Department of Natural Resources and Environment, Bendigo, Vic 3550. www.nre.vic.gov.au Email kieran.ransom@nre.vic.gov.au
Lucerne was sown at 1 and 3 kg/ha with subterranean clover at a site near Boort in north central Victoria to test the hypothesis that the dry matter production of lucerne is unaffected by seeding rate. Over 6 years, lucerne yields averaged 612 and 653 kg DM/ha per year for the 1 and 3 kg/ha seeding rates respectively, while the annual species component yielded on average 3112 and 3179 kg DM/ha per year, respectively. The 3 kg/ha lucerne produced significantly more dry matter in only the first 2 winter - spring periods. The data indicate little if any advantage from sowing lucerne at 3 kg/ha in this dryland environment.
Introduction
Lucerne is highly recommended for crop and livestock enterprises. In north central Victoria, the lucerne seeding rates used by farmers vary from 0.5 to 6 kg/ha, with an average of 2 kg/ha. Farmers using low (<2 kg/ha) seeding rates claim their lucerne yields are similar to, or better than those obtained with higher rates. This suggests that for lucerne at low plant densities, higher yields per plant compensate for the low densities. To test this hypothesis, lucerne was sown at two rates and growth per unit area measured regularly.
Method
A seeding rate experiment with lucerne was established at Fernihurst (143°50’E, 36°14’S), 15 km south of Boort in north central Victoria. The average annual rainfall forof the site is 396 mm, with an April-October average of 264 mm. The topsoil (0-10 cm) is a clay loam with a pHwater of 6.2 and an Olsen P of 4 mg/kg. The 40 ha paddock was subdivided into 3 equal sized sub-paddocks. In June 1985 the lucerne was sown with subterranean clover under a barley crop. One half of each sub-paddock was sown with 1 kg/ha, and the other half with 3 kg/ha of lucerne (Medicago sativa cv. CUF 101), both with subterranean clover (Trifolium subterraneum cv. Seaton Park and cv. Nungarin, each at 2 kg/ha). From August 1986 to August 1993, dry sheep rotationally grazed the 3 sub-paddocks at an average stocking rate of 4.5/ha. Pasture growth was measured at 6 weekly intervals using 6 pairs of sheep exclusion cages, with the cages from each pair positioned approximately 10 metres apart on the 1 kg/ha and 3 kg/ha lucerne blocks. There were 2 pairs of cages in each sub-paddock. They were shifted approximately 3 metres at the beginning of each measurement period to avoid sheep exclusion effects on production. Lucerne yields were estimated by cutting lucerne to 1 cm height using 1.0 m2 quadrats at the beginning and end of each period. Lucerne density was measured in each quadrat. Yields of annual pasture were estimated in 0.25m2 quadrats in the same manner as the lucerne yields. Pasture production was aggregated for each calendar season. All data were analysed by analysis of variance using Genstat 4.2 (1).
Results and discussion
Six years after the lucerne was sown, lucerne plant densities had declined to about 10% of their first year densities for both seeding rates (Table 1).
Table 1. Average densities (plants/m2) of lucerne sown at 1 and 3 kg/ha in 1985 (** = P<0.01, *** = P<0.001).
Seeding Rate (kg/ha) |
1987 |
1988 |
1989 |
1990 |
1991 |
1992 |
1993 |
1 |
16.7 |
11.9 |
7.3 |
5.6 |
3.9 |
2.6 |
1.7 |
3 |
39.8 |
27.9 |
15.4 |
11.7 |
8.2 |
5.5 |
3.9 |
LSD(P=0.05) |
5.3 |
3.7 |
2.3 |
4.1 |
2.0 |
1.7 |
1.1 |
*** |
*** |
*** |
** |
*** |
** |
** |
Over this period, the 3 kg/ha lucerne yielded more (P<0.05) dry matter than the 1 kg/ha lucerne in only the winter - spring of the first two years (Table 2). When seasonal production was averaged over the 6 years, the 1 kg/ha lucerne produced 23% less dry matter than the 3 kg/ha lucerne in winter, with no differences at other times of the year (Table 2). However the average winter lucerne yields were so low (71 versus 92 kg/ha) that the additional 21 kg/ha of dry matter was unlikely to feed many extra stock. There were no significant differences between the two seeding rates in average spring production of lucerne, nor in the yields of the annual pasture component on any occasion.
Table 2. Effects of lucerne seeding rate on the yields (kg DM/ha) of the lucerne and annual pasture components at Fernihurst from 1986 to 1993. (ns = not significant, * = P<0.05, ** = P<0.01), and rainfall (mm), for 1987-1993.
Lucerne |
Annual pasture |
Rainfall | |||||||
Lucerne seeding rate (kg/ha) |
Lucerne seeding rate (kg/ha) |
(mm) | |||||||
Period |
1 |
3 |
LSD(P=0.05) |
1 |
3 |
LSD(P=0.05) |
|||
Summer-autumn 1986-87 |
407 |
476 |
128 |
ns |
57 |
57 |
126 | ||
Winter-spring 1987 |
297 |
358 |
48 |
* |
1196 |
1151 |
275 |
ns |
161 |
Summer-autumn 1987-88 |
634 |
521 |
143 |
* |
393 |
422 |
199 |
ns |
235 |
Winter-spring 1988 |
210 |
292 |
71 |
* |
2864 |
3241 |
1181 |
ns |
262 |
Summer-autumn 1988-89 |
741 |
709 |
178 |
ns |
1775 |
2003 |
545 |
ns |
278 |
Winter-spring 1989 |
164 |
99 |
164 |
ns |
3678 |
3836 |
1685 |
ns |
218 |
Summer-autumn 1989-90 |
372 |
365 |
293 |
ns |
41 |
83 |
42 |
ns |
140 |
Winter-spring 1990 |
220 |
294 |
130 |
ns |
2466 |
2310 |
657 |
ns |
162 |
Summer-autumn 1990-91 |
285 |
305 |
94 |
ns |
72 |
79 |
33 |
ns |
103 |
Winter-spring 1991 |
162 |
187 |
83 |
ns |
3519 |
3299 |
1415 |
ns |
243 |
Summer-autumn 1991-92 |
160 |
146 |
61 |
ns |
337 |
364 |
68 |
ns |
145 |
Winter-spring 1992 |
107 |
147 |
47 |
ns |
2570 |
2537 |
825 |
ns |
337 |
Summer-autumn 1992-93 |
331 |
445 |
225 |
ns |
104 |
139 |
64 |
ns |
211 |
Autumn pooled |
190 |
185 |
33 |
ns |
397 |
450 |
145 |
ns |
|
Winter pooled |
71 |
92 |
16 |
* |
1355 |
1374 |
194 |
ns |
|
Spring pooled |
122 |
137 |
31 |
ns |
1360 |
1355 |
269 |
ns |
|
Summer pooled |
229 |
239 |
40 |
ns |
0 |
0 |
|||
The average water-use efficiency of the pasture (lucerne plus annual species) for the April-November growing season was 16 kg DM/mm, after allowing 70 mm for evaporation (2). This is considerably less than the 24 kg/mm monitored by the author on 60 paddocks in north central Victoria from 1993 to 1997. In the experiment reported in this paper, it is likely that annual pasture growth was severely constrained by the low soil phosphorus (3). Also, lucerne growth at the site may have been constrained by a saline (22,000 mg/kg total soluble salts) watertable that fluctuated between 0.6 m depth in winter and 2 m depth in summer. Lucerne roots were observed no deeper than 1.1 m depth in a soil pit dug and left open for 4 years. These data indicate no advantage from seeding lucerne at 3 kg/ha in this dryland environment. This result is similar to one from Condobolin in central west NSW where the cumulative production of lucerne over 20 months was 11.9, 9.1 and 9.6 t/ha for seeding rates of 1, 2 and 4 kg/ha, respectively (L. Roesner personal communication). These results suggest that the roots of lucerne sown at 1 kg/ha can just as effectively explore the soil volume and utilise all of the available soil water as the roots of lucerne sown at higher rates.
References
(1) Genstat 4.2. 2000. Lawes Agricultural Trust, Rothamsted Experimental Station.
(2) French, R.J. 1991. In: Dryland farming, a systems approach. Ed. V. Squires and P. Tow, p222-238. Sydney University Press, Sydney.
(3) Jones, H.R., Maling, I.R.and Curnow, B.C. 1984. Aust. J. Exp. Agric. Anim. Husb., 24: 579-585.



