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Merck
CN

45407

草净津

PESTANAL®, analytical standard

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关于此项目

经验公式(希尔记法):
C9H13ClN6
化学文摘社编号:
分子量:
240.69
UNSPSC Code:
41116107
NACRES:
NA.24
PubChem Substance ID:
EC Number:
244-544-9
Beilstein/REAXYS Number:
615509
MDL number:
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InChI key

MZZBPDKVEFVLFF-UHFFFAOYSA-N

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)

SMILES string

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

grade

analytical standard

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

Quality Level

General description

用于 Supelco MIP SPE 柱的标准品欲知更多信息,请索取 Supelco 资料 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

pictograms

Skull and crossbonesEnvironment

signalword

Danger

hcodes

Hazard Classifications

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

存储类别

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

ppe

dust mask type N95 (US), Eyeshields, Faceshields, Gloves

法规信息

农药列管产品
此项目有

历史批次信息供参考:

分析证书(COA)

Lot/Batch Number

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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)
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
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
A H Tennant et al.
Mutation research, 493(1-2), 1-10 (2001-08-23)
Triazine herbicides are prevalent contaminants of groundwater in the agricultural regions of the United States. The literature on the genotoxicity of triazines is rife with conflicting data, though the general tendency is for most studies to report negative results. In

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