Dinoseb

Last updated
Dinoseb
Dinoseb Grundstruktur V1-Seite001.svg
Names
Preferred IUPAC name
2-(Butan-2-yl)-4,6-dinitrophenol
Other names
2-(sec-Butyl)-4,6-dinitrophenol
Identifiers
3D model (JSmol)
ChEBI
ChemSpider
ECHA InfoCard 100.001.692 OOjs UI icon edit-ltr-progressive.svg
KEGG
PubChem CID
UNII
  • InChI=1S/C10H12N2O5/c1-3-6(2)8-4-7(11(14)15)5-9(10(8)13)12(16)17/h4-6,13H,3H2,1-2H3 Yes check.svgY
    Key: OWZPCEFYPSAJFR-UHFFFAOYSA-N Yes check.svgY
  • InChI=1/C10H12N2O5/c1-3-6(2)8-4-7(11(14)15)5-9(10(8)13)12(16)17/h4-6,13H,3H2,1-2H3
    Key: OWZPCEFYPSAJFR-UHFFFAOYAU
  • [O-][N+](=O)c1cc(cc(c1O)C(CC)C)[N+]([O-])=O
Properties
C10H12N2O5
Molar mass 240.215 g·mol−1
Density 1.35 g/cm3
Melting point 38–42 °C (100–108 °F; 311–315 K)
Acidity (pKa)4.4 [1]
Hazards
GHS labelling:
GHS-pictogram-skull.svg GHS-pictogram-silhouette.svg GHS-pictogram-pollu.svg GHS-pictogram-acid.svg
Danger
H300, H311, H315, H317, H318, H360, H410 [2]
P201, P273, P280, P302+P352, P305+P351+P338, P310 [2]
Safety data sheet (SDS) [2]
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
X mark.svgN  verify  (what is  Yes check.svgYX mark.svgN ?)

Dinoseb is a common industry name for 6-sec-butyl-2,4-dinitrophenol, a herbicide in the dinitrophenol family. It is a crystalline orange solid which does not readily dissolve in water. Dinoseb is banned as an herbicide in the European Union (EU) and the United States because of its toxicity.

Contents

It also finds use as a polymerisation inhibitor, where it is often referred to as DNBP. It is used to prevent the thermally induced polymerisation of styrene and other unsaturated monomers when they are being purified by distillation.

History

In 1892, dinitro-ortho-cresol (2,4-dinitro-6-methylphenol), a chemical compound closely related to dinoseb, was discovered in Germany and first used as an insecticide. It was later also used as an herbicide and also fungicide after those characteristics were discovered. In 1945 the ortho-methyl group was replaced by a sec-butyl group, producing dinoseb. This compound had a superior contact and stomach activity on insects and mites. [3] Dinoseb became commercially available in 1945 and was approved for use in the United States based on safety data from Industrial Bio-Test Laboratories. [4] On January 13, 1984 the Danish ship Dana Optima lost 80 drums of Dinoseb during their trip from North Shields, England to Esbjerg, Denmark. After four months 72 drums were found and recovered. [5] Dinoseb was withdrawn from the market in 1986 due to an increased threat of birth defects after female field workers were exposed to the chemical. It could also cause sterility in men who were exposed to the chemical. [6]

Uses

Dinoseb is an herbicide that was once widely used for weed-control when producing crops like soybeans, vegetables, fruits and nuts, or citrus. In the present, dinoseb is banned in the EU, and the United States due to its high toxicity. However, dinoseb is still used in China for example; evidenced by the fact that it is found in rain- and drinking water. Nowadays there are other, safer herbicides that can be used. [7] Dinoseb was also used as an insecticide to protect grapes. On the internet, dinoseb and other dinitrophenols are bought as weight-loss pills. It is very dangerous however, and many people have died of accidental overdose. [8]

Mechanism of action

Dinoseb is an uncoupler of oxidative phosphorylation. It is a weak acid that can pass through lipid membranes when it's in the undissociated form.

