I.
Effects of DDT on soil and water
A.
Persistence
1.
Has a half life of 15-20 years.
2.
After 15 years, residue levels of 18% and 24% DDT were found in soil after applications of 10 and 100 lbs per acre, respectively. (Lichtenstein et al., 1971)
3.
DDT lasts longer in cool, dry soils but evaporates more quickly in warm, wet ones.
B.
Vertical Distribution
1.
Rainfall washes DDT from surface layer of soil to lower levels.
(Mohapatra et al., 1995)
2.
Plowing mixes contaminated soil on the surface with deeper soil. (Perfect,
1980)
3.
Sandy soils allow for rapid vertical movement while clay-based soils limit vertical distribution.
C.
Reduced Rate of Decomposition
1.
DDT has been shown to reduce the rate of decomposition of both easily degradable materials and more resistant matter in soil.
2.
Reduced surface earthworm activity has also been linked to DDT.
(Perfect, 1980)
3.
This could have implications for the fertility of the soil.
D.
DDT Absorbed From Soil into Aerial Parts of Plants
1.
Plants exposed to DDT experienced translocation from the shoot system to the roots. (Perfect, 1980)
2.
Plants in soil contaminated by DDT were shown to have absorbed residues from the soil and transferred them to the aerial parts of plants. (Perfect,
1980)
E.
Decline of Yield in Areas Treated with DDT
1.
DDT has been linked to decline in yield.
2.
Treated plots had the most decline in yield, followed by contaminated
(plots where DDT had been applied in one or two growing seasons), plots that were untreated showed the least decline.
3.
This study did acknowledge that there could be underlying factors causing this relationship.
F.
Insoluble in Water
1.
DDT is very persistent due to its insolubility in water.
2.
DDT does not experience degradation by microorganisms but does experience photochemical degradation.
3.
Can be broken down to DDE, but is still toxic.
G.
Travels though Water
1.
DDT can travel through rivers and lakes to spread to and contaminate a wider area.
2.
DDT can travel through rainfall, runoff and spray drifts.
3.
DDT has been found as far away as the Arctic and Antarctica showing the long distance it can travel. (U.S. Department of Health and Human
Services)
4.
In rivers and lakes, DDT can be absorbed from water into silt at the bottom, contaminating and spreading to more area.
H.
Gets Washed into Ground Water
1.
After application of DDT, the water evaporates and a layer of DDT remains on the top of the soil. Rainfall then washes these layers down to deeper layers of soil and into groundwater. (Mohapatra et al., 1995)
2.
This causes most problems for those who rely on groundwater as their main source of water.
I.
DDT as Compared to Other Pesticides
1.
After 15 years, residues of 10.6%, 5.8% and.2% per acre were detected for
DDT, Aldrin and Lindane, respectively.
2.
In a study of ground water, DDT had the highest level of residues of all other insecticides studied, including HCH, Aldrin, Endosulfan, and
Heptachlor.
II.
The effects of DDT on wildlife
A.
Food web accumulation (Niering, 1968)
1.
“Accumulates in higher and higher concentrations as it travels through a food chain” (Williams, 1970)
2.
Stored in fat (Moore, 1967)
3.
Long persistence (Williams, 1970; Tiedeken and Ramdell, 2009)
4.
Effects high order carnivores most strongly (Williams, 1970; Sherburne and Dimond, 1969)
B.
Effects on Insects
1.
Lethal on contact (Surber, 1946)
2.
Accumulate insecticides from soil (Beyer and Gish, 1980; Sherburne and
Dimond, 1969)
3.
Effects nervous system (Surber, 1946) a.
Paralysis
4.
Develop resistance (Williams, 1970; Moats and Moats, 1970) a.
Need higher concentrations of DDT b.
Higher populations of insects
C.
Effects on animals
1.
Poison animals (Williams, 1970; Surber, 1946; Moats and Moats, 1970)
2.
Cancer and cysts (Heinrichs et al., 1971)
3.
