Every year, a substantial quantity of pesticides is introduced into the environment. The continued use of pesticides is necessary in order to meet the demands of the growing human population. However, only a small fraction of the applied pesticide reaches the target organisms, and there is a large potential for adverse effects on non-target organisms. Organophosphorus (OP) insecticides have largely replaced organochlorine compounds and are now one of the main groups of pesticides used in agriculture worldwide. The work presented in this thesis aimed to assess the impact of OP insecticides on the soil microbial community. The soil microbial community has many important functions in the soil, including carbon and nitrogen
transformations, maintenance of soil structural stability and the degradation of organic pollutants. Any adverse effects of OP insecticides on the soil microbial community could lead to a decrease in soil quality and a loss of agricultural sustainability.
The toxicity of OP insecticides was initially assessed using the lux-marked biosensors E. coli HB101 pUCD607 and P. fluorescens 10586r pl)CD607. The production of light is linked to metabolic activity in these genetically modified bacteria. Therefore, a toxic effect is observed as a decrease in light output. The biosensors were used to test OP insecticide toxicity in aqueous solution and in soil pore water. The effect of OP insecticides on soil microbial processes (respiration and nitrification) and the soil microbial community (viable counts and fatty acid analysis of whole soil extract) was investigated. Three soils (Insch, Countesswells and Boyndie) were used to determine the influence of soil type on the response of the microbial community to OP insecticides. These soils had contrasting soil texture, organic matter content and pH values, and were representative of many agricultural soils across the UK. The relative impact of a formulated insecticide (biomalathion)
and the corresponding active ingredient (malathion) was also investigated.
The lux-biosensors successfully reported on the toxicity of OP insecticides in aqueous bioassays. P. fluorescens was the most sensitive biosensor and biomalathion was the most toxic of the OP insecticides tested. When spiked soil pore water was used, the EC50 value both increased and decreased relative to the
aqueous bioassay, depending on soil type.
OP insecticides generally had stimulatory effects on soil microbial processes. The greatest increase in soil respiration rate was observed with biomalathion application. The effect of OP insecticides on potential nitrification rate was more complex, with stimulation and inhibition being reported for Insch and Countesswelis soil, respectively. The lux-biosensors detected toxicity in the OP spiked perfusate where no OP was detectable by GC-FID analysis. However, it did not prove possible to predict effects on soil microbial processes on the basis of lux-biosensor response. This is partly due to the difficulties in interpreting the results of the microbial process tests. For example, it is not clear whether a stimulatory effect should be classed as a toxic impact.
Plate counts of OP spiked soil showed an increase in the number of both total heterotrophic bacteria and Pseudomonas. However, fatty acid analysis of whole soil extracts failed to detect any effect of OP insecticide treatment on the soil microbial community. This may be because the OP insecticides are having a selective effect on the culturable fraction of the soil microbial community.
In this study, traditional methods for investigating pesticide effects on non-target soil microorganisms (plate counts, soil respiration, potential nitrification rate) were used in conjunction with more modern techniques (fatty acid analysis and lux-biosensors). These methods are complementary as they examine the impact of OP insecticide treatment on different levels of organisation of the soil microbial community (single species, whole community, process level). At present, it is not possible to adequately assess whether changes in the soil microbial community will have an effect on soil quality, as baseline values for a ‘healthy’ soil have not been
established. In this study, OP insecticides were shown to have a toxic effect towards bacteria. OP insecticide treatment also resulted in changes in soil processes and the soil bacterial populations, as determined by plate counts. Therefore, despite the lack of effect of OP insecticides on the soil fatty acid profile, there is evidence that OP insecticides can alter the soil microbial community.
The work presented in this thesis attempted to assess the impact of an agrochemical on the soil microbial community using an array of techniques. Both the traditional and modern techniques provided useful information about the effect of OP insecticides on the soil microbial community. Changes due to insecticide treatment were evident. However, further research is needed to assess whether these changes will have a long term impact on soil quality and agricultural sustainability.