Dinoseb metabolism.png

It uses this property to transport protons through the inner mitochondrial membrane (IMM). [9] Protons are taken up from the intermembrane space and after transport through the IMM, they are released again in the mitochondrial matrix. Dinoseb in the dissociated form is negatively charged, which causes it to move to the intermembrane space because of the electrochemical gradient that exists across the IMM. The negative charge is delocalized over the ring, increasing the anion's membrane permeability.

By lowering the proton gradient, dinoseb removes the cell's ability to produce ATP, resulting in the death of the cell.

Dinoseb is also a weak inhibitor of mitochondrial Complex III [10] and Complex II of the repiratory chain. [11]

In plants, dinoseb also inhibits photosynthesis by inhibiting the electron flow from photocomplex II to plastoquinone. [12] As a result, the plastoquinone can't create a proton gradient and no ATP is produced by the ATP synthase. Also, NADP can't be reduced to form NADPH, which removes the ability to create glucose from carbon dioxide. This also leads to cell death.

Metabolism and biotransformation

The mechanism of plants to produce ATP. Photocomplex II is inhibited by dinoseb, so NADP cannot be reduced to NADPH and the ability to create glucose from carbondioxide is removed. Thylakoid membrane 3.svg
The mechanism of plants to produce ATP. Photocomplex II is inhibited by dinoseb, so NADP cannot be reduced to NADPH and the ability to create glucose from carbondioxide is removed.

After oral administration of dinoseb tagged with 14C to rats and mice, it turned out that 40 to 65% of the 14C was excreted in the urine and 30 to 40% ended up in the feces. TLC data showed the presence of different metabolites of dinoseb, although these were not identified. [13] This finding was confirmed by different in vitro and in vivo studies.

During one study, 14C-dinoseb was administered to pregnant mice. The data showed that the rate of absorption after intraperitoneal administration was much higher than after an oral administration. Furthermore, molecules containing 14C were found in all tissues of the mother and the embryo, although the embryonic tissues contained a lower concentration.

Three hours after oral or intraperitoneal administration, the 14C in the kidneys and liver of the mother was about 50% dinoseb and 50% metabolites. However, the 14C in the kidneys and liver of the embryo was 85% dinoseb after oral administration and 57% after intraperitoneal administration.

Toxicity

Dinoseb is highly toxic when ingesting, inhaling or at skin contact. Symptoms include fatigue, sweating, headaches, nausea, stomach aches and fever. [14] It is also an irritant for the eyes. Skin contact causes burns and it turns yellow. For pregnant women this substance is especially dangerous as it can cause growth defects in unborn children (it is teratogenic).

Dinoseb interferes with the oxidative phosphorylation by acting as an uncoupler, which is the production of ATP in the mitochondria. This is done by making the inner membrane of the mitochondria more permeable to protons. The protons can return to the mitochondrial matrix more easily, which results in a lower difference in proton concentration on either side of the inner mitochondrial membrane. In other words: The proton gradient is lower, so the membrane potential will be lower. As the membrane potential is the driving force for the production of ATP, the cell is unable to produce energy. [15]

Exposure to dinoseb also induces ER-mediated calcium release, resulting in increased intracellular calcium levels. This is followed by activation of caspase, which is a protease involved in cell apoptosis. The surviving cells have an increase of alpha-synuclein levels which leads to dopaminergic neurodegeneration. [7]

Dinoseb can cross biological membranes like the blood-brain barrier and the placental barrier. This explains why dinoseb is particularly dangerous for pregnant women. If the compound can pass the placental barrier, the unborn child will be exposed to dinoseb via the blood of the mother. [7]

Oral LD50 values of dinoseb range from 14 to 114 mg/kg in rats, mice, rabbits, and guinea pigs. [8] For humans, this is 5–50 mg/kg. [16]

Effects on animals

Dinoseb is not only a toxic compound for human but also for animals such as rats, fish and birds.

