Hubbry Logo
search
logo
Aldrin avatar
Aldrin
Aldrin
current hub
1987247

Aldrin

logo
Community Hub0 Subscribers
Read side by side
Aldrin
View on Wikipedia
from Wikipedia
Aldrin
Aldrin
Aldrin
Names
Preferred IUPAC name
(1R,4S,4aS,5S,8R,8aR)-1,2,3,4,10,10-Hexachloro-1,4,4a,5,8,8a-hexahydro-1,4:5,8-dimethanonaphthalene
Other names
HHDN[1]
octalene[1]
Identifiers
3D model (JSmol)
ChEBI
ChEMBL
ChemSpider
ECHA InfoCard 100.005.652 Edit this at Wikidata
EC Number
  • 206-215-8
KEGG
RTECS number
  • IO2100000
UNII
UN number 2762, 2761
  • InChI=1S/C12H8Cl6/c13-8-9(14)11(16)7-5-2-1-4(3-5)6(7)10(8,15)12(11,17)18/h1-2,4-7H,3H2/t4-,5+,6+,7-,10+,11- checkY
    Key: QBYJBZPUGVGKQQ-SJJAEHHWSA-N checkY
  • InChI=1/C12H8Cl6/c13-8-9(14)11(16)7-5-2-1-4(3-5)6(7)10(8,15)12(11,17)18/h1-2,4-7H,3H2/t4-,5+,6+,7-,10+,11-
    Key: QBYJBZPUGVGKQQ-SJJAEHHWBI
  • ClC4(Cl)[C@@]2(Cl)C(/Cl)=C(/Cl)[C@]4(Cl)[C@@H]3[C@@H]\1C[C@@H](/C=C/1)[C@H]23
Properties
C12H8Cl6
Molar mass 364.90 g·mol−1
Appearance Colorless solid
Density 1.60 g/mL[1]
Melting point 104 °C (219 °F; 377 K)
slightly soluble (0.003%)[1]
Vapor pressure 7.5 × 10−5 mmHg @ 20 °C
Pharmacology
Legal status
  • AU: S6 (Poison)
Hazards
Occupational safety and health (OHS/OSH):
Main hazards
 Toxic and is a suspected human carcinogen[1]
GHS labelling:
GHS06: ToxicGHS08: Health hazardGHS09: Environmental hazard
Danger
H300, H301, H310, H311, H351, H372, H410
P201, P202, P260, P262, P264, P270, P273, P280, P281, P301+P310, P302+P350, P302+P352, P308+P313, P310, P312, P314, P321, P322, P330, P361, P363, P391, P405, P501
NFPA 704 (fire diamond)
NFPA 704 four-colored diamondHealth 4: Very short exposure could cause death or major residual injury. E.g. VX gasFlammability 0: Will not burn. E.g. waterInstability 0: Normally stable, even under fire exposure conditions, and is not reactive with water. E.g. liquid nitrogenSpecial hazards (white): no code
4
0
0
Flash point 66 °C (151 °F; 339 K)
Lethal dose or concentration (LD, LC):
50 mg/kg (rabbit, oral)
33 mg/kg (guinea pig, oral)
39 mg/kg (rat, oral)
44 mg/kg (mouse, oral)[2]
5.8 mg/m3 (rat, 4 hr)[2]
NIOSH (US health exposure limits):
PEL (Permissible)
 TWA 0.25 mg/m3 [skin][1]
REL (Recommended)
 Ca TWA 0.25 mg/m3 [skin][1]
IDLH (Immediate danger)
 25 mg/m3[1]
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
checkY verify (what is checkY☒N ?)

Aldrin is an organochlorine insecticide that was widely used until the 1990s, when it was banned in most countries. Aldrin is a member of the so-called "classic organochlorines" (COC) group of pesticides. COCs enjoyed a very sharp rise in popularity during and after World War II. Other noteworthy examples of COCs include dieldrin and DDT.[3] After research showed that organochlorines can be highly toxic to the ecosystem through bioaccumulation, most were banned from use. Before the ban, it was heavily used as a pesticide to treat seed and soil. Aldrin and related "cyclodiene" pesticides (a term for pesticides derived from Hexachlorocyclopentadiene) became notorious as persistent organic pollutants.[4]

Structure and Reactivity

[edit]

Pure aldrin takes form as a white crystalline powder. Though it is not soluble in water (0.003% solubility), aldrin dissolves very well in organic solvents, such as ketones and paraffins.[5] Aldrin decays very slowly once released into the environment. Though it is rapidly converted to dieldrin by plants and bacteria, dieldrin maintains the same toxic effects and slow decay of aldrin.[6] Aldrin is easily transported through the air by dust particles. Aldrin does not react with mild acids or bases and is stable in an environment with a pH between 4 and 8. It is highly flammable when exposed to temperatures above 200 °C[7] In the presence of oxidizing agents aldrin reacts with concentrated acids and phenols.

Synthesis

[edit]

Aldrin is not formed in nature. It is named after the German chemist Kurt Alder, one of the coinventors of this kind of reaction. Aldrin is synthesized by combining hexachlorocyclopentadiene with norbornadiene in a Diels-Alder reaction to give the adduct.[8] In 1967, the composition of technical-grade aldrin was reported to consist of 90.5% of hexachlorohexahydrodimethanonaphthalene (HHDN).[6]

Synthesis of aldrin via a Diels-Alder reaction

Similarly, an isomer of aldrin, known as isodrin, is produced by reaction of hexachloronobornadiene with cyclopentadiene.[9] Isodrin is also produced as a byproduct of aldrin synthesis, with technical-grade aldrin containing about 3.5% isodrin.[6]

Isodrin

An estimated 270 million kilograms of aldrin and related cyclodiene pesticides were produced between 1946 and 1976.[10] The estimated production volume of aldrin in the US peaked in the mid-1960s at about 18 million pounds (8.2 kt) a year and then declined.[11]

Available forms

[edit]

There are multiple available forms of aldrin. One of these is the isomer isodrin, which cannot be found in nature, but needs to be synthesized like aldrin. When aldrin enters the human body or the environment it is rapidly converted to dieldrin. Degradation by ultraviolet radiation or microbes can convert dieldrin to photodieldrin and aldrin to photoaldrin.[6]

Mechanism of action

[edit]

Even though many toxic effects of aldrin have been discovered, the exact mechanisms underlying the toxicity are yet to be determined. The only toxic aldrin induced process that is largely understood is that of neurotoxicity.

Neurotoxicity

[edit]

One of the effects that intoxication with aldrin gives rise to is neurotoxicity. Studies have shown that aldrin stimulates the central nervous system (CNS), which may cause hyperexcitation and seizures.[12] This phenomenon exerts its effect through two different mechanisms.

