N	85	78	64	91	82	93	108	143	132	180	201	226
PRG/120N	96	80	65	82	83	101	96	115	124	167	188	231
PRG/240N	119	96	76	102	123	135	119	128	137	179	197	241
PRG/360N	142	106	87	138	142	168	157	172	174	201	231	271
Mix 1/0N	156	126	97	167	147	152	183	209	207	252	272	290
Mix 1/120N	132	104	89	124	123	134	165	172	165	228	245	269
Mix 1/240N	148	104	97	140	120	138	161	160	169	214	236	269
Mix 1/360N	145	116	92	147	138	157	179	176	178	222	259	274
Mix 2/0N	156	120	90	145	143	149	171	188	198	211	234	255
Mix 2/120N	136	116	87	127	114	127	157	158	159	192	219	245
Mix 2/240N	145	110	92	125	124	134	149	157	151	196	224	266
Mix 2/360N	162	124	93	142	136	148	173	176	186	217	245	282

¹See footnotes beneath Table 3.

Table 8:

Standard errors of the mean (SEM) and P-values for crude protein content (g/kg DM) at each cut, for each harvest schedule and sward species × inorganic N treatment (averaged across years)

Group¹		1				2		3

Effect		Species	Source	Species × Source	Species × Source × Schedule	Species	Species × Schedule	Species	N rate	Species × N rate	Species × N rate × Schedule
Cut 1	SEM	2.4	2	3.4	5.9	4.1	7.1	2.2	2.4	3.3	5.6
Cut 1	P	<0.001	0.253	<0.001	0.033	<0.001	<0.001	<0.001	<0.001	<0.001	0.124
Cut 2	SEM	3.2	2.6	4.5	7.8	4.9	8.6	2.3	2.5	3.7	6.3
Cut 2	P	<0.001	0.328	0.006	0.316	<0.001	0.799	<0.001	<0.001	<0.001	0.435
Cut 3	SEM	3.9	3.2	5.4	9.4	6.2	10.7	2.2	2.4	3.8	6.7
Cut 3	P	<0.001	<0.001	0.247	0.819	<0.001	0.599	<0.001	<0.001	<0.001	0.701
Cut 4	SEM	2.3	1.9	3	5.6	3.7	6.7	2.3	2.6	4.4	8.2
Cut 4	P	<0.001	0.511	<0.001	0.36	<0.001	0.998	<0.001	<0.001	<0.001	0.998

¹See footnotes beneath Table 4.

The mean chemical composition of five individual herbage species at Cuts 1–3 of the multi-species swards is presented in Table 9.

Table 9:

Mean chemical composition of individual herbage species at Cuts 1–3 of multi-species swards, for each harvest schedule

Species		Timothy			Red clover			White clover			Ribwort plantain			Chicory

Schedule¹		E	M	L	E	M	L	E	M	L	E	M	L	E	M	L
	Cut
DMD	1	827	765	700	833	831	739	848	839	812	787	730	690	863	876	811
	2	764	771	776	742	735	681	760	742	764	604	641	631	777	792	713
	3	781	778	746	774	761	799	807	817	821	681	710	745	825	826	831
WSC	1	225	177	146	111	120	128	110	120	77	129	110	88	136	117	93
	2	108	102	89	84	89	87	58	73	79	66	91	71	74	128	137
	3	133	136	115	107	100	127	117	105	109	91	109	127	161	166	166
CP	1	128	131	119	287	246	226	285	270	253	175	161	151	244	194	160
	2	132	126	108	214	208	201	240	230	236	111	113	123	132	156	109
	3	149	155	177	212	215	235	246	200	248	118	127	150	126	110	189
DM	1	256	257	259	154	152	167	150	150	204	129	125	131	121	107	111
	2	255	213	259	181	180	172	183	139	146	191	206	175	136	161	146
	3	245	267	250	178	184	185	185	145	150	203	220	168	150	165	169
Ash	1	60	71	61	91	87	96	89	85	89	114	99	118	107	99	112
	2	75	62	72	99	89	87	88	87	90	97	108	87	108	108	103
	3	80	82	84	94	95	90	89	91	87	92	94	107	120	121	111

¹Harvest schedule: E = Early, M = Middle and L = Late. DMD = Dry matter digestibility (g/kg), WSC = water-soluble carbohydrates (g/kg DM), ash (g/kg DM), CP = crude protein (g/kg DM).

