Phosphorus transfer in runoff following application of fertilizer, manure, and sewage sludge.

Phosphorus (P) transfer in surface runoff from field plots receiving either no P, triplesuperphoshate (TSP), liquid cattle manure (LCS), liquid anaerobically digested sludge (LDS), or dewatered sludge cake (DSC) was compared over a 2-yr period. Dissolved inorganic P concentrations in runoff increased from 0.1 to 0.2 mg L(-1) on control and sludge-treated plots to 3.8 and 6.5 mg L(-1) following application of LCS and TSP, respectively, to a cereal crop in spring. When incorporated into the soil in autumn, runoff dissolved P concentrations were typically < 0.5 mg L(-1) across all plots, and particulate P remained the dominant P form. When surface-applied in autumn to a consolidated seedbed, direct loss of LCS and LDS increased both runoff volume and P transfers, but release of dissolved P occurred only from LCS. The largest P concentrations (>70 mg L(-1)) were recorded following TSP application without any increase in runoff volume, while application of bulky DSC significantly reduced total P transfers by 70% compared with the control due to a reduced runoff volume. Treatment effects in each monitoring period were most pronounced in the first runoff event. Differences in the release of P from the different P sources were related to the amounts of P extracted by either water or sodium bicarbonate in the order TSP > LCS > LDS > DSC. The results suggest there is a lower risk of P transfer in land runoff following application of sludge compared with other agricultural P amendments at similar P rates.

Lactic acid-stabilised albumin for microsphere formulation and biomedical coatings.

Microspheres of ovalbumin (OVA) ranging from 1 to 15 microm were prepared by emulsifying an aqueous solution of albumin in soya oil at room temperature then raising the temperature to 45 degrees C for 30 min, prior to harvesting of the microspheres. Production of OVA nanospheres with size less than 500 nm was achieved by desolvation from aqueous albumin solutions using acetone. In both cases, lactic acid was added to the starting albumin solution to stabilise the resulting particles. Utilisation of an endogenous substance avoids the use of chemical crosslinking agents such as glutaraldehyde and associated toxicological concerns. Protein coating of knitted Dacron vascular grafts was performed by impregnation of the textile structure with lactic acid-stabilised ovalbumin nanospheres thereby providing a surface potentially resistant to blood platelet adhesion but conducive to endothelialisation. Protein release testing carried out in PBS at 37 degrees C revealed that approximately 60% of the original albumin coating was retained by the Dacron graft material after 4 days and remained at this level for upto 4 weeks. Apart from the formulation of albumin microspheres for drug delivery, diagnostic applications and coating of biomedical textiles, the process of albumin stabilisation using lactic acid may be usefully applied to improve protein immobilisation on a wide range of biomaterial surfaces.

Surveillance of stored grain from the 1997 harvest in the United Kingdom for ochratoxin A.

This survey examined 306 samples of farm-stored wheat, barley and oats as received at, or tested by, central grain depots in the UK. Samples were taken from lorries or from stored grain using the existing in-house procedures used for quality checking and examined for ochratoxin A using a fully validated analytical HPLC method with a detection limit of 0.1 microgram/kg. Ochratoxin A was detected in 21% of the samples examined, with barley more frequently contaminated than wheat. Mean concentrations of ochratoxin A found for all samples were 0.69 microgram/kg in barley, 0.29 microgram/kg in wheat and 0.15 microgram/kg in oats. The highest concentration found was 17.8 micrograms/kg in a barley feed although concentrations of 81 and 30 micrograms/kg were found in 'reject-grade' wheat samples whose results were excluded from the main survey. In summary, 2.7 and 0.3% of samples exceeded concentrations of 5 and 10 micrograms/kg respectively. There appeared to be significant relationships between ochratoxin A concentrations and moisture content, storage time and geographical area. Although conditions at harvest in 1997 were quite variable countrywide and often wet, results were similar to those found in earlier surveys carried out in the UK.

Vapour of the free acid of the herbicide 2,4-D is toxic to tomato and lettuce plants.

Tomato and lettuce plants were exposed to vapour of the free acid of [14C-phenyl] 2,4-D at concentrations in the range 1-600 pg litre(-1) for periods of 6, 24 or 72 h. The rate of uptake of radiolabel by tomato was about twice that by lettuce at the same vapour concentration. Uptake rates were linearly related to external vapour concentration. The relationship between uptake and vapour concentration of 2,4-D for the two species was similar to published values for the butyl and iso-octyl esters. The distribution of herbicide residue in the plant immediately after exposure indicated that the apical leaves of lettuce are particularly active in assimilating vapour, whereas for tomato, leaf position had no influence. Forty days after exposure, both species showed symptoms of toxicity and reduction in shoot dry weight typical of similar doses of 2,4-D esters. It is concluded that the vapour of 2,4-D represents a potential hazard to susceptible plants, and that further work is needed to determine the conditions likely to lead to the production of vapour of the free acids of phenoxyalkanoic herbicides following spraying.