One of the mechanisms uses the ability of aldrin to inhibit brain calcium ATPases.[13] These ion pumps relieve the nerve terminal from calcium by actively pumping it out. However, when aldrin inhibits these pumps, the intracellular calcium levels rise. This results in an enhanced neurotransmitter release.

The second mechanism makes use of aldrin's ability to block gamma-aminobutyric acid (GABA) activity.[14] GABA is a major inhibitory neurotransmitter in the central nervous system. Aldrin induces neurotoxic effects by blocking the GABAA receptor-chloride channel complex. By blocking this receptor, chloride is unable to move into the synapse, which prevents hyperpolarization of neuronal synapses. Therefore, the synapses are more likely to generate action potentials.

Metabolism

[edit]

The metabolism of oral aldrin exposure has not been studied in humans. However, animal studies are able to provide an extensive overview of the metabolism of aldrin. This data can be related to humans.

Biotransformation of aldrin starts with epoxidation of aldrin by mixed-function oxidases (CYP-450),[15] which forms dieldrin. This conversion happens mainly in the liver. Tissues with low CYP-450 expression use the prostaglandin endoperoxide synthase (PES) instead.[16] This oxidative pathway bisdioxygenises the arachidonic acid to prostaglandin G2 (PGG2). Subsequently, PGG2 is reduced to prostaglandin H2 (PGH2) by hydroperoxidase.

Dieldrin can then be directly oxidized by cytochrome oxidases, which forms 9-hydroxydieldrin. An alternative for oxidation involves the opening of the epoxide ring by epoxide hydrases, which forms the product 6,7-trans-dihydroxydihydroaldrin.[17] Both products can be conjugated to form 6,7-trans-dihydroxydihydroaldrin glucuronide and 9-hydroxydieldrin glucuronide, respectively. 6,7-trans-dihydroxydihydroaldrin can also be oxidized to form aldrin dicarboxylic acid.[18][19]

Efficacy and side effects

[edit]

Considering the toxicokinetics of aldrin in the environment, the efficacy of the compound has been determined. In addition, the adverse effects after exposure to aldrin are demonstrated, indicating the risk regarding the compound.

Efficacy

[edit]

The ability of aldrin, in its use for the control of termites, is examined in order to determine the maximum response when applied. In 1953 US researchers tested aldrin and dieldrin on terrains with rats known to carry chiggers, at a rate of 2.25 pounds per acre (2.52 kg/ha). The aldrin and dieldrin treatment demonstrated a decrease of 75 times less chiggers on rats for dieldrin treated terrains and 25 times less chiggers on the rats when treated with aldrin. The aldrin treatment indicate a high productivity, especially in comparison to other insecticides that were used at the time, such as DDT, sulfur or lindane.[20]

Adverse effects

[edit]

Exposure of aldrin to the environment leads to the localization of the chemical compound in the air, soil, and water.[6] Aldrin gets changed quickly to dieldrin and that compound degrades slowly, which accounts for aldrin concentrations in the environment around the primary exposure and in the plants.[21] These concentrations can also be found in animals, which eat contaminated plants or animals that reside in the contaminated water. This biomagnification can lead to a high concentrations in their fat.

There are some reported cases of workers who developed anemia after multiple dieldrin exposures. However the main adverse effect of aldrin and dieldrin is in relationship to the central nervous system.[6] The accumulated levels of dieldrin in the body were believed to lead to convulsions.[22] Besides that other symptoms were also reported like headaches, nausea and vomiting, anorexia, muscle twitching and myoclonic jerking and EEG distortions. In all these cases removal of the source of exposure to aldrin/dieldrin led to a rapid recovery.[23]

Toxicity

[edit]

The toxicity of aldrin and dieldrin is determined by the results of several animal studies. Reports of a significant increase in workers death in relation to aldrin has not been found, although death by anemia is reported in some cases after multiple exposure to aldrin. Immunological tests linked an antigenic response to erythrocytes coated with dieldrin in those cases.[24] Direct dose-response relations being a cause for death are yet to be examined.

The NOAEL that was derived from rat studies:[6]

  • The minimal risk level at acute oral exposure to aldrin is 0.002 mg/kg/day.
  • The minimal risk level at intermediate exposure to dieldrin is 0.0001 mg/kg/day.
  • The minimal risk level at chronic exposure to aldrin is 0.00003 mg/kg/day.
  • The minimal risk level at chronic exposure to dieldrin is 0.00005 mg/kg/day.

In addition to these studies, breast cancer risk studies were performed demonstrating a significant increased breast cancer risk. After comparing blood concentrations to number of lymph nodes and tumor size a 5-fold higher risk of death was determined, comparing the highest quartile range in the research to the lower quartile range.[25]

Effects on animals

[edit]

Most of the animal studies done with aldrin and dieldrin used rats. High doses of aldrin and dieldrin demonstrated neurotoxicity, but in multiple rat studies also showed a unique sensitivity of the mouse liver to dieldrin induced hepatocarcinogenicity.[26] Furthermore, aldrin treated rats demonstrated an increased post-natal mortality, in which adults showed an increased susceptibility to the compounds compared to children in rats.[27]

Environmental impact and regulation

[edit]

Like related polychlorinated pesticides, aldrin is highly lipophilic. Its solubility in water is only 0.027 mg/L, which exacerbates its persistence in the environment. It was banned by the Stockholm Convention on Persistent Organic Pollutants. In the U.S., aldrin was cancelled in 1974. The substance is banned from use for plant protection by the EU.[28]

Safety and environmental aspects

[edit]

Aldrin has rat LD50 of 39 to 60 mg/kg (oral in rats). For fish however, it is extremely toxic, with an LC50 of 0.006–0.01 for trout and bluegill.[4]

In the US, aldrin is considered a potential occupational carcinogen by the Occupational Safety and Health Administration and the National Institute for Occupational Safety and Health; these agencies have set an occupational exposure limit for dermal exposures at 0.25 mg/m3 over an eight-hour time-weighted average.[29] Further, an IDLH limit has been set at 25 mg/m3, based on acute toxicity data in humans to which subjects reacted with convulsions within 20 minutes of exposure.[30]

It is classified as an extremely hazardous substance in the United States as defined in Section 302 of the U.S. Emergency Planning and Community Right-to-Know Act (42 U.S.C. 11002), and is subject to strict reporting requirements by facilities which produce, store, or use it in significant quantities.[31]