Perennial ryegrass, Italian ryegrass and timothy receiving inorganic N or grown with RC (PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC)

Herbage DMD at Cut 1 was greater (P < 0.001) for grass grown with RC than with inorganic N (739 vs. 719 g/kg) (Tables 3 and 4). Digestibility declined when the harvest date was delayed (778, 737 and 672 g/kg) but there was a lesser (P < 0.001) decline for grass/RC (785 to 691 g/kg) than grass/360N (772 to 652 g/kg), while delaying the PRG/360N harvest date resulted in a greater (P < 0.05) DMD decline (784 to 631 g/kg) than for IRG/360N (757 to 654 g/kg) and TIM/360N (775 to 673 g/kg). Red clover had a greater (P < 0.05) DMD than IRG/360N or PRG/360N (735 vs. 711 and 718 g/kg). At Cut 2, PRG/360N (754 g/kg) had a greater (P < 0.001) DMD value than IRG/360N (664 g/kg) and TIM/360N (700 g/kg); however, PRG/RC (719 g/kg) had a lower (P < 0.001) value than PRG/360N. The DMD of RC (700 g/kg) was greater (P < 0.01) than IRG/360N and IRG/RC (675 g/kg) but less (P < 0.001) than PRG/360N. Herbage harvested at the Early (719 g/kg) and Late (709 g/kg) schedules had greater (P < 0.001) values than that harvested at the Middle harvest schedule (678 g/kg). At Cut 3, PRG/360N (798 g/kg) had a greater (P < 0.001) DMD value than IRG/360N (731 g/kg) and TIM/360N (765 g/kg); however, when grasses were grown with RC, there was no difference in values. Herbage DMD increased (P < 0.05) when Cut 1 had been harvested later (736, 765 and 770 g/kg). RC (751 g/kg) was lower (P < 0.001) than PRG/360N but greater (P < 0.05) than IRG/360N (731 g/kg). At Cut 4 the Early harvest schedule had the lowest (P < 0.001) value (716 vs. 760 and 784 g/kg) while RC did not differ (P > 0.05) from the other sward species treatments.

At Cuts 1 and 2 but not Cut 3, IRG/360N (184 and 135 g/kg DM; 128 g/kg DM) had a greater (P < 0.001) WSC content than PRG/360N (134 and 106 g/kg DM; 117 g/kg DM) but these were in turn greater (P < 0.001) than TIM/360N (72, 65 and 62 g/kg DM) (Tables 5 and 6). Delaying the harvest date from the Early to the Late schedules at Cut 1 reduced (P < 0.001) the herbage WSC in swards containing Italian (247 to 151 g/kg DM) and perennial (154 to 107 g/kg DM) ryegrasses but not timothy, while at Cut 2 the Late schedule had a greater (P < 0.05) value compared to the Early schedule. At Cuts 1–3, the WSC content of RC did not differ (P > 0.05) from that of TIM/360N but was less (P < 0.001) than that of IRG/360N and PRG/360N.

At Cut 1, CP contents for the Early and Middle harvest schedules were greater (P < 0.001) for swards containing timothy (166 and 135 g/kg DM) than perennial ryegrass (148 and 119 g/kg DM) which in turn were greater (P < 0.001) than swards with Italian ryegrass (115 and 99 g/kg DM) (Tables 7 and 8). Furthermore, PRG/RC (124 g/kg DM) and TIM/RC (138 g/kg DM) had greater (P < 0.05) values than PRG/360N (112 g/kg DM) and TIM/360N (127 g/kg DM) while the opposite effect was observed for Italian ryegrass (93 and 107 g/kg DM). Delaying the harvest date reduced (P < 0.001) the CP content with a greater reduction for swards containing perennial ryegrass (148 to 86 g/kg DM) and timothy (166 to 98 g/kg DM) than Italian ryegrass (115 to 85 g/kg DM). The CP content at Cut 2 was greater (P < 0.01) for PRG/360N (149 g/kg DM) than TIM/360N (126 g/kg DM) which was greater than IRG/360N (110 g/kg DM); however, there was no difference (P > 0.05) between PRG/RC and TIM/RC. At Cut 3, swards containing Italian ryegrass had the lowest (P < 0.001) CP contents, grass/360N (166 g/kg DM) had lower (P < 0.001) values than grass/RC (189 g/kg DM) and the Early harvest schedule (157 g/kg DM) had lower (P < 0.001) values than the Middle (182 g/kg DM) or Late (194 g/kg DM) schedules. For Cut 4, swards containing timothy had the greatest (P < 0.001) values, while the Early harvest schedule (215 g/kg DM) had the lowest (P < 0.001) and the Late schedule (283 g/kg DM) the greatest (P < 0.001) values. The CP values at each cut were greater (P < 0.001) for RC than any of the grass monocultures.