Rats: Dinoseb causes acute toxicity in rats after a single dose after circa fourteen days. About 50% of the rats die when they are given 25–28 mg/kg dinoseb orally. Much more is needed when the rats are exposed to dinoseb via the skin. In this case 50% dies when the rats are exposed to 80 mg/kg. When the dinoseb is injected a dose of 20 mg/kg will cause death of 50% of the rats. [16] But also for rats turned out dinoseb was capable to go through the placenta and therefore causes embryotoxic and teratogenic effects. [14]

Fish: Dinoseb is also highly toxic for fish, because fish are able to take up dinoseb very quickly. For small fish like goldfish only 0,4 ppm is needed to kill all fish in the water. When a fish lives in an acidic water environment dinoseb is more toxic than when a fish lives in a neutral or alkaline water environment. This is because dinoseb is slightly acidic. [17]

Birds: It was found that dinoseb was also highly toxic to birds. When birds are given a single dose between 7–9 mg/kg around 50% of the birds dies. The most birds are exposed to dinoseb via the small streams of water. [18]

Research has also shown that dinoseb is carcinogenic for female mice, but not for male mice. [18]

First aid measures

Nowadays dinoseb is banned in a lot of places in the world due to high incidences of birth defects. Because of this ban not a lot of people are exposed to dinoseb anymore. But when someone is exposed, a few things can be done as first aid. The victim can be exposed via four ways: inhalation, skin, eyes, ingestion. These are the first aid measures for the four ways of exposure:

Inhalation: The victim should get some fresh air. When needed the victim can be administered oxygen and assisted ventilation. Bronchospasm can be treated with beta2 agonist and corticosteroid aerosols.

Skin: The contaminated clothing and jewellery should be removed from the victim. The victim's skin, hair and nails should be washed thoroughly with soap several times.

Eyes: The victim's eyes should be immediately rinsed with running water. This is needed for at least 20 minutes. The contact lenses should be removed if possible.

Ingestion: The victim's mouth should be rinsed at first. The victim should be given charcoal as a slurry (240 ml water/30 g charcoal). This is only possible when the victim is conscious.

In all of the four cases the victim should see a doctor. [19]

Chemistry

Synthesis

The first step in the synthesis of dinoseb is the synthesis of 2-(1-methylpropyl)phenol from 1-butene and phenol. [20] First, 1-butene is protonated so that a secondary carbocation is formed. This can only happen under acidic conditions. The formed carbocation can undergo electrophilic aromatic substitution with phenol. The product of this reaction is 2-(1-methylpropyl)phenol.

Synthesis 1.jpg

The second step in the synthesis of dinoseb is the nitration of 2-(1-methylpropyl)phenol. First, the nitronium ion is formed from nitric acid and sulfuric acid. [21]

Synthesis 2.jpg

2-(1-methylpropyl)phenol takes up the nitronium ion to form the arenium ion, which has three resonance structures. Water can cleave off the additional proton to form a neutral compound. [21]

Synthesis of dinoseb step 3.jpg

The product of this reaction can undergo a second nitration to form dinoseb.

Synthesis 4.jpg

Stereoisomerism

Dinoseb is a racemic mixture of two enantiomers.

Dinoseb
(2 stereoisomers)
(S)-Dinoseb V1.svg
(S)-configuration
(R)-Dinoseb V1.svg
(R)-configuration

See also

Related Research Articles

<span class="mw-page-title-main">Cypermethrin</span> Chemical compound

Cypermethrin (CP) is a synthetic pyrethroid used as an insecticide in large-scale commercial agricultural applications as well as in consumer products for domestic purposes. It behaves as a fast-acting neurotoxin in insects. It is easily degraded on soil and plants but can be effective for weeks when applied to indoor inert surfaces. Exposure to sunlight, water and oxygen will accelerate its decomposition. Cypermethrin is highly toxic to fish, bees and aquatic insects, according to the National Pesticides Telecommunications Network (NPTN). It is found in many household ant and cockroach killers, including Raid, Ortho, Combat, ant chalk, and some products of Baygon in Southeast Asia.

<span class="mw-page-title-main">2,4-Dinitrophenol</span> Chemical compound

2,4-Dinitrophenol (2,4-DNP or simply DNP) is an organic compound with the formula HOC6H3(NO2)2. It has been used in explosives manufacturing and as a pesticide and herbicide.