References

[edit]
Revisions and contributorsEdit on WikipediaRead on Wikipedia

Aldrin

View on Grokipedia
from Grokipedia
Aldrin is a synthetic organochlorine compound with the molecular formula C₁₂H₈Cl₆, classified as a cyclodiene insecticide due to its bicyclic structure formed via the Diels-Alder reaction between hexachlorocyclopentadiene and norbornadiene.[1][2] Introduced commercially in the 1950s, it was applied to soils to control pests such as termites, grasshoppers, and corn rootworms, exhibiting high efficacy through disruption of insect nervous systems via GABA receptor antagonism.[3][4] In vivo, aldrin undergoes rapid epoxidation to dieldrin, its more stable and toxic metabolite, contributing to its environmental persistence with half-lives exceeding years in soil and sediment.[5][6] Both compounds bioaccumulate in fatty tissues and food chains, posing risks of neurotoxicity, carcinogenicity, and endocrine disruption in mammals, including humans, as evidenced by liver tumors in rodent studies and acute poisoning cases involving convulsions and tremors.[3][7][1] These properties prompted regulatory actions, including a U.S. EPA ban on most uses by 1974 and inclusion as a persistent organic pollutant under the 2001 Stockholm Convention, restricting production and trade globally despite residual detections in legacy contamination.[8][4]

Chemical Properties

Molecular Structure and Reactivity

Aldrin possesses the molecular formula C12H8Cl6 and a molar mass of 364.91 g/mol, consisting of a rigid, bridged bicyclic framework characteristic of cyclodiene organochlorines.[1] [9] This structure arises from the Diels-Alder [4+2] cycloaddition of hexachlorocyclopentadiene as the diene with norbornadiene serving as the dienophile, yielding a norbornene-derived adduct with the six chlorine atoms symmetrically positioned on the five-membered ring portion.[10] The resulting 1,4:5,8-dimethano-naphthalene core features a fused cyclopentadiene ring bridged to a six-membered ring containing a reactive double bond, with the stereochemistry predominantly endo for the dienophile approach, enhancing molecular planarity and electron delocalization.[10] [11] The bridged architecture imparts significant steric hindrance and conformational rigidity, shielding the chlorinated carbons from nucleophilic attack and contributing to overall chemical stability under neutral conditions.[12] This stability is evidenced by resistance to hydrolysis and photolysis in inert media, though the molecule exhibits selective reactivity at the electron-rich norbornene double bond.[6] A primary reactivity pathway involves electrophilic epoxidation of the aforementioned double bond, converting aldrin to dieldrin via addition of an oxygen atom across the C=C bond, often facilitated by peracids or environmental oxidants.[6] [13] This transformation proceeds stereospecifically to yield the exo-epoxide isomer, reflecting the molecule's endo-facial accessibility and underscoring aldrin's propensity for oxidative metabolism in aerobic settings.[6] Under ambient environmental conditions, such as exposure to atmospheric oxygen or microbial enzymes, aldrin undergoes this epoxidation quantitatively, with the resulting dieldrin exhibiting enhanced persistence due to ring strain in the epoxide.[6]

Physical Characteristics

Aldrin exists as a colorless crystalline solid in its pure form.[14] Technical-grade preparations may appear tan to brown due to impurities.[15] It has a density of 1.6 g/cm³ and a melting point of 104–105°C.[16] The compound exhibits low volatility, with a vapor pressure of approximately 0.009 Pa at 20°C.[16] Aldrin demonstrates extremely low solubility in water, reported at 0.011–0.027 mg/L at 20–27°C, which contributes to its limited mobility in aqueous environments and potential for persistence in soils and sediments.[15] [17] In contrast, it possesses high solubility in nonpolar organic solvents such as hexane, benzene, and oils, reflecting its lipophilic nature with a log Kow value exceeding 6, which facilitates bioaccumulation in fatty tissues of organisms.[15] [3] Under standard conditions, aldrin remains chemically stable, resisting decomposition at temperatures up to 200°C and within pH ranges of 4–8, though it may react with strong oxidizing agents or concentrated acids.[1] [18] This stability influences its handling as a persistent solid requiring careful storage to prevent dust formation and inhalation risks during processing.[16]

Synthesis and Production

Industrial Synthesis Methods

The industrial synthesis of aldrin primarily employs the Diels-Alder cycloaddition reaction, in which hexachlorocyclopentadiene acts as the diene and norbornadiene (bicyclo[2.2.1]hepta-2,5-diene) serves as the dienophile.[14] This process, developed in the late 1940s, involves heating the reactants to approximately 100 °C, often with an excess of norbornadiene to drive the reaction forward, yielding the bridged polycyclic structure of aldrin.[14] The reaction proceeds thermally without additional catalysts, leveraging the electron-deficient nature of the chlorinated diene for efficient [4+2] cycloaddition.[19] In the transition from laboratory to industrial scale post-1940s, the process was optimized for high throughput by conducting the reaction in batch reactors under controlled temperatures to minimize side reactions. Yields typically exceed 95%, with the primary byproduct being isodrin, a stereoisomeric endo-endo adduct formed via alternative diastereofacial addition.[19] Byproduct management involves selective crystallization or distillation to isolate pure aldrin, as the isomers exhibit differing solubilities and melting points, ensuring technical-grade product purity above 95%. Solvents, if used, are minimal or avoided to facilitate direct recovery, aligning with the reaction's compatibility with neat conditions for scalability.[14] Purification steps post-reaction include recrystallization from organic solvents to remove unreacted precursors and minor impurities, enhancing the compound's stability for downstream formulation. Commercial production, initiated around 1950, capitalized on this robust methodology to produce aldrin efficiently until regulatory restrictions curtailed manufacturing. The Diels-Alder route's high atom economy and lack of complex catalysis contributed to its adoption in large-scale operations.[14]

Historical Production Scale

Aldrin entered commercial production in the United States in 1950, following its initial synthesis as a pesticide in 1948, with Shell Chemical Corporation licensing the manufacturing process and initiating large-scale output primarily for agricultural applications.[14][20] Domestic production expanded significantly through the 1950s and into the 1960s, driven by demand for soil insecticides, attaining a peak of approximately 18 to 20 million pounds annually by the mid-1960s, reflecting its widespread adoption in crop protection.[20][21] Output began diminishing after 1970 amid mounting regulatory pressures, falling to around 10.5 million pounds that year, before halting entirely in the United States by 1974.[20]