Perennial ryegrass versus binary- and multi-species mixtures at 0N (PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N)

Delaying the Cut 1 harvesting date reduced (P < 0.001) herbage DMD (796, 745 and 693 g/kg), while there was no difference (P > 0.05) in DMD between the four sward species treatments. At Cut 2, PRG/0N (780 g/kg) had the greatest (P < 0.001) DMD and Mix 1/0N (731 g/kg) was greater (P < 0.01) than Mix 2/0N (705 g/kg), while the Middle harvest schedule (717 g/kg) resulted in a lower (P < 0.001) DMD than the Early (748 g/kg) or Late (735 g/kg) schedules. At Cut 3, PRG/0N (815 g/kg) had a greater (P < 0.01) DMD than all other sward species treatments (722–745 g/kg) in the Early harvest schedule. When harvested in the Middle schedule, only PRG/RC (758 g/kg) and Mix 2/0N (765 g/kg) were less than PRG/0N (798 g/kg), and there was no difference (P > 0.05) between the sward species treatments in the Late schedule. At Cut 4, PRG/0N (771 g/kg) was greater (P < 0.05) than PRG/RC (752 g/kg), while the Early harvest schedule (740 g/kg) gave lower (P < 0.01) values than the two later schedules (766 and 780 g/kg).

At Cut 1, PRG/0N had the greatest (P < 0.001) WSC content only at the Early (248 vs. 132–158 g/kg DM) and Middle (197 vs. 97–115 g/kg DM) harvest schedules (Tables 5 and 6). PRG/0N had the greatest (P < 0.001) WSC content at Cuts 2 (179 vs. 75–85 g/kg DM) and 3 (147 vs. 65–68 g/kg DM). The Early harvest schedule had the greatest (P < 0.001) values at Cut 1 (168 vs. 113–130 g/kg DM) and the lowest (P < 0.05) values at Cut 2 (92 vs. 110–111 g/kg DM).

Herbage CP content was lowest (P < 0.001) for PRG/0N at all cuts although at Cut 1 the magnitude of this effect declined as the harvest date was delayed (Tables 7 and 8). The Early harvest schedule had the greatest (P < 0.001) value and the Late schedule the lowest (P < 0.001) value at Cut 1 (138 vs. 84 g/kg DM), although the magnitude of this effect was quite small for PRG/0N. At Cut 3, CP was lowest (P < 0.05) for the Early harvest schedule, and at Cut 4 the values for Mix 2/0N (233 g/kg DM) were lower (P < 0.01) than for PRG/RC (249 g/kg DM) which in turn were lower (P < 0.001) than for Mix 1/0N (272 g/kg DM).

Perennial ryegrass versus multi-species mixtures at increasing rates of inorganic N (PRG, Mix 1 and Mix 2 at 0, 120, 240 and 360 kg N/ha per year)

Herbage DMD was lower (P < 0.001) for Mix 1 (723 g/kg) and Mix 2 (729 g/kg) than perennial ryegrass (764 g/kg) at Cut 2, while at Cut 3 the same effect was significant only in the Early (758 and 736 vs. 796 g/kg) and Middle (788 and 767 vs. 800 g/kg) harvest schedules (Tables 3 and 4). At Cut 3, a greater DMD for Mix 1 than Mix 2 also occurred only at the Early and Middle schedules. At Cut 1, inorganic N application (744–722 g/kg for 0–360 kg N/ha) (P < 0.001) and later harvesting dates (784, 735 and 670 g/kg) (P < 0.001) reduced DMD. For Cut 2, DMD was greatest (P < 0.01) for the Early (745 g/kg) and Late (737 g/kg) compared to the Middle (717 g/kg) schedules, while for Cut 3 it was greatest (P < 0.01) for the Middle and Late schedules of the Mix 1 and Mix 2 swards. No effect of sward species treatment or rate of inorganic N applied occurred (P > 0.05) at Cut 4, but values were lowest (P < 0.001) for the Early (729 g/kg) and greatest (P < 0.05) for the Late (785 g/kg) harvest schedules.

For Cut 1, WSC was greater (P < 0.001) for perennial ryegrass than Mix 1 and Mix 2 when harvested in the Early (194 vs. 120 and 121 g/kg DM) and Middle (158 vs. 101 and 95 g/kg DM) schedules but not in the Late schedule (Tables 5 and 6). The application of inorganic N reduced (P < 0.01) the WSC content and this effect was most pronounced in perennial ryegrass and in the Early harvest schedule. At Cuts 2 and 3, perennial ryegrass had a greater (P < 0.001) WSC content than Mix 1 and Mix 2 (151 vs. 81 and 76 g/kg DM, 145 vs. 77 and 76 g/kg DM, respectively), although this effect diminished at increasing rates of inorganic N application.

