enilconazole

{{Distinguish|Econazole}}

{{chembox

| Verifiedfields = changed

| Watchedfields = changed

| verifiedrevid = 414454456

| ImageFile = Enilconazole.svg

| ImageName = Chemical structure of enilconazole

| ImageFile2 = Imazalil 3D BS.png

| ImageName2 = Chemical structure of enilconazole 3D

| PIN = 1-{2-(2,4-Dichlorophenyl)-2-[(prop-2-en-1-yl)oxy]ethyl}-1H-imidazole

| OtherNames = 1-[2-(Allyloxy)-2-(2,4-dichlorophenyl)ethyl]-1H-imidazole
Imazalil
Chloramizole

| Section1 = {{Chembox Identifiers

| ChemSpiderID_Ref = {{chemspidercite|correct|chemspider}}

| ChemSpiderID = 34116

| UNII_Ref = {{fdacite|correct|FDA}}

| UNII = 6K0NOF3XQ6

| InChI = 1/C14H14Cl2N2O/c1-2-7-19-14(9-18-6-5-17-10-18)12-4-3-11(15)8-13(12)16/h2-6,8,10,14H,1,7,9H2

| InChIKey = PZBPKYOVPCNPJY-UHFFFAOYAI

| ChEMBL_Ref = {{ebicite|correct|EBI}}

| ChEMBL = 356918

| StdInChI_Ref = {{stdinchicite|correct|chemspider}}

| StdInChI = 1S/C14H14Cl2N2O/c1-2-7-19-14(9-18-6-5-17-10-18)12-4-3-11(15)8-13(12)16/h2-6,8,10,14H,1,7,9H2

| StdInChIKey_Ref = {{stdinchicite|correct|chemspider}}

| StdInChIKey = PZBPKYOVPCNPJY-UHFFFAOYSA-N

| CASNo_Ref = {{cascite|correct|CAS}}

| CASNo = 35554-44-0

| PubChem = 37175

| KEGG_Ref = {{keggcite|correct|kegg}}

| KEGG = D03997

| ChEBI_Ref = {{ebicite|changed|EBI}}

| ChEBI = 81927

| SMILES = Clc1ccc(c(Cl)c1)C(OCC=C)Cn2ccnc2

}}

| Section2 = {{Chembox Properties

| C=14 | H=14 | Cl=2 | N=2 | O=1

| Appearance=Slightly yellow to brown solidified oil{{cite web | title = Pesticide Information Profile: Imazalil | url = http://extoxnet.orst.edu/pips/imazalil.htm | publisher = Extension Toxicology Network}}

| Density = 1.23 g/mL

| MeltingPtC = 50

| MeltingPt_ref =

| BoilingPtC = 347

| BoilingPt_ref = {{GESTIS|ZVG=496439}}

| Solubility = 1400 mg/L (20 °C)

}}

| Section6 = {{Chembox Pharmacology

| ATCvet = yes

| ATCCode_prefix = D01

| ATCCode_suffix = AC90

}}

| Section7 = {{Chembox Hazards

| MainHazards =

| FlashPtC = 181

| FlashPt_ref =

| AutoignitionPt =

| LD50 = 227 mg/kg (oral rat)
4200 mg/kg (dermal, rabbit)
16 mg/l/4 h (inhalation, rat)

}}

}}

Enilconazole (synonyms imazalil, chloramizole) is a fungicide widely used in agriculture, particularly in the growing of citrus fruits.{{cite journal |author1=Kaplan, H. J. |author2=Dave, B. A. | journal = Proceedings of the Florida State Horticultural Society | title = The current status of Imazalil: a post harvest fungicide for citrus | year = 1979 | volume = 92 | pages = 37–43}} Trade names include Freshgard, Fungaflor, and Nuzone.

Enilconazole is also used in veterinary medicine as a topical antimycotic.[https://wayback.archive-it.org/all/20120226045524/http://www.ema.europa.eu/pdfs/vet/mrls/049698en.pdf EMA Committee for Veterinary Products: Enilconazole]

History

In 1983, enilconazole was first introduced by Janssen Pharmaceutica and it has since consistently been registered as an antifungal postharvest agent.{{Cite journal | title = R.E.D. Facts: Imazalil | url = http://archive.epa.gov/pesticides/reregistration/web/pdf/2325fact.pdf | publisher = Environmental Protection Agency | date = February 2005}} Shortly after its introduction, enilconazole was used for seed treatment in 1984 and later used in chicken hatcheries in 1990. Like any fungicide, it was used to protect crops from becoming diseased and unable to yield a profitable harvest. Today, it continues to be utilized as an agricultural aid for its contribution to maintaining crop integrity and production output.{{cn|date=December 2022}}

Use on crops

Enilconazole is found on a wide variety of fruits and vegetables, but it is primarily used on tubers for storage.{{cite web | url = http://www.certiseurope.com/our-products/imazalil.html | publisher = Certis Europe | title = Imazalil | access-date = 2013-04-18 | archive-date = 2018-04-05 | archive-url = https://web.archive.org/web/20180405050427/http://www.certiseurope.com/our-products/imazalil.html | url-status = dead }} Common fungi that are attracted to tubers are Fusarium spp, Phoma spp, and Helminthosporium solani which depreciate the crop quality. In 1984, when enilconazole was initially used for seed treatment, barley was a main target to mitigate crop loss due to disease.

In addition, the antifungal agent is commonly used on citrus fruits.

In the EU its use as a fungicide is permitted within some limits and imported fruits may contain limited amounts.

{{CELEX|32019R1582|text=Commission Regulation (EU) 2019/1582 of 25 September 2019 amending Annexes II and III to Regulation (EC) No 396/2005 of the European Parliament and of the Council as regards maximum residue levels for imazalil in or on certain products}}

Hazards

{{Globalize|section|USA|2name=the United States|date=August 2018}}

In 1999, based on studies in rodents, enilconazole was identified as "likely to be carcinogenic in humans" under The Environmental Protection Agency's Draft Guidelines for Carcinogenic Assessment. However, because pesticide residues are well below the concentrations associated with risk, the lifetime cancer risk estimate associated with citrus fruit contamination was valued as insignificant.

The EPA has established an equivalent toxicity level for human exposure at 6.1 x 10−2 mg/kg/day. This level placed it in Category II, II, and IV for oral, dermal, and inhalation toxicity respectively. Category I is classified as highly irritating to the eyes, but not to the skin. As for oral toxicity, when the fungicide is transferred via food into the body, it must be metabolized before it can do any damage.

Under California's Proposition 65, enilconazole is listed as "known to the State to cause cancer".[http://www.oehha.org/prop65.html Proposition 65] {{Webarchive|url=https://web.archive.org/web/20190729170906/http://www.oehha.org/prop65.html |date=2019-07-29 }}, Office of Environmental Health Hazard Assessment

The EPA determined there is no substantial risk of enilconazole toxicity through food and water exposure. Enilconazole has a very minute degree of mobility, so its level of drinking water contamination is quite low. The estimated environmental concentration (EEC) found the levels to be 0.072 ppb for surface water, which is much less than the 500 ppb comparison level for drinking water.

References

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