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CAS 1 record

CAS 103361-09-7

CAS 103361-09-7 matches 1 EU annex record across Annex II–VI of Regulation 1223/2009.

Chemical identity and properties

PubChem 2D chemical structure for CAS 103361-09-7
CAS 103361-09-7PubChem CID 92425

Flumioxazin

Flumioxazin is a benzoxazine that is N-(prop-2-yn-1-yl)-2H-1,4-benzoxazin-3(4H)-one which is substituted at position 6 by a 1,3-dioxo-1,3,4,5,6,7-hexahydro-2H-isoindol-2-yl group and at position 7 by a fluorine. A protoporphyrinogen oxidase inhibitor, it is used for the control of weeds in soya, peanuts, and a variety of vegetable and fruit crops. It has a role as a herbicide, an agrochemical, a teratogenic agent and an EC 1.3.3.4 (protoporphyrinogen oxidase) inhibitor. It is a dicarboximide, an organofluorine compound, a benzoxazine and a terminal acetylenic compound. ChEBI

IUPAC name
2-(7-fluoro-3-oxo-4-prop-2-ynyl-1,4-benzoxazin-6-yl)-4,5,6,7-tetrahydroisoindole-1,3-dione
Molecular formula
C19H15FN2O4
Molecular weight
354.3 g/mol
Exact mass
354.10158513 Da
XLogP3
1.8
Topological polar surface area
66.9 Ų
Hydrogen-bond donors
0
Hydrogen-bond acceptors
5
Covalent units
1
Defined stereocentres
0

Also known as

SumisoyaS-53482VALORS 53482V 53482EINECS Annex I Index 613-166-00-XL0PX7OGI22CHEBI:8939
16 more reported names
7-Fluoro-6-(3,4,5,6-tetrahydrophthalimido)-4-(2-propynyl)-1,4-benzoxazin-3(2H)-one7-fluoro-6-((3,4,5,6-tetrahydro)phthalimido)-4-(2-propynyl)-1,4-benzoxazin-3(2 H)-oneV-53482n-(7-fluoro-3,4-dihydro-3-oxo-4-prop-2-ynyl-2h-1,4-benzoxazin-6-yl)cyclohex-1-ene-1,2-dicarboxamide2-(7-fluoro-3-oxo-4-(prop-2-yn-1-yl)-3,4-dihydro-2H-1,4-benzoxazin-6-yl)-2,3,4,5,6,7-hexahydro-1H-isoindole-1,3-dione2-[7-fluoro-3-oxo-4-(prop-2-yn-1-yl)-3,4-dihydro-2H-1,4-benzoxazin-6-yl]-2,3,4,5,6,7-hexahydro-1H-isoindole-1,3-dioneRefChem:1408481H-Isoindole-1,3(2H)-dione, 2-(7-fluoro-3,4-dihydro-3-oxo-4-(2-propyn-1-yl)-2H-1,4-benzoxazin-6-yl)-4,5,6,7-tetrahydro-Flumioxazin [ISO]Sumisoya; V 534822-[7-Fluoro-3,4-dihydro-3-oxo-4-(2-propyn-1-yl)-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dioneFlumioxazineFlumizinFlumioxazin Solution in Acetonitrile1H-Isoindole-1,3(2H)-dione,2-[7-fluoro-3,4-dihydro-3-oxo-4-(2-propynyl)-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-2-[7-fluoro-3-oxo-4-(prop-2-yn-1-yl)-3,4-dihydro-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione
External database identifiers

Evidence from additional scientific databases

EMBL-EBI ChEBI
Exact identifier matchCHEBI:8939

flumioxazin

A benzoxazine that is N-(prop-2-yn-1-yl)-2H-1,4-benzoxazin-3(4H)-one which is substituted at position 6 by a 1,3-dioxo-1,3,4,5,6,7-hexahydro-2H-isoindol-2-yl group and at position 7 by a fluorine. A protoporphyrinogen oxidase inhibitor, it is used for the control of weeds in soya, peanuts, and a variety of vegetable and fruit crops.

Formula
C19H15FN2O4
Average mass
354.337 g/mol
Monoisotopic mass
354.10159 Da
Formal charge
0
  • benzoxazine — is a (CHEBI:46969)
  • terminal acetylenic compound — is a (CHEBI:73477)
  • dicarboximide — is a (CHEBI:35356)
  • organofluorine compound — is a (CHEBI:37143)
  • teratogenic agent — has role (CHEBI:50905)
  • herbicide — has role (CHEBI:24527)
  • agrochemical — has role (CHEBI:33286)
  • EC 1.3.3.4 (protoporphyrinogen oxidase) inhibitor — has role (CHEBI:73192)
  • teratogenic agent — has role (CHEBI:50905)
  • herbicide — has role (CHEBI:24527)
  • agrochemical — has role (CHEBI:33286)
  • EC 1.3.3.4 (protoporphyrinogen oxidase) inhibitor — has role (CHEBI:73192)
  • benzoxazine — is a (CHEBI:46969)
  • terminal acetylenic compound — is a (CHEBI:73477)
  • dicarboximide — is a (CHEBI:35356)
  • organofluorine compound — is a (CHEBI:37143)
Additional curated names
2-[7-fluoro-3-oxo-4-(prop-2-yn-1-yl)-3,4-dihydro-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione2-[7-fluoro-3,4-dihydro-3-oxo-4-(2-propyn-1-yl)-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione7-fluoro-6-(3,4,5,6-tetrahydrophthalimido)-4-(2-propynyl)-1,4-benzoxazin-3(2H)-oneN-(7-fluoro-3,4-dihydro-3-oxo-4-prop-2-ynyl-2H-1,4-benzoxazin-6-yl)cyclohex-1-ene-1,2-dicarboxamideflumioxazineS 53482S-53482V 53482
Cross-references from this source
  • CAS: 103361-09-7 — Alan Wood's Pesticides
  • CAS: 103361-09-7 — KEGG COMPOUND
  • CAS: 103361-09-7 — ChemIDplus
  • MANUAL_X_REF: 335 — PPDB
  • MANUAL_X_REF: C11035 — KEGG COMPOUND
  • MANUAL_X_REF: flumioxazin — Alan Wood's Pesticides
  • MANUAL_X_REF: HMDB0034854 — HMDB
  • REGISTRY_NUMBER: 8290535 — Reaxys