Effects hormones (Williams, 1970; Heinrichs et al., 1971)
4.
Decrease reproduction (Williams, 1970)
5.
Decreased metabolism (Williams, 1970)
6.
Immunosuppression (Storelli et al., 2009)
7.
Enhanced susceptibility to effects from other chemicals (Tiedeken and
Ramsdell, 2009) a.
Domoic acid
8.
Strong selective pressures (Moore, 1967)
D.
Effects on fish
1.
Long food chains (Williams, 1970; Moats and Moats, 1970)
2.
Effects nervous system (Surber, 1946)
a.
Hyperirritability b.
Muscular incoordination c.
Muscular spasms d.
Prostration
3.
High mortality of newly hatched fry (Moats and Moats, 1970)
E.
Effects on birds
1.
Thinner egg shells (Williams, 1970; Grier, 1982; Fry and Toone, 1981;
Ratcliffe, 1970; Moats and Moats, 1970) a.
Eggs crack when parents sit on them b.
Steroid hormones (Progesterone)
2.
Chicks die shortly after hatching or don’t hatch (Moats and Moats, 1970;
Niering, 1968)
3.
Feminization (Fry and Toone, 1981) a.
Inability to breed, reduced number of breeding males b.
Highly skewed sex ration
4.
Effects nervous system (Michigan DNR, 2002) a.
Hyperirritablility b.
Twitching and tremors c.
Incoordination d.
Convulsions
F.
Effects on ecosystems
1.
Destabilizes natural systems (Moore, 1967)
2.
Destabilizes food chains (Moore, 1967) a.
Food shortage
3.
Change predator/prey relationships (Moore, 1967)
4.
Change competitive relationships (Moore, 1967)
5.
Change habitat (Moore, 1967)
6.
Accumulation (Niering, 1968)
G.
Species effected by DDT (Williams, 1970; Beyer and Gish, 1980; Herman and
Bulger, 1979; Tiedeken and Ramsdell, 2009; Moore, 1967; Surber, 1946; Grier, 1982;
Fry and Toone, 1981; Ratcliffe, 1970; Sherburne and Dimond, 1969; Moats and
Moats, 1970; Storelli et al., 2009; Niering, 1968)
H.
Effects on fauna compared to other pesticides
1.
Dieldrin a.
Many of the same effects i.
Poisoning (Flickinger et al., 1986) ii.
Reproductive productivity (Grier, 1982; Moats and Moats,
1970) iii.
Nervous system (Frank and Lutz, 1999; Michigan DNR,
2002) b.
Doesn’t seem to effect eggs (Frank and Lutz, 1999) c.
Less persistent in tissue (Beyer and Gish, 1980)
2.
Endrin a.
Many of the same effects i.
Poisoning (Fleming et al., 1982)
1.~80 x more toxic than DDT
2.~8 x more toxic than Dieldrin ii.
Reproductive productivity (Fleming et al., 1982) b.
Doesn’t cause thin eggs (Fleming et al., 1982) c.
Some organisms develop resistance (Moats and Moats, 1970) i.
Insects ii.
Fish
3.
Methoxychlor a.
Used to control Dutch Elm disease (Niering, 1968; Moats and
Moats, 1970) b.
Much less hazards to wildlife (Niering, 1968; Moats and Moats,
1970)
III.
Effects of DDT on farm workers
A.
Discuss lack of data specifically related to question
B.
Effects on humans in general
1.
Utero exposure (Eskenazi et al., 2006)
a.
Neurodevelopment
2.
Possible carcinogenic (Eskenazi et al., 2009)
3.
Male reproductive health and fertility (Jager et al., 2006)
4.
Effects by route of exposure (ATSDR) a.
Inhalation b.
Oral c.
Dermal
C.
Effects of other pesticides (ATSDR)
1.
Limitations in data
2.
Aldrin/Dieldrin
3.
Limits in evaluation of pesticides and DDT
I.
Effects of DDT contamination in soil and drinking water in residential areas
A.
