Abstracts
Flumioxazin
CAS No. 103361-09-7

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Adverse Effects

ACTIVITY: Herbicide (unclassified)

CAS Name: 2-[7-fluoro-3,4-dihydro-3-oxo-4-(2-propynyl)-2H-1,4-benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-isoindole-1,3(2H)-dione

Structure:


From Toxline at Toxnet

Congenital Anomalies 1995 Mar;35(1):123-32

Species difference in developmental toxicity of an N-phenylimide herbicide between rats and rabbits and sensitive period of the toxicity to rat embryos.

Kawamura S, Kato T, Matsuo M, Sasaki M, Katsuda Y, Hoberman AM, Yasuda M

Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., Osaka, Japan.

An N-phenylimide herbicide, S-53482, exhibited developmental toxicity in rats in the absence of maternal toxicity at a dose of 30 mg/kg. The developmental toxicities noted were embryolethality, teratogenicity (mainly ventricular septal defect (VSD) and wavy ribs) and growth retardation. In contrast to rats, the herbicide showed no developmental toxicity in rabbits even at a maternal toxic dose of 3,000 mg/kg. There was a remarkable species difference between rats and rabbits. A single dose of S-53482 was administered to pregnant rats on one of gestation days 11 through 15 (detection of plug = day 0). Day 12 of gestation was the most sensitive day for embryonic death, VSD, and decreased fetal body weight. It is likely that there is a common mechanism for the three types of developmental toxicity and that S-53482 does not produce VSD by its direct damage to embryonic heart tissue.


Toxicology and Applied Pharmacology, Vol. 141, No. 2, pages 520-525, 17 references, 1996

Species Difference in Protoporphyrin IX Accumulation Produced by an N-Phenylimide Herbicide in Embryos between Rats and Rabbits

Kawamura S, Kato T, Matsuo M, Katsuda Y, Yasuda M

Species differences in protoporphyrin-IX accumulation produced by an N-phenylimide herbicide were studied in rat and rabbit embryos. Rats and rabbits exhibit differences in developmental toxicity following treatment with the herbicide S-53482 (103361-09-7). S-53482 causes embryolethality, teratogenicity, and growth retardation in rats, while no developmental toxicity is seen in rabbits. The herbicidal activity of S-53482 is due to the photodynamic action of accumulated protoporphyrin-IX as a result of inhibition of protoporphyrinogen-oxidase, one of the key enzymes in prophyrin biosynthesis common to plants and animals as part of chlorophyll and heme synthesis. To determine if there is a link between developmental toxicity and enzyme inhibition, protoporphyrin-IX accumulations were investigated using embyros from Crj:CD-rats and JW-rabbits. Pregnant females were dosed with S-53482 at 1,000mg/kg on day 12 of gestation. Protoporphyrin-IX concentration was increased in rat embryos by two orders of magnitude when compared to that of untreated embryos. On the other hand, no increase in proporphyrin accumulation was seen in rabbit embryos. The authors conclude that the species differences in proporphyrin accumulation correspond very well to differences in developmental toxicity exhibited by S-53482.


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=9035345&dopt=Abstract

Teratology. 1996 Nov;54(5):237-44.

Histological changes in rat embryonic blood cells as a possible mechanism for ventricular septal defects produced by an N-phenylimide herbicide.

Kawamura S, Yoshioka T, Kato T, Matsuo M, Yasuda M.

Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., Osaka, Japan.

An N-phenylimide herbicide, S-53482, inhibits protoporphyrinogen oxidase, an enzyme common to chlorophyll and heme biosynthesis, and produces embryolethality, teratogenicity [mainly ventricular septal defects (VSD) and wavy ribs], and growth retardation in rats. In order to elucidate the mechanism of the developmental toxicity, in particular VSD, effects of the herbicide on rat embryonic blood cells were investigated histologically at the light and electron microscopic levels at 6, 12, 24, 36, and 48 h after oral administration of the chemical to pregnant rats on day 12 of gestation, the most sensitive day for toxicity. Electron and light microscopy demonstrated mitochondrial lesions, including abnormal iron deposits that were probably due to inhibition of heme biosynthesis, in erythroblasts derived from the yolk sac. Subsequently, degeneration of these erythroblasts occurred followed by erythrophagocytosis. Histologically hearts from exposed embryos had a thin ventricular wall, which may reflect a compensatory reaction to a loss of embryonic blood cells. Thus, the herbicide may induce VSD due to hematological dysfunction caused by the inhibition of heme biosynthesis rather than by direct injurious effects on the heart.

