Although grasses of the short grass type are more suitable for grazed pastures than those of the tall grass type, there are not so many reports about dry matter production in the grazed pasture of the short grass type. The purposes of this study are to clarify (1) the seasonal change of dry matter production and (2) the effect of the heavy rate application of nitrogen on dry matter production and annual net production in the grazed pasture of Agrostis alba L. (redtop) as the short grass type. The grazing experiment was carried out in the Experiment Station on Highland Animal Production, Kitashitara, Aichi in 1979, 1980 and 1981. The weather data measured in this station are as follows (Fig.1). Annual mean air temperature, rainfall and mean solar radiation are 10.3℃, 2800mm and 3000kcal/m^2/day, respectively. The experimental pasture was divided into ten paddocks, and the area of each paddock was 0.3ha. In 1979 and 1980, the five paddocks (as the CN plot) were applied with the conventional rate of nitrogen, phosphorus and potassium (N: 290, P_2O_5: 230, K_2O: 280kg/ha/year), and the rest five paddocks (as the HN plot) were applied with the same rate except nitrogen (810kg/ha/year). Two herds of six steers were used for the grazing experiment. One of them grazed in the CN plot, the other did in the HN plot. In 1981, both plots were applied with the lower rate (N: 110, P_2O_5: 50, K_2O: 50kg/ha/year), and one herd of eight steers grazed both plots in turn. The rotations were six times in 1979 and 1980, and five times in 1981. Biomass of grasses and separated parts as leaf, stem, standing dead and underground were measured at the end of each grazing period in the rotation from May to October, and also in March, April and November. In each period in the rotation, six movable protect cages were used to protect from grazing by steers. Aboveground part was cut at the height of 3cm from ground with the 1m^2 quadrat both in and out of the cages. Only out of the cages, biomass of stubble (0-3cm) was sampled with the 1/16m^2 quadrat. Surface litter was sampled at the same place. After that, underground part was sampled to 15cm depth also at the same place. Results obtained were as follows. The seasonal change of total biomass (Fig.2) was mainly affected by that of underground rather than that of aboveground. The total biomass attained its maximum (1200g/m^2) in May in 1979, but in April in 1980. This value was nearly same to that of orchardgrass pastures (750-1370g/m^2). The seasonal change of above-ground living biomass (Fig.3) was affected by that of stem biomass (60-380g/m^2) rather than that of leaf biomass (30-170g/m^2). The seasonal change of underground biomass varied with years. Biomass of underground attained its maximum (about 800g/m^2) in July in 1979, but in April in 1980. The quantity of standing dead (Fig.4) was very low (25-50g/m^2) through the grazing period, though it was high in spring (200-250g/m^2) and in autumn (150-170g/m^2). Biomass of surface litter was 100-350g/m^2 (Fig.4). Biomass of underground in the HN plot was significantly higher (p<0.05) than those in the CN plot for the effect of the heavy rate application of nitrogen. Biomass of other parts in the HN plot was also higher than those in the CN plot, but the differences were not significant. Annual net production (Table 1) in the CN plot were 930g/m^2 in 1979, 960g/m^2 in 1980 and 870g/m^2 in 1981, respectively. Those in the HN plot were 1140g/m^2 in 1979, 1000g/m^2 in 1980 and 1290g/m^2 in 1981, respectively. It was mainly affected by the amount of intake by steers and net production of underground. Annual net production in the grazed redtop pasture was higher than that in the Zoysia type pasture (500g/m^2), but lower than that in the tall fescue (1650g/m^2) or the orchardgrass pastures (1200-1450g/m^2).
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