The effect of pasture feed on offer in spring on pest populations and pasture production

Livestock Library/Manakin Repository

Show simple item record

dc.contributor Grimm, M
dc.contributor Hyder, M
dc.contributor Doyle, P
dc.contributor Michael, P
dc.date.accessioned 2012-01-25T12:31:32Z
dc.date.available 2012-01-25T12:31:32Z
dc.date.issued 1994
dc.identifier.citation Proc. Aust. Soc. Anim. Prod. (1994) 20: 233-236
dc.identifier.uri http://livestocklibrary.com.au/handle/1234/8483
dc.description.abstract Proc. Aust. Soc. Anim. Prod. 1994 Vol. 20 THE EFFECT OF PASTURE FEED ON OFFER IN SPRING ON PEST POPULATIONS AND PASTURE PRODUCTION M. GRIMMA, M. HYDERB, P. DOYLEB, and P. MICHAEL C AEntomology Branch, Dept of Agriculture, Albany, W.A. 6330 *Sheep Industries Branch, Dept of Agriculture, Albany, W.A. 6330 CEntomology Branch, Dept of Agriculture, South Perth, W.A. 6151 SUMMARY Grazing annual pastures to defined levels of feed on offer (FOO) through spring significantly reduced redlegged earthmite (RLEM, Halotydeus destructor Tucker) numbers compared to set stocked plots. Effects carried over to the break of season in the following year, presumably because fewer aestivating eggs were produced in the previous spring. Insecticides controlled RLEM for all grazing treatments, with significant increases in dry matter production only recorded for set stocked treatments. Spraying did not change 'sheep grazing days' where pastures were maintained at FOO levels of 1400 and 2800 kg DM/ha through spring. These results indicate that grazing management offers a tool for managing RLEM on farms, with potential decreases in use of insecticides. Keywords: redle gged earthmites, pests, grazing management. INTRODUCTION Redlegged earthmite (RLEM, Halotydeus destructor Tucker) and lucerne flea (LF, Sminthurus viridis Linnaeus) have been recognized as pests of subterranean clover (SC, Trifolium subterraneum L.) since the 1930' (Norris 1944). Bluegreen aphid (BGA, Acythosiphon kondoi Shinji) has colonised the s southern agricultural areas of Australia since 1979 and has become a major pest of pasture legumes including SC (Franzmann et al. 1979; Brennan and Grimm 1992). Losses in pasture production caused by these pests have been estimated at $238 million annually (Sloane et al. 1988). Most of the evidence for losses in dry matter (DM) production is from experiments where grazing animals were excluded from plots, and pests were controlled with insecticides. Wallace and Mahon (1963) concluded that heavy infestations of RLEM and LF cause significant losses in DM production, especially in spring, but that the value in lost animal production was questionable because many pastures are under-grazed at this time. We are not aware of published data that examines relationships between grazing practices and the population dynamics of RLEM, LF or BGA in annual SC based pastures. Grazing intensity has been shown to affect other pasture pests (Roberts and Morton 1985) and invertebrate fauna of grasslands (Hutchinson and King 1980). This paper presents results from the first year of an experiment investigating relationships between RLEM populations, pastures grazed to defined levels of feed on offer (FOO), pasture production and numbers of sheep carried through the spring. MATERIALS AND METHODS The experiment commenced in 1992 on the Manurup Annexe of Mount Barker Research Station (34'34' 117' ' S, 31 E). The climate is Mediterranean, average rainfall 620 mm, with 75% of rain falling between May and November. Pastures consisted of SC (predominantly cv. Trikkalla and cv. Esperance) with volunteer grasses (Lolium rigidum Gaudin, Hordeum leporinum Link, Vulpia spp., Bromus spp., Poa annua L.) and capeweed (Arctotheca calendula L. (Levyns)). The soils are forest sandy gravelly loams over clay. A maintenance dressing of 90 kg/ha superphosphate (9.1% P, 10% S, 24% Ca) was applied in 1992. The plots had been used for 3 years in supplementary feeding experiments and were stocked with 10 adult or 12 weaner sheep/ha over summer-autumn until 19 June 1992. All plots were destocked from 19 June to 24 July 1992. Treatments were applied in 3 blocks and consisted of 3 grazing practices, with and without pest 0 control (total of 18 plots). Grazin, treatments were FOO maintained at 1400 kg DM/ha or 2800 kg DM/ha in spring (0.5 ha plots), and set stocking at the district average of 8 wethers/ha through spring (1 ha plots). Pests were either not controlled or insecticides