PMID: 9035345 [PubMed - indexed for MEDLINE]

 

http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?cmd=Retrieve&db=pubmed&dopt=Abstract&list_uids=15382510

Pest Manag Sci. 2004 Sep;60(9):939-43.

Hydrolysis and photolysis of flumioxazin in aqueous buffer solutions.

Kwon JW, Armbrust KL, Grey TL.

Mississippi State Chemical Laboratory, Mississippi State University, PO Box CR, Mississippi State, MS 39762-5622, USA.

To determine the degradation rates and degradation products of the herbicide flumioxazin in aqueous buffer solutions (pH 5, 7 and 9), its hydrolysis and photolysis were investigated at 30 degrees C in the dark, and in a growth chamber fitted with fluorescent lamps simulating the UV output of sunlight. The rate of hydrolysis of flumioxazin was accelerated by increasing pH. The t(1/2) values at pH 5, 7 and 9 were 16.4, 9.1 and 0.25 h, respectively. Two degradation products were detected and their structural assignments were made on the basis of LC-MS data. Degradation product I was detected in all buffer solutions while degradation product II was detected in acidic buffer only. Both degradation products appeared to be stable to further hydrolysis. After correcting for the effects of hydrolysis, the photolytic degradation rate also increased as a function of pH and was approximately 10 times higher at pH 7 than that at pH 5, showing t(1/2) values of 4.9 and 41.5 h, respectively. Degradation products formed by photolysis were the same as those formed by hydrolysis. Flumioxazin was degraded more extensively at high pH and should degrade in surface water.

PMID: 15382510 [PubMed - in process]


http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?cmd=Retrieve&db=pubmed&dopt=Abstract&list_uids=15234090

Environ Pollut. 2004 Sep;131(2):233-41.
 
Comparison of different physiological parameter responses in Lemna minor and Scenedesmus obliquus exposed to herbicide flumioxazin.

Geoffroy L, Frankart C, Eullaffroy P.

Laboratoire d'Eco-Toxicologie, Unite de recherche Vignes et Vins de Champagne, UPRES-EA 2069, Universite de Reims Champagne-Ardenne BP 1039, F51687 Reims 2, France.

The sensitivity of different physiological parameters in Scenedesmus obliquus and Lemna minor exposed to herbicide (flumioxazin) was investigated to indicate the most convenient and sensitive parameter. To assess toxicity of flumioxazin, we used a panel of biomarkers: pigment contents, chlorophyll fluorescence parameters and antioxidative enzyme activities. Algae and duckweed were exposed to 48-h IC50 for growth rate. In L. minor, the sensitivity of the parameters was as follows: QN > Oxygen emmision > phiS(PSII) > QP > phi(PSII) > CAT, GR > Pigment> APO > Growth. For S. obliquus, this ranking was as follows: CAT > Oxygen emission > QP > APO > GR > Pigment > phiS(PSII) > Growth > phi(PSII) > QN (from the greatest to the least sensitive). The results demonstrated that the observed toxicity is related not only to interspecific variations but also to the selected parameter.

PMID: 15234090 [PubMed - in process]


http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?cmd=Retrieve&db=pubmed&dopt=Abstract&list_uids=15084087

J AOAC Int. 2004 Jan-Feb;87(1):56-9.

Gas chromatographic/mass spectrometric determination of flumioxazin extracted from soil and water.

Ferrell JA, Vencill WK.

University of Georgia, Department of Crop and Soil Sciences, Athens, GA 30602, USA.

A method was developed for determining flumioxazin in soil and water. Recovery efficiencies for solid-phase extraction (SPE) of flumioxazin from deionized, well, and surface water were between 72 and 77%. SPE was superior to liquid-liquid extraction, using water-hexane and water-chloroform emulsions, which resulted in retrieval efficiencies of 25 and 22%, respectively. However, liquid-liquid extraction with ethyl acetate improved recovery of total flumioxazin to >64%. Extraction from soil samples by direct solvent/soil extraction methods recovered between 18 and 76% of applied flumioxazin, depending on the solvent combination used. However, the use of accelerated solvent extraction techniques resulted in a 106 +/- 8% recovery of flumioxazin from soil. In analysis by capillary gas chromatography with mass selective detection, flumioxazin had a calculated limit of detection of 9 ng/mL with a retention time of 16.66 min.