<span class="mw-page-title-main">Ethion</span> Chemical compound

Ethion (C9H22O4P2S4) is an organophosphate insecticide. Ethion is known to affect a neural enzyme called acetylcholinesterase and prevent it from working.

<span class="mw-page-title-main">Amitraz</span> Chemical compound

Amitraz is a non-systemic acaricide and insecticide and has also been described as a scabicide. It was first synthesized by the Boots Co. in England in 1969. Amitraz has been found to have an insect repellent effect, works as an insecticide and also as a pesticide synergist. Its effectiveness is traced back on alpha-adrenergic agonist activity, interaction with octopamine receptors of the central nervous system and inhibition of monoamine oxidases and prostaglandin synthesis. Therefore, it leads to overexcitation and consequently paralysis and death in insects. Because amitraz is less harmful to mammals, amitraz is among many other purposes best known as insecticide against mite- or tick-infestation of dogs. It is also widely used in the beekeeping industry as a control for the Varroa destructor mite, although there are recent reports of resistance.

<span class="mw-page-title-main">Cetrimonium bromide</span> Chemical compound

Cetrimonium bromide, also known with the abbreviation CTAB, is a quaternary ammonium surfactant with a condensed structural formula [(C16H33)N(CH3)3]Br.

<span class="mw-page-title-main">Citrinin</span> Chemical compound

Citrinin is a mycotoxin which is often found in food. It is a secondary metabolite produced by fungi that contaminates long-stored food and it causes different toxic effects, like nephrotoxic, hepatotoxic and cytotoxic effects. Citrinin is mainly found in stored grains, but sometimes also in fruits and other plant products.

<span class="mw-page-title-main">Benzotrichloride</span> Chemical compound

Benzotrichloride (BTC), also known as α,α,α-trichlorotoluene, phenyl chloroform or (trichloromethyl)benzene, is an organic compound with the formula C6H5CCl3. Benzotrichloride is an unstable, colorless or somewhat yellowish, viscous, chlorinated hydrocarbon with a penetrating odor. Benzotrichloride is used extensively as a chemical intermediate for products of various classes, i.e. dyes and antimicrobial agents.

MPP<sup>+</sup> Chemical compound

MPP+ (1-methyl-4-phenylpyridinium) is a positively charged organic molecule with the chemical formula C12H12N+. It is a neurotoxin that acts by interfering with oxidative phosphorylation in mitochondria by inhibiting complex I, leading to the depletion of ATP and eventual cell death.

<span class="mw-page-title-main">Methiocarb</span> Chemical compound

Methiocarb is a carbamate pesticide which is used as an insecticide, bird repellent, acaricide and molluscicide since the 1960s. Methiocarb has contact and stomach action on mites and neurotoxic effects on molluscs. Seeds treated with methiocarb also affect birds. Other names for methiocarb are mesurol and mercaptodimethur.

<span class="mw-page-title-main">Microcystin-LR</span> Chemical compound

Microcystin-LR (MC-LR) is a toxin produced by cyanobacteria. It is the most toxic of the microcystins.

Dimethyl tetrachloroterephthalate (DCPA, with the main trade name Dacthal) is an organic compound with the formula C6Cl4(CO2CH3)2. It is the dimethyl ester of tetrachloroterephthalic acid, used as a preemergent herbicide with the ISO common name chlorthal-dimethyl. It kills annual grasses and many common weeds without killing sensitive plants such as turf grasses, flowers, fruits, vegetables, and cotton.

An uncoupler or uncoupling agent is a molecule that disrupts oxidative phosphorylation in prokaryotes and mitochondria or photophosphorylation in chloroplasts and cyanobacteria by dissociating the reactions of ATP synthesis from the electron transport chain. The result is that the cell or mitochondrion expends energy to generate a proton-motive force, but the proton-motive force is dissipated before the ATP synthase can recapture this energy and use it to make ATP. Uncouplers are capable of transporting protons through mitochondrial and lipid membranes.