Formulations and Applications

Commercial Forms

Aldrin was commercially formulated in the mid-20th century primarily as dusts, granules, emulsifiable concentrates, wettable powders, and solutions in hydrocarbon liquids to facilitate various application methods, including soil incorporation, spraying, and seed treatment.[1][22] These formulations were designed for compatibility with agricultural equipment, such as dusters for fine powders and sprayers for liquid or suspension types.[23] Concentrations of active ingredient varied by form: emulsifiable concentrates typically contained 30% aldrin, wettable powders ranged from 40% to 70%, and dusts were generally 2.5% to 5%, with granules and seed dressings often in similar lower ranges for targeted soil or planting applications.[24] Dust concentrates and oil-based solutions provided additional options for specialized delivery, ensuring even distribution during deployment.[23]

Target Pests and Usage Methods

Aldrin was primarily employed against soil-dwelling insects, including termites, wireworms, corn rootworms, weevils, and grasshoppers.[3][14] These pests were targeted through direct contact or ingestion following soil application, exploiting aldrin's persistence in treated zones.[25] In agricultural settings, aldrin saw widespread use from the 1950s onward for protecting crops such as corn, cotton, and fruit orchards against root-infesting larvae and surface-feeding insects.[26] Standard methods involved broadcast incorporation into soil prior to planting or band application along rows, typically at rates of 1 to 2 pounds per acre to establish barriers against larval penetration.[14][6] Non-agricultural applications focused on subterranean termite control in building construction, where aldrin was applied as a soil drench or injected around foundations to create protective chemical barriers pre- or post-construction.[22][27] This included trenching along perimeters and rodding beneath slabs to ensure thorough coverage against termite foraging galleries.[6]

Mechanism of Action

Biochemical Mechanism

Aldrin is rapidly converted to its epoxide metabolite dieldrin through enzymatic oxidation of the exocyclic double bond in its norbornadiene ring, primarily by cytochrome P450 monooxygenases present in the tissues of both invertebrates and vertebrates.[6][13] This biotransformation enhances the compound's stability and potency, as dieldrin exhibits greater persistence and neurotoxic efficacy than the parent aldrin.[28] In target insects, the conversion occurs efficiently, rendering dieldrin the principal active agent responsible for pesticidal activity. Dieldrin functions as a noncompetitive antagonist at GABA-gated chloride channels, binding to a modulatory site distinct from the GABA recognition site on the receptor complex.[29] This binding inhibits the channel's ability to conduct chloride ions upon GABA activation, preventing membrane hyperpolarization and disrupting inhibitory neurotransmission in the central nervous system.[30] The blockade leads to unchecked neuronal firing, convulsions, and paralysis in susceptible organisms, with the interaction occurring at low nanomolar concentrations in insect preparations.[31] Selective toxicity toward invertebrates arises from structural and compositional differences in their GABA receptors compared to those in vertebrates. Insect GABA channels, often homopentamers incorporating the RDL (resistance to dieldrin) subunit, display markedly higher sensitivity to dieldrin blockade than the heteropentameric GABAA receptors predominant in mammals, which incorporate diverse subunits conferring reduced affinity.[30][32] This differential receptor pharmacology underlies the compound's targeted disruption of invertebrate neural inhibition while exhibiting lower potency against vertebrate chloride channels.[33]

Neurotoxic Effects

Aldrin primarily exerts neurotoxic effects in insects through antagonism of GABA_A-gated chloride channels, preventing inhibitory chloride ion influx and thereby disrupting normal neuronal inhibition.[34] This blockade causes sustained membrane depolarization, leading to uncontrolled excitatory signaling in the central nervous system.[35] The cyclodiene structure of aldrin binds to a convulsant site within the channel pore, similar to picrotoxin, with key chlorine substitutions on the methano bridge enhancing affinity for insect receptors over those in vertebrates.[36][37] The resulting physiological disruptions manifest as hyperexcitability, followed by tremors and convulsive activity that progress to paralysis in target pests.[34] This sequence arises from the first-principles disruption of chloride flux equilibrium, where unopposed excitatory inputs overwhelm inhibitory control, amplifying synaptic transmission until motor function fails. Insect GABA receptors, encoded by genes like Rdl (resistance to dieldrin), exhibit particular sensitivity to this mechanism, conferring selective toxicity.[38] Parallels exist in higher organisms due to conserved channel architecture, though insect channels demonstrate greater vulnerability to blockade, enabling aldrin's efficacy as an insecticide.[39] The rapid binding kinetics ensure onset of effects shortly after exposure, typically eliciting symptoms in minutes for contact-active applications against mobile insects.[35]

Metabolism and Fate

Biological Metabolism

In biological systems, aldrin is primarily metabolized through enzymatic epoxidation to form dieldrin, a process catalyzed by cytochrome P450 monooxygenases present in the livers of mammals and in insect tissues.[6][40] This conversion occurs rapidly, with aldrin serving as a substrate for mixed-function oxidases, leading to the incorporation of an oxygen atom across the double bond in its molecular structure.[41] In mammals, this transformation is predominantly hepatic, while in insects, it contributes to the compound's neurotoxic action without significant detoxification.[40] The resulting dieldrin accumulates in adipose tissues due to its lipophilic nature, exhibiting a biological half-life in mammals ranging from approximately 50 to 370 days, depending on species and exposure duration; for instance, studies in cattle reported half-lives of 53–231 days in body fat.[42][43] This prolonged retention stems from slow release from fat depots and limited further metabolism, with only minor hydroxylation or other oxidative pathways observed under high exposure conditions.[44] Excretion of aldrin and its metabolites occurs mainly via feces through biliary elimination, with urinary output representing a minor route (e.g., fecal-to-urinary ratios of about 19:1 in rats and mice).[44][7] In mammals, unmetabolized aldrin and dieldrin are detected in fecal matter, while urine contains trace conjugated metabolites like hydroxydieldrin, underscoring the dominance of enterohepatic circulation in clearance.[43] Insects exhibit similar fecal elimination patterns post-metabolism, though systemic distribution is more limited due to rapid toxic effects.[40]

