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Safety Information

45407

Supelco

Cyanazine

PESTANAL®, analytical standard

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About This Item

Empirical Formula (Hill Notation):
C9H13ClN6
CAS Number:
21725-46-2
Molecular Weight:
240.69
Beilstein:
615509
EC Number:
244-544-9
MDL number:
MFCD00055514
UNSPSC Code:
41116107
PubChem Substance ID:
329756707
NACRES:
NA.24

grade

analytical standard

Quality Level

100

product line

PESTANAL®

shelf life

limited shelf life, expiry date on the label

technique(s)

HPLC: suitable
gas chromatography (GC): suitable
solid phase extraction (SPE): suitable

application(s)

agriculture
environmental

format

neat

SMILES string

CCNc1nc(Cl)nc(NC(C)(C)C#N)n1

InChI

1S/C9H13ClN6/c1-4-12-7-13-6(10)14-8(15-7)16-9(2,3)5-11/h4H2,1-3H3,(H2,12,13,14,15,16)

InChI key

MZZBPDKVEFVLFF-UHFFFAOYSA-N

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General description

Standard for Supelco MIP SPE cartridges. For more information request Supelco Literature T407075, T706023

Application

Refer to the product′s Certificate of Analysis for more information on a suitable instrument technique. Contact Technical Service for further support.

Legal Information

PESTANAL is a registered trademark of Merck KGaA, Darmstadt, Germany

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Pictograms

Skull and crossbonesEnvironment
GHS06,GHS09

Signal Word

Danger

Hazard Statements

H301,H410

Hazard Classifications

Acute Tox. 3 Oral - Aquatic Acute 1 - Aquatic Chronic 1

Storage Class Code

6.1C - Combustible acute toxic Cat.3 / toxic compounds or compounds which causing chronic effects

WGK

WGK 3

Flash Point(F)

212.0 °F - closed cup

Flash Point(C)

100 °C - closed cup

Personal Protective Equipment

dust mask type N95 (US), Eyeshields, Gloves

Regulatory Information

农药列管产品

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Certificates of Analysis (COA)

Lot/Batch Number
BCCG9629
BCBV4875

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Ying Jin-Clark et al.
Environmental toxicology and chemistry, 21(3), 598-603 (2002-03-07)
Toxicities of two triazine herbicides (atrazine and cyanazine) and an organophosphate insecticide (chlorpyrifos) were evaluated individually and with each herbicide in binary combination with chlorpyrifos using fourth-instar larvae of the aquatic midge, Chironomus tentans. Chlorpyrifos at 0.25 microg/L resulted in
Cynthia V Rider et al.
Environmental toxicology and chemistry, 29(9), 2064-2071 (2010-09-08)
Reproductive abnormalities in alligators exposed to contaminants in Lake Apopka, Florida, USA represent a clear example of endocrine disruption in wildlife. Several of these contaminants that are not able to bind to mammalian estrogen receptors (such as atrazine and cyanazine)
N C Hansen et al.
Journal of environmental quality, 30(6), 2120-2126 (2002-01-16)
Herbicides transported to surface waters by agricultural runoff are partitioned between solution and solid phases. Conservation tillage that reduces upland erosion will also reduce transport of herbicides associated with the solid phase. However, transport of many herbicides occurs predominantly in
Mary Anne Nelson et al.
Analytical chemistry, 76(3), 805-813 (2004-01-31)
A portable system based on immunoextraction and reversed-phase HPLC was developed for the field analysis of herbicides in groundwater and surface water. Atrazine, simazine, and cyanazine were used as model analytes for this work. These were measured in water by
S M Schraer et al.
Journal of agricultural and food chemistry, 48(12), 5881-5886 (2001-04-21)
Enzyme-linked immunosorbent assay (ELISA) data from surface water reconnaissance were compared to data from samples analyzed by gas chromatography for the pesticide residues cyanazine (2-[[4-chloro-6-(ethylamino)-1,3,5-triazin-2-yl]amino]-2-methylpropanenitrile) and metolachlor (2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-1-methylethyl)acetamide). When ELISA analyses were duplicated, cyanazine and metolachlor detection was found to
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