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Methoprene:
Profile Excerpts from the Extension Toxicology Network (Extoxnet)
(Extoxnet is a Pesticide Information Project of Cooperative
Extension Offices of Cornell University, Oregon State University,
the University of Idaho, and the University of California at Davis
and the Institute for Environmental Toxicology, Michigan State
University. Major support and funding was provided by the
USDA/Extension Service/National Agricultural Pesticide Impact
Assessment Program. EXTOXNET primary files maintained and archived
at Oregon State University)
Methoprene
Introduction:
Methoprene is a compound which mimics the action of an insect
growth regulation hormone. It is used as an insecticide because it
interferes with the normal maturation process. It is used in
aquatic areas to control mosquitoes and several types of ants,
flies, lice, moths, beetles, and fleas.
Toxicological Effects:
Acute toxicity: Methoprene is
slightly toxic by skin exposure.
Organ toxicity: The target organ
primarily affected by methoprene after long-term exposure is
the liver.
Ecological Effects:
Effects on birds: Methoprene is
slightly toxic to birds [1,158]. The reported 5- to 8-day LC50
values for Altosid, a methoprene formulation, are greater than
10,000 ppm in mallard ducks and bobwhite quail, and the acute
oral LD50 for Altosid is greater than 4640 ppm in chickens
[1,158]. In mallards an acute oral LD50 of greater than 2000
mg/kg was determined [158]. Nonlethal effects that may affect
survival of the birds did appear at acute oral doses of 500
mg/kg. These effects appeared as soon as 2 hours after
treatment and persisted for up to 2 days and included
slowness, reluctance to move, sitting, withdrawal, and
incoordination [63]. These effects may decrease bird survival
by making them temporarily more susceptible to predation. No
effects were observed in the reproduction of bobwhite quail
and mallard ducks at 30 ppm constant feeding of Altosid [158].
Effects on aquatic organisms:
Methoprene is slightly to moderately toxic to fish [157]. The
reported 96-hour LC50 values for the methoprene formulation
Altosid were 4.6 mg/L in bluegill sunfish, 4.4 mg/L in trout,
and greater than 100 mg/L in channel catfish and largemouth
bass [1,8]. Methoprene residues may have a slight potential
for bioconcentration in bluegill sunfish and crayfish [155].
Methoprene is very highly toxic to some species of freshwater,
estuarine, and marine invertebrates, while the acute LC50
values are greater than 100 mg/L in freshwater shrimp, and it
is greater than 0.1 mg/L in estuarine mud crabs [159]. Altosid
had very little effect, if any, on exposed non-target aquatic
organisms including waterfleas, damselflies, snails, tadpoles,
and mosquito fish [159].
Environmental Fate:
Breakdown in soil and groundwater:
Methoprene is of low persistence in the soil environment;
reported field half-lives are up to 10 days [155]. In sandy
loam, its half-life was calculated to be about 10 days [155].
When Altosid was applied at an extremely high application rate
of 1 pound per acre, its half-life was less than 10 days
[155]. In soil, microbial degradation is rapid and appears to
be the major route of its disappearance from soil [155,157].
Methoprene also readily undergoes degradation by sunlight
[157]. Methoprene is rapidly and tightly sorbed to most soils
[155]. It is slightly soluble in water [1]. These properties,
along with its low environmental persistence make it unlikely
to be significantly mobile. In field leaching studies, it was
observed only in the top few inches of the soil, even after
repeated washings with water [155,159].
Breakdown in water: Methoprene
degrades rapidly in water [8]. Studies have demonstrated
half-lives in pond water of about 30 and 40 hours at initial
concentrations of 0.001 mg/L and 0.01 mg/L, respectively [49].
At normal temperatures and levels of sunlight, technical
Altosid is rapidly degraded, mainly by aquatic microorganisms
and sunlight [159,49].
Breakdown in vegetation: Altosid is
biodegradable and nonpersistent, even in plants treated at
very high rates. It has a half-life of less than 2 days in
alfalfa when applied at a rate of 1 pound per acre [159]. In
rice, the half-life is less than 1 day [49]. In wheat, its
half-life was estimated to be 3 to 7 weeks, depending on the
level of moisture in the plant [155]. Plants grown in treated
soil are not expected to contain methoprene residues.
References for the information in this PIP can be found in
Reference List Number 10
Other Notes:
Aside from adding to the cost (of, already, the
most expensive option), retention of the said lagoons, along with
the subsequent on-going requirement for repeated use of methoprene, has several
attendant safety and environmental disadvantages.
Because methoprene's aqueous half life
(especially in sunlight) is only 30 to 40 hours, there would a
reguirement for "repeated saturation usage" of the product, in
order for it to be effective for each of the 7-10 day breeding
cycles of mosquitoes, throughout the summer.
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