| Rural Industries Research & Development Corporation |
The main remedy in Australia, the fumigant methyl bromide, has been identified as an ozone depleting chemical and many of its uses are being phased out in accordance with the Montreal Protocol, an international agreement to which Australia is a signatory.
Alternative fumigant treatments need to be found. This report documents research on the development of techniques to replace methyl bromide.
2. The requirement for extended exposure periods (15û16 hours) for effective fumigation.
3. The requirement that treatments are undertaken at or above 15?C.
4. While the technique killed several important insect pest species of cut flowers, other insects associated with cut flowers may have a different tolerance for phosphine.
5. There is a need for other, supporting,
pre-harvest pest control measures.
Phosphine treatment also provides an alternative
to insecticidal dips which may leave undesirable residues on flowers. Capital
costs of establishing a fumigation facility are greater than for dipping,
but this is compensated by reduced labour costs as dipping is more worker
intensive.
Various forms of phosphine were trialled, with Phosfume« proving the most successful. Phosfume« is a cylinder gas phosphine formulation (2% phosphine with carbon dioxide as a carrier gas).
The fumigations were completed within a working day which mirrors the time required for methyl bromide treatments. A range of flowers also was screened with methyl bromide for comparison.
Fumigant concentrations used were based, where possible, on established quarantine dosages. They ranged from 0.1 mg Lû1 for phosphine to 32 mgLû1 for methyl bromide and exposure times ranged from half-an-hour for hydrogen cyanide to six hours for phosphine.
In some of the tests, flowers from various areas of Australia were air freighted in cartons to Canberra. On arrival, their stems were trimmed, placed in water and stored in a cool room at 4?C. Bunches of flowers were taken out of water and placed in 63.5 litre metal drums at 20?C for treatment with various fumigants.
Control bunches of flowers were placed in drums but not fumigated.
Following fumigation, the flower stems were trimmed, placed in fresh water and aired under a fume hood for one hour. They were then returned to the cool room. When all treatments had been completed, the flowers were repacked into cartons and air freighted back to the growers for assessment. Large-scale tests followed
After these initial laboratory experiments identified phosphine as the most suitable chemical assessed, large-scale fumigations were undertaken.
These involved a 27m3 fumigation chamber (see Fig.1) fitted out for use of 'cylinder gas' aerosols: Pestigas (0.4% pyrethrum and 2% piperonyl butoxide with carbon dioxide as a carrier gas) and Insectigas (5% dichlorvos with carbon dioxide as a carrier gas), which are registered for disinfestation of cut flowers.
Phosfume was substituted for the Insectigas«. With 16 hours exposure at a temperature of 15?C or above, the 1 gmû3 concentration of phosphine controlled several problem pests.
Additionally it was found that if Pestigas« was applied to give a concentration of 0.02 gmû3 of pyrethrum, followed 10 minutes later by Phosfume« applied to give a concentration of 0.42 gmû3 of phosphine, a similar or better result for control particularly of eggs of the species tested was obtained. (See Table 1)
Table 1.
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| 20.5 (19.6-22.8) |
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| 20.0 |
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| 21.0 (16.3-23.1) |
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| 20.0 |
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| 21.9 (19.5-26.7) |
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| 20.0 |
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| 18.1 (17.5-18.9) |
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| 20.0 |
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| 18.2 (16.1-22.2) |
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| 20.0 |
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| S. aff = Severely affected. | |||||||||||||||||||
Observations of the effects of Pestigas« and Phosfume treatments on a range of flowers are summarised in Table 2.
Table2
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| Andresonia simplex | Spiked Andresonia |
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| Anigozanthos pulcherrimus | Kangaroo Paw |
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| Banksia baxteri | Bird's Nest Banksia |
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| Banksia coccinea | Scarlet Banksia |
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| Banksia prionotes | Acorn Banksia |
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| Banksia speciosa | Showy Banksia |
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| Brunia albiflora | Albiflora |
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| Chamelaucium uninatum | Geraldton Waxflower |
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| Dryandra nobilis | Golden Dryandra |
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| Eucalyptus (foliage) | Eucalyptus |
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| Gerbera | Transvaal Daisy |
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| Gloriosa rothschildiana | Gloriosa Lily |
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| Lachnostachys verbascifolia | Lambstail |
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| Leucadendron discolor (male and female) | Discolor |
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| Leucadendron coniferum | Sablosum |
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| Leucadendron floridum | Floridum |
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| Leucadendron eucalyptifolium | Eucalyptifolium |
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| Leptospermum rotundifolium | Round Leaf Tea Tree |
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| Leucadendron | Safari Sunset |
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| Leucadendron salignum | Salignum |
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| Leucadendron | Silvan Red |
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| Leucospermum cordifolium | Sun Burst |
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| Ozothamnus diosmifolium | Rice Flower |
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| Protea cynaroides | King Protea |
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| Protea | Pink Ice |
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| Protea repens | Honey Protea |
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| Podocarpus drouynianus | Emu Grass |
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| Scholtzia laxiflora | Red Scholtzia |
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| Serruria florida | Blushing Bride |
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| Telopea speciosissima | Waratah |
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| Thryptomene calycina | Grampians Thryptomene |
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| Verticordia nitens | Yellow Morrison |
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| Some flowers tended to fall more readily 7days after fumigation than the untreated controls; these were waxflowers, tea tree, Scholtzia and Thryptomene. Browning of tips occurred on some Leucadendrons, particularly with young soft growth and the leaves of some Proteas turned brown more rapidly on fumigated as compared with unfumigated flowers. All control flowers were rated as good. | ||||
The Pestigas/Phosfume combination was found to be effective provided material was not closely packed such that only Phosfume could penetrate.
In field trials of the technique, it was found that fumigation chambers must meet the required standard of gas tightness when Phosfume is used.
In some fumigation situations, the trials
found the Pestigas/Phosfume« combination to be more effective in
controling certain insects. But because Pestigas is an aerosol, it will
not penetrate plant material which is closely packed in boxes. Consequently
only Phosfume« can be used effectively in such situations.
The flowers were successfully exported
to Japan, one of the most discerning markets for cut flowers.
Acknowledgments
This research was undertaken as an initiative
of RIRDC which supplied core funding.
Additional financial support and contributions
in kind were received from; Associated Flowers International, Ausflora
Pacific Pty. Ltd., Austbloom Pty. Ltd., BOC Gases, the Commonwealth Environment
Protection agency (now the Department of the Environment), the Flower Export
Council of Australia (FECA), G.W. & L.R. Winfield Enterprises Harris
Park Holdings, Longford Flowers, the Partners to the Stored Grain Research
Laboratory, Tesselaar Nominees and Van Wyk and Son Flower Supply.
The work of this project was also extended
by funding from the Horticultural Research and Development Corporation
(HRDC), the Australian Horticultural Exporters Association (AHEA) and the
Nursery Industry Association of Victoria for whom a separate report will
be presented.
This was a collaborative project between Agriculture Victoria, CSIRO and the WA Department of Agriculture