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Material type: Botanical
U.S. EPA toxicity Category: III, “Caution”
USDA – NOP status:
Considered nonsynthetic, allowed. Preventive, cultural, mechanical
and physical methods must be first choice for pest control, and
conditions for use of a biological or botanical material must
be documented in the organic system plan (NOP 2000).
Active ingredient description:
Pyrethrum is the generic name given
to a plant based insecticide derived from the powdered, dried flower
heads of the pyrethrum daisy, chiefly Chrysanthemum cinerariaefolium,
but also in C. coccineum and C. marshalli. Pyrethrins are the six
constituent compounds with insecticidal properties that occur in
these Chrysanthemum species. The pyrethrum daisy is native to southwest
Asia. Kenya is the leading producer of pyrethrum followed by Australia.
Note: Pyrethroids are synthetic compounds whose structure and
mode of action are similar to pyrethrins but they are not approved
for use in organic production. There are many pyrethoids including
Ambush®, Ammo®, Aztec®, Pounce® and Warrior ®.
How it works:
Pyrethrum is a fast acting contact poison that ‘knocks
down’ susceptible insects. Insects are left paralyzed by
the toxic effect of pyrethrum. The normal function of the nervous
system is affected, stimulating repetitive nerve discharges leading
to paralysis. However, some insects are able to recover after the
initial knockdown if the dose is too low.
Synergists:
Mortality may be enhanced with the addition of a synergist,
a chemical not considered strongly insecticidal in itself, but
which enhances the activity of the material being applied. Piperonyl
butoxide (PBO) is a common synthetic synergist that reduces an
insect’s ability to detoxify pyrethrum. It is added to most
pyrethrum products. Piperonyl butoxide is not allowed under the
National Organic Program. Care should be taken not to use pyrethrum
products that contain prohibited synergists.
Recently, pyrethrum products containing various oils but without
PBO have come on the market. Such oils may increase the efficacy
of pyrethrum. Two 1987 studies examined pyrethrum augmented with
nutmeg, parsley, sassafras, and safrole oils as well as PBO (Noetzel
et al. 1989, Noetzel and Ricard 1989). Nutmeg oil appeared to show
promise against cabbage looper. None of the synergists improved
efficacy against imported cabbageworm, however. In trials against
Colorado potato beetles, these synergists showed insecticidal properties
with or without pyrethrum (Noetzel et al. 1989).
Types of pests it controls:
Pyrethrum is used widely throughout
the world to control many human and household pests such as mosquitoes
and houseflies. While it was used widely in agriculture before
World War II, cheaper and more effective synthetic products have
mostly replaced it for farm use (Casida 1973, Casida and Quistad
1995). More recently, new pyrethrum products, often solvent-based
and including PBO, have appeared on the agriculture market. Only
a few are approved for organic production under the NOP.
Formulations and Application guidelines:
Pyrethrum is sometimes available blended with rotenone to increase
the range of pests controlled (i.e. flea beetles) and perhaps
efficacy. However, mixing insecticides against a specific target
insect is not recommended because it will promote the development
of resistance. Currently, none of these mixtures is OMRI-approved.
Liquid formulations typically contain 0.1-6 % pyrethrum and up
to 60% PBO (not permitted); dusts contain 0.2-0.4 % pyrethrum.
Availability and Sources:
Readily available from garden and farm
suppliers; however few products are approved for organic production.
OMRI LISTED PRODUCTS:
Pyganic® Crop
Protection EC 5.0 II
Pyganic® Crop Protection EC 1.4 II
Safer® Brand Yard & Garden Insect Killer Concentrate
II (with soap)
Safer® Brand Yard & Garden Insect Killer II (with soap)
References to OMRI listed products in this Guide are based
on the June 2004 edition of the OMRI Brand Name List. Please
consult www.omri.org for
changes and updates in the brand name product listings. Non-OMRI listed (incomplete list):
Pyrellin® (pyrethrum
and rotenone; petroleum solvent)
Pyola® (pyrethrum and canola oil)
Pyrenone® (6%; 60% PBO) [cancelled registration]
Pyronyl® (6%; 60% PBO)
Evergreen® (6%; 60% PBO)
Diatect V®
Reentry interval
(REI) and pre-harvest interval (PHI):
The EPA
Workers Protection Standard requires a minimum of 12 hours before
reentering a treated field.