Although the overall CP concentration at each cut was greater (P < 0.001) for both Mix 1 and Mix 2 than perennial ryegrass (Tables 7 and 8), the magnitude of this difference was reduced or eliminated (P < 0.001) by the application of inorganic N up to 360 kg N/ha per year and the response to inorganic N was evident only with perennial ryegrass.

Discussion

Perennial ryegrass, Italian ryegrass and timothy receiving inorganic N or grown with RC (PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC)

The generally lower DMD recorded at the first three cuts for IRG/360N compared to the other two grass species monocultures suggests that in order to produce silage of equal DMD to these other grasses, Italian ryegrass needs to be harvested after shorter growth intervals and therefore more frequent harvesting during the year is required compared to perennial ryegrass or timothy. When the latter strategy was employed by Keating & O’Kiely (2000a), comparably high DMD values were obtained from both ryegrass species. Although the DMD of PRG/360N was lower than anticipated at Cut 1, the similar values for PRG/360N and TIM/360N agree with King et al. (2012) while the clear advantage of PRG/360N over TIM/360N for the two mid-season cuts is likely explained by the more advanced growth stage observed with TIM/360N at Cuts 2 and 3 (Table 10; Appendix Tables A1 and A2).

Table 10:

Mean growth stage indices for each herbage species from each sward species × inorganic N treatment at Cuts 1–3 on the Middle harvest schedule, averaged across years

Species	PRG¹			IRG¹			TIM¹			RC²			WC³			PLANT³			CHIC³

Cut	1	2	3	1	2	3	1	2	3	1	2	3	1	2	3	1	2	3	1	2	3
IRG/360N				2.8	3.4	2.7
TIM/360N							2.9	3.1	2.4
RC										2.8	5.0	4.2
IRG/RC				2.8	3.2	2.6				2.1	4.1	3.8
TIM/RC							2.5	2.8	2.4	2.6	4.7	4.0
PRG/RC	2.5	3.0	1.3							2.5	5.1	4.2
PRG/0N	2.4	2.1	1.5
PRG/120N	2.7	2.7	1.5
PRG/240N	2.7	2.9	1.5
PRG/360N	2.7	3.0	1.5
Mix 1/0N	2.9	3.0	1.4				2.5	2.8	1.7	2.3	4.8	4.4	1.0	2.3	3.5
Mix 1/120N	2.8	2.8	1.5				2.5	3.0	2.1	1.9	4.7	4.3	1.0	2.3	3.5
Mix 1/240N	2.9	2.9	1.6				2.7	3.1	2.3	2.2	4.4	4.6	1.0	2.3	3.5
Mix 1/360N	2.8	3.1	1.5				2.5	3.0	2.1	2.2	3.9	3.4	1.0	2.3	2.3
Mix 2/0N	2.7	3.1	1.6				2.5	3.0	1.7	2.3	4.7	4.5				3.3	4.5	3.8	2.3	2.0	2.3
Mix 2/120N	2.8	2.9	1.7				2.6	2.9	2.6	2.4	4.3	4.1				3.3	4.5	3.8	2.8	2.5	2.0
Mix 2/240N	3.0	2.9	1.4				2.6	3.1	2.2	2.3	4.6	3.8				3.3	4.0	3.8	2.8	2.5	1.8
Mix 2/360N	3.0	3.1	1.6				2.7	3.1	2.5	2.0	4.1	4.2				3.3	4.0	3.3	2.8	2.5	1.3

¹Growth stage indices for perennial ryegrass (PRG), Italian ryegrass (IRG) and timothy (TIM) are from Moore et al. (1991).

²Indices for red clover (RC) are from Ohlsson & Wedin (1989).

³Indices for white clover (WC), ribwort plantain (PLANT) and chicory (CHIC) are from Table 2. Indices for the Early and Late harvest schedules are in Appendix Tables A1 and A2, respectively.