Mapped by: Exact CAS cross-reference in the ChEBI compound record. Source updated: 2017-08-11. Retrieved: 2026-08-31. Open source record

NIH PubChem PUG-View
Exact identifier match92425

Attributed physical-property, hazard, environmental and use annotations.

  • Environmental Bioconcentration: An estimated BCF of 18 was calculated for flumioxazin(SRC), using an experimental log Kow of 2.55(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is low(SRC). Source: Hazardous Substances Data Bank (HSDB)
  • Environmental Fate: TERRESTRIAL FATE: Based on column leaching studies and the short aerobic soil half-life, the potential for flumioxazin to leach in field agricultural soil is low(1). In soils that have been treated with flumioxazin, it is generally not found below 3 inches in depth(2). Volatilization losses from soil surfaces are negligible(1). Flumioxazin degrades rapidly in soil water via hydrolysis with half-lives of 3.4 to 5.1 days at pH 5.0, 21.4-24.6 hours at pH 7.0, and 14.6-22.0 minutes at pH 9.0(1); therefore, aqueous hydrolysis in moist soils will be an important fate process(SRC). Microbial degradation in soil is also an important fate process(1); the half-life for aerobic soil metabolism is 11.9 to 17.5 days, with an average of 14.7 days(1,2). The photolysis half-life on soil is 3.2 to 8.4 days (average 5.8 days)(2). The rapid soil dissipation rate indicates flumioxazin is not persistent in soil(1). Source: Hazardous Substances Data Bank (HSDB)
  • Environmental Fate: AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 13000(SRC), determined from a structure estimation method(2), indicates that flumioxazin is expected to adsorb to suspended solids and sediment(SRC). The hydrolytic degradation half-life of flumioxazin in soil water is 3.4 to 5.1 days at pH 5.0, 21.4-24.6 hours at pH 7.0, and 14.6-22.0 minutes at pH 9.0(3); therefore, hydrolysis will be the major degradation process in water(SRC). An anaerobic aquatic metabolism half-life of 0.2 days has been reported(4). The photolysis half-life in water at pH 5 is 1 day(4). Volatilization from water surfaces is expected to be slow(5) based upon an estimated Henry's Law constant of 6.28X10-7 atm-cu m/mole(SRC), derived from its vapor pressure, 2.41X10-6 mm Hg(6), and water solubility, 1.79 mg/l(4). Using this estimated Henry's Law constant and an estimation method(5), volatilization half-lives for a model river and model lake are 1,765 hours and 809 days, respectively(SRC). According to a classification scheme(7), an estimated BCF of 18(SRC), from a log Kow of 2.55(4) suggests the potential for bioconcentration in aquatic organisms is low(SRC). Source: Hazardous Substances Data Bank (HSDB)
  • Environmental Fate: ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), flumioxazin, which has a vapor pressure of 2.41X10-6 mm Hg at 25 °C (2), will exist in both the vapor and particulate phases in the ambient atmosphere. Vapor-phase flumioxazin is degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals(SRC); the half-life for this reaction in air is estimated to be 6.8 hours(SRC), calculated from its rate constant of 5.68X10-11 cu cm/molecule-sec at 25 °C(SRC) (that was derived using a structure estimation method(3). Particulate-phase flumioxazin may be removed from the air by wet and dry deposition(SRC). Source: Hazardous Substances Data Bank (HSDB)

Mapped by: Existing checksum-valid CAS to unique PubChem CID match. Retrieved: 2026-08-31. Open source record

Scientific classifications and hazard annotations provide context and do not replace the market-specific regulatory decision shown above.

Additional source coverage and match status
SourceResultChecked
EMBL-EBI ChEBIExact match2026-08-31
NIH PubChem PUG-ViewExact match2026-08-31

A recorded no-match is useful evidence that the source was checked; it is not a claim that the substance does not exist elsewhere.

Retrieved from NIH PubChem on 2026-09-02 by checksum-valid CAS matching. Chemical properties do not replace the regulatory decision on this page.

Records for CAS 103361-09-7

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CAS 103361-09-7 is the Chemical Abstracts Service identifier used to pin this page to a specific substance. In the current dataset, 1 EU annex record shares this identifier, which helps you cross-check whether the same substance appears under one regulatory context or several.

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