559784
N,N-二乙基-2-(1-萘氧基)丙酰胺
97%
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关于此项目
线性分子式:
C10H7OCH(CH3)CON(CH2CH3)2
化学文摘社编号:
分子量:
271.35
UNSPSC Code:
12352100
NACRES:
NA.22
PubChem Substance ID:
EC Number:
239-333-3
Beilstein/REAXYS Number:
6809160
MDL number:
Assay:
97%
Form:
solid
InChI key
WXZVAROIGSFCFJ-UHFFFAOYSA-N
InChI
1S/C17H21NO2/c1-4-18(5-2)17(19)13(3)20-16-12-8-10-14-9-6-7-11-15(14)16/h6-13H,4-5H2,1-3H3
SMILES string
CCN(CC)C(=O)C(C)Oc1cccc2ccccc12
assay
97%
form
solid
mp
73-78 °C (lit.)
存储类别
11 - Combustible Solids
wgk
WGK 2
flash_point_f
Not applicable
flash_point_c
Not applicable
ppe
Eyeshields, Gloves, type N95 (US)
法规信息
农药列管产品
此项目有
Li E Cui et al.
Journal of hazardous materials, 190(1-3), 81-86 (2011-03-29)
Napropamide belongs to the amide herbicide family and widely used to control weeds in farmland. Intensive use of the herbicide has resulted in widespread contamination to ecosystems. The present study demonstrated an analysis on accumulation of the toxic pesticide napropamide
Rui Zhang et al.
Journal of agricultural and food chemistry, 58(5), 3232-3240 (2010-02-11)
Napropamide is a herbicide widely used for controlling annual weeds. Substantial use of napropamide in recent years has led to its bioaccumulation in ecosystems and thus contamination to crops. Meanwhile, application of dissolved organic matters (DOMs) to soils in the
J P Aguer et al.
Journal of environmental science and health. Part. B, Pesticides, food contaminants, and agricultural wastes, 35(6), 725-738 (2000-11-09)
The influence of soil and sediment composition on sorption and photodegradation of the herbicide napropamide [N,N-diethyl-2-(1-naphthyloxy)propionamide] was investigated. Five soils and one sediment were selected for this study and the clay fractions were obtained by sedimentation. Sorption-desorption was studied by
Hua Guo et al.
Journal of environmental sciences (China), 21(4), 494-502 (2009-07-29)
The effect of pesticide napropamide (N,N-diethyl-2-(1-naphthalenyloxy) propanamide) on soil microorganisms for long-term (56 d) was assessed by monitoring changes in soil microbial biological responses. Soils were treated with napropamide at 0, 2, 10, 20, 40, and 80 mg/kg soil and
Hua Guo et al.
Huan jing ke xue= Huanjing kexue, 29(6), 1729-1736 (2008-09-04)
Chromatography (HPLC and GC-MS) and spectroscopy (UV and FT-IR) methods were conducted to study the degradation and adsorption behavior of napropamide in soils. Influence factors of degradation, degradation products and adsorption mechanism were analyzed. The results showed that degradation rate
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