N., and Bakry, N. M. (2006)

Takeuchi, Ryo and Akiyama, Yasushi (2002). Iridium complex-catalyzed carbonylation of allylic phosphates. Journal of Organometallic Chemistry 651: 137-145.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.

Iridium/ Carbonylation/ Allylic phosphates/ syn-anti Isomerization/ [beta],[gamma]-Unsaturated esters/ [pi]-Allyl iridium [Ir(cod)Cl]2 with a ligand such as P(2-furyl)3, PPh2C6F5 or AsPh3 showed high catalytic activity for the carbonylation of allylic phosphates in the presence of alcohols to give the corresponding [beta],[gamma]-unsaturated esters. The carbonylation of diethyl (E)-3-phenyl-2-propenyl phosphate in the presence of EtOH under an initial carbon monoxide pressure of 40 kg cm-2 at 100 [deg]C gave ethyl (E)-4-phenyl-3-butenoate in 90% yield. No (Z)-isomer was obtained. The reaction proceeded smoothly without using an amine as an additive. The carbonylation of 2-alkenyl diethyl phosphates in the presence of EtOH gave a mixture of ethyl (E)- and (Z)-3-alkenoate. The stereochemistry of the starting material was lost by syn-anti isomerization of the [pi]-allyl iridium intermediate prior to the insertion of carbon monoxide into the iridium---carbon bond. Increasing the steric bulkiness of the substituent at the [gamma]-position of the allyl system or increasing the initial carbon monoxide pressure increased the selectivity for a product with the same stereochemistry as the starting material.

Talebi, K. (1998). Diazinon Residues in the Basins of Anzali Lagoon, Iran. Bulletin of Environmental Contamination and Toxicology [Bull. Environ. Contam. Toxicol.]. Vol. 61, no. 4, pp. 477-483. Oct 1998.
Chem Codes: Chemical of Concern: DZ Rejection Code: SURVEY.

ISSN: 0007-4861

Descriptors: Insecticides
Descriptors: Pollutant persistence
Descriptors: Pollution monitoring
Descriptors: Water pollution
Descriptors: Sediment pollution
Descriptors: Coastal lagoons
Descriptors: Diazinon
Descriptors: Pesticides
Descriptors: Water Pollution Sources
Descriptors: Sediment Contamination
Descriptors: Effluents
Descriptors: Rivers
Descriptors: Lagoons
Descriptors: Surface water
Descriptors: Water pollution measurements
Descriptors: Streams
Descriptors: Basins
Descriptors: Rice fields
Descriptors: Agrochemicals
Descriptors: ISW, Iran
Abstract: In the present study the level of diazinon was investigated in the surface water and sediment of the lagoon. The study began in May 1996 and continued until February 1997. In order to elucidate the pattern of diazinon pollution in the streams and rivers, one effluent river from central basin of the lagoon was chosen and the water samples were analyzed for the residue during the granule application season in ricefields.
DOI: 10.1007/s001289900787
Language: English
Publication Type: Journal Article
Classification: Q5 01503 Characteristics, behavior and fate
Classification: O 4060 Pollution - Environment
Classification: SW 3020 Sources and fate of pollution
Classification: P 2000 FRESHWATER POLLUTION
Subfile: Water Resources Abstracts; Oceanic Abstracts; ASFA 3: Aquatic Pollution & Environmental Quality; Pollution Abstracts

Tanaka, A., Masago, H., Karino, K., and Ujie, A. (1983). Determination of Trace Agrochemicals in Water and Toxicity of Agrochemicals toFish. 2. Toxicity of Decomposition Products From Uv-Irradiated. C.A.Sel.-Environ.Pollut.18:4 (1984) / Gunma-Ken Eisei Kogai Kenkyusho Nenpo 15: 119-122.

EcoReference No.: 12241

Chemical of Concern: DZ,MLN,CPYM; Habitat: A; Effect Codes: MOR; Rejection Code: NO ABSTRACT.

Tanigawa, Yoshio, Nishimura, Kazuaki, Kawasaki, Akihiko, and Murahashi, Shun-Ichi (1982). Palladium(O)-catalyzed allylic alkylation and amination of allylic phosphates. Tetrahedron Letters 23: 5549-5552.

Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.

Allyl diethyl phosphates (1) can be easily substituted with malonates and amines in the presence of palladium(O) catalyst. Synthetic utility of the reaction is demonstrated by the sequential amination-amination and alkylation-amination of (Z)-4-acetoxybut-2-enyl diethyl phosphate (1b) with high regio- and stereoselectivity.

Tashiro, H. and Kuhr, R. J. (1978). Some Factors Influencing the Toxicity of Soil Applications of Chlorpyrifos and Diazinon to European Chafer Grubs. J.Econ.Entomol. 71: 904-907.