Application tips:
Care should be taken not to mix pyrethrum with lime, sulfur,
or soap solutions, since pyrethrum is broken down by both acid
and alkaline conditions.
Pyrethrum is rapidly broken down by sunlight. Use of UV-inhibiting
adjuvants may allow for a longer period of control. Growers should
decide whether the advantage of having a longer activity period
for pyrethrum to protect the crop from reinfestations is appropriate
for their management system, or would be a concern for its impact
on beneficial species.
Since pyrethrum is a contact poison the target pest must be present
and hit by the spray. Flighty insects such as cucumber beetle should
be sprayed early in the morning when they are sluggish and bee
pollinators have not begun to fly.
Effect on the environment:
Leaf persistence. Pyrethrum is quickly degraded in sunlight (Casida
and Quistad 1995).
Fate in water. Pyrethrum compounds are broken down in water to
nontoxic products (Extoxnet 1994)
Soil persistence. Soil application studies of pyrethrum showed
a half life of only 1-2 hours (Casida and Quistad 1995). When used
indoors, pyrethrum can persist much longer; up to two months or
more in carpet dust (Cox 2002).
Wildlife. Pyrethrum is extremely toxic to fish such as bluegill
and lake trout, while it is slightly to moderately toxic to bird
species, such as mallards and bobwhite quail. Natural pyrethrins
are highly fat soluble, but are easily metabolized and thus do
not accumulate in the body. Because pyrethrin-I and pyrethrin-II
have multiple sites in their structures that can be readily attacked
in biological systems, it is unlikely that they will concentrate
in the food chain (Extoxnet 1994, Casida and Quistad 1995).
Effect on beneficial arthropods. Synthetic pyrethroids are broad
spectrum insecticides and are notorious for killing and repelling
beneficial arthropods. However, since pyrethrum residues on the
plant break down quickly, the effect on natural enemies is reduced.
Pyrethrum is highly toxic to bees. The average lethal dose (LD50)
for honeybees was measured at .022 micrograms per bee (Casida and
Quistad 1995). Direct hits on honeybees and beneficial wasps are
likely to be lethal (Cox 2002).
Effect on human health:
Acute Toxicity: Compared to many other insecticides, pyrethrum
is relatively non-toxic to humans and therefore only carries
the signal word CAUTION. However, care is warranted.
Rats and rabbits are not affected by high dermal applications.
On broken skin, pyrethrum produces irritation and sensitization,
which is further aggravated by sun exposure. Absorption of pyrethrum
through the stomach and intestines and through the skin is slow.
However, humans can absorb pyrethrum more quickly through the lungs
during respiration. Response appears to depend on the pyrethrum
compound used. Inhaling high levels of pyrethrum may bring about
asthmatic breathing, sneezing, nasal stuffiness, headache, nausea,
lack of coordination, tremors, convulsions, facial flushing and
swelling, and burning and itching sensations (Extoxnet 1994).
The lowest lethal oral dose of pyrethrum is 750 mg/kg for children
and 1,000 mg/kg for adults. Oral LD50 values of pyrethrins in rats
range from 200 mg/kg to greater than 2,600 mg/kg. Some of this
variability is due to the variety of constituents in the formulation.
Mice have a pyrethrum oral LD50 of 370 mg/kg. Animals exposed to
very high amounts may experience tongue and lip numbness, nausea,
diarrhea, lack of coordination, tremors, convulsions, paralysis,
respiratory failure, and death. Recovery from serious poisoning
in mammals is fairly rapid (Extoxnet 1994).
Organ Toxicity: In mammals, tissue accumulation has not been recorded.