Environmental Persistence and Bioaccumulation

Aldrin exhibits notable persistence in soil, with a reported half-life ranging from 20 to 100 days under aerobic conditions, though this is often overshadowed by its rapid epoxidation to the more stable dieldrin, which has a soil half-life of 2 to 5 years in temperate environments.[45][14] This conversion occurs abiotically or via microbial action shortly after application, effectively extending the residence time of cyclodiene residues in the pedosphere to several years.[6] Aldrin resists hydrolysis in neutral pH soils due to the absence of readily hydrolyzable functional groups, limiting breakdown via this pathway.[1] Photolytic degradation is possible on exposed soil surfaces or in shallow water but proceeds slowly, with aldrin absorbing UV light to form products like dieldrin or photodieldrin, further contributing to overall environmental durability rather than rapid dissipation.[45][7] The compound's high octanol-water partition coefficient (log Kow ≈ 6.5) underscores its strong affinity for lipids over water, promoting sorption to soil organic matter and sediments while minimizing mobility and leaching into groundwater.[46][6] This hydrophobicity drives bioaccumulation, as aldrin and its dieldrin derivative partition into fatty tissues of organisms, with bioconcentration factors exceeding 10,000 in aquatic species like fish.[7] In food webs, this leads to biomagnification, where concentrations amplify by factors of 2 to 16 across trophic levels, from invertebrates to top predators in both aquatic and terrestrial systems.[47] Such patterns have been documented in field studies, attributing higher residues in birds and mammals to dietary uptake from contaminated prey.[7] As a persistent organic pollutant, aldrin residues persist in environmental matrices long after usage cessation; detections in river sediments from agricultural watersheds have occurred decades post-ban, linked to remobilization from legacy soil deposits via erosion.[48] Similarly, trace levels in biota, including fish and wildlife tissues, continue to be reported in regions with historical applications, reflecting ongoing cycling through sediments and low-level volatilization.[28] These findings align with its listing among the initial 12 POPs under international agreements, based on empirical evidence of long-range transport and accumulation potential.[49]

Efficacy in Pest Control

Effectiveness Against Pests

Aldrin exhibited strong efficacy against soil pests such as corn rootworms (Diabrotica spp.) in agricultural field applications during the 1950s and early 1960s, prior to the emergence of resistance that rendered control ineffective by the mid-1960s.[50] Treatments at rates of 1 lb per acre effectively suppressed rootworm populations through contact and ingestion, contributing to its widespread adoption for corn protection.[51] Against termites, aldrin soil treatments demonstrated prolonged residual activity, with 0.5% concentrations in coral and clay soils significantly reducing termite tunneling even after 28 years of exposure, thereby limiting reinfestation over extended periods.[52] This persistence in soil, where aldrin converts to dieldrin, maintained barriers effective for months to years against subterranean species.[53] In comparative field evaluations pre-1960s, aldrin showed potency equal to dieldrin and superior to alternatives like certain organophosphates for targeted soil insects, including wireworms and seed corn maggots, due to its broad-spectrum neurotoxic action via the GABA receptor.[54][28] Its high effectiveness stemmed from rapid knockdown and long-lasting residues, outperforming earlier chlorinated hydrocarbons like DDT for deep-soil pests.[55]

Agricultural and Economic Benefits

Aldrin played a key role in protecting major crops from soil-dwelling insects during the 1950s and 1960s, when it was widely applied to fields of corn, potatoes, and rice to target pests such as corn rootworms (Diabrotica spp.), wireworms (Agriotes spp.), and rice water weevils (Lissorhoptrus oryzophilus). These insects can severely damage root systems, leading to lodging, reduced nutrient uptake, and substantial harvest losses if uncontrolled. Field trials demonstrated aldrin's efficacy in suppressing such populations; for instance, seed treatments reduced rice water weevil densities by 80-90%, thereby safeguarding plant stands and potential yields.[56] Similarly, applications against corn rootworms resulted in measurable yield gains, with one study reporting a 9% increase attributable to pest suppression in treated plots.[57] In clover fields, aldrin at 0.75 pounds per acre achieved 85.6% control of root borers, supporting hay production levels of 2.01 tons per acre in the second cutting compared to untreated benchmarks.[58] This pest control contributed to broader agricultural productivity gains in the post-World War II era, as organochlorine insecticides like aldrin enabled farmers to expand cultivation into previously marginal or infested lands while minimizing mechanical interventions such as tillage or hand labor. Pesticide adoption, including aldrin, aligned with a tripling of average U.S. corn yields from the 1940s to the late 20th century through enhanced crop protection.[59] By preventing losses estimated in severe infestations to reach 20% or more in vulnerable crops, aldrin supported food security amid global population growth and wartime disruptions.[60] Economically, aldrin's persistence in soil allowed for single, low-dose applications—often 1-2 pounds per acre—to deliver season-long protection, outperforming less residual alternatives and reducing overall input costs relative to biological or cultural methods. Reviews of soil insect control highlighted its reasonable pricing and high performance at minimal rates, making it a preferred option for corn rootworm management over competitors like BHC.[61] This efficiency lowered per-unit production expenses, facilitating profitability in staple crop farming during a period of rising demand.[62]

Health and Toxicity

Human Exposure and Acute Effects

Aldrin exposure in humans primarily occurs through ingestion, inhalation of dust or aerosols, and dermal contact, especially during manufacturing, formulation, or agricultural application in the mid-20th century.[6] Acute poisoning is characterized by rapid onset of central nervous system excitation, with major motor convulsions as the hallmark symptom, often preceded by a brief prodrome of nausea, vomiting, headache, dizziness, or tremors.[63] Other immediate effects include malaise, incoordination, fatigue, gastrointestinal distress, and sensory disturbances such as numbness or paresthesia.[34] The oral LD50 for aldrin in rats is approximately 39–67 mg/kg body weight, indicating high acute toxicity in rodents, with rapid conversion to dieldrin contributing to neurotoxic effects via GABA receptor antagonism.[6] In humans, ingestion of around 25.6 mg/kg has induced convulsions, while estimated lethal doses range from 1.25–70 mg/kg, underscoring lower tolerance compared to rodents due to metabolic and physiological differences.[64][7] Inhalation exposure up to 18 mg/m³ for one day showed no immediate effects in reported cases, though dermal absorption can lead to systemic uptake, particularly from contaminated skin or clothing.[64] Occupational incidents of acute aldrin poisoning were documented in the 1950s and 1960s, often resulting from accidental ingestion or heavy dermal exposure during pesticide handling without adequate protective measures.[55] For instance, manufacturing workers experienced convulsive episodes treatable with supportive care, including gastric lavage, activated charcoal administration, and anticonvulsant therapy to manage seizures.[63] Fatalities occurred in severe cases of intentional or accidental high-dose ingestion, but most acute exposures resolved with prompt medical intervention focused on symptom control rather than specific antidotes, as no targeted reversal agent exists.[6]