EcoReference No.: 54739

Chemical of Concern: CPY,DZ; Habitat: T; Effect Codes: MOR,ACC; Rejection Code: NO ENDPOINT(ALL CHEMS).

TAYLOR AW and SPENCER WF ( 1990). VOLATILIZATION AND VAPOR TRANSPORT PROCESSES. CHENG, H. H. (ED.). SSSA (SOIL SCIENCE SOCIETY OF AMERICA) BOOK SERIES, NO. 2. PESTICIDES IN THE SOIL ENVIRONMENT: PROCESSES, IMPACTS, AND MODELING. XXIII+530P. SOIL SCIENCE SOCIETY OF AMERICA, INC.: MADISON, WISCONSIN, USA. ILLUS. ISBN 0-89118-791-X.; 0 (0). 1990. 213-270.

Chem Codes: Chemical of Concern: DZ Rejection Code: FATE.

BIOSIS COPYRIGHT: BIOL ABS. RRM PESTICIDE DISPERSAL VAPOR PRESSURE RESIDUE DISTRIBUTION SURFACE MOISTURE STATUS SOIL Biochemistry/ Environment/ Air Pollution/ Soil Pollutants/ Water Pollution/ Soil/ Fertilizers/ Soil/ Herbicides/ Pest Control/ Pesticides

Taylor, R. N. (1982). Insecticide Resistance in Houseflies from the Middle East and North Africa with Notes on the Use of Various Bioassay Techniques. Pestic.Sci. 13: 415-425.

EcoReference No.: 71355

Chemical of Concern: DDT,HCCH,RSM,DZ; Habitat: T; Effect Codes: MOR; Rejection Code: TARGET(DZ,RSM).

Teh, S. J., Deng, D. F., Werner, I., Teh, F. C., and Hung, S. S. O. (2005). Sublethal Toxicity of Orchard Stormwater Runoff in Sacramento Splittail (Pogonichthys macrolepidotus) Larvae. Mar.Environ.Res. 59: 203-216.

Chem Codes: Chemical of Concern: DZ,ESV Rejection Code: EFFLUENT.

Teh, Swee J, Deng, DongFang, Werner, Inge, Teh, FooChing, and Hung, Silas S O (2005). Sublethal toxicity of orchard stormwater runoff in Sacramento splittail (Pogonichthys macrolepidotus) larvae. Marine Environmental Research 59: 203-216.

Chem Codes: Chemical of Concern: EFV Rejection Code: MIXTURE.

The sublethal effects of stormwater runoff from sections of a plum orchard treated with esfenvalerate or diazinon were evaluated in 7-day-old Sacramento splittail (Pogonichthys macrolepidotus) larvae. Fish were exposed to eight runoff samples using the USEPA standard static renewal method for 96 h acute toxicity testing, then transferred to clean water for three-month to assess the survival, growth, histopathological abnormalities, and heat stress proteins (hsp). No significant mortality was observed at 96 h in exposed fish. At one week, histopathological abnormalities included severe glycogen depletion, cytoplasmic protein droplets, vacuolar degeneration, and cell necroses in liver of all exposure groups. Pyknotic nerve cells were seen in brain of one exposure group. Significantly higher cumulative mortality, lower condition factor, and elevated hsp60 and hsp70 levels (p < 0.05) were occurred in several exposure groups. No histopathological abnormalities were observed after three months in any exposure group. This study confirms that standard acute toxicity tests have underestimated the toxicity of stormwater runoff, and although splittail larvae survived the 96 h exposure, they exhibited reduced survival and growth and showed signs of cellular stress even after a three month recovery period. [Journal Article; In English; England]

Teixeira, H., Rosilio, V., Laigle, A., Lepault, J., Erk, I., Scherman, D., Benita, S., Couvreur, P., and Dubernet, C. (2001). Characterization of oligonucleotide/lipid interactions in submicron cationic emulsions: influence of the cationic lipid structure and the presence of PEG-lipids . Biophysical Chemistry 92: 169-181.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.