While Clavin et al. (2017) noted a lower DMD for RC than for perennial ryegrass receiving inorganic N at each cut of a four harvest annual schedule, this was evident only with Cuts 2 and 3 in the current study. Therefore, the greater DMD value for RC than PRG/360N at Cut 1 supports the observation that the DMD from this cut of PRG/360N was lower than anticipated. This is further supported by King et al. (2012) who also reported that RC had a lower DMD in late May compared to perennial ryegrass receiving inorganic N. The DMD of binary mixtures of RC with each of the three grass species sometimes reflected the ranking of their DMD values in monoculture and their relative contents in the binary mixture at each cut (Moloney et al., 2020). This agrees with the findings of Clavin et al. (2017) for RC and perennial ryegrass. However, in the case of IRG/RC, the DMD values were generally greater than the contribution of the relatively moderate proportion of RC would suggest. This outcome may be at least partly related to the observation that Italian ryegrass in IRG/RC was often at a less developed growth stage compared to that in IRG/360N (Table 10; Appendix Tables A1 and A2). The slower development of Italian ryegrass in IRG/RC may be a response to an inadequate supply of N due to the reduced RC content reported by Moloney et al. (2020).

The daily rate of decline in DMD of IRG/360N and TIM/360N between 12–13 May and 9–10 June, at 3.7 and 3.6 g/kg, respectively, was less than the daily rate for PRG/360N in the current study (5.5 g/kg) and also that reported by Gilliland et al. (1995). Furthermore, the inclusion of RC in a binary mixture with each grass species slowed the rate of DMD decline to one intermediate between the respective grass monocultures and the RC monoculture. The reduction in the rate of herbage DMD decline due to the inclusion of RC in mixtures with grasses was previously noted by Dewhurst et al. (2009) and Peyraud et al. (2009).

The phenomenon demonstrated by Gilliland et al. (1995) that as the date of the first cut of the primary growth of a perennial ryegrass sward is delayed, the digestibility of its regrowth taken 6 wk later increases, was evident for the Early versus the Late harvest schedules of PRG/360N. However, no such response occurred for IRG/360N or TIM/360N, while for Cut 2 of RC its DMD declined in response to delaying the primary growth harvest. The latter in turn meant that the DMD of PRG/RC also declined at Cut 2 in response to later harvesting of the primary growth.

The relative ranking for the WSC content of IRG/360N > PRG/360N > TIM/360N agrees with King et al. (2012), while RC, noted for its typically low WSC content, was similar to TIM/360N which also agrees with King et al. (2012). The magnitude by which the average WSC content of PRG/RC was lower than that of PRG/360N increased from Cut 1 through to Cut 3, reflecting the increasing proportion and relatively low WSC content of RC in these swards. This negative effect of the elevated proportion of RC in mid-season agrees with findings previously described by Clavin et al. (2017). In contrast, the similar WSC contents in TIM/RC and TIM/360N reflect the similar WSC content of the monocultures of these species. This is supported by the findings of Hetta et al. (2003). In the case of Italian ryegrass, the absence of a consistent difference in WSC content between being grown with RC or inorganic N is likely due to the low proportion of RC in these swards. Furthermore, the low RC proportion led to the relatively high WSC content recorded for IRG/RC.

The generally lower CP content of IRG/360N, compared in particular to TIM/360N, and the consistently lower CP content of the three grass species monocultures receiving 360 kg N/ha per year compared to RC agree with the findings of King et al. (2012). In the case of both perennial ryegrass and timothy, the trend for higher contents of CP for their mixtures with RC compared to the corresponding grass monocultures receiving inorganic N supports previous observations of Clavin et al. (2017) for perennial ryegrass and Hetta et al. (2003) for timothy. This trend suggests that in addition to the CP content of the binary mixtures being elevated by the proportion of RC present and its relatively high CP content, the atmospheric N fixed within the RC and made available to the companion grass increased the CP content of the latter compared to the grass monoculture when no inorganic N was applied, as was described by Gierus et al. (2012). In contrast to the outcomes for perennial ryegrass and timothy, the absence of a comparable response for the binary mixture of Italian ryegrass with RC reflects the effects of the relatively low proportion of RC in these swards (Moloney et al., 2020).

Perennial ryegrass versus binary- and multi-species mixtures at 0N (PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N)

The relatively high DMD values at each cut of PRG/0N conform with results for perennial ryegrass grown without inorganic N fertiliser reported by Keating & O’Kiely (2000b), Conaghan et al. (2012) and Clavin et al. (2017). The explanation for the tendency for the inclusion of RC with perennial ryegrass to reduce herbage DMD, with the scale of this effect being particularly marked at Cuts 2 and 3, resides with the consistently lower DMD values recorded for RC compared to PRG/0N and the relative proportions of these two species present at each cut (Moloney et al., 2020). Clavin et al. (2017) also repeatedly recorded lower DMD values for RC than perennial ryegrass under comparable conditions. However, as noted by Clavin et al. (2017), caution is required when interpreting such results as the relationship between in vitro digestibility and animal performance indices such as forage intake or animal growth rate can differ for grasses and legumes. This differential response may extend to herbs such as ribwort plantain and chicory.

