Scaling of ‘landscapes’ in landscape ecology,or, landscape ecology from a beetle's perspective

Research performed on microlandscapes embodies the essence of landscape ecology by focusing on the ecological consequences of the mosaic structure of different landscape elements. As an illustration, observations and simulations were used to test whether the fractal structure of grassland microlandscapes affected the movement patterns of tenebrionid beeetles in natural environments. The significant tendency of beetles to avoid 1 m² cells with fractal dimensions of 1.85 to 1.89 (indicating the area-filling tendency of bare ground) demonstrated the role of landscape structure as a modifier of beetle movements or diffusion in heterogeneous landscapes. Experiments in microlandscapes may accelerate the development of quantitative conceptual frameworks applicable to landscapes at all scales.     

The economics of systems research

There are three broad aspects of Systems Research worthy of particular consideration by professional personnel earning their keep within or about the agricultural research system. I will discuss these three aspects seriatim. The first is the conjecture that the systems approach constitutes a technological change in our mode of thinking about the world of such magnitude as to imply that we are now moving from one sociotechnical age to another. The second aspect, a corollary of the first, is the use of the systems approach as a framework for the selection of research programmes. The third, which also follows from the first, is the efficiency of conducting research on a systems basis. Many would think of this last aspect of efficiency as constituting ‘the economics of systems research’, but I believe the systems approach, via the first two aspects I have mentioned, has far wider implications of economic import for agricultural research.     

Daminozide residues in sweet cherries,and their determination by colorimetric and gas-liquid chromatographic methods

Daminozide residues in fruit from sweet cherry trees were determined over a period of 4 years as part of an investigation into the effects of growth regulators. Analysis was by the usual colorimetric method. Additionally, for the 2 final years, a gas-liquid chromatographic method was developed to determine the 1,1- dimethylhydrazine produced by hydrolysis of daminozide residues and to confirm the results from the first method.     

Uptake of the systemic fungicide triadimefon by clover and its effect on symbiotic nitrogen fixation

Clover is frequently grown in rotation with cereals in order to increase soil nitrogen. The systemic fungicide triadimefon, widely used against cereal pathogens, is readily taken up from soil by clover and degraded to a single major metabolite. Plant weight and symbiotic nitrogen fixation by Rhizobium trijolii are affected only by concentrations of triadimefon in soil that are much in excess of those likely to be encountered in practice. Triadimefon residues are thus unlikely to affect nitrogen fixation by clover under field conditions.     

The effect of seven substituted urea herbicides on the soil microflora

Chloroxuron, diuron, fluometuron, metobromuron and monuron added to soil at 500 parts/million a.i. on a dry weight basis caused an initial stimulation of CO₂ production, followed by indications of inhibition. Nitrification was clearly inhibited, particularly by monuron and metobromuron. Metoxuron at 5 and 50 parts/million a.i. had no effect on CO₂ output and nitrification, but at 500 parts/million a.i. both were greatly reduced. Numbers of fungal propagules were temporarily lower at 50 parts/million a.i., and severely curtailed at 500 parts/million a.i. but total counts of bacterial propagules were greatly increased. Linuron had an inhibitory effect on CO₂ evolution at 500 parts/million a.i. but this varied in extent and duration; some reduction was also found at 50 parts/ million a.i. At 500 parts/million a.i. there was no effect on mineralisation of N but in soil supplemented with ammonium sulphate nitrification was reduced. Changes in microbial equilibrium occurred, but were less marked than with metoxuron. Cellulose decomposition was also reduced. Small amounts of 3,4dichloroaniline were found in linuron-treated soils, but microbial activities were not affected when 5 parts/million 3,4-dichloroaniline was added to the soil. However, at 140 parts/million microbial activities were affected adversely, but in a different pattern to that for linuron; nitrification was severely reduced, but numbers of fungal propagules were hardly affected, suggesting that the effects observed in linuron-treated soil were not due to this metabolite.