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Technical Report

Efficacy of Fumigation of Empty Ship Holds With
ECO2FUME,
the Horn Generator or MeBr With Recapture
Paul Fields1 and Sheila Jones2
1. Agriculture and Agri-Food
Canada, Cereal Research Centre, 195 Dafoe Rd., Winnipeg, MB, R3T 2M9,
Telephone: 204-983-1468, Email: pfields@em.agr.ca
2. Agriculture and Agri-Food Canada, Policy Branch, Environment Bureau, 930
Carling Ave., Ottawa, ON, K1A 0C5, Telephone: 613-759-7300, Email:
jonessh@em.agr.ca
Why Investigate Alternatives to Methyl Bromide for Ship Hold Fumigations?
The Montreal Protocol presently exempts the use of methyl bromide for
quarantine and pre-shipment purposes. The use in this sector is growing. This
exemption, however, was one of the main topics of discussion at the Meeting of
the Parties in Cairo in 1998, and again at the Open Ended Working Group meeting
in Geneva. The definitions for quarantine and pre-shipment are unclear, and
there is apparent abuse of this exemption. In particular, the pre-shipment
exemption is the most contentious.
Members of the Canadian Industry/Government Working Group on Methyl Bromide
Alternatives believe that an investigation into alternatives for ship hold
applications would demonstrate the effectiveness of potential alternatives that
are either currently registered or not registered for use in Canada, and their
associated costs. Furthermore, these techniques may be useful in other
situations where methyl bromide is used to control insect infestations.
Methods
The test was conducted on lake-going ship, the "Canadian Trader",
that has six holds, 5000 to 7000 m3 each. There were four
treatments: methyl bromide at approximately 16 000 ppm (21 oz/1000 ft3) with
recapture after one day (hold 1), phosphine at 500 ppm applied using the
ECO2FUME method (hold 4), phosphine at 1000 ppm applied using
the Horn Generator using magnesium phosphide (Magtoxin® Granules) (hold 6),
and an untreated control (hold 3). To recapture the methyl bromide, the air
from the ship hold was passed over a molecular sieve, a technique developed by
Cryo-Line Supplies Inc. ECO2FUME is 2% phosphine with 98%
carbon dioxide in pressurized cylinders, and is produced by Cytec Canada Inc.
The Horn Generator produces phosphine by mixing magnesium phosphide with water,
and is produced by Degesch America Inc.
Four insect species were used in the bioassay: rusty grain beetle
(Cryptolestes ferrugineus (Stephens)), rice weevil (Sitophilus oryzae
(L.)), red flour beetle (Tribolium castaneum (Herbst)), and the lesser
grain borer (Rhyzopertha dominica (Fabricus)). Twenty-five adults were
held in plastic vials with screen tops containing wheat for several days before
fumigation. Hence all vials contained both eggs and adults in the same vial.
Vials were taped to a rope, with 12 vials per species for each rope. Three
ropes were hung from the manhole access to the hold, and one rope was pulled
from each hold 32, 48 and 72 h after the beginning of the fumigation. For the
methyl bromide treatment there was only one rope, and it was pulled at the
completion of the methyl bromide fumigation, 32 h after the beginning of the
fumigation. Temperatures were measured using thermocouple wires taped to the
ship hold and the vials in each of the holds at the bottom, middle and top
levels.
After removing a rope from a hold, adults were sieved out of the wheat from
each vial, survival noted and the adults placed on clean wheat. After one week
the number of live and dead adults was assessed a second time to detect delayed
mortality or revival of insects that could have been counted as dead but were
in a fumigant-induced stupor. To assess the survival of the eggs, the wheat
that was held in the ship holds was placed at 30 °C for five weeks and the
number of emerged adults counted.
Results
Temperatures in the ship holds varied between a high of 33 °C to a low
of 15 °C during the three days of the test, with an average temperature
during the first day of fumigation of 23 °C. The target gas concentrations
were reached at all three levels after 9 h for methyl bromide, 1 h for
ECO2FUME 500 ppm phosphine application and 5.5 h for Horn
Generator at 1000 ppm phosphine. Some phosphine was detected in the untreated
hold at the bottom level, but it was never greater than 11 ppm.
After 32 h, none of the adult insects survived in any of the three
fumigation treatments. In the untreated hold there was not more than 2% adult
mortality for any of the species. After one week, none of the insects in the
fumigated holds had revived, and the mortality of insects taken from the
untreated hold was not more than 5% for all species, except lesser grain borer
which had an average mortality of 31±8% (mean±SEM). The emergence of
adults from infested grain in the untreated hold varied between insects (Table
1). Given the low emergence for rusty grain beetles from the untreated samples,
it was impossible to estimate the mortality due to fumigation. For the other
insects, there was less than 7% survival of eggs after 32 h in the fumigated
holds and less than, 1% survival after 48 h and no survival after 72 h (Table
1).
Discussion
All three of the methods tested in this trial have potential for reducing
methyl bromide emissions resulting from empty ship fumigations. These methods
could be scaled up for treating entire ocean-going vessels which have
capacities ranging from 30,000 to 100,000 m3. Larger recapture units
would have to be built. This may be addressed in part by reducing the volume
needed to fumigate, and hence the total amount of methyl bromide by inflating
balloons in the holds.
The temperatures during this trial were warm. Ships often need to be
fumigated in cooler weather. Phosphine efficacy is reduced more by low
temperatures then is methyl bromide efficacy. Higher phosphine concentrations
do increase mortality, however, higher concentrations cannot entirely
compensate for shorter durations, ie doubling the concentration will not half
the time needed for control. Ships are heated for painting, and this technique
could be used to preheat ships before a phosphine fumigation, and this may
increase the effectiveness of the fumigation.
Another solution to infested empty ships would be to treat the grain as it
is loaded into ships with a residual insecticide such as malathion or
diatomaceous earth, or to fumigate the grain in-transit with phosphine after
the grain had been loaded. However, this approach would require a change in
policy and possibly require a change in legislation before these methods could
be used to deal with the problem of infested ship holds, in Canada.
All three of these methods could easily be adapted for shipping containers,
and some tests with the recapture had already demonstrated its effectiveness.
Another hurdle for the phosphine-based methods would be the certification that
the control is sufficient for quarantine purposes, as most importing countries
only recognize methyl bromide as adequate for quarantine treatment.
Acknowledgments
This was a collaborative study that would not have been possible without the
help of the following people: Pierre Beauchamp, Denis Bureau, Roger Cavasin,
Geoff Cuttin, Nancy Kummen, Dorothy Laidlaw, Brett MacKillop, Bernie McCarthy,
John McIssac, Mike McLean, Micheal Maheu, Mark Matthews, Dave Meuller, Stephen
Murch, Don Shaheen, Martin St-Pierre, Blaine Timlick, Alan Van Ryckeghem and
Murray Weightman.
[January 2000 Table of Contents]
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Last Updated: February 24, 2000
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