Chronic Health Risks

Aldrin, rapidly metabolized to dieldrin in the body, accumulates primarily in adipose tissue due to its lipophilic nature, leading to potential prolonged exposure from sustained low-level intake.[65] Human studies have detected dieldrin residues in fat samples from the general population and exposed workers, with levels correlating to historical environmental contamination.[7] This bioaccumulation raises concerns for chronic effects, though elimination half-lives in humans range from months to years depending on body fat and exposure cessation.[6] The International Agency for Research on Cancer (IARC) classifies aldrin (as metabolized to dieldrin) as Group 2A, probably carcinogenic to humans, based on sufficient evidence in experimental animals showing liver tumors but limited evidence in humans. Epidemiological studies of occupationally exposed workers, including a cohort of over 500 individuals followed for more than 50 years, report no significant excess cancer mortality, with standardized mortality ratios below expected values overall.[66] Similarly, long-term follow-up of manufacturing and formulation workers exposed to aldrin and dieldrin shows no clear increase in cancer incidence attributable to these compounds after adjusting for confounders.[67] Neurological effects from chronic low-level exposure remain uncertain, with some reports of tremors, irritability, and abnormal EEGs in high-exposure groups, often confounded by co-exposures to other pesticides or solvents.[63] In occupational cohorts, such symptoms typically resolved within months to years after exposure ended, and large-scale mortality studies do not indicate elevated rates of neurodegenerative diseases or overall neurological morbidity.[68] No consistent excess mortality from chronic aldrin exposure has been observed beyond potential acute incidents in applicators.[69]

Ecological and Environmental Effects

Impacts on Wildlife and Ecosystems

Aldrin demonstrates high acute toxicity to birds, with oral LD50 values varying by species from 6.6 mg/kg to 520 mg/kg body weight, though values for many avian species fall in the lower range of 7-50 mg/kg as reported in laboratory tests on species such as Japanese quail (LD50 13 mg/kg for aldrin) and chickens (10-15 mg/kg).[70][14][71] These toxicities primarily manifest as neurotoxic effects, including convulsions and mortality, following rapid metabolism to the more persistent and potent dieldrin.[6] Aquatic organisms, particularly fish, exhibit extreme sensitivity to aldrin, with 96-hour LC50 values often below 0.1 mg/L for sensitive species in acute exposure studies conducted by regulatory agencies.[72][73] This low threshold contributes to widespread lethality in freshwater and saltwater fish populations upon environmental contamination. Aldrin and dieldrin biomagnify through aquatic and terrestrial food webs, accumulating to higher concentrations in predators than in prey, as evidenced by field monitoring in the 1960s and 1970s that documented elevated residues in top-level consumers.[74][75] This process disrupts ecosystem dynamics by reducing populations of intermediate and apex species, altering predator-prey balances in contaminated habitats. Empirical studies link aldrin/dieldrin exposure to direct mortality in raptors, such as sparrowhawks and kestrels in Britain, where residues correlated with population declines starting in the late 1950s coinciding with pesticide introduction, though these declines were multi-factorial and intertwined with effects from DDT and habitat factors.[76][77] In bald eagles, organochlorine residues including dieldrin have been implicated in reproductive impairments and overall population reductions observed mid-20th century, based on residue analyses from failed nests and carcasses, despite challenges in isolating causal contributions from co-occurring pollutants.[78][79] Unlike DDE from DDT, aldrin/dieldrin do not directly cause eggshell thinning but exacerbate vulnerabilities through sublethal neurotoxicity and reduced breeding success.[14]

Soil and Water Contamination

Aldrin exhibits limited mobility in soil due to its strong adsorption to organic matter and clay particles, resulting in low leaching potential into groundwater.[80] [81] Its primary transformation product, dieldrin, formed rapidly via epoxidation in aerobic soils, similarly binds tightly, with Koc values typically exceeding 5,000 indicating immobility.[6] Half-lives for aldrin/dieldrin in soil range from 2 to 4 years under field conditions, though persistence can extend beyond a decade in anaerobic or low-microbial-activity environments.[72] Surface runoff represents the main pathway for aldrin and dieldrin entry into aquatic systems, transporting sorbed residues from treated fields during precipitation events.[20] In water bodies, these compounds partition preferentially to sediments, where dieldrin accumulates due to its hydrophobicity (log Kow ≈ 6.2) and resistance to hydrolysis.[14] Post-ban monitoring (after U.S. restrictions in 1974) has revealed dieldrin concentrations in sediments persisting at levels up to 83.9 ng/g dry weight in some riverine systems as late as 2017.[82] Global surveys decades after widespread bans (e.g., 1970s–1980s) confirm residual soil burdens, with dieldrin detected at 1.8–63 ng/g in riparian soils from historical applications.[48] In U.S. agricultural soils, levels around 26 ng/g were noted in the 1980s, with some sites showing increases attributable to resuspension or slow release from deeper horizons.[6] Volatilization serves as a dissipation route from soil surfaces, with aldrin losses up to 50% within months under warm, dry conditions, though incorporation into soil reduces this rate significantly.[20] Photodegradation on exposed surfaces contributes minimally, yielding half-lives of several weeks to months under sunlight, primarily forming polar photoproducts that may enhance minor leaching compared to the parent compounds.[83] Overall, these abiotic processes account for less than 20% of total dissipation in most soils, overshadowed by microbial conversion and bound residue formation.[84]

Regulatory Framework

Historical Approvals and Restrictions

Aldrin was registered for use in the United States in 1949 under the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA), administered by the U.S. Department of Agriculture (USDA), which authorized its application for soil treatment against agricultural pests in crops such as corn, cotton, and potatoes.[85] This approval facilitated widespread adoption due to its efficacy against soil-dwelling insects.[63] Following the 1962 publication of Rachel Carson's Silent Spring, which raised alarms about bioaccumulative pesticides, regulatory scrutiny intensified; in 1963, the USDA canceled the registration label for aldrin on commercial white potatoes amid concerns over residues.[86] Manufacturers began voluntary reductions in promotional efforts and certain formulations during the early 1960s in response to emerging environmental data and public pressure.[7] In 1970, the USDA canceled all registrations for aldrin uses, citing risks of severe aquatic environmental damage.[20] The newly formed Environmental Protection Agency (EPA) then permitted limited re-registration in 1972 solely for subsurface termite control via ground insertion.[26] By 1974, the EPA suspended all other applications, retaining only the termiticide exemption.[25] The remaining termite control registration was voluntarily canceled by the sole manufacturer, Shell Chemical Company, in 1987, resulting in a complete prohibition on aldrin production and use in the U.S.[87]

