Mixing dispersants

Mixing dispersants

MT 220 gas chromatograph equipped with a NP 3 electron capture detector. The column used was of glass, 'U' shaped, 6' long x ¼" outer diameter. It was...

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MT 220 gas chromatograph equipped with a NP 3 electron capture detector. The column used was of glass, 'U' shaped, 6' long x ¼" outer diameter. It was packed with a 1 : 1 mixture consisting of 10% I3(2200 silicone oil and 157/o QF1 fluorosilicone coated on a support of chromsorb W AW/DMCS, 80-100 mesh. A small glass precolumn filled with quartz wool was used and was discarded after each set of analyses. The cohnm temperature was maintained at 215°C and the detector at 250°C. The carrier gas was htgh purity nitrogen; it was passed through a filter of Molecular Sieve 5A, 60-80 mesh at a flowrate of 100 ml/min.

Results A total of sixteen samples was analysed and the results obtained were as shown m Table 1. Although the results encompass only four species of marine animals, certain remarkable trends are evident. In both the snoek and rock lobster the DDT concentration m the ¢hgestive tract is several orders of magnitude higher than in the flesh. The same trend apphes to a lesser extent for dieldrin. High concentrations of pesticide residues were also found m the liver of the snook as opposed to the flesh. It is interesting to note that Shannon (1970) found the gross alpha-act~wty in the digestave gland of the rock lobster to be 14800 ± 2000 pc/kg (wet weight) in comparison with 150 ± 30 pc/kg m the tad meat. In the case of Risso's dolphin the concentrations of pesticide residues in the blubber and liver were at comparable levels. Not unexpectedly the level of total DDT is considerably higher than that of dieldrin m all samples analysed. Comparison of our results with figures obtained for slmdar species in other parts of the world is not always feasible. Values obtained by Jonson et al. (1969) for herring, a clupeold fish, could probably be used as

Mixing Dispersants Sir--The mixing energy to produce fine droplets of od m water has been g~ven as 1 W K

-----

A

7

where W K

--

nuxmg energy

A o/w

=

mterfaclal area

70/w

=

lnterfacial tension

o/w o/w

The effect of the addition of a surface active agent (dispersant) is to reduce the mterfacial tension by as much as a whole number of times. Nevertheless, to produce a reasonably stable mixture the dispersant must be applied so that it is available at all of the interface, and the mixing energy must be adequate and properly applied. This fact has been known for a long time and is frequently cited in the literature? When spills occur, dispersants are applied m the hope that wave action and/or the screws of the application vessels, will provide sufficient mixing energy,

a basis for comparison voth anchovy. Total DDT levels m herring ussues range from 0.093 to 2.3 ppm whde in anchovy the values for total DDT are 0 196 to 0 228 ppm for the whole fish. In samples collected from the north east coast of England, Robinson et al. (1967) found 0.64 ppm dieldrin m the blubber of common dolphin (Delphmus delphinus) and 0 04 ppm in the liver. Our values for Rasso's dolphin are 0.068 ppm and 0.048 ppm, respectively. The same authors reported 0.024 ppm dieldrin in the flesh of lobster (Homarus vulgarls) whle our values for the flesh of rock lobster are 0 004 to 0.012 ppm. The results of the analyses reported in this paper are few in number and relate to only four species. Worm is at present m progress which wall increase the number of analyses and extend the sampling to include a greater selection of South African manne species P J. AUCAMP* J L. HENRY G H. STANDER

D~vision of Sea F~sheries, Department of Industries, Beach Road, Sea Point, Cape Town, S. Africa. *Formerly of Department of Agricultural Techmcal Services, South Africa.

de Faubert Maunder, M J, Egan, H, Godley, E W, Hammond, E. W, Roburn, J. and Thomson, J (1964) Analyst, 89, 168 Jenzen, S, Johnels, A. G, Olsson, M. and Otterhnd, G (1969),

Nature, 224, 247.

Peterle, Tony J. (1969) Nature, 224, 620 Robinson, J, Rtehaxdson, A., Grabtree, A. N, Coulson, J. C and Ports, G. R (1967) Nature, 214, 1307 Shannon, L V. (1970) PhD. Thesis, Umvemty of Cape Town

and only too frequently the ¢hspersant is reported as valueless without due consideration being given to the possibtlxty that the nuxing energy was inadequate. Mtxing energy produced by the wind has been calculated ~ to give 6.82 kg m of energy per hour for every square metre vertically through the sea surface with a wind speed of 5 kts. A reahstic spray system has been calculated to give 1.696 kg m per nun for each square metre of sea surface when spraying at 5 kts. The same text gives the mixing energy of a 25 ft (8 2 m) launch as 62.5 kg m per m 2 of area swept, at the same speed; tins assumes that the energy of the propeller is uniformly distributed across the whole width covered by the launch, 10 ft (3 m), voth a 20 ft (6 1 m) spray boom each side, i.e 50 ft (15 3 m) at each pass, which is a dubious assumption. The nuxing energy given by the Warren Spring Laboratory system has been measured under working conchtions 3 The tests show that the 4 fl 6 m (1.57 m) board assembly, when towed at 4 kts, exercised a pull of 30 lb (13 6 kg). If it is assumed that the depth to which the board sinks at the rear is 9 in (0.228 m), then per m ~ of vertical 191

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