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(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 化学構造式
エンドスルファンB;エンドスルファンII;(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド;β-ベンゾエピン;β-エンドスルファン;Β-エンドスルファン標準品;ヘキサクロロヘキサヒドロメタノベンゾジオキサチエピンオキサイド(β);Β‐エンドスルファン標準品;CS_N-11118-100MG_Β-エンドスルファン;Β-エンドスルファン STANDARD;エンドスルファン-II (13C9, 99%) 100±10ΜG/MLノナン溶液;エンドスルファンII STANDARD;Β-エンドスルファン 溶液;β-エンドスルファン Standard, 1000 µg/mL in p-Dioxane;エンドスルファンII Standard, 100 µg/mL in Methanol;エンドスルファンII Standard, 1000 µg/mL in MeOH
endosulfan2;endosulfanb;B-ENDOSULFAN;'LGC' (1120);beta-Thiodan;ENDOSULFAN II;alpha-thionex;BETA-BENZOEPIN;BETA-ENDOSULFAN;Endosulfan-beta
MOL File:

(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 物理性質

融点 :
比重(密度) :
1.6568 (estimate)
450 at 20 °C (shake flask-GLC, Bowman and Sans, 1983)
闪点 :
11 °C
貯蔵温度 :
外見 :
Henry's Law Constant:
0.022 at 5 °C, 0.037 at 15 °C, 0.043 at 20 °C, 0.065 at 25 °C, 0.80 at 35 °C:in 3% NaCl solution: 0.20 at 5 °C, 0.37 at 15 °C, 0.46 at 25 °C, 0.56 at 35 °C (gas stripping-GC, Cetin et al., 2006)
ACGIH TLV: TWA 0.1 mg/m3.
Endosulfan ii(33213-65-9)
6,9-Methano-2,4, 3-benzodioxathiepin, 6,7,8,9,10,10-hexachloro-1, 5,5a,6,9,9a-hexahydro-, 3-oxide, (3.alpha.,5a.alpha.,6.beta., 9.beta.,9a.alpha.)-(33213-65-9)
  • リスクと安全性に関する声明
  • 危険有害性情報のコード(GHS)
主な危険性  Xn,N,F,T
Rフレーズ  22-67-65-62-51/53-48/20-38-11-50/53-25
Sフレーズ  36/37-61-62-33-29-16-9-60-45
RIDADR  2761
WGK Germany  3
RTECS 番号 RB9875200
国連危険物分類  6.1(b)
容器等級  III
毒性 LC50 (96-hour) for golden orfe 2 mg/L (Hartley and Kidd, 1987), rainbow trout 0.3 mg/L and white sucker 3.0 mg/L (Verschueren, 1983).
化審法 第1種特定化学物質 &_& 化審法施行令第7条 &_& 化審法施行令第8条
安衛法 57-2
PRTR法 1-388
毒劇物取締法 II
注意喚起語 Danger
コード 危険有害性情報 危険有害性クラス 区分 注意喚起語 シンボル P コード
H225 引火性の高い液体および蒸気 引火性液体 2 危険 P210,P233, P240, P241, P242, P243,P280, P303+ P361+P353, P370+P378,P403+P235, P501
H301 飲み込むと有毒 急性毒性、経口 3 危険 P264, P270, P301+P310, P321, P330,P405, P501
H304 飲み込んで気道に侵入すると生命に危険のおそ れ 吸引性呼吸器有害性 1 危険
H315 皮膚刺激 皮膚腐食性/刺激性 2 警告 P264, P280, P302+P352, P321,P332+P313, P362
H336 眠気やめまいのおそれ 特定標的臓器毒性、単回暴露; 麻酔作用 3 警告 P261, P271, P304+P340, P312,P403+P233, P405, P501
H373 長期にわたる、または反復暴露により臓器の障 害のおそれ 特定標的臓器有害性、単回暴露 2 警告 P260, P314, P501
H410 長期的影響により水生生物に非常に強い毒性 水生環境有害性、慢性毒性 1 警告 P273, P391, P501
H413 長期的影響により水生生物に有害のおそれ 水生環境有害性、慢性毒性 4
P210 熱/火花/裸火/高温のもののような着火源から遠ざ けること。-禁煙。
P261 粉じん/煙/ガス/ミスト/蒸気/スプレーの吸入を避ける こと。
P273 環境への放出を避けること。
P281 指定された個人用保護具を使用すること。
P301+P310 飲み込んだ場合:直ちに医師に連絡すること。
P331 無理に吐かせないこと。
P391 漏出物を回収すること。
P501 内容物/容器を...に廃棄すること。

(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 価格 もっと(12)