DDT exposure pathway to residential areas (Ramsay, 1991)
1.
Runoff and leaching primary modes
2.
Attaches to soil particles; minimizes volatilization
3.
Improper application
4.
Soil overloading
5.
Insufficient buffer zone from water source
6.
Poor storage methods
B.
Current DDT Concentrations in Residential Drinking Water and Soil (ATSDR)
1.
DDT sediments disperse into agricultural/ urban streams
2.
DDT in surface soils leach into ground water
3.
DDT in surface soils deposited long distances by wind onto top soil
4.
Since U.S. ban of DDT, concentrations decreasing
C.
DDT Use in South Africa and Negative Human Health Impacts (IPEN)
1.
Extensive DDT usage in disease vector control a.
Banned in 1996, Reintroduced in 2000 b.
Estimated 33 tons of DDT used each year
2.
Direct casual link seen between exposure to DDT and poorer semen parameters; adverse affects on testicular functions, and reproductive hormone regulation
3.
Evidence of incomplete DNA condensation
4.
Indications of increased stillbirths, neonatal deaths, congenital defects in children, and post-generational impacts on female
5.
Increase in incidents of pre-term birth and underweight babies
6.
High prevalence of urogenital birth defects
7.
Contaminated breast milk in lactating mothers a.
Intake by breast-fed babies in DDT sprayed areas exceeds allowable daily intake levels
8.
Potential increases in infant mortality
9.
Lack of extensive research into long-term health effects in regions where
DDT is still used
D.
Major Sources of Pesticidal Contamination in Drinking Water and Soil (Gilliom,
2009)
1.
Agricultural areas a.
Herbicides: Atrazine, Metalochlor, Cyanozine, Alachlor,
Acetochlor
2.
Urban areas a.
Herbicides: Simazine, Prometon, Tebuthiuron, 2,4-D, Diuron b.
Insecticides: Diazinon, Chlorpyrifos, Carbaryl
E.
Potential Health Impacts of Residential DDT Contamination
1.
Low concentrations in soil and water, no serious risk of cancer a.
Inhalation has a higher risk of carcinogen intake
2.
Lack of research into long-term effects
3.
Current DDT concentrations pose no serious health risks (WHO, 2004)
F.
Potential Health Impacts of Other Pesticidal Contaminants (USEPA, 2007)
1.
Acute health effects a.
Irritation of the nose, throat, and skin b.
Nausea, dizziness, and diarrhea c.
Symptoms that mimic the flu
2.
Chronic health effects a.
Cancer and tumors
b.
Brain and nervous system damage c.
Reproductive problems; infertility d.
Damage to liver, kidney, lungs, and other organs e.
Endocrine disruption
G.
Maximum Contaminant Levels (MCLs) (NJDEP)
1.
Limits that public water systems are required to meet by law
2.
Set well below levels known to have negative health impacts
3.
Regulations have been set for all known contaminants with adverse health effects
H.
Current Pesticide Use (Gilliom, 2009)
1.
Agricultural a.
Herbicides i.
Atrazine ii.
Metolachlor iii.
Cyanazine iv.
Alachlor v.
Acetochlor
2.
Urban a.
Herbicides i.
Simazine ii.
Prometon iii.
Tebuthiuron iv.
2,4-D v.
Diuron b.
Insecticides i.
Diazinon ii.
Chlorpyrifos iii.
Carbaryl
I.
Current Contamination Risks (Gilliom, 2009)
1.
Occurrence of pesticide compounds (streams) a.
Urban: 97%, Agricultural: 97%, Mixed: 94%
2.
One half of the wells surveyed contained one or more pesticide compounds
3.
One third of deeper wells (used to tap aquifers) contained one or more pesticides
4.
Annual mean concentrations of one or more pesticides exceeding benchmarks in streams a.
Agricultural: 8 of 83, Urban: 2 of 30
5.
Ground water sources exceeding benchmarks is about 1% of 2,356 domestic and 364 public supply wells a.
Occurring mostly in shallow ground water sources
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