Global Bans and Compliance

Aldrin was designated as one of the twelve initial persistent organic pollutants (POPs) under Annex A of the Stockholm Convention on Persistent Organic Pollutants, adopted in 2001 and entering into force on May 17, 2004, obligating signatory parties to eliminate its production, use, and release through comprehensive legal and administrative measures.[4][88] No specific exemptions for aldrin were registered, distinguishing it from certain other POPs, with the treaty emphasizing global cooperation for monitoring stockpiles, waste management, and unintentional releases via agricultural or industrial activities.[89] In the European Union, aldrin was prohibited under Council Directive 79/117/EEC, enacted in 1979 to restrict marketing and use of hazardous substances, effectively banning it across member states by the early 1980s as part of broader organochlorine phase-outs; it remains listed under the EU's Prior Informed Consent (PIC) procedure for export controls.[90][91] Comparable timelines applied in other developed regions, with bans implemented in the 1970s and 1980s following national assessments of its bioaccumulative properties, supplemented by ongoing residue monitoring programs to enforce zero-tolerance thresholds in imported goods. Enforcement in developing countries, particularly agriculture-dependent areas in Africa and Asia, faces persistent hurdles due to aldrin's environmental longevity and historical stockpiles, leading to documented trace detections in foodstuffs such as shellfish and produce destined for export, even post-ban.[92][93] The Stockholm Convention's Compliance Committee addresses non-conformance through national reporting requirements and technical assistance for remediation, yet challenges include limited regulatory capacity, illicit trade, and difficulties in verifying elimination amid ongoing bioaccumulation in soils and biota.[94][95] As of recent assessments, over 180 parties have committed to these targets, but residue exceedances in global supply chains underscore the need for enhanced international surveillance.[88]

Controversies and Debates

Risk-Benefit Analyses

Aldrin's application in agriculture demonstrated significant efficacy against soil pests, including corn rootworms (Diabrotica virgifera) and termites, which often resulted in yield protections exceeding 50% in treated fields compared to untreated controls, as evidenced by field trials prior to regulatory suspensions.[14][96] This effectiveness stemmed from its contact, stomach, and slight fumigant actions, enabling broad-spectrum control that minimized crop damage and supported higher productivity in staples like corn and cotton.[14][97] At recommended low dosages, early toxicological evaluations concluded that acute human health risks were manageable, with benefits in preventing economic losses from pest infestations outweighing potential exposures during standard handling and application.[63] The chemical's environmental persistence, converting rapidly to dieldrin in soil with half-lives ranging from 2–4 years under aerobic conditions, provided a dual advantage and drawback: sustained pest suppression reduced reapplication needs and labor costs, yet amplified bioaccumulation in food chains, elevating chronic exposure risks to wildlife and humans beyond initial application sites.[63][14] Pre-suspension analyses, such as those by industry and agricultural extension services, quantified net gains in food security, estimating that organochlorine insecticides like aldrin contributed to overall U.S. crop yield doublings from 1940–1970 by curbing insect-related losses averaging 10–20% annually.[59] Debates centered on empirical trade-offs, with agricultural advocates emphasizing causal links between aldrin use and stabilized yields essential for population growth—evident in its widespread adoption across 20+ years for protecting high-value crops—against environmental perspectives prioritizing precaution due to documented magnification factors in fatty tissues exceeding 10-fold.[63][98] Worker cohort studies from manufacturing sites reported no statistically significant excess mortality from aldrin exposure at occupational levels, supporting claims of controlled risks when adherence to guidelines mitigated acute effects like convulsions at doses above 50 mg/kg.[69] However, this view clashed with emerging data on dieldrin's role in neurological disruptions, prompting arguments that alternatives like organophosphates, despite shorter persistence, incurred higher immediate application risks without matching long-term efficacy.[63]

Criticisms of Regulatory Decisions and Alternatives

Critics of the U.S. Environmental Protection Agency's (EPA) 1974 suspension of aldrin registrations contended that the agency's determination of an "imminent hazard" overly depended on high-dose animal studies demonstrating liver tumors in mice, without sufficient adjustment for human exposure thresholds or the marked decline in aldrin application rates during the preceding decade.[99] [100] Extrapolations from such rodent data to human carcinogenicity risks have faced broader scientific scrutiny for underestimating species-specific metabolic differences and overemphasizing effects at doses far exceeding environmental levels, potentially inflating perceived threats relative to actual human dietary or occupational exposures, which epidemiological data showed remained below no-observed-adverse-effect levels in most monitored populations.[101] [102] Replacement pesticides, particularly organophosphates promoted as less persistent alternatives, introduced elevated risks of acute poisoning incidents, with global estimates indicating approximately 385 million cases annually, many resulting from occupational or accidental exposures during application. Unlike aldrin's primarily chronic bioaccumulation concerns, organophosphates inhibit cholinesterase enzymes rapidly, leading to immediate neurological symptoms and treatment costs averaging $85 per case in studied regions, cumulatively burdening public health systems with millions in annual expenditures that arguably exceeded the societal costs of regulated organochlorine use.[103] [104] Debates persist over whether aldrin bans favored speculative long-term ecological fears—such as unverified magnification in food chains at post-restriction residues—against documented agricultural imperatives, evidenced by economic assessments of analogous organochlorine cancellations like DDT, which projected average annual U.S. losses of $15 million from reduced pest control efficacy and yield shortfalls in crops reliant on soil insecticides.[105] Similar analyses for restricted insecticides, including chlordane, quantified farm-level costs at $1.84 million in 1971 alone due to heightened pest pressures and the need for more frequent or costlier substitutes, suggesting that aldrin's prohibition may have imposed verifiable productivity declines in termite and soil pest management without commensurate reductions in verified human health incidents.[106][107]