The comparison between the DMD of PRG/RC and Mix 1/0N is more complex than the preceding contrast as, even though both treatments are composed of grass and legume functional groups, there are possible additional but contrasting effects from the presence of timothy and white clover in Mix 1/0N. Furthermore, there is evidence that for some species at least, their DMD may be greater when in a multi-species sward than when in monoculture. For example, timothy in the multi-species swards generally had greater DMD values than when in monoculture (TIM/360N) and RC in these multi-species swards also recorded higher values compared to when in monoculture (RC) (Tables 3 and 9; note the values in Table 9 are from the following year). Finally, it is noteworthy that the proportion of the grass functional group present was generally slightly greater in Mix 1/0N than in PRG/RC (37–86% vs. 22–78% across cuts) and that for each cut of Mix 1/0N the proportions of both grasses were alike and of both clovers were alike. Thus, the outcome of these and possibly other factors was that even though herbage DMD values for both PRG/RC and Mix 1/0N were similar at Cut 1 they were 12–26 g/kg greater for Mix 1/0N at subsequent cuts. Some of the advantage to Mix 1/0N is likely associated with the presence of white clover which in this study and as reported by Dewhurst et al. (2009) had a greater digestibility than RC. This is supported by Elgersma & Schlepers (1997) who have shown a greater digestibility through the growing season for a mixed perennial ryegrass and white clover sward compared to a monoculture of the grass.

Compared to Mix 1/0N, Mix 2/0N involved the replacement of white clover by two species from a third functional group. In general, changes in the proportion of grass and RC present were modest (values for Mix 1/0N vs. Mix 2/0N across cuts were 37–5% vs. 35–74% grass and 7–33% vs. 9–41% RC) and the DMD values for chicory were generally at least as high as those for white clover (Table 9). Thus, the lower DMD values for Mix 2/0N than Mix 1/0N for the two mid-season cuts likely reflect the lower values recorded for ribwort plantain particularly at these two mid-season cuts.

The differences between the four treatments in their daily rates of decline in DMD between 12–13 May and 9–10 June (4.6, 3.5, 4.0 and 2.5 g/kg for PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N, respectively) are potentially of practical importance. However, the slowest rate of decline that occurred, with Mix 2/0N, is partially due to it having the lowest DMD among these treatments on 12–13 May.

The beneficial effect of a delayed first-cut harvest on the digestibility of a subsequent second cut described by Gilliland et al. (1995) for perennial ryegrass was not evident for any of the four treatments. Thus, it appears that this response for perennial ryegrass differs when it receives no inorganic N fertiliser (PRG/0N) compared to when it receives 360–400 kg N/ha annually (PRG/360N and Gilliland et al. (1995)). The numerical decline in Cut 2 DMD for PRG/RC and Mix 2/0N compared to Mix 1/0N when managed under the Late compared to the Early harvest schedules likely relates to a beneficial effect of white clover in Mix 1/0N and negative impacts of RC in PRG/RC and of both RC and chicory in Mix 2/0N (Table 9). Chicory has previously been shown to be capable of developing a woody stem quite rapidly in early summer (Li & Kemp, 2005) and this would explain its reduced DMD.

Perennial ryegrass typically has a greater WSC content than most other grass and legume species commonly found in temperate permanent grassland (Wilson & Collins, 1980; Dewhurst et al., 2009), and this relativity was reflected in the current study where PRG/0N had consistently greater values than the remaining three treatments. This outcome agrees with Ergon et al. (2017) when comparing perennial ryegrass with a four species grass and legume mixture. The values in Tables 5 and 9 suggest that the WSC advantage for PRG/0N emanated mainly from perennial ryegrasses’ considerably greater WSC content than either legume or either herb present in the mixed species swards. However, they also suggest that the finding of Barry (1998) in which herbs such as chicory typically have a greater WSC content than legumes, specifically RC, was not consistently repeated when they were grown in multi-species swards in this study. In contrast to the relative values for perennial ryegrass and the legumes or herbs, timothy in the multi-species swards frequently had values much closer to PRG/0N than their relative WSC contents when grown in monoculture and supplied with 360 kg N/ha per year would indicate. This again suggests that aspects of the relative nutritive value of some species differ when they are grown in monoculture compared to when grown in multi-species swards.

