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DDT 1874-2005DDT 1874-2005
Paul JepsonPaul JepsonIntegrated Plant Protection Center
Oregon State [email protected]
November 17th, 2005
Pre-1940’s Pre-1940’s insecticidesinsecticides
• Household– Clothes moth:
camphor, naphalene, p-dichlorbenzene
– Fumigation: ethylene oxide, hydrocyanic acid
• Garden and farm– Nicotine, methyl
bromide, acetonitrile, calcium copper and lead arsenates, pyrethrins, rotenone
Dipping apples in 1% hydrochloric acid for 4 min removes 66-73% of the arsenic residue: 1930
Average arsenic after treatment: 0.006 grains/lb
FDA tolerance:
1927: 0.025 grains/lb
1932: 0.01 grains/lb
Experimental hop Experimental hop duster, Corvallis duster, Corvallis Oregon, 1940Oregon, 1940
Applying 4,6-dinitro-o-cyclohexyl phenol dust in walnut shell flour for spider mite control
DDT
• Highly toxic• Very persistent• Low acute toxicity to humans• 1941, little interest expressed• 1944, use to manage typhus epidemic created high
demand in wartime• High use in agriculture from first year of introduction• Impacts on humans and environment overridden by
commercial imperatives• Facilitated establishment of modern environmental
movement
Chronology of the modern pesticide industry• World War I
– Increase in supply of agricultural products to USA and allies– Growth of chemical industry incl. Chemical Warfare Service (PDB)– Development of pest control as a metaphor for war and vice versa
• Between wars– Testing of war gases as insecticides– Attempts to establish “Chemical Peace Service”– Entomologists increasingly use war metaphor for pest control
• World War II– Total war concept feeds warfare and pest control (annihilation)– Factory capacity for production grows after DDT introduction
• US government enables scarce materials to be used to build 14 factories for 11 companies in 1944/4
• 35-100% tax relief given to companies– DuPont awarded post war license for DDT in exchange for production agreement– Wide scale spraying in vector control using chemical warfare equipment– Restrictions on wide use of DDT under war powers legislation, because of side-effects on
humans and wildlife, detected at an early stage• Aftermath of war
– Organophosphate nerve gases tested as pesticides– No license or patent restrictions on US industry initially– Surplus production capacity directed to agriculture– No legal powers of government to restrict sale of properly labeled chemicals– Wildlife and conservation groups and many entomologists raise concerns by 1945– War metaphor used nationally to promote DDT use– Efficiency in military use, and for medicine used as an argument for promoting use in
agriculture
Introduction and wide-scale use of Introduction and wide-scale use of organochlorine insecticides, 1946organochlorine insecticides, 1946
Pyrethrum flower imports peaked at 13 million lbs 1945, but feel sharply in 1946, not resuming until 1955
Early promise, early Early promise, early cautioncaution
• DDT, HCH: combined contact activity and high toxicity of pyrethrins, with stomach activity and persistence of arsenates
• But, were not the universal insecticides that popular accounts made it appear– Toxicity to beneficials (e.g.parasites, bees, beetles, flies)
reported in early 1940’s– Research prior to 1946 was more cautious (problems
with lack of selectivity in potato, invertebrate loss in carrots, mite outbreaks in apple)
DDT used widely in the house, farm and DDT used widely in the house, farm and zoozoo
(Leary, Fishbein & Salter, 1946)
Pesticide treatments by 13 commercial Pesticide treatments by 13 commercial applicators in Oregon, 1957applicators in Oregon, 1957 (Mumford, 1959)
Application type
No. jobs Acres treated
Mean area per job
Application charge per acre
Ground treatment
767(DDT 49)
10,272(DDT 386)
13.4 $2.60
Aerial spraying
1,841(DDT 714)
146,481(DDT
25,231)
80.0 $1.33
The Hale centrifugal sprayer, capable of projecting spray upwards 30ft
The Hurst hang-on sprayer
Mist blowers, 1952Mist blowers, 1952(Garman, 1953)
50 gals/min, 1mph, gives 11.2 gals per tree, at 20 ft tree spacing
Serious drift problems reported in 1950’s literature
Application efficiency was not high
Pesticide utilization efficiencyPesticide utilization efficiency (Graham-Bryce, 1977)
Pesticide Application method
Target Efficiency of utilization
Demeton-S-methyl
Foliar spray Aphids on sugar beet
0.000008%
Dieldrin Seed treatment
Wheat bulb fly larvae
0.0015%
Dimethoate Foliar spray Aphids on field beans
0.03%
Lindane Foliar spray Capsids on Cocoa
0.02%
Dieldrin Aerial swarm spray
Locusts 6.0%
Summary• Organochlorines seemed a vast improvement upon
what went before• They were inexpensive and often gave high economic
return• High persistence and broad spectrum of toxicity did not
require them to be used efficiently• Chemists were ignorant of how OC properties impacted
ecological processes• Over-optimism and over-marketing led to complacency• Pest outbreaks (caused by loss of natural enemies)
were common following OC use• Evidence of wildlife impacts emerged by the late 1950’s
but hazard was known in 1945• The ‘Green Revolution’ relied upon broad spectrum
pesticides
Silent Spring Silent Spring byby Rachel Rachel CarsonCarson
• Main arguments– Pesticides represent new risk, parallel with
radioactivity, that deserves to be watched critically
– The most severe problems are the long term genetic and ecological ones; ecologists have new responsibilities
– The administrative machinery is inadequate• Response in UK:
– All scientific claims and statistics checked for accuracy and errors (minor), published in Journal of Ecology, 1963
– Public and parliamentary focus on pollution, ecology, risks and benefits
– Gradual restriction of OC’s, 1962-1976
The peregrin falcon(Moriarty, 1999)
• 1960, UK racing pigeon owners thought that falcon predation was increasing
• Analysis revealed a falcon population decline since 1955
• 1962: 92% of pre-war territories deserted, only 2% of nests successful
• pp-DDE and dieldrin seed dressings implicated• Pigeon mortality common, and 2-3 pigeons
consumed could prove lethal to falcons• If dieldrin was responsible for the decline, what
explains the poor breeding success?
Changes in egg shell thickness index, 1845-1979, Changes in egg shell thickness index, 1845-1979, for British peregrine falcons (for British peregrine falcons (Falco peregrinusFalco peregrinus)) (Ratcliffe, 1993)
Shell strength Shell strength and thickness in and thickness in Falco peregrinusFalco peregrinus (Cooke, 1979)
Open circles: 1850-1942
Closed circles: 1970-1974
pp-DDE thickens eggs of bengalese finch, hen, quail and pheasant
DDE implicated in egg shell thinningDDE implicated in egg shell thinning
SOILSOIL
0.730.73
EARTHWORMEARTHWORMSS
1.631.63
BLACKBIRDSBLACKBIRDS
87.1 (liver)87.1 (liver)
BLACKBIRDBLACKBIRDSS
52.7 (eggs)52.7 (eggs)
THRUSHTHRUSH
119.5 (liver)119.5 (liver)
THRUSHTHRUSH
46.2 (eggs)46.2 (eggs)
MOLESMOLES
1.78 (liver)1.78 (liver)
JANJAN
MARMAR
MAYMAY
Food chain Food chain accumulation of accumulation of pppp-DDE in UK -DDE in UK orchards after orchards after April sprays April sprays (ppm)(ppm)Bailey et al. (1974)Many equivalent datasets: Clear lake; land and sea bird carcass
studies
Epidemiological criteria for inferring causation
Criterion Inference strengthened…
Problems
Strength of association
Cause associated with large increase in risk
Difficulties measuring exposure and effects
Probability of causal association
Statistical significance Requires large study population and large effect
Time order Introduction of cause precedes effects
Long latency
Specificity of association
Specific cause linked to specific effect
Chemicals cause suites of effects, and they interact with other chemicals and stresses to cause disease
Consistency of association
Different authors, places, times
Impacts vary in space and time
Dos-response relationship
High exposure, high effect
Difficulty in measuring exposure, variation in modifying factors between groups, non-linear relationships
Biological plausibility Known mechanism Many processes not well understood, epidemiological data often precede mechanism
Benefits of OC’s?Benefits of OC’s?
Locust control in Africa
Disease vector control
Band spraying with insect growth Band spraying with insect growth regulators, using ULV sprayers, regulators, using ULV sprayers,
replaces OC’s and OP’sreplaces OC’s and OP’s
Returns to approach used for dieldrin and the OC’s, but without the
environmental risk
Alternatives to DDT proving harder to find, but they do exist
DDT still used as a wall treatment, and against the vectors of sleeping sickness. Pyrethroid-treated bed nets are just as effective
Impact of the modern insecticide era on biological control?
Numbers of introduced natural Numbers of introduced natural enemies by decadeenemies by decade (Gurr, et al.,
2000)
0
100
200
300
400
500
600
700
800
900
1890-9 1900-9 1910-9 1920-9 1930-9 1940-9 1950-9 1960-9 1970-9 1980-9 1990-8
% Biological introductions leading to success, % Biological introductions leading to success,
establishment, failure (or unknown)establishment, failure (or unknown) (Gurr et al., 2000)
0
10
20
30
40
50
60
70
80
90
100
1880-9 1900-9 1910-9 1920-9 1930-9 1940-9 1950-9 1960-9 1970-9 1980-9 1990-8
SuccessEstablishmentFailure
How can success rate be improved?
The organochlorine legacyThe organochlorine legacy• Remaining OC residues and polar
accumulation• Human body burdens, declining,
but still there• Clean-up and disposal
internationally• Gradual shift towards more
effective chemicals• Chemophobia among public• Lack of public understanding of
agriculture• Regulation improving• Alternative technology
suppressed• Recycling of arguments about
causation with respect to human disease and environmental impact
• POP’s convention permits use in malaria management
OC’s in aquatic ecosystems of the Columbia Plateau (USGS)
Continued use of DDT in vector control
• Express the trade-offs in terms of costs and benefits
• Is lack of DDT the real underlying cause of malaria resurgence?
• Do advocacy groups contribute to or detract from progress?