<span class="mw-page-title-main">Sulfotep</span> Chemical compound

Sulfotep (also known as tetraethyldithiopyrophosphate and TEDP) is a pesticide commonly used in greenhouses as a fumigant. The substance is also known as Dithione, Dithiophos, and many other names. Sulfotep has the molecular formula C8H20O5P2S2 and belongs to the organophosphate class of chemicals. It has a cholinergic effect, involving depression of the cholinesterase activity of the peripheral and central nervous system of insects. The transduction of signals is disturbed at the synapses that make use of acetylcholine. Sulfotep is a mobile oil that is pale yellow-colored and smells like garlic. It is primarily used as an insecticide.

Methacrylonitrile, MeAN in short, is a chemical compound that is an unsaturated aliphatic nitrile, widely used in the preparation of homopolymers, copolymers, elastomers, and plastics and as a chemical intermediate in the preparation of acids, amides, amines, esters, and other nitriles. MeAN is also used as a replacement for acrylonitrile in the manufacture of an acrylonitrile/butadiene/styrene-like polymer. It is a clear and colorless liquid, that has a bitter almond smell.

<span class="mw-page-title-main">Ethoprophos</span> Chemical compound

Ethoprophos (or ethoprop) is an organophosphate ester with the formula C8H19O2PS2. It is a clear yellow to colourless liquid that has a characteristic mercaptan-like odour. It is used as an insecticide and nematicide and it is an acetylcholinesterase inhibitor.

<span class="mw-page-title-main">Imazaquin</span> Chemical compound

Imazaquin is an imidazolinone herbicide, so named because it contains an imidazolinone core. This organic compound is used to control a broad spectrum of weed species. It is a colorless or white solid, although commercial samples can appear brown or tan.

<span class="mw-page-title-main">EPN (insecticide)</span> Chemical compound

EPN is an insecticide of the phosphonothioate class. It is used against pests such as European corn borer, rice stem borer, bollworm, tobacco budworm, and boll weevil.

<span class="mw-page-title-main">Bentazon</span> Chemical compound

Bentazon is a chemical manufactured by BASF Chemicals for use in herbicides. It is categorized under the thiadiazine group of chemicals. Sodium bentazon is available commercially and appears slightly brown in colour.

Fish acute toxicity syndrome (FATS) is a set of common chemical and functional responses in fish resulting from a short-term, acute exposure to a lethal concentration of a toxicant, a chemical or material that can produce an unfavorable effect in a living organism. By definition, modes of action are characterized by FATS because the combination of common responses that represent each fish acute toxicity syndrome characterize an adverse biological effect. Therefore, toxicants that have the same mode of action elicit similar sets of responses in the organism and can be classified by the same fish acute toxicity syndrome.

<span class="mw-page-title-main">PR toxin</span> Chemical compound

Penicillin Roquefort Toxin is a mycotoxin produced by the fungi Penicillium roqueforti. In 1973, PR toxin was first partially characterized by isolating moldy corn on which the fungi had grown. Although its lethal dose was determined shortly after the isolation of the chemical, details of its toxic effects were not fully clarified until 1982 in a study with mice, rats, anesthetized cats and preparations of isolated rat auricles.