applied to remove RLEM, LF and BGA. Within blocks, pest treatment plots were grouped together, with grazing treatments completely randomised over the plus and minus pest plots. The FOO on each plot was assessed weekly from 14 July 1992 using the visual appraisal and calibration methods described by Thompson et aZ. (1994). On the basis of FOO measurements and estimates of weekly growth rates, non-experimental sheep were added or removed from plots to maintain 233 Proc. Amt. Sot. Anim. Prod. 1994 Vol. 20 FOO at target values of 1400 and 2800 kg DM/ha through spring. Once pastures stopped growing at the end of spring, plots were set stocked at 8 sheep/ha through summer, autumn and winter. Differential grazing treatments were not applied in autumn or winter of 1993 because no pastures had grown to 1400 kg DM/ha during this period. Pasture growth rates were measured using exclosure cages shifted every 3-4 weeks, and total DM production calculated for the period between 4 August and 3 December. Between 24 July and 5 August 1992, l-year-old non-experimental wethers grazed set stocked plots at 8 sheep/ha and 1400 and 2800 kg DM/ha plots at differential rates depending on the FOO present. On 5 August, l-year-old merino wethers (experimental sheep n = 8/plot) which had been stratified on a liveweight (LW) basis were randomly allocated to plots. Sheep of similar age were used to maintain target FOO levels. The numbers of sheep grazing each plot at any time were recorded and 'sheep Orazing days' between 24 July and 19 November were calculated. Experimental sheep were removed gorn all treatments when pastures were thought to have stopped growing on 19 November, after which non-experimental sheep grazed each plot at 8 wethers/ha until spring 1993. New weaners replaced the 1992 animals at shearing in March 1993. Dimethoate (Roger@ 400 g a.i./lE.C.) was applied at 100 mL/ha of product in 100 L/ha spray volume on 2 and 26 June 1992. Insecticide was re-applied on 10 and 24 July 1992, 10 November 1992 and 8 June 1993 using dimethoate (Roxion @ 400 g a.i./L) at a rate of 300 mL/ha product in 100 L/ha spray volume. A tractor mounted spray boom fitted with flat fan nozzles was used each time. Insects and mites were collected from pasture into vials containing 70% ethanol using a suction machine based on the design of Wallace (1972). An area of 227 cm2 (17 cm diameter) was sampled at each placement of the machine. Samples were taken randomly while walking a 'W' shaped transect across each plot, and were spaced to adequately cover the plot area. Samples were taken on 22 September 1992 (n = 30 samples/plot), 6 November 1992, (n = 25 samples/plot), 7 December 1992 (n = 50 samples/plot) and 26 May 1993 and 14 June 1993 (n = 20 samples/plot). Bulked samples from each plot were counted under a stereo microscope. Analysis of variance of a block design using plot means was used to test for significance of differences between treatments. Table 1. Effects of grazing treatment (feed on offer, kg DM/ha) and insecticide (+ with mites; - sprayed) on numbers of redlegged earthmite (RLEM, number/m2) for 5 dates of sampling RESULTS Insecticide applications reduced (P c 0.05 or 0.001) RLEM numbers at all dates except 26 May 1993 (Table 1). G razing to 1400 or 2800 kg DM/ha decreased (P < 0.05 or 0.01) RLEM numbers on 22 September and 6 November 1992 and 14 June 1993 compared to set stocking. There were no significant differences due to grazing treatments on 7 December 1992 and 26 May 1993. On all dates where there were significant effects due to both insecticide and grazing treatments, the insecticide x grazing treatment interaction was significant (P < 0.05 or 0.001). There were no significant effects of blocks on RLEM populations. In 1992, FOO on set stocked plots changed (P < 0.001) with time (Figure l), and while the only significant (P c 0.05) effect of insects was on 23 November, the insect x time interaction was significant (P < 0.001). This indicates that late in spring FOO tended to be less in unsprayed set stocked plots (Figure 1). Weekly adjustments of sheep numbers to maintain FOO at 1400 or 2800 kg DM/ha precluded any differences in FOO due to insects,. 