We have recently described how oligonucleotide (ON) stability and release from O/W cationic emulsions are governed by the lipid composition. The aim of the present paper was to investigate the properties of the ON/lipid complexes through fluorescence resonance energy transfer (FRET), size, surface tension measurements and cryomicroscopy. Starting from a typical emulsion containing stearylamine as a cationic lipid, the influence of the lipid structure (monocationic molecules bearing mono or diacyl chains, or polycations) as well as of the presence of PEGylated lipids, were studied. The presence of a positive charge on the droplet surface clearly contributed to enhance the ON interaction with lipid monolayers and to bring the ON molecules closer to the interface. Hydrophobic interactions through the acyl chains were shown to further enhance the anchorage of the ON/lipid complexes. In contrast, the incorporation of PEGylated lipids acted as a barrier against the establishment of electrostatic bindings, the polyethyleneglycol chains acting themselves as interaction sites for the ON leading to hydrophilic complexes. Similar features were observed for the polycationic lipid, and cryomicroscopy revealed the existence of bridges of various intensities between the droplets of the emulsion containing either PEG or the polycation, probably because of the configuration of the ON at the interface. Cationic emulsion/ Oligonucleotide delivery/ Stearylamine/ DSPE-PEG/ FRET/ Surface tension

Terada, Megumi, Mizuhashi, Fukutaro, Murata, Kyoji, and Tomita, Takako (1999). Mepanipyrim, a New Fungicide, Inhibits Intracellular Transport of Very Low Density Lipoprotein in Rat Hepatocytes. Toxicology and Applied Pharmacology 154: 1-11.
Chem Codes: Chemical of Concern: DZ Rejection Code: MIXTURE, IN VITRO.

We have previously reported that ingestion of mepanipyrim induces fatty liver in rats due to the inhibitory effect on the synthesis or secretion of hepatocytic very low density lipoproteins (VLDL). To clarify the mechanism by which mepanipyrim induces fatty liver, morphological and biochemical effects of mepanipyrim on the movement of VLDL in rat liver and in the primary culture of rat hepatocytes were investigated. Inin vivoexperiments, rats were fed for 4 days a diet containing mepanipyrim at 4,000 ppm. VLDL accumulation in the Golgi apparatus of the liver, especially in the secretory vacuoles, was observed in the treated rats and in the hepatocytes treated for 2 hr with 25 [mu]g/ml mepanipyrim. Using 6-[N-(7-nitrobenz-2-oxa-1,3-diazol-4-yl)amino]caproyl-sphingosine (C6-NBD-ceramide), a selective staining agent for the Golgi apparatus, it was found that mepanipyrim inhibited C6-NBD-ceramide transport from the Golgi to the cell surface of cultured hepatocytes. The density of the VLDL-loaded secretory vacuoles isolated from the Golgi fractions was greater in mepanipyrim-treated rat livers compared with that in the control. Immunofluorescence micrograph of rat hepatocytes stained with anti-[alpha]-tubulin monoclonal antibody demonstrated that mepanipyrim neither affected microtubule network nor changed the intracellular ATP level. These results together suggested that fatty liver induced by mepanipyrim results mainly from the inhibition of the transport of hepatic VLDL from the Golgi to the cell surface. The inhibition of the transport of hepatic VLDL appears to result from qualitative changes in VLDL such as alteration of the apoprotein composition and/or insufficient lipidation of VLDL.

Termonia, A. and Termonia, M. (1997). FULL SCAN GC-MS QUANTITATION OF PESTICIDES IN SPRING WATER AT THE 10 PPT LEVEL USING LARGE VOLUME ON-COLUMN INJECTION. Hrc Journal of High Resolution Chromatography 20 : 447-450.
Chem Codes: MTL Rejection Code: FATE.

ABSTRACT: BIOSIS COPYRIGHT: BIOL ABS. RRM RESEARCH ARTICLE METHODOLOGY SPRING WATER DICHLORVOS POLLUTANT PESTICIDE ALPHA-HCH HCB ATRAZINE BETA-HCH DIAZINON DELTA-HCH LINDANE MALATHION METOLACHLOR PARATHION ENDOSULFAN ETHION CARBOPHENOTHION METHOXYCHLOR AZINPHOS-ETHYL TRACE LEVEL POLLUTANT DETECTION LARGE VOLUME ON-COLUMN INJECTION FULL SCAN GC-MS LARGE VOLUME ON-COLUMN INJECTION FULL SCAN GAS CHROMATOGRAPHY-MASS SPECTROMETRY POLLUTION ANALYTICAL METHOD

KEYWORDS: Ecology
KEYWORDS: Biochemical Methods-General
KEYWORDS: Biophysics-General Biophysical Techniques
KEYWORDS: Public Health: Environmental Health-Air
KEYWORDS: Pest Control

Thelin, G. P. (1997). National Assessment of Pesticides in the Streams, Rivers, and Ground Water of the United States. U.S.G.S.National Water Quality Assessment Pesticide National Synthesis Project 7.

Chem Codes: EcoReference No.: 45855
Chemical of Concern: DZ Rejection Code: NO SPECIES/NO TOX DATA.

Thomas, B. V. (1998). Organophosphate Insecticides: Metabolism, Excretion, Forensic and Mechanistic Investigations in Fish.

Chem Codes: Chemical of Concern: DZ Rejection Code: NO COC.