References

  1. Szeto, Sunny Y.; Price, Patricia M. (September 1991). "Persistence of pesticide residues in mineral and organic soils in the Fraser Valley of British Columbia". Journal of Agricultural and Food Chemistry. 39 (9): 1679–1684. doi:10.1021/jf00009a027.
  2. 1 2 3 Sigma-Aldrich Co., Dinoseb. Retrieved on 2020-03-24.
  3. Topliss, John (2012-12-02). Quantitative Structure-Activity Relationships of Drugs. Elsevier. p. 427. ISBN   9780323146876.
  4. Meyer, Carl (1998-12-29). Expert Witnessing: Explaining and Understanding Science. CRC Press. p. 149. ISBN   9780849311970.
  5. Bockholts, P.; Heidebrink, I. (2012-12-06). Chemical Spills and Emergency Management at Sea: Proceedings of the First International Conference on "Chemical Spills and Emergency Management at Sea", Amsterdam, the Netherlands, November 15–18, 1988. Springer Science & Business Media. pp. 325–328. ISBN   9789400908871.
  6. Times, Philip Shabecoff, Special To The New York (1986-10-08). "EMERGENCY ORDER BANS MUCH-USED PESTICIDE". The New York Times. ISSN   0362-4331 . Retrieved 2017-03-13.{{cite news}}: CS1 maint: multiple names: authors list (link)
  7. 1 2 3 Heusinkveld, Harm J.; van Vliet, Arie C.; Nijssen, Peter C. G.; Westerink, Remco H. S. (2016-06-11). "In vitro neurotoxic hazard characterisation of dinitrophenolic herbicides". Toxicology Letters. 252: 62–69. doi:10.1016/j.toxlet.2016.04.014. ISSN   1879-3169. PMID   27106277.
  8. 1 2 Zaharia, M.; Tudorachi, L.; Pintilie, O.; Drochioi, C.; Gradinaru, R.; Murariu, M. (2016). "Banned dinitrophenols still trigger both legal and forensic issues". Environmental Forensics. 17 (1): 120–130. doi:10.1080/15275922.2015.1133735. S2CID   112923764.
  9. Walker, C. H. (2001-04-26). Organic Pollutants: An Ecotoxicological Perspective. CRC Press. ISBN   9780748409617.
  10. Saitoh, I., Miyoshi, H., Shimizu, R., and Iwamura, H. (1992). "Comparison of structure of quinone redox site in the mitochondrial cytochrome-bc1 complex and photosystem II (QB site)". Eur. J. Biochem. 209 (1): 73–79. doi:10.1111/j.1432-1033.1992.tb17262.x. PMID   1327783.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  11. K S Oyedotun, B D Lemire (1997). "The Carboxyl Terminus of the Saccharomyces cerevisiae Succinate Dehydrogenase Membrane Subunit, SDH4p, Is Necessary for Ubiquinone Reduction and Enzyme Stability*". J Biol Chem. 272 (50): 31382–8. doi: 10.1074/jbc.272.50.31382 . PMID   9395469.
  12. Matsunaka, S.; Hutson, D. H.; Murphy, S. D. (2013-10-22). Mode of Action, Metabolism and Toxicology: Pesticide Chemistry: Human Welfare and the Environment. Elsevier. ISBN   9781483150451.
  13. Gunther, Francis A.; Gunther, Jane Davies (2012-12-06). Residue Reviews: Residues of Pesticides and Other Contaminants in the Total Environment. Springer Science & Business Media. ISBN   9781461393948.
  14. 1 2 "Dinoseb - Toxipedia". www.toxipedia.org. Retrieved 2017-03-13.
  15. Palmeira, C.M.; Moreno, A.J.; Madeira, V.M.C. (1994). "Interactions of Herbicides 2,4-D and Dinoseb with Liver Mitochondrial Bioenergetics". Toxicology and Applied Pharmacology. 127 (1): 50–57. doi:10.1006/taap.1994.1138. PMID   8048053.
  16. 1 2 Copius Peereboom, J.W. (1991). Hoe gevaarlijk zijn milieugevaarlijke stoffen?. pp. 179–183. ISBN   978-90-6009-477-8.
  17. "EXTOXNET PIP - DINOSEB". extoxnet.orst.edu. Retrieved 2017-03-13.
  18. 1 2 "Dinoseb". pmep.cce.cornell.edu. Retrieved 2017-03-13.
  19. "Material safety data sheets 222: Dinoseb" (PDF). Central Pollution Control Board. Retrieved 2017-03-16.
  20. Ashford, R.D. (1994). Ashford's Dictionary of Industrial Chemicals. London, England: Wavelength Publications Ltd. p. 159. ISBN   978-0-9522674-3-0.
  21. 1 2 "Chapter 21:Reactions of Aromatics". research.cm.utexas.edu. Retrieved 2017-03-13.