234 Proc. Aust. Sot. Anim. Prod. 1994 Vol. 20 The total DM produced in sprin g was affected by grazing treatment (P c 0.001) and by insects (P c 0.05) (Table 2), and the interaction of grazing treatment x insects was not significant. There were significant differences (P c 0.01) between grazing days for the 1400 and 2800 kg DM/ha (Table 2) but the effects of insects and the interaction between grazing treatment and insects were not significant. DISCUSSION Grazing pastures to 1400 and 2800 kg DM/ha in spring significantly reduced RLEM populations over the grazing period, compared to set stocked plots (Table 1). The lack of a significant difference for the December 1992 count coincides with senescence and death of pastures, and the decline of mites before summer. The RLEM populations in the following autumn showed that the spring grazing effects were carried over into the following year. The non-significant differences for the first count in May 1993 coincided with the onset of mite hatching. By 14 June 1993, hatching was complete, and the effects of grazing practices in the previous spring on RLEM populations were again significant. The mechanism 0 by which increased grazing pressure reduced RLEM populations is not clear, but may be due to factors such as incidental predation of mites and eggs by sheep, disturbance of mite feeding, or habitat modification leading to desiccation of mites. Insecticide sprays reduced RLEM densities to very low numbers, with repeated applications needed to control mites migrating into plots from adjacent untreated areas and to control other pests. Either grazing to low FOO or insecticide treatment reduced mite populations to levels at which they caused no significant loss in plant growth, and therefore no differences in sheep grazing days. Mite populations increased to damaging levels under set stocking where grazing pressure was 10~ and FOO was high (Figure 1). This supports the conclusion of Wallace and Mahon (1963) that high numbers of RLEM can cause significant dry matter losses in spring when pastures are undergrazed. We conclude that grazing to defined levels of FOO in spring can control RLEM and reduce the risk 235 Proc. Aust. Sot. Anim. Prod. 1994 Vol. 20 Table 2. Effects of grazing treatment (feed on offer, kg DM/ha) and insects on pasture production in spring (PP, kg DM/ha) and on grazing days (GD) of pasture dry matter losses. The same effect may occur under set stocking in seasons where growing conditions or higher set stocking rates limit FOO accumulation. We cannot say from our data whether the effects on mite populations are due to grazing per se, or to the absolute amount of FOO. The results imply that to adequately interpret RLEM population changes in field studies, it may be necessary to define pasture conditions in terms of FOO, plant growth rate and plant consumption rate. The results further indicate prospects for use of grazing management on farms to manage RLEM' and reduce the s use of insecticides. However, grazing to low FOO during flowering and seed set will reduce legume and grass seed production (Thompson A.N. unpublished data), indicating that such practices may not be used year-in year-out on the same paddock. ACKNOWLEDGMENTS We thank Mr D. Pfeiffer, MS H. Mitchell, MS M. Gre gg, M S P. Coombe and staff of Mt. Barker Research Station for technical assistance in the field and laboratory. The work was partially supported by a grant from the Meat Research Corporation. REFERENCES BRENNAN, R.F. and GRIMM, M. (1992). Aust. J. Exp. Agric. 32: 39-47. FRANZMANN, B.A., SCATTINI, W.F., RYNNE, K.P. and JOHNSON, B. (1979). Amt. J. Exp. Anim. Husb. 19: 59-63. HUTCHINSON, K.J. and KING, K.L. (1980). J. Appl. Ecol. 17: 369-87. NORRIS, K.R. (1944). Council for Scientific and Industrial Research, Australia, Bulletin No. 183. ROBERTS, R.J. and MORTON, R. (1985). J. Appl. Ecol. 22: 863-74. SLOANE, COOK and KING PTY. LTD. (1988). Report to the Australian Wool Corporation, Melbourne, p. 205. THOMPSON, A.T., DOYLE, P.T. and GRIMM, M. (1994). Aust. J. Agric. Res. 45: 367-89. WALLACE, M.M.H. (1972). J. AUG. Ent. Sot. 11: 261-3. WALLACE, M.M.H. and MAHON, J.A. (1963). Amt. J. Exp. Agric. Anim. Hub. 3: 39-50. 236
dc.publisher ASAP
dc.source.uri http://www.asap.asn.au/livestocklibrary/1994/Grimm94.PDF
dc.subject Red-legged earthmites
dc.subject Pest control
dc.subject Grazing management
dc.subject set stocking rate
dc.subject insect populations
dc.title The effect of pasture feed on offer in spring on pest populations and pasture production
dc.type Research
dc.identifier.volume 20
dc.identifier.page 233-236


Files in this item

This item appears in the following Collection(s)

Show simple item record

Search Livestock Library


Advanced Search

Browse

My Account