メーカー 製品番号 製品説明 CAS番号 包装 価格 更新時間 購入
富士フイルム和光純薬株式会社(wako) W01ACSAPP-9-100 エンドスルファンII Standard
Endosulfan II Standard, 100 ug/mL in Methanol
33213-65-9 1mL ¥8100 2018-12-26 購入
富士フイルム和光純薬株式会社(wako) W01ACSAS-E0094 β-エンドスルファン Standard
beta-Endosulfan Standard, 1000 ug/mL in p-Dioxane
33213-65-9 1mL ¥14700 2018-12-26 購入
関東化学株式会社(KANTO) 49802-75 β‐エンドスルファン標準品
β‐Endosulfan standard
33213-65-9 100mg ¥16000 2018-12-13 購入
Sigma-Aldrich Japan 36582 β-エンドスルファン 溶液 100?μg/mL in hexane, PESTANAL?, analytical standard
β-Endosulfan solution 100?μg/mL in hexane, PESTANAL?, analytical standard
33213-65-9 2ml ¥14500 2018-12-25 購入
Sigma-Aldrich Japan 33385 β-エンドスルファン PESTANAL?, analytical standard
β-Endosulfan PESTANAL?, analytical standard
33213-65-9 100mg ¥18800 2018-12-25 購入

(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 化学特性,用途語,生産方法


Endosulfan is a chlorinated cyclodiene insecticide. The pure product is a colorless crystalline solid. The technical product is a light to dark brown waxy solid. It has a rotten egg or sulfur odor.


Colorless to brown, nonflammable solid or crystals with a mild odor similar to terpene or sulfur dioxide.


Insecticide for vegetable crops.


Brown crystals. Melting point 208-210°C. Used as an insecticide.


Insoluble in water. Reacts slowly with water to generate sulfur dioxide.


BETA-ENDOSULFAN is a sulfite ester of a chlorinated cyclic diol. Decomposed rapidly by alkali to generate sulfur dioxide. Decomposed by acid. Incompatible with strong oxidizing and reducing agents. may be incompatible with many amines, nitrides, azo/diazo compounds, alkali metals, and epoxides.


ACUTE/CHRONIC HAZARDS: Highly toxic by ingestion, inhalation, and skin absorption.


Non-combustible, substance itself does not burn but may decompose upon heating to produce corrosive and/or toxic fumes. Containers may explode when heated. Runoff may pollute waterways.


Those engaged in the manufacture, formulation, and application of this material


Soil. Metabolites of endosulfan identified in soils included endosulfandiol, endosulfanhydroxy ether, endosulfan lactone and endosulfan sulfate (Martens, 1977; Dreher and Podratzki, 1988). These compounds, including endosulfan ether, were also reported as metabolites identified in aquatic systems (Day, 1991). In aerobic soils, b-endosulfan is converted to the corresponding alcohol and ether (Perscheid et al., 1973). Endosulfan sulfate was the major biodegradation product in soils under aerobic, anaerobic and flooded conditions (Martens, 1977). In flooded soils, endolactone was detected only once whereas endodiol and endohydroxy ether were identified in all soils under these conditions. Under anaerobic conditions, endodiol formed in low amounts in two soils (Martens, 1977). Indigenous microorganisms obtained from a sandy loam degraded b-endosulfan to endosulfan diol. This diol was converted to endosulfan a-hydroxy ether and trace amounts of endosulfan ether and both were degraded to endosulfan lactone (Miles and Moy, 1979).
Plant. In addition, endosulfan sulfate was formed when endosulfan was translocated from the leaves to roots in both bean and sugar beet plants (Beard and Ware, 1969). In tobacco leaves, b-endosulfan hydrolyzed into endosulfandiol (Chopra and Mahfouz, 1977). Stewart and Cairns (1974) reported the metabolite endosulfan sulfate was identified in potato peels and pulp at concentrations of 0.3 and 0.03 ppm, respectively. They also reported that the half-life for the oxidative conversion of b-endosulfan to endosulfan sulfate was 800 days.
In carnation plants, the half-lives of b-endosulfan stored under four different conditions, non-washed and exposed to open air, washed and exposed to open air, non-washed and placed in an enclosed container and under greenhouse conditions were 23.40, 12.64, 37.42 and 7.62 days, respectively (Ceron et al., 1995).
Surface Water. Endosulfan sulfate was also identified as a metabolite in a survey of 11 agricultural watersheds located in southern Ontario, Canada (Frank et al., 1982). When endosulfan (a- and b- isomers, 10 mg/L) was added to Little Miami River water, sealed and exposed to sunlight and UV light for 1 week, a degradation yield of 70% was observed. After two and four weeks, 95% and 100% of the applied amount degraded. The major degradation product was identified as endosulfan alcohol by IR spectrometry (Eichelberger and Lichtenberg, 1971).
Photolytic. Thin films of endosulfan on glass and irradiated by UV light (l >300 nm) produced endosulfan diol with minor amounts of endosulfan ether, lactone, a-hydroxyether and other unidentified compounds (Archer et al., 1972). Gaseous b-endosulfan subjected to UV light (l >300 nm) produced endosulfan ether, endosulfan diol, endosulfan sulfate, endosulfan lactone, a-endosulfan and a dechlorinated ether (Schumacher et al., 1974). Irradiation of b-endosulfan in n-hexane by UV light produced the photoisomer a-endosulfan (Putnam et al., 1975). When an aqueous solution containing endosulfan was photooxidized by UV light at 90–95°C, 25, 50 and 75% degraded to carbon dioxide after 5.0, 9.5 and 31.0 hours, respectively (Knoevenagel and Himmelreich, 1976).
Chemical/Physical. Endosulfan detected in Little Miami River, OH was readily hydrolyzed to a compound tentatively identified as endosulfan diol (Eichelberger and Lichtenberg, 1971). Sulfuric acid is also an end product of hydrolysis (Kollig, 1993). The hydrolysis half-lives at pH values (temperature) of 3.32 (87.0°C), 6.89 (68.0°C) and 8.69 (38.0°C) were calculated to be 2.7, 0.07 and 0.04 days, respectively (Ellington et al., 1988). Greve and Wit (1971) reported the hydrolysis half-lives of b-endosulfan at 20°C and pH values of 7 and 5.5 were 37 and 187 days, respectively.