At high doses, pyrethrum can be damaging to the central nervous
system and the immune system. When the immune system is attacked
by pyrethrum, allergies can be worsened. Animals fed large doses
of pyrethrins may experience liver damage. Rats fed pyrethrin at
high levels for two years showed no significant effect on survival,
but slight, definite damage to the livers was observed. Inhalation
of high doses of pyrethrum for 30 minutes each day for 31 days
caused slight lung irritation in rats and dogs (Extoxnet 1994).
Fate in Humans and Animals: Pyrethrins and their metabolites are
not known to be stored in the body nor excreted in the milk. The
urine and feces of people given oral doses of pyrethrum contain
chrysanthemumic acid and other metabolites. These metabolites are
less toxic to mammals than are the parent compounds. Pyrethrins
I and II are excreted unchanged in the feces. Other pyrethrum components
undergo rapid destruction and detoxification in the liver and gastrointestinal
tract (Extoxnet 1994).
Chronic Toxicity: Overall, pyrethrins have low chronic toxicity
to humans and the most common problems in humans have resulted
from the allergenic properties of pyrethrum. Patch tests for allergic
reaction are an important tool in determining an individual’s
sensitivity to these compounds. Pyrethrum can produce skin irritation,
itching, pricking sensations and local burning sensations. These
symptoms may last for about two days (Extoxnet 1994). Cox (2002)
reports more serious chronic effects, including circulatory and
hormonal effects.
Casida and Quistad (1995) performed 90 day feeding tests on animals.
They found no effects at 1000 ppm or less on rats, none at 300
ppm or less on mice, and none at 600 ppm or less on dogs.
Reproductive Effects: Rabbits that received pyrethrins orally
at high doses during the sensitive period of pregnancy had normal
litters. A group of rats fed very high levels of pyrethrins daily
for three weeks before first mating had litters with weanling weights
much lower than normal. Overall, pyrethrins appear to have low
reproductive toxicity (Extoxnet 1994).
Teratogenic Effects: A rabbit reproduction study performed showed
no effect of pyrethrins on development of the offspring (Extoxnet
1994). Casida and Quistad (1995) found that in rats, there were
no teratogenic effects at feeding doses of up to 600 mg/kg/day.
According to the Agency for Toxic Substances and Disease Registry,
part of the US Center for Disease Control, “There is no evidence
that pyrethrins or pyrethroids cause birth defects in humans or
affect the ability of humans to produce children” (ATSDR
2001).
Mutagenic Effects: None observed in salmonella,
rat primary hepatocyte, or Chinese hamster ovary cell tests (Casida
and Quistad 1995).
Carcinogenic Effects: “There is no proof that pyrethrins
or pyrethroids cause cancer in people. Pyrethrins and pyrethroids
do not appear to cause cancer in animals” (ATSDR 2001). However,
Cox (2002) cites several studies indicating the possibility of
a connection between pyrethrins and cancer, including one study
showing a 3.7-fold increase in leukemia among farmers who had handled
pyrethrins compared to those who had not. In 1999, a USEPA memo
classified pyrethrins as “likely to be a human carcinogen
by the oral route” (Cox 2002). Currently EPA is undertaking
a review for pyrethrin, which is scheduled for completion and issuance
of a Reregistration Eligibility Decision (RED document) in June
2006. The RED summarizes the risk assessment conclusions and outlines
any risk reduction measures necessary for the pesticide to continue
to be registered in the U.S. (EPA 2004).
Efficacy
Older studies: Pyrethrum is a broad-spectrum insecticide used to
control true bugs, caterpillars, beetles, aphids, flies, mites,
whiteflies, thrips and leafhoppers (Casida 1973). Within these
groups, pests may have a greater or lesser susceptibility to
pyrethrum products. Specific pest species controlled by pyrethrum
as noted in the older literature include potato leafhopper, beet
leafhopper, cabbage looper, celery leaf tier, Say’s stink
bug, twelve-spotted cucumber beetle, six-spotted leafhopper,
lygus bugs on peaches, grape thrips, flower thrips, grape leafhopper,
and cranberry fruitworm. It was not considered particularly effective
against flea beetles, imported cabbageworm, diamondback moth,
aphids on spinach, or lygus bugs on alfalfa (Casida 1973).
Recent studies: A summary of recent university field trials of
pyrethrum products on vegetable crops commonly grown in the Northeast
was compiled. These university-based trials typically test products
with untreated buffer rows and other conditions that create unusually
severe pest pressure.
The level of pest control is likely to be higher on fields in
which a good program of cultural controls has been implemented.
In the tables below,”good control” means statistically
significant reductions in pest numbers or damage of 75% or more,
compared to an untreated control. “Fair control” includes
those with significant reductions of 50-74%, and any non-signnificant
reductions of over 50%. The “poor control” group includes
any results with less than 50% reduction.
Pest Reduction Relative
to Untreated Control |
Crop |
Pest |
| 61-100% |
Celery
Celery
Cabbage
Blueberry
Tomato
Cucumber
Lettuce
Cabbage
Apple
Potato
Celery
Grape
Potato
Alfalfa
Grape
Blueberry
Potato
Potato
Blueberry
Onion
Blueberry |
Beet armyworm
Black cutworm
Imported cabbag eworm
Blueberry spanworm
Greenhouse whitefly
Greenhouse whitefly
Greenhouse whitefly
Cabbage aphid
Green peach aphid
Potato aphid
Sunflower aphid
Grape leafhopper
Potato leafhopper
Potato leafhopper
Variegated leafhopper
Blueberry flea beetle
Colorado potato beetle
Potato flea beetle
Blueberry thrips
Onion thrips
Blueberry sawfly |
| 41-60% |
Tomato
Cabbage
Tomato
Apple
Potato |
Beet armyworm
Cabbage looper
Tomato fruitworm
Apple aphid
Tarnished plant bug |
| Less than 41% |
Tomato
Sweet corn
Sweet corn
Sweet corn
Tomato
Celery
Blueberry
melon |
Tomato pinworm
Fall armyworm
Corn earworm
European corn borer
Vegetable leafminer
Vegetable leafminer
Blueberry maggot
Spider mite |


References
ATSDR 2001. Draft Public Health Statement for Pyrethrum and Pyrethroids.
Agency for Toxic Substances and Disease Registry, US Dept. of
Health and Human Services. http://www.atsdr.cdc.gov/toxprofiles/phs155.html
Casida, J. E. and G. B.Quistad, eds. 1995. Pyrethrum Flowers—Production,
Chemistry, Toxicology, and Uses. Oxford University Press, Oxford.
Casida, J. E., ed. 1973. Pyrethrum, The Natural Insecticide. Academic
Press, New York.
Cox, C. 2002. Pyrethrins/Pyrethrum Insecticide Factsheet. Journal
of Pesticide Reform 22(1) 14-20.
EPA. 2004. Pesticide Reregistration Status. US Environmental Protection
Agency. http://cfpub2.epa.gov/oppref/rereg/status.cfm?show=rereg
Extoxnet 1994. Pyrethrins And Pyrethroids. Pesticide Information
Profiles. Extension Toxicology Network. http://ace.ace.orst.edu/info/extoxnet/pips/pyrethri.htm
Noetzel D., M. Ricard, and J. Wiersma. 1989. Effect of 3 pyrethroid
and 4 suggested synergist combinations on pyrethroid-resistant
Colorado Potato Beetle, 1987. Insecticide and Acaricide Tests 14:159-160.
Noetzel, D. and M.Ricard. 1989. Control of imported cabbageworm
and cabbage looper using pyrethrin, rotenone, or Asana with of
without one of four "synergists". Insecticide and Acaricide
Tests 14:96-97.
NOP. 2000. USDA National Organic Program regulations, 7CFR 205.206(e).
http://www.ams.usda.gov/nop/
Silcox, C. A. and E. S. Roth. 1995. Pyrethrum for Control of Pests
of Agriculture and Stored Products. Casida, John E. and Gary B.
Quistad, eds. 1995. Pyrethrum Flowers—Production, Chemistry,
Toxicology, and Uses. Oxford University Press, Oxford.
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