References

  1. Aldrin | C12H8Cl6 | CID 12310947 - PubChem - NIH
  2. Table 4-1, Chemical Identity of Aldrin and Dieldrina - NCBI - NIH
  3. Aldrin (Ref: OMS 194) - AERU - University of Hertfordshire
  4. All POPs listed in the Stockholm Convention
  5. Aldrin/Dieldrin - Toxic Substance Portal - CDC
  6. [PDF] Toxicological Profile for Aldrin/Dieldrin
  7. [PDF] Health Effects Support Document for Aldrin/Dieldrin - EPA
  8. Pesticide Fact Sheet: Aldrin - epa nepis
  9. Aldrin - the NIST WebBook
  10. Theoretical Study of the Diastereofacial Isomers of Aldrin and Dieldrin
  11. (IUCr) Crystallographic data for aldrin C12H8Cl6
  12. Mechanisms of thermal decomposition of cyclodiene pesticides ...
  13. The EFSA Journal (2005) 285, 1
  14. Aldrin and Dieldrin (EHC 91, 1989) - INCHEM
  15. Table 4-2, Physical and Chemical Properties of Aldrin and Dieldrina
  16. ICSC 0774 - ALDRIN - Inchem.org
  17. [PDF] Aldrin and Dieldrin - à www.publications.gc.ca
  18. ALDRIN | 309-00-2 - ChemicalBook
  19. Diels-Alder additions of hexachlorocyclopentadiene to some 7 ...
  20. [PDF] Toxicological Profile for Aldrin/Dieldrin
  21. [PDF] Aldrin and Dieldrin: A Review of Research on Their Production ...
  22. [PDF] Aldrin
  23. Aldrin (Ref: OMS 194) - AERU
  24. http://www.pic.int/Portals/5/download.aspx?d=UNEP-FAO-RC-DGD-GUID-Aldrin-1991.En.pdf
  25. [PDF] Contaminant Candidate List Regulatory Determination Support ...
  26. [PDF] PUBLIC HEALTH STATEMENT ALDRIN AND DIELDRIN
  27. [PDF] Past Use of Chlordane, Dieldrin, and other Organochlorine ...
  28. Microbial Degradation of Aldrin and Dieldrin - PubMed Central - NIH
  29. Mechanisms of Action, Resistance and Toxicity of Insecticides ...
  30. Differential actions of fipronil and dieldrin insecticides on GABA ...
  31. Differential Actions of Fipronil and Dieldrin Insecticides on GABA ...
  32. Variations in the Insect GABA Receptor, RDL, and Their Impact on ...
  33. Full article: Ion channels as insecticide targets
  34. Aldrin (PIM 573) - INCHEM
  35. ION CHANNELS AS TARGETS FOR INSECTICIDES - Annual Reviews
  36. Structural model for γ-aminobutyric acid receptor noncompetitive ...
  37. Tert Butylbicyclophosphorothioate - an overview - ScienceDirect.com
  38. Ion channels as insecticide targets - PMC - PubMed Central
  39. Insecticide Actions on Gaba Receptors and Voltage-Dependent ...
  40. Cytochromes P450 and insecticide resistance - ScienceDirect.com
  41. Aldrin Epoxidation in Flathead Mullet (Mugil cephalus): Possible ...
  42. Aldrin intoxication and clearance of associated dieldrin residues in a ...
  43. Mechanistic and Other Relevant Data - Pentachlorophenol ... - NCBI
  44. [PDF] Toxicological Profile for Aldrin/Dieldrin
  45. APPENDIX 3 Fact sheets on pesticides
  46. [PDF] Update of Human Health Ambient Water Quality Criteria: Aldrin 309 ...
  47. Aldrin - an overview | ScienceDirect Topics
  48. Historical and post-ban releases of organochlorine pesticides ...
  49. The 12 initial POPs under the Stockholm Convention
  50. [PDF] DigitalCommons@University of Nebraska - Lincoln
  51. CHANGING ROLE OF INSECTICIDES IN CROP PROTECTION
  52. [PDF] Persistence of Organochlorine Insecticides for Formosan ... - CTAHR
  53. 404 Not Found
  54. Report of the Aldrin/Dieldrin Advisory Committee to William D ...
  55. Criteria Document: Aldrin/Dieldrin
  56. value of insecticidal seed treatments for US rice farmers
  57. Effects on Populations of Corn Rootworms of Aldrin Residues in Soil ...
  58. [PDF] Further Tests of Band Placement of Insecticides for Clover Root ...
  59. [PDF] Pesticide Use in U.S. Agriculture: 21 Selected Crops, 1960-2008
  60. The Use of Insecticides to Manage the Western Corn Rootworm ...
  61. SOIL INSECTS THEIR CONTROLl - Annual Reviews
  62. [PDF] Agricultural Pesticide Use Trends and Policy Issues - AgEcon Search
  63. ALDRIN/DIELDRIN - An Assessment of the Health Risks of ... - NCBI
  64. Aldrin - IDLH | NIOSH - CDC
  65. [PDF] Toxicological Profile for Aldrin/Dieldrin
  66. Cancer mortality in workers exposed to dieldrin and aldrin - PubMed
  67. Monograph: Reassessment of human cancer risk of aldrin/dieldrin
  68. Occupational exposure to aldrin: clinical and laboratory findings
  69. Mortality study of industrial workers exposed to aldrin, dieldrin and ...
  70. [PDF] DECISION GUIDANCE DOCUMENTS
  71. Toxicity of Aldrin to Chickens<sup>1</sup>
  72. [PDF] Ambient Aldrin/Dieldrin - EPA
  73. Aldrin/Dieldrin: Ambient Water Quality Criteria - epa nepis
  74. ADEQUACY OF THE DATABASE - Toxicological Profile for Aldrin ...
  75. Biological Magnification and Degradation of DDT and Aldrin by ...
  76. [PDF] Mortality from the pesticides aldrin and dieldrin in British ...
  77. Mortality from the pesticides aldrin and dieldrin in British ...
  78. [PDF] Organochlorines, Reproductive Impairment and Declines in Bald ...
  79. Changes in Productivity and Environmental Contaminants in Bald ...
  80. [PDF] ToxGuide for Aldrin and Dieldrin
  81. PESTICIDE WAREHOUSE III | Superfund Site Profile - gov.epa.cfpub
  82. Factors influencing organochlorine pesticides distribution in the ...
  83. [PDF] Ecological Soil Screening Levels for Dieldrin
  84. [PDF] 5.4 Fate and Effects of Aldrin/ Dieldrin in ... - Scope
  85. Guidance for the Reregistration of Pesticide Products Containing ...
  86. LABEL ON PESTICIDE DECERTIFIED BY U.S. - The New York Times
  87. Dieldrin - OEHHA - CA.gov
  88. Persistent Organic Pollutants: A Global Issue, A Global Response
  89. [PDF] Stockholm Convention on Persistent Organic Pollutants Elimination ...
  90. Chemicals subject to PIC - ECHA - European Union
  91. Banned and authorised - PAN Europe
  92. Organochlorine pesticide contamination of foods in Africa
  93. Microbial Degradation of Aldrin and Dieldrin - Frontiers
  94. Persistent Organic Pollutants: A Global Health Threat - ACTenviro
  95. Occurrence of emerging and persistent organic pollutants in ...
  96. [PDF] The Effectiveness {If Four Insecticides Applied at Planting for the ...
  97. [PDF] COTTON INSECTS THEIR CONTROL INSECTICIDES
  98. [PDF] PESTICIDE USAGE IN THE UNITED STATES - USDA NIFA
  99. Controversy over New Pesticide Regulations - Science
  100. EPA firm on pesticides ban - Nature
  101. Why animal studies are often poor predictors of human reactions to ...
  102. Extrapolation of animal toxicity data to man - PubMed
  103. Estimating the government health-care costs of treating pesticide ...
  104. Organochlorine pesticides, their toxic effects on living organisms ...
  105. EPA Pesticide Cancellations/Suspensions: a Survey of Economic ...
  106. [PDF] economic impact of discontinuing farm use of chlordane
  107. [PDF] indiana farm-level impacts of possible
User Avatar
No comments yet.