PMID: 15084087 [PubMed - in process]


http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?cmd=Retrieve&db=pubmed&dopt=Abstract&list_uids=14705902

J Agric Food Chem. 2003 Jul 30;51(16):4719-21.
 
Flumioxazin soil persistence and mineralization in laboratory experiments.

Ferrell JA, Vencill WK.

Department of Crop and Soil Sciences, University of Georgia, Athens, Georgia 30602.

Flumioxazin is an herbicide registered for use in soybean and peanut. However, few published papers concerning the soil persistence of flumioxazin are available. Therefore, laboratory studies were initiated to determine the half-life (t(1/2)) of flumioxazin in Greenville sandy clay loam and Tifton loamy sand soils when incubated at 15 and 25 degrees C. Results indicated that temperature had little effect on flumioxazin persistence. The t(1/2) for the Greenville soil was 17.9 and 16.0 days while the Tifton soil was 13.6 and 12.9 days, at 15 and 25 degrees C, respectively. These data correspond to the greater clay content of the Greenville soil (32%) as compared to the Tifton soil (2%). Therefore, the Greenville soil had greater soil adsorption and less flumioxazin was generally available to be degraded by soil microorganisms. In soils that were heat treated to reduce microbe populations, 99% of initial flumioxazin was accounted for after 16 days. Mineralization of flumioxazin, measured as (14)CO(2) evolution, was also greater in the Tifton soil (2.2% after 64 days) than in the Greenville soil (2.0% after 64 days). From these data, it was concluded that microbes were the most influential factor concerning the degradation of flumioxazin.

PMID: 14705902 [PubMed - in process]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=12919779&dopt=Abstract

Chemosphere. 2003 Oct;53(3):199-206.

Stress reactions in Vitis vinifera L. following soil application of the herbicide flumioxazin.

Saladin G, Magne C, Clement C.

Laboratoire de Biologie et Physiologie Vegetales, URVVC UPRES EA 2069, Universite de Reims Champagne Ardenne, UFR Sciences, Moulin de la Housse, BP 1039, F-51687 Cedex 2, Reims, France

In order to evaluate the stress effects of flumioxazin (fmx) on grapevine, a non-target plant (Vitis vinifera L.), physiological parameters such as carbohydrate content, water status or nitrogenous metabolites were investigated on fruiting cuttings and plants grown in vineyard. In the leaves of cuttings, the soil-applied herbicide induced stress manifestations including a decrease of the dry weight percentage and the soluble carbohydrate content during the first week after treatment. Thereafter, a decrease of the osmotic potential was observed, as well as a decrease of total protein content and a parallel accumulation of free amino acids, including proline. Altogether, these results suggest that soil-applied fmx induced a stress in grapevines, leading to leaf proteolysis. However, this stress was partially recovered 3 weeks after herbicide application, suggesting that the cuttings were capable to adapt to the fmx exposure. In the vineyard, the flumioxazin effects were still significant 5 months after the treatment, particularly in the CH cv. They included a decrease of the leaf dry weight percentage and soluble carbohydrate content, as well as an increase of the osmotic potential. The decrease of leaf soluble carbohydrates may have dramatic consequences for the berry growth and the reserve constitution. Moreover, treated plants were characterized by a decrease of the free amino acid content and an accumulation of ammonium, while the protein level did not significantly increase, suggesting a degradation of amino acids. The alteration of carbon and nitrogen status after herbicide treatment may affect the grapevine vigour in a long term.

PMID: 12919779 [PubMed - in process]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=12822940&dopt=Abstract

J Agric Food Chem. 2003 Jul 2;51(14):4017-22.

Effects of Flumioxazin Herbicide on Carbon Nutrition of Vitis vinifera L.

Saladin G, Magne C, Clement C.

Laboratoire de Biologie et Physiologie Vegetales, URVVC UPRES EA 2069, Universite de Reims Champagne-Ardenne, UFR Sciences, Moulin de la Housse, BP 1039, 51687 Reims Cedex 2, France.