UN2761 Organochlorine pesticides, solid, toxic, Hazard Class: 6.1; Labels: 6.1-Poisonous materials. UN2811 Toxic solids, organic, n.o.s., Hazard Class: 6.1; Labels: 6.1-Poisonous materials, Technical Name Required.


Those engaged in the manufacture, formulation, and application of this material


A recommended method for disposal is burial 18 in deep in noncropland, away from water supplies, but bags can be burned. Large quantities should be incinerated at high temperature in a unit with effluent gas scrubbing. Consult with environmental regulatory agencies for guidance on acceptable disposal practices. Generators of waste containing this contaminant (≥100 kg/ mo) must conform with EPA regulations governing storage, transportation, treatment, and waste disposal. In accordance with 40CFR165, follow recommendations for the disposal of pesticides and pesticide containers. Must be disposed properly by following package label directions or by contacting your local or federal environmental control agency, or by contacting your regional EPA office.

(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 上流と下流の製品情報



(6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド 生産企業

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  • 33213-65-9
  • 'LGC' (1120)
  • 1,4,5,6,7,7-hexachloro-,cyclicsulfite,exo-5-norbornene-3-dimethanol
  • 5-Norbornene-2,3-dimethanol, 1,4,5,6,7,7-hexachloro-, cyclic sulfite, exo-
  • alpha-thionex
  • b-endosulfan-beta
  • beta-Thiodan
  • (6S,9R)-6,7,8,9,10,10-Hexachloro-1,5,5aα,6,9,9aα-hexahydro-6β,9β-methano-2,4,3-benzodioxathiepin 3-oxide
  • (3alpha,5a beta,6beta,9beta,9a beta)-6,7,8,9,10,10-Hexachloro-1,5,5a,6,9,9a-hexahydro-6,9-methano-2,4,3-benzodioxathiepin-3-oxide
  • 6,7,8,9,10,10-Hexachloro-1,5,5a,6,9,9a-Hexahydro-6,9-Methano-2,4,3-Benzodioxathiepin-3-Oxide Beta Isomer
  • β-benzoepin standard
  • b-Endosulfan 100mg [33213-65-9]
  • Endosulfan (beta isomer) 100mg [33213-65-9]
  • Endosulfan II (β isomer) 99%
  • β-Endosulfan Standard
  • endosulfan2
  • endosulfanb
  • Endosulfan-beta
  • endosulfanii(beta)
  • General Weed Killer
  • generalweedkiller
  • エンドスルファンB
  • エンドスルファンII
  • (6S,9R)-6,7,8,9,10,10-ヘキサクロロ-1,5,5aα,6,9,9aα-ヘキサヒドロ-6β,9β-メタノ-2,4,3-ベンゾジオキサチエピン3-オキシド
  • β-ベンゾエピン
  • β-エンドスルファン
  • Β-エンドスルファン標準品
  • ヘキサクロロヘキサヒドロメタノベンゾジオキサチエピンオキサイド(β)
  • Β‐エンドスルファン標準品
  • CS_N-11118-100MG_Β-エンドスルファン
  • Β-エンドスルファン STANDARD
  • エンドスルファン-II (13C9, 99%) 100±10ΜG/MLノナン溶液
  • エンドスルファンII STANDARD
  • Β-エンドスルファン 溶液
  • β-エンドスルファン Standard, 1000 µg/mL in p-Dioxane
  • エンドスルファンII Standard, 100 µg/mL in Methanol
  • エンドスルファンII Standard, 1000 µg/mL in MeOH
  • 有機塩素系殺虫剤
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