The relatively low herbage CP content for PRG/0N, particularly at Cuts 1 and 2, is similar to the findings under comparable conditions by Keating & O’Kiely (2000b), Conaghan et al. (2012) and Clavin et al. (2017). The marked increase in values consistently recorded for PRG/RC, Mix 1/0N and Mix 2/0N, and the similarity of the values for these treatments within cuts, are likely due mainly to the direct effects of the high CP contents of both legumes as well as to an indirect effect of N fixed by the legumes increasing the CP content of the companion species. Thus, for example, the CP values for timothy within the multi-species swards (Table 9) are similar to those of TIM/360N and clearly greater than those of PRG/0N. It seems reasonable to assume that the CP content of both herbs will also have been enhanced by fixed N provided by the legumes, with particularly high values occurring in their primary growths. It is noteworthy that the CP content of RC within the multi-species swards was generally greater than when it was grown in monoculture. These examples are further evidence that the chemical composition of species grown in monoculture can differ from when grown with other species and that predicting the nutritive value of multi-species swards based on the proportion of each species in the observed mixture and the composition of each one when grown in monoculture can be problematic. The aforementioned findings are consistent with Sanderson (2010), Brink et al. (2015) and Ergon et al. (2017) who have shown that inclusion of forage legumes in multi-species swards with grasses and sometimes also herbs will elevate herbage CP content, occasionally in an apparently synergistic way.

Perennial ryegrass versus multi-species mixtures at increasing rates of inorganic N (PRG, Mix 1 and Mix 2 at 0, 120, 240 and 360 kg N/ha per year)

Although the application of inorganic N to perennial ryegrass swards has been reported to have little effect on herbage DMD (Whitehead, 1995), both Cameron (1967) and Conaghan et al. (2012) have reported declines in DMD in response to inorganic N, and the results of this study agree with the latter findings. The exact cause of this decline is not clear, although it may be associated with factors such as an accumulation of decaying herbage of reduced DMD or an increase in the proportion of stem present as DM yields increased in response to inorganic N (Wilman, 2004), and to the decline in WSC content in response to inorganic N (Conaghan et al., 2012; Clavin et al., 2017).

An important side-effect of applying inorganic N to grass–clover swards or to multi-species swards such as Mix 1 and Mix 2 is the alteration in their botanical composition, most commonly by reducing legume and increasing grass proportions (Hopkins, 1986; Harris & Clark, 1996; Moloney et al., 2020). As sward botanical composition strongly influences herbage chemical composition (Michaud et al., 2012), the DMD response of the multi-species swards to inorganic N is at least partially explained by changes in sward botanical composition. Results from the current study, however, show little or no DMD decline for any cut of either multi-species sward in response to inorganic N, except for Cut 1 of Mix 1 where there was a 25-g/kg decline when 360 kg N/ha was applied annually. This general outcome occurred despite inorganic N application having been shown to reduce DMD in both perennial ryegrass (Conaghan et al., 2012) and timothy (Thorvaldsson & Andersson, 1986) and that the proportions of both these grasses similarly increased in both mixtures with inorganic N application (Moloney et al., 2020). The latter increases were at the expense of both legumes in Mix 1 and the legume and both herbs in Mix 2. This raises the possibility that within Mix 1 and Mix 2 the mean DMD of the grass functional group may have been similar to the mean values of the legume or the legume plus herb functional groups.

There was no evidence in this study that applying increasing rates of inorganic N to perennial ryegrass, Mix 1 or Mix 2 had a clear-cut or substantive impact on the rates of decline in the DMD during their primary growth. In contrast, the beneficial response of Cut 2 perennial ryegrass herbage DMD to delaying the primary growth harvest that was first shown by Gilliland et al. (1995) occurred in this study only when perennial ryegrass received the highest rate of inorganic N, which was a rate comparable to that used by Gilliland et al. (1995).

When considered at equivalent rates of inorganic N input some interactions of PRG, Mix 1 and Mix 2 with harvest schedule were evident, even if their magnitudes were sometimes relatively modest. Thus, at Cut 1 the slightly greater DMD for PRG than the multi-species swards on 12–13 May but its relatively lower value on 9–10 June suggest that this PRG would have a narrower timeframe than the multi-species swards in which to be harvested at optimal DMD. In contrast, at Cut 2, PRG had a superior DMD to the multi-species swards irrespective of the harvest schedule, but the DMD disadvantage for the multi-species swards at Cut 3 was associated mainly with the Early schedule for Mix 1 and with the Early and Middle schedules for Mix 2. Thus, for example, the Late harvest schedule might be a more appropriate strategy with Mix 2 in particular.

The general decline in the WSC content of perennial ryegrass in response to inorganic N application is similar to the findings of Keating & O’Kiely (2000b), Conaghan et al. (2012) and Clavin et al. (2017). However, compared to the aforementioned relationship, the responses for Mix 1 and Mix 2 were greatly reduced or absent. In general in this study, species from the grass functional group had greater WSC contents than species from the legume or herb functional groups (Tables 5 and 9) and the effects on sward WSC content from the increasing proportion of grasses in Mix 1 and Mix 2 as inorganic N application increased may have been counter-balanced by a corresponding decline in grass WSC content, and possibly also in the WSC content of some of the legumes or herbs.

The increase in perennial ryegrass CP content in response to inorganic N agrees with previous studies by Keating & O’Kiely (2000b), Conaghan et al. (2012) and Clavin et al. (2017). In contrast, the response for both Mix 1 and Mix 2 to the same increases in inorganic N application generally showed an initial decline followed by a partial or complete recovery in CP content. The initial decline was likely due to the concurrent reduction in legume and increase in grass proportions (Elgersma et al., 2000; Brink et al., 2015), while the subsequent increase in CP content probably reflects the increase in N concentration in grass and herb species associated with elevated inputs of inorganic N, as reported in the current study for perennial ryegrass and as described by Martin et al. (2017).

Conclusion

The relative nutritive values of perennial ryegrass, Italian ryegrass, timothy and RC grown in monoculture and in grass–legume binary mixtures suggest that the values for each binary mixture were determined mainly by the presence of RC. Thus, the nutritive value of such binary mixtures may be predicted from their monoculture nutritive values weighted for the relative proportions of each species present. In the case of Italian ryegrass, however, its relatively low DMD and CP content when managed in monoculture and subjected to similar harvest schedules as perennial ryegrass, timothy and RC suggest that it has a limited role in binary (or multi-species) mixtures as used in this study.

When managed without inorganic N application, the lower DMD for PRG/RC, Mix 1 and Mix 2 compared to PRG/0N, which was particularly evident for the two mid-season cuts, was counter-balanced by a corresponding increase in CP content. However, caution is required when interpreting DMD values for grasses versus legumes. Multi-species swards such as Mix 1 and Mix 2 may have a broader timeframe than perennial ryegrass in which to be harvested for first cut silage at optimal DMD. In a practical setting, however, the decision to harvest is also strongly influenced by factors such as herbage DM yield and weather conditions.

Although the herbage nutritive value in Mix 1 and Mix 2 was directly influenced by botanical composition, especially the contribution of their legume species, this alone does not explain all of the effects observed. Thus, for example, various species exhibited greater DMD, WSC or CP values when growing in multi-species swards compared to in monoculture. This phenomenon was in contrast to observations for binary mixtures. It is likely that the more complex growing conditions and interspecific interactions that occur in multi-species swards underpin these apparent differences. Consequently, predictions of the nutritive value of such multi-species swards based on the relative nutritive value of their component species in monoculture should be avoided.

The effects of inorganic N application to perennial ryegrass of reducing DMD and WSC content but increasing CP content were as expected. The responses recorded with the two multi-species swards studied differed from this, mainly due to the associated changes in botanical composition.

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Irish Journal of Agricultural and Food Research

Herbage nutritive value of binary- and multi-species swards relative to single-species swards in intensive silage systems

Abstract

Main article text

Introduction

Materials and methods

Field plots

Chemical analysis

Statistical analysis

Results

Perennial ryegrass, Italian ryegrass and timothy receiving inorganic N or grown with RC (PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC)

Perennial ryegrass versus binary- and multi-species mixtures at 0N (PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N)

Perennial ryegrass versus multi-species mixtures at increasing rates of inorganic N (PRG, Mix 1 and Mix 2 at 0, 120, 240 and 360 kg N/ha per year)

Discussion

Perennial ryegrass, Italian ryegrass and timothy receiving inorganic N or grown with RC (PRG/360N, IRG/360N, TIM/360N, PRG/RC, IRG/RC, TIM/RC and RC)

Perennial ryegrass versus binary- and multi-species mixtures at 0N (PRG/0N, PRG/RC, Mix 1/0N and Mix 2/0N)

Perennial ryegrass versus multi-species mixtures at increasing rates of inorganic N (PRG, Mix 1 and Mix 2 at 0, 120, 240 and 360 kg N/ha per year)

Conclusion

Acknowledgements

Declarations of interest

References

Appendices

Author and article information

Journal

Affiliations

Author notes

Article

History

Page count

Categories

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