InChI=1S/C7H6N2O5/c1-4-2-5(8(11)12)3-6(7(4)10)9(13)14/h2-3,10H,1H3 |
ZXVONLUNISGICL-UHFFFAOYSA-N |
Cc1cc(cc(c1O)[N+]([O-])=O)[N+]([O-])=O |
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fungicide
A substance used to destroy fungal pests.
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dinitrophenol insecticide
fungicide
A substance used to destroy fungal pests.
herbicide
A substance used to destroy plant pests.
pesticide
Strictly, a substance intended to kill pests. In common usage, any substance used for controlling, preventing, or destroying animal, microbiological or plant pests.
(via organonitrogen pesticide )
acaricide
A substance used to destroy pests of the subclass Acari (mites and ticks).
(via organonitrogen acaricide )
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View more via ChEBI Ontology
2-methyl-4,6-dinitrophenol
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2,4-Dinitro-6-methylphenol
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KEGG COMPOUND
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3,5-dinitro-2-hydroxytoluene
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ChemIDplus
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4,6-dinitro-o-cresol
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NIST Chemistry WebBook
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4,6-Dinitro-o-cresol
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KEGG COMPOUND
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6-methyl-2,4-dinitrophenol
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NIST Chemistry WebBook
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Antinonnin
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NIST Chemistry WebBook
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DNOC
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ChemIDplus
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2054389
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Reaxys Registry Number
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Reaxys
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534-52-1
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CAS Registry Number
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KEGG COMPOUND
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534-52-1
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CAS Registry Number
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NIST Chemistry WebBook
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534-52-1
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CAS Registry Number
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ChemIDplus
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Broholm MM, Tuxen N, Rugge K, Bjerg PL (2001) Sorption and degradation of the herbicide 2-methyl-4,6-dinitrophenol under aerobic conditions in a sandy aquifer in Vejen, Denmark. Environmental science & technology 35, 4789-4797 [PubMed:11775154] [show Abstract] A pulse (7 days) and a continuous (216 days), natural gradient field injection experiment with herbicides, including 2-methyl-4,6-dinitrophenol (4,6-dinitro-o-cresol, abbreviated DNOC), and a bromide tracer were conducted in a shallow, aerobic aquifer near Vejen, Denmark. The pulse and continuous plume were monitored in a dense, three-dimensional monitoring network installed in the aquifer downgradient of the injection. The sorption and degradation of DNOC were evaluated based on moment analysis of breakthrough curves, cross sections, and snapshots of the DNOC plume and supported by results from laboratory experiments. Significant and spatially variable sorption of DNOC (Kd range, 0.10-0.98 L/kg) was observed due to a specific binding of DNOC to clay minerals. The spatial variation was mainly a result of variation in pH, with stronger sorption at lower pH, whereas other factors such as cation composition on the solid matrix appeared to be negligible. Significant degradation of DNOC in the aquifer was revealed by moment analysis of data from the continuous field injection experiment. Degradation of DNOC in the field was slow and/or subject to long lag phases, and the data suggested spatially varying degradation potentials. This was supported by the laboratory experiments. The potential for natural attenuation of DNOC in aerobic aquifers appears promising. | Grilli S, Ancora G, Rani P, Valenti AM, Mazzullo M, Colacci A (1991) In vivo unwinding fluorimetric assay as evidence of the damage induced by fenarimol and DNOC in rat liver DNA. Journal of toxicology and environmental health 34, 485-494 [PubMed:1960763] [show Abstract] Five pesticides [amitraz, cyanazine, cyhexatin, dinitro-o-cresol (DNOC), and fenarimol] were tested as pure active ingredients for in vivo induction of DNA strand breaks on rat hepatocytes after intraperitoneal (ip) treatment. Two pesticides, fenarimol and DNOC, were capable of inducing DNA damage because they significantly increased the DNA unwinding rate. On the contrary, amitraz, cyanazine, and cyhexatin were not DNA-damaging agents. |
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