To evaluate the impact of the herbicide flumioxazin (fmx) on nontarget grapevines, its effects were assessed on fruiting cuttings and field-grown plants. The stress caused by the herbicide differed according to the grapevine model. In cuttings, leaf gas exchange and photosynthetic pigment levels as well as hexose contents decreased, whereas sucrose and starch accumulated, suggesting an inhibition of photosynthesis and an increase of carbohydrate reserves as a response to the fmx-induced stress. Paradoxically, in the field-grown grapevine leaves, fmx caused a stimulation of photosynthesis, an accumulation of photosynthetic pigments and monosaccharides, in parallel with a mobilization of sucrose and starch. These results suggest that fmx reaches grapevine leaves via root uptake and has prolonged effects. In cuttings, fmx generated a toxic effect related to its target, whereas in field-grown plants, fmx had rather positive physiological effects and acts as a signal further stimulating photosynthesis and related parameters.

PMID: 12822940 [PubMed - in process]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=12789529&dopt=Abstract

Plant Cell Rep. 2003 Apr;21(8):821-7. Epub 2003 Mar 06.

Impact of flumioxazin herbicide on growth and carbohydrate physiology in Vitis vinifera L.

Saladin G, Magne C, Clement C.

Laboratoire de Biologie et Physiologie Vegetales, URVVC UPRES EA 2069, Universite de Reims Champagne-Ardenne, UFR Sciences, Moulin de la Housse, BP 1039, 51687, Reims Cedex 2, France.

The impact of flumioxazin herbicide on in vitro-grown grapevine ( Vitis vinifera L. cv. Chardonnay) was investigated. The herbicide treatments (1, 10 or 100 micro M flumioxazin in MM medium) had a negative impact on photosynthesis, as revealed by a reduction in foliar chlorophyll and carotenoid contents, gas exchanges and alteration in plastid structure and, consequently, resulted in a strong inhibition of plantlet growth. Surprisingly, soluble sugars and starch accumulated in all organs, suggesting a stimulation of sugar uptake from the medium. Moreover, photosynthetic activity and starch content partially recovered within 3 weeks of treatment at the weakest herbicide concentration. These results provide new insights into the physiological responses of non-target crops to flumioxazin, showing that flumioxazin is active in photosynthetic tissues of the non-target grapevine via root uptake, which is contrary to what is mentioned in the literature, and that the in vitro-grown plantlet is a good model for investigating the physiological effects of pesticides on crop species.

PMID: 12789529 [PubMed - in process]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=12819925&dopt=Abstract

Plant Cell Rep. 2003 Jun 18 [Epub ahead of print].

Stress effects of flumioxazin herbicide on grapevine ( Vitis vinifera L.) grown in vitro.

Saladin G, Clement C, Magne C.

UPRES EA 2069 URVVC, Laboratoire de Biologie et Physiologie Vegetales, UFR Sciences, Universite de Reims Champagne-Ardenne, Moulin de la Housse, BP 1039, 51687, Reims Cedex 2, France.

Among the herbicides used in vineyards, the pre-emergence soil-applied flumioxazin (FMX) is a recently synthesized molecule that inhibits chlorophyll biosynthesis in weed species. The aim of this work was to characterize the effects of FMX on non-target grapevine ( Vitis vinifera L. cv. Chardonnay) plantlets grown in vitro. FMX treatment (from 1 to 100 &mgr; M) represented a stress, as revealed by measurement of several parameters. Stem and leaves underwent dehydration and a decrease in both water- and osmotic-potential. Treated plantlets exhibited concomitant accumulation of soluble carbohydrates in all tissues and of free proline in stems and leaves. Moreover, FMX caused lipid peroxidation and electrolyte leakage in leaf tissues. These results indicate that the herbicide FMX is toxic for grapevine grown in vitro. In addition to inhibiting protoporphyrinogen IX oxidase, it causes water stress and membrane alteration in tissues and, as a consequence, generates the accumulation of carbohydrates and free proline.

PMID: 12819925 [PubMed - as supplied by publisher]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=12485590&dopt=Abstract

Ecotoxicol Environ Saf. 2002 Nov;53(3):439-45.

Photosynthetic responses of Lemna minor exposed to xenobiotics, copper, and their combinations.

Frankart C, Eullaffroy P, Vernet G.

Laboratory of Eco-Toxicology, Europol'Agro, Faculty of Sciences, University of Reims Champagne-Ardenne, Reims, France. cecile.frankart@univ-reims.fr

The effects on the photosynthetic process of copper and pesticides, used in vineyards, and their combinations, were investigated by measuring different chlorophyll fluorescence parameters in Lemna minor. Cu and flumioxazin had a severe impact on duckweed since a decrease in their photosynthetic capacity was detected after 24h of exposure to 200 and 1 microg.L(-1), respectively. However, fungicides used to control Botrytis cinerea (procymidone, pyrimethanil, and fludioxonil) seem to have no marked effects on duckweed even at very high concentrations (50 mg.L(-1)). Analysis of the combinations between copper (200 microg.L(-1)) and pesticides revealed different patterns of response: a synergistic effect was observed when Cu(2+) was added to flumioxazin (1 microg.L(-1)). In contrast, an antagonism was detected when duckweed was exposed to a mixture of Cu(2+) and fludioxonil or procymidone. However, these interactions always tended toward additivity when pesticide concentrations increased. Additivity was also observed for the Cu(2+)-pyrimethanil mixture at each fungicide concentration.

PMID: 12485590 [PubMed - indexed for MEDLINE]


Full free report available at http://www.genesdev.org/cgi/content/full/15/1/90

Genes Dev. 2001 Jan 1;15(1):90-103.

A plastidic ABC protein involved in intercompartmental communication of light signaling.

Moller SG, Kunkel T, Chua NH.

Laboratory of Plant Molecular Biology, Rockefeller University, 1230 York Avenue, New York, New York 10021-6399, USA.

Plants perceive light via specialized photoreceptors of which the phytochromes (phyA-E), absorbing far-red (FR) and red light (R) are best understood. Several nuclear and cytoplasmic proteins have been characterized whose deficiencies lead to changes in light-dependent morphological responses and gene expression. However, no plastid protein has yet been identified to play a role in phytochrome signal transduction. We have isolated a new Arabidopsis mutant, laf (long after FR) 6, with reduced responsiveness preferentially toward continuous FR light. The disrupted gene in laf6 encodes a novel plant ATP-binding-cassette (atABC1) protein of 557 amino acids with high homology to ABC-like proteins from lower eukaryotes. In contrast to lower eukaryotic ABCs, however, atABC1 contains an N-terminal transit peptide, which targets it to chloroplasts. atABC1 deficiency in laf6 results in an accumulation of the chlorophyll precursor protoporphyrin IX and in attenuation of FR-regulated gene expression. The long hypocotyl phenotype of laf6 and the accumulation of protoporphyrin IX in the mutant can be recapitulated by treating wild-type (WT) seedlings with flumioxazin, a protoporphyrinogen IX oxidase (PPO) inhibitor. Moreover, protoporphyrin IX accumulation in flumioxazin-treated WT seedlings can be reduced by overexpression of atABC1. Consistent with the notion that ABC proteins are involved in transport, these observations suggest that functional atABC1 is required for the transport and correct distribution of protoporphyrin IX, which may act as a light-specific signaling factor involved in coordinating intercompartmental communication between plastids and the nucleus.

PMID: 11156608 [PubMed - indexed for MEDLINE]


http://www.fluorideaction.org/pesticides/flumioxazin.epafacts.apr01.pdf

Environmental Protection Agency, Washington, DC. Office of Prevention, Pesticides and Toxic Substances - 2001

Pesticide Fact Sheet: Flumioxazin.

This document contains up-to-date chemical information, including a summary of the Agency's regulatory position and rationale, on a specific pesticide or group of pesticides. A Fact Sheet is issued after one of the following actions has occurred. Issuance or reissuance of a registration standard; Issuance of each special review document; Registration of a significantly changed use pattern; Registration of a new chemical or; An immediate need for information to resolve controversial issues relating to a specific chemical or use pattern.


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=10794647&dopt=Abstract

J Agric Food Chem. 1999 Jun;47(6):2429-38.

Metabolism of 7-fluoro-6-(3,4,5,6-tetrahydrophthalimido)-4- (2-propynyl)-2H-1,4-benzoxazin-3(4H)-one (S-53482, flumioxazin) in the rat: II. Identification of reduced metabolites.

Tomigahara Y, Onogi M, Kaneko H, Nakatsuka I, Yamane S.

Environmental Health Science Laboratory, Sumitomo Chemical Co., Ltd., Kasugade-Naka, Konohana-Ku, Osaka, Japan.

On single oral administration of (14)C-S-53482 [7-fluoro-6-(3,4,5, 6-tetrahydrophthalimido)-4-(2-propynyl)-2H-1,4-benzoxazin-3( 4H)-one, Flumioxazin] labeled at the 1- and 2-positions of tetrahydrophthaloyl group to rats at 1 (low dose) or 100 (high dose) mg/kg, the radiocarbon was almost completely eliminated within 7 days after administration in both groups with generally very low residual (14)C tissue levels. The predominant excretion route was via the feces. The major fecal and urinary metabolites involved reduction or sulfonic acid addition reactions at the 1,2-double bond of the 3,4,5,6-tetrahydrophthalimide moiety and hydroxylation of the cyclohexene or cyclohexane ring. One urinary and four fecal metabolites were identified using chromatographic techniques and spectroanalyses (NMR and MS). Three of five identified metabolites were unique forms, reduced at the 1,2-double bond of the 3,4,5, 6-tetrahydrophthalimide moiety. On the basis of the metabolites identified in this study, the metabolic pathways of S-53482 in rats are proposed. To specify tissues forming reduced metabolites, an in vitro study was conducted. Reduction was found to take place in red blood cells.

PMID: 10794647 [PubMed - indexed for MEDLINE]


http://www.ncbi.nlm.nih.gov:80/entrez/query.fcgi?cmd=Retrieve&db=PubMed&list_uids=10563890&dopt=Abstract

J Agric Food Chem. 1999 Jan;47(1):305-12.

Metabolism of 7-fluoro-6-(3,4,5,6-tetrahydrophthalimido)-4- (2-propynyl)-2H-1,4-benzoxazin-3(4H)-one (S-53482) in rat. 1. Identification of a sulfonic acid type conjugate.

Tomigahara Y, Matsui M, Matsunaga H, Isobe N, Kaneko H, Nakatsuka I, Yoshitake A, Yamane S.

Environmental Health Science Laboratory, Sumitomo Chemical Company, Ltd., 1-98, 3-Chome, Kasugade-Naka, Konohana-Ku, Osaka 554, Japan.

To examine the metabolic fate of 7-fluoro-6-(3,4,5, 6-tetrahydrophthalimido)-4-(2-propynyl)-2H-1,4-benzoxazin-3( 4H)-one (S-53482), rats were given a single oral dose of [phenyl-(14)C]-S-53482 at 1 (low) or 100 (high) mg/kg. The radiocarbon was almost completely eliminated within 7 days after administration in both groups. (14)C recoveries (expressed as percentages relative to the dosed (14)C) in feces and urine were 56-72 and 31-43%, respectively, for the low dose and 78-85 and 13-23%, respectively, for the high dose. S-53482 and seven metabolites were identified in urine and feces. Six of them were purified by several chromatographic techniques and identified by spectroanalyses (NMR and MS). Alcohol derivatives and an acetoanilide derivative were isolated from urine. Three sulfonic acid conjugates having a sulfonic acid group incorporated into the double bond of the 3,4,5,6-tetrahydrophthalimide moiety were isolated from feces. On the basis of the metabolites identified in this study, the metabolic pathways of S-53482 in rats are proposed.

PMID: 10563890 [PubMed - indexed for MEDLINE]


Teratology, Vol. 54, No. 5, pages 237-244, 22 references, 1996

Histological Changes in Rat Embryonic Blood Cells as a Possible Mechanism for Ventricular Septal Defects Produced by an N-Phenylimide Herbicide

Kawamura S, Yoshioka T, Kato T, Matsuo M, Yasuda M

[Note: S-53482 is Flumioxazin]

The effects of the N-phenylimide herbicide S-53482 (103361097) on rat embryonic blood cells were examined histologically at the light and electron microscopic levels. Pregnant Crj:CD-rats were administered S-53482 at 1,000mg/kg by oral intubation on day 12 of gestation. Rats were sacrificed at 6, 12, 24, 36, or 48 hours after treatment, and embryos were examined. Mitochondrial lesions were noted on electron and light microscopic examination, including abnormal iron deposits likely the result of inhibition of heme biosynthesis in erythroblasts derived from the yolk sac. Degeneration of these erythroblasts occurred followed by erythrophagocytosis. The findings showed that S-53482 did not induce ventricular septal defects (VSD) due to direct injurious effects on embryonic heart tissue. The authors suggest that S-53482 did inhibit protoporphyrinogen-oxidase in rat embryos which suppressed normal heme biosynthesis and produced erythroblastic regeneration. This in turn resulted in embryonic anemia. Anemic hypoxia was compensated for by enlargement of the heart. VSD was then produced by mechanical distortion of the heart or abnormal cardiac hemodynamics.


From Toxline at Toxnet

PESTICIDE BIOCHEMISTRY AND PHYSIOLOGY; 57 (1). 1997. 36-43.

Protoporphyrinogen oxidase of mouse and maize: Target site selectivity and thiol effects on peroxidizing herbicide action.

BIRCHFIELD NB, CASIDA JE

Environ. Chem. Toxicol. Lab., Dep. Environ. Sci. Policy Manage., Univ. Calif., Berkeley, CA 94720-3112, USA.

BIOSIS COPYRIGHT: BIOL ABS. The action of light-dependent peroxidizing herbicides involves inhibition of protoporphyrinogen oxidase (protox) at a high-affinity specific binding site readily assayed with our new N-aryltetrahydrophthalimide radioligand ((3H)THP), the desmethyl analog of flumipropyn. Protox of mouse liver mitochondria and maize etioplasts is similar in sensitivity to most of the 14 herbicides and analogs examined as inhibitors of (3H)THP binding, indicating that target site specificity is not a major factor in selective toxicity between mammals and plants. In assays using mouse protox, the 14 compounds fall into two groups upon correlating their ability to inhibit (3H)THP binding (without added thiol) and enzymatic activity (with added glutathione (GSH) or dithiothreitol (DTT) as an antioxidant for the substrate). The inhibitory potency of the THPs in protox activity assays is reduced by DTT relative to their potency in (3H)THP binding assays without added thiol. This "thiol effect"

CAS Registry Numbers: (CAS Nos. in blue are fluorinated pesticides)
126100-25-2 - unknown
103361-09-7 - Flumioxazin
87547-04-4 - Flumiclorac
84478-42-2 - 1H-Isoindole-1,3(2H)-dione, 2-(4-chloro-2-fluoro-5-(2-propynyloxy)phenyl)-4,5,6,7-tetrahydro-
50594-67-7 - Acifluorfen-methyl
50594-66-6 - Acifluorfen
42874-03-3 - Oxyfluorofen
40575-34-6 - 1-Pyrrolidinecarboxylic acid, 2,4-dichlorophenyl ester
39986-11-3 - 1H-Isoindole-1,3(2H)-dione, 2-(4-((4-chlorophenyl)methoxy)phenyl)-4,5,6,7-tetrahydro-
39985-63-2 - 1H-Isoindole-1,3(2H)-dione, 2-(4-chlorophenyl)-4,5,6,7-tetrahydro-
19666-30-9 - Oxadiazon
1836-75-5 - Nitrofen


From Toxline at Toxnet

PEANUT SCIENCE; 23 (1). 1996. 30-36

Flumioxazin for weed control in Texas peanuts (Arachis hypogaea L.).

GRICHAR WJ, COLBURN AE

Res. Sci., Tex. Agric. Exp. Stn., Yoakum, TX 77995, USA.

Abstract: BIOSIS COPYRIGHT: BIOL ABS. Field experiments were conducted in 1991 and 1993 to evaluate flumioxazin alone and in various herbicide programs for weed control in peanut. Flumioxazin alone provided inconsistent control of annual grasses, while the addition of pendimethalin or trifluralin improved control considerably. Pitted morningglory (Ipomoea lacunosa L.) and ivy leaf morning glory (Ipomoea hederacea (L.) Jacq.) control was >75% when flumioxazin was used alone. Flumioxazin caused early season peanut stunting with some recovery within 4 to 6 wk. Postemergence applications of imazethapyr or lactofen increased peanut stunting.


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