Descriptors: Bioaccumulation

Descriptors: Fish physiology
Descriptors: Insecticides
Descriptors: Bioassays
Descriptors: Ictalurus punctatus
Abstract: Organophosphate insecticides (OPs) can move off of application sites into non-target areas such as waterways and intoxicate fish and other biota. Methods of assessing OP exposure to fish need to be developed, and hydrolytic behavior of the compounds is important to characterize. After waterborne dosing the in vivo metabolism and excretion of terbufos and the associated acetylcholinesterase (AChE) depression were studied in channel catfish. Also, hydrolysis rates and mechanisms were determined for several OPs, and the relationship between hydrolytic stability and potency toward fish brain AChE from several species using five OPs was investigated. The major dialkyl phosphate metabolite of terbufos detected in the urine, bile and other matrices of dosed fish was diethylthiophosphate (DETP). A novel catheter design allowed measurement of a biphasic DETP excretion pattern in the urine up to 72 h post-dose. Terbufos was identified in the abdominal fat of dosed fish, and AChE activity in plasma and brain of dosed fish was significantly depressed. The amounts of DETP in urine, terbufos in fat and AChE inhibition were positively correlated with dose. DETP in bile, terbufos in fat, and brain AChE depression were also useful post-mortem indicators of OP exposure. Hydrolysis rates of selected OPs were similar to some published results but were higher than other reports. There were two different mechanisms (neutral and basic) by which terbufos, phorate and disulfoton were hydrolyzed. The neutral mechanism involved reaction in the leaving group and was the major degradation pathway for both terbufos and phorate under acidic and neutral conditions. The neutral mechanism was not a major pathway for disulfoton hydrolysis at any pH tested. At high pH the base-catalyzed mechanism (hydroxide reaction at the phosphorus) predominated for all three compounds. The dissimilarity in hydrolytic behavior under acid and neutral conditions for disulfoton compared to terbufos and phorate can be attributed to a slight difference in the leaving group structures of these compounds. The base- catalyzed hydrolysis rate constants for five OPs showed generally inverse linear correlation with their in vitro IC50s toward fish brain AChE when compared after log-log transformation.
Thesis publ. date: 1996, 149pp. Source UMI, 300 N Zeeb Rd, POB 1346, Ann Arbor, MI 48106, USA (800.521.0600) or www.umi.com/hp/Products/Dissertations.html.
Other numbers: AAT 9816627
Language: English
English
Publication Type: Book Monograph
Publication Type: Dissertation
Environmental Regime: Freshwater
Classification: Q5 01504 Effects on organisms
Classification: Q1 01582 Fish culture
Classification: Q3 01582 Fish culture
Subfile: ASFA 1: Biological Sciences & Living Resources; ASFA 3: Aquatic Pollution & Environmental Quality; ASFA Aquaculture Abstracts

Thompson, A. R. (1973). Persistence of Biological Activity of Seven Insecticides in Soil Assayed with Folsomia Candida. J.Econ.Enthomol. 66: 855-857 (OECDG Data File).

EcoReference No.: 56391

Chemical of Concern: CBF,DLD,DZ,PRT,CPY; Habitat: T; Effect Codes: MOR; Rejection Code: NO ENDPOINT(ALL CHEMS).

Thompson, A. R. and Gore, F. L. (1972). Toxicity of Twenty-Nine Insecticides to Folsomia candida: Laboratory Studies. J.Econ.Entomol. 65: 1255-1260.

EcoReference No.: 40474

Chemical of Concern: DLD,DDT,CBF,ADC,MOM,CBL,HCCH,AND,AZ,EN,PRN,MP,DS,DZ,CPY,CHD,PRT,FNT,DZ,FNF,HPT; Habitat: T; Effect Codes: MOR; Rejection Code: NO ENDPOINT(ALL CHEMS).

Thompson, C. R., Kats, G., Dawson, P., and Doyle, D. (1981). Development of a Protocol for Testing Effects of Toxic Substances on Plants. EPA-600/3-81-006, U.S.EPA, Corvallis, OR 37 p. (U.S.NTIS PB81-157901).

EcoReference No.: 72129

Chemical of Concern: EDT,DZ,ACP,PAQT,SFL,NACl0; Habitat: T; Effect Codes: BCM; Rejection Code: NO ENDPOINT(ALL CHEMS).

THOMPSON HM, LANGTON SD, and HART, A. DM (1995). Prediction of inter-species differences in the toxicity of organophosphorus pesticides to wildlife: A biochemical approach. COMPARATIVE BIOCHEMISTRY AND PHYSIOLOGY C PHARMACOLOGY TOXICOLOGY & ENDOCRINOLOGY; 111 1-12.

Chem Codes: Chemical of Concern: DZ Rejection Code: IN VITRO.

BIOSIS COPYRIGHT: BIOL ABS. The activation of organophosphorus pesticides and sensitivity of 'B' esterases to inhibition (I50) by the oxon metabolites were investigated in brain, liver and serum as the basis for a model to predict the toxicity of organophosphorus pesticides to four avian species. There were statistically significant correlations between LD50 and brain rate of activation of the OP (r = 0.68), brain acetylcholinesterase I50 (r = 0.88), and serum carboxylesterase I50 (r = 0.60). A significant proportion of the oxon produced within the liver is unlikely to reach the brain, due to irreversible binding by 'B' esterases. The production of the active oxon form of the pesticide within the brain, and the sensitivity of the brain AChE to inhibition, are probably the most important factors in determining the avian toxicity of organophosphorus pesticides. Animals/ Ecology/ Biochemistry/ Amino Acids/ Peptides/ Proteins/ Biophysics/ Macromolecular Systems/ Molecular Biology/ Enzymes/Physiology/ Physiology, Comparative/ Metabolism/ Amino Acids/Metabolism/ Peptides/Metabolism/ Proteins/Metabolism/ Digestive System Diseases/Pathology/ Digestive System/Pathology/ Blood Chemical Analysis/ Body Fluids/Chemistry/ Lymph/Chemistry/ Nervous System Diseases/Pathology/ Poisoning/ Animals, Laboratory/ Herbicides/ Pest Control/ Pesticides/ Birds/ Birds/ Birds/ Birds

Thompson, Nancy L., Brian, Adrienne A., and McConnell, Harden M. (1984). Covalent linkage of a synthetic peptide to a fluorescent phospholipid and its incorporation into supported phospholipid monolayers. Biochimica et Biophysica Acta (BBA) - Biomembranes 772: 10-19.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.

A number of fluorescent peptide-lipid conjugates have been synthesized. Peptides with ten or eleven amino acids are linked through a single lysine residue to the headgroup of phosphatidylethanolamine, fluorescently labelled on one acyl chain, using homobifunctional disuccinimidyl crosslinking reagents. Peptide-lipids can be further derivatized with the hapten dinitrophenyl. Purified peptide-lipids have been incorporated into dimyristoylphosphatidylcholine monolayers at the interface of air and phosphate-buffered saline, at concentrations of up to 11 mol%. For equal average molecular areas, monolayers containing peptide-lipids have higher surface pressures than pure lipid monolayers; for equal surface pressures, peptide-lipid monolayers are have higher average molecular areas than pure lipid monolayers. When the peptide-lipid monolayers are transferred to hydrophobic glass slides, the fluorescence appears uniformly distributed. Fluorescence recovery after photobleaching measurements indicate that peptide-lipids diffuse in the monolayer with coefficient 1.5 [middle dot] 10-9 cm2/s, which is much smaller than that of typical lipids in fluid membranes. In addition, the diffusion coefficient of peptide-lipids decreases with increasing peptide-lipid concentration. We conclude that the peptide portion of the peptide-lipid associates with the lipid monolayer and/or that peptide-lipids oligomerize. Peptide-lipid conjugate/ Lipid monolayer/ Surface pressure/ Diffusion coefficient

Tice, Colin M (2002). Selecting the right compounds for screening: use of surface-area parameters. Pest Management Science 58: 219-233.
Chem Codes: Chemical of Concern:PCZ,FZS,DSP,PYZ,RTN,RSM Rejection Code: CHEM METHODS.

Polar surface area, total surface area and percentage surface area have been calcd. from three-dimensional structures of 88 post-emergence herbicides, 93 pre-emergence herbicides and 237 insecticides. Preferred ranges of values of these parameters were identified. Since the compds. in the training sets are used on a wide variety of species and target sites with various application modes, the parameter ranges are necessarily broad. The utility of the surface-area parameter ranges in selection of compds. for agrochem. screening was compared with the use of ranges of the Lipinski Rule of 5 parameters: mol. mass, calcd. log P, no. of hydrogen-bond donors and no. of hydrogen-bond acceptors. The more computationally intensive surface-area parameters did not offer any obvious advantage over the Lipinski Rule of 5 parameters. [on SciFinder (R)] Copyright: Copyright 2005 ACS on SciFinder (R))

Database: CAPLUS
Accession Number: AN 2002:210355
Chemical Abstracts Number: CAN 136:381730
Section Code: 5-4
Section Title: Agrochemical Bioregulators
Document Type: Journal
Language: written in English.
Index Terms: Surface area (mol.; use of surface-area parameters for agrochem. screening of herbicides and insecticides); Herbicides; Insecticides; Polar effect (use of surface-area parameters for agrochem. screening of herbicides and insecticides)
CAS Registry Numbers: 162320-67-4 (Flufenzine) Role: AGR (Agricultural use), PRP (Properties), BIOL (Biological study), USES (Uses) (Flufenzine; use of surface-area parameters for agrochem. screening of herbicides and insecticides); 50-29-3 (DDT); 52-68-6 (Trichlorfon); 54-11-5 (Nicotine); 55-38-9 (Fenthion); 56-38-2 (Parathion); 57-39-6 (Metepa); 58-89-9 (Lindane); 60-51-5 (Dimethoate); 61-82-5 (Amitrole); 62-73-7 (Dichlorvos); 63-25-2 (Carbaryl); 70-43-9 (Barthrin); 72-43-5 (Methoxychlor); 72-54-8 (TDE); 72-56-0 (Ethylan); 76-03-9 (TCA); 76-44-8 (Heptachlor); 78-57-9 (Menazon); 80-33-1 (Chlorfenson); 83-79-4 (Rotenone); 86-50-0 (Azinphos-methyl); 93-65-2 (Mecoprop); 93-71-0 (CDAA); 94-74-6 (MCPA); 94-75-7 (2,4-D); 94-81-5 (MCPB); 94-82-6 (2,4-DB); 97-17-6 (Dichlofenthion); 101-42-8 (Fenuron); 107-49-3 (TEPP); 114-26-1 (Propoxur); 115-26-4 (Dimefox); 115-32-2 (Dicofol); 115-90-2 (Fensulfothion); 116-06-3 (Aldicarb); 116-29-0 (Tetradifon); 119-12-0 (Pyridaphenthion); 120-36-5 (Dichlorprop); 121-20-0 (Cinerin II); 121-21-1 (Pyrethrin I); 121-75-5 (Malathion); 122-10-1 (Bomyl); 122-14-5 (Fenitrothion); 122-34-9 (Simazine); 126-22-7 (Butonate); 133-90-4 (Chloramben); 139-40-2 (Propazine); 141-66-2 (Dicrotophos); 143-50-0 (Chlordecone); 144-41-2 (Morphothion); 150-68-5 (Monuron); 152-16-9 (Schradan); 297-78-9 (Isobenzan); 297-97-2 (Thionazin); 298-00-0 (Parathion-methyl); 298-02-2 (Phorate); 298-04-4 (Disulfoton); 299-84-3 (Fenchlorphos); 300-76-5 (Dibrom); 301-12-2 (Oxydemeton-methyl); 311-45-5 (Paraoxon); 315-18-4 (Mexacarbate); 327-98-0 (Trichloronate); 333-41-5 (Diazinon); 470-90-6 (Chlorfenvinfos); 510-15-6 (Chlorobenzilate); 534-52-1 (DNOC); 545-55-1 (TEPA); 555-37-3 (Neburon); 563-12-2 (Ethion); 584-79-2 (Allethrin); 640-15-3 (Thiometon); 644-64-4 (Dimetilan); 709-98-8 (Propanil); 732-11-6 (Phosmet); 741-58-2 (Bensulide); 759-94-4 (EPTC); 786-19-6 (Carbophenothion); 834-12-8 (Ametryne); 841-06-5 (Methoprotryne); 886-50-0; 919-86-8 (Demeton-S-methyl); 944-22-9 (Fonofos); 947-02-4 (Phosfolan); 950-10-7; 950-37-8 (Methidation); 957-51-7 (Diphenamid); 1031-47-6 (Triamiphos); 1071-83-6 (Glyphosate); 1113-02-6 (Omethoate); 1114-71-2 (Pebulate); 1129-41-5 (Metolcarb); 1134-23-2 (Cycloate); 1172-63-0 (Jasmolin II); 1194-65-6 (Dichlobenil); 1420-07-1 (Dinoterb); 1563-66-2 (Carbofuran); 1582-09-8 (Trifluralin); 1610-18-0 (Prometon); 1646-88-4 (Aldoxycarb); 1689-83-4 (Ioxynil); 1689-84-5 (Bromoxynil); 1698-60-8 (Chloridazon); 1702-17-6 (Clopyralid); 1836-75-5 (Nitrofen); 1861-32-1 (Dacthal); 1861-40-1 (Benfluralin); 1912-24-9 (Atrazine); 1912-26-1 (Trietazine); 1918-00-9 (Dicamba); 1918-11-2 (Terbucarb); 1918-16-7 (Propachlor); 1982-47-4 (Chloroxuron); 1982-49-6 (Siduron); 2008-41-5 (Butylate); 2032-65-7 (Methiocarb); 2104-64-5 (EPN); 2104-96-3 (Bromophos); 2164-08-1 (Lenacil); 2164-17-2 (Fluometuron); 2212-67-1 (Molinate); 2227-17-0 (Dienochlor); 2275-18-5 (Prothoate); 2275-23-2 (Vamidothion); 2303-16-4 (Diallate); 2303-17-5 (Triallate); 2310-17-0 (Phosalone); 2312-35-8 (Propargite); 2385-85-5 (Mirex); 2425-10-7 (Xylylcarb); 2439-01-2 (Quinomethionate); 2463-84-5 (Dicapthon); 2497-07-6 (Oxydisulfoton); 2540-82-1 (Formothion); 2595-54-2 (Mecarbam); 2597-03-7 (Phenthoate); 2631-37-0 (Promecarb); 2631-40-5 (Isoprocarb); 2636-26-2 (Cyanophos); 2655-14-3 (XMC); 2655-19-8 (Butacarb); 2674-91-1 (Oxydeprofos); 2921-88-2 (Chlorpyriphos); 2941-55-1 (Ethiolate); 3060-89-7 (Metobromuron); 3244-90-4 (Aspon); 3309-87-3 (DMCP); 3337-71-1 (Asulam); 3689-24-5 (Sulfotep); 3766-81-2 (Fenobucarb); 3792-59-4 (EPBP); 3811-49-2 (Dioxabenzofos); 3813-05-6 (Benazolin); 3942-54-9 (CPMC); 4151-50-2 (Sulfluramid); 4824-78-6 (Bromophos-ethyl); 4849-32-5 (Karbutilate); 5598-13-0; 5827-05-4 (IPSP); 5902-51-2 (Terbacil); 5915-41-3 (Terbuthylazine); 6164-98-3 (Chlordimeform); 6923-22-4 (Monocrotophos); 6988-21-2 (Dioxacarb); 7287-19-6 (Prometryn); 7287-36-7 (Monalide); 7292-16-2 (Propaphos); 7696-12-0 (Tetramethrin); 7700-17-6 (Crotoxyphos); 7786-34-7 (Mevinphos); 8001-35-2 (Toxaphene); 10265-92-6 (Methamidophos); 10311-84-9 (Dialifor); 10453-86-8 (Resmethrin); 11141-17-6 (Azadirachtin); 12407-86-2 (Trimethacarb); 13067-93-1 (Cyanofenphos); 13071-79-9 (Terbufos); 13171-21-6 (Phosphamidon); 13181-17-4 (Bromofenoxim); 13194-48-4 (Ethoprophos); 13360-45-7 (Chlorbromuron); 13593-03-8 (Quinalphos); 13684-56-5 (Desmedipham); 13684-63-4 (Phenmedipham); 14816-18-3 (Phoxim); 14816-20-7 (Chlorphoxim); 15263-53-3 (Cartap); 15299-99-7 (Napropamide); 15972-60-8 (Alachlor); 16752-77-5 (Methomyl); 17606-31-4 (Bensultap); 18181-70-9 (Iodofenphos); 18181-80-1 (Bromopropylate); 18854-01-8 (Isoxathion); 19044-88-3 (Oryzalin); 19937-59-8 (Metoxuron); 20354-26-1 (Methazole); 21548-32-3 (Fosthietan); 21609-90-5 (Leptophos); 21725-46-2 (Cyanazine); 22224-92-6 (Fenamiphos); 22248-79-9 (Tetrachlorvinfos); 22259-30-9 (Formetanate); 22781-23-3 (Bendiocarb); 23031-36-9 (Prallethrin); 23103-98-2 (Pirimicarb); 23184-66-9 (Butachlor); 23505-41-1 (Pirimiphos-ethyl); 23560-59-0 (Heptenophos); 23950-58-5 (Pronamide); 24017-47-8 (Triazophos); 24151-93-7 (Piperophos); 24934-91-6 (Chlormephos); 25057-89-0 (Bentazone); 25171-63-5 (Thiocarboxime); 25311-71-1 (Isofenphos); 25319-90-8 (MCPA-thioethyl); 25402-06-6 (Cinerin I); 26002-80-2 (Phenothrin); 26399-36-0 (Profluralin); 27314-13-2 (Norflurazon); 28249-77-6 (Thiobencarb); 29091-05-2 (Dinitramine); 29091-21-2 (Prodiamine); 29104-30-1 (Benzoximate); 29973-13-5 (Ethiofencarb); 30560-19-1 (Acephate); 31218-83-4 (Propetamphos); 32861-85-1 (Chlomethoxyfen); 33089-61-1 (Amitraz); 33245-39-5 (Fluchloralin); 33820-53-0 (Isopropalin); 34256-82-1 (Acetochlor); 34622-58-7 (Orbencarb); 34643-46-4 (Prothiofos); 34681-10-2 (Butocarboxim); 35256-85-0 (Butam); 35367-38-5 (Diflubenzuron); 35400-43-2 (Sulprofos); 35575-96-3 (Azamethiphos); 35597-43-4 (Bialaphos); 36335-67-8 (Butamifos); 36614-38-7 (Isothioate); 36756-79-3 (Tiocarbazil); 38260-54-7 (Etrimfos); 38727-55-8 (Diethatyl-ethyl); 39196-18-4 (Thiofanox); 39300-45-3 (Dinocap); 39515-40-7 (Cyphenothrin); 39515-41-8 (Fenpropathrin); 40487-42-1 (Pendimethalin); 40596-69-8 (Methoprene); 41096-46-2 (Hydroprene); 41198-08-7 (Profenofos); 41295-28-7 (Methoxyphenone); 42509-80-8 (Isazophos); 42588-37-4 (Kinoprene); 42609-52-9 (Dymron); 42609-73-4 (Methyldymron); 50512-35-1; 50594-66-6 (Acifluorfen); 51218-45-2 (METOLACHLOR); 51218-49-6 (Pretilachlor); 51276-47-2 (Glufosinate); 51338-27-3 (Diclofop-methyl); 51487-69-5 (Cloethocarb); 51630-58-1 (Fenvalerate); 52315-07-8 (Cypermethrin); 52570-16-8 (Naproanilide); 52645-53-1 (Permethrin); 52756-25-9 (Flamprop-methyl); 52888-80-9 (Prosulfocarb); 52918-63-5 (Deltamethrin); 54593-83-8 (Chlorethoxyfos); 55283-68-6 (Ethalfluralin); 55285-14-8 (Carbosulfan); 55335-06-3 (Triclopyr); 55512-33-9 (Pyridate); 55634-91-8 (Alloxydim); 58011-68-0 (Pyrazolate); 59669-26-0 (Thiodicarb); 59682-52-9 (Fosamine); 59756-60-4 (Fluridone); 61213-25-0 (Flurochloridone); 62850-32-2 (Fenothiocarb); 63782-90-1 (Flamprop-M-isopropyl); 63935-38-6 (Cycloprothrin); 64249-01-0 (Anilofos); 64628-44-0 (Triflumuron); 65907-30-4 (Furathiocarb); 66215-27-8 (Cyromazine); 66441-23-4 (Fenoxaprop-ethyl); 66841-25-6 (Tralomethrin); 67129-08-2 (Metazachlor); 68085-85-8 (Cyhalothrin); 68359-37-5 (Cyfluthrin); 69327-76-0 (Buprofezin); 69335-91-7 (Fluazifop); 69377-81-7 (Fluroxypyr); 69806-40-2 (Haloxyfop-methyl); 69806-50-4 (Fluazifop-butyl); 70124-77-5 (Flucythrinate); 71422-67-8 (Chlorfluazuron); 71751-41-2 (Abamectin); 73250-68-7 (Mefenacet); 74051-80-2 (Sethoxydim); 74070-46-5 (Aclonifen); 74115-24-5 (Clofentezine); 76578-12-6 (Quizalofop); 77501-63-4 (Lactofen); 77501-90-7 (Fluoroglycofen-ethyl); 78587-05-0 (Hexythiazox); 79277-27-3 (Thifensulfuron methyl); 79538-32-2 (Tefluthrin); 80060-09-9 (Diafenthiuron); 80844-01-5 (Chloproxyfen); 80844-07-1 (Etofenprox); 81335-77-5 (Imazethapyr); 81405-85-8 (Imazamethabenz-methyl); 81777-89-1 (Clomazone); 82558-50-7 (Isoxaben); 82560-54-1 (Benfuracarb); 82657-04-3 (Bifenthrin); 83121-18-0 (Teflubenzuron); 83130-01-2 (Alanycarb); 83164-33-4 (Diflufenican); 85785-20-2 (Esprocarb); 85830-77-9 (Triazofenamide); 86209-51-0 (Primisulfuron-methyl); 86763-47-5 (Propisochlor); 87310-56-3 (Butenachlor); 87546-18-7 (Flumiclorac-pentyl); 87674-68-8 (Dimethenamid); 87757-18-4 (Isoxapyrifop); 87818-31-3 (Cinmethylin); 87820-88-0 (Tralkoxydim); 88402-43-1 (Chlorphthalim); 89784-60-1 (Pyraclofos); 90982-32-4 (Chlorimuron-ethyl); 94593-91-6 (Cinosulfuron); 95465-99-9 (Cadusafos); 95617-09-7 (Fenoxaprop); 95737-68-1 (Pyriