Abstract

Soil microbial and nematode populations, soil microbial community structure, and microbial and nematode functional diversity were studied in two fertiliser trials on perennial pasture at three sampling times. The N trial involved the application of 0, 200 and 400kg N ha−1 y−1 in the form of urea. The P trial involved the application of 0, 30, 50 and 100kg P ha−1 y−1 as superphosphate. The purpose of this study was to determine biological characteristics that may be used as indicators of soil quality as affected by fertiliser inputs.The N or P treatments had no effect on total bacteria, cellulolytic microbes, or the fluorescein diacetate hydrolysis. The fungus Fusarium culmorum was found only in the 200kg N treatment (P<0.01). Gliocladium roseum declined in isolation frequency with increasing N (P<0.05,) while other Gliocladium spp. increased (P<0.01).The microbial community structure, ecophysiological index (EP), and colony-development index (CD) were determined using: colony development rates in 1/10 tryptose soy agar (TSA), a Pseudomonas medium, and a nutrient poor medium. These parameters were not affected by the addition of the N or P fertilisers. In the N trial, the functional diversity of soil microbes, as determined by Shannon Diversity Index (H) and average well colour development (AWCD) (using Biolog gram negative microplates) was higher in the unfertilised than fertilised treatments. The values for H and AWCD were 4.2 and 0.78 in the unfertilised compared to 4.0 and 0.53 in fertilised treatment (P<0.01, 48h, mean for both N treatments), respectively. There were no significant differences in these values in the P trial.Populations of the plant feeding nematodes Pratylenchus and Paratylenchus were greater (P<0.05) whereas those of Meloidogyne were lower (P<0.001), in soils fertilsed with N than in unfertilised soils. The genera Aporcelaimus, Dorylaimellus, and Tylencholaimellus were found only in control plots and their loss paralleled faunal changes resulting from pasture improvement reported elsewhere. Nematode Maturity Index (MI) values were 1.78, 1.85, and 1.53 for the N fertiliser treatments (P<0.05) suggesting a reduction at 400kg N. The MI was not affected by the application of P (mean, 2.01), however, but all values in the P trial were greater than in the N trial. In the N and P trials an average of 29 and 35 nematode taxa were discriminated. The ratio of bacterial-feeding nematodes to bacterial-feeding plus fungal-feeding nematodes was similar across all treatments of the N (0.90–0.92) and P (0.84–0.90) trials, suggesting no relative change in the importance of bacterial- and fungal-mediated decomposition pathways in these soils as a result of fertiliser application.The finding that most microbiological characteristics did not respond to many years of fertiliser treatments suggests that the microbial community in the soils are similar and fertiliser amendments are insufficient to induce changes (either direct or indirect due to plant effects) in these communities. However, the consistent decrease in functional diversity of soil microflora and nematode populations with the application N, but not P, indicates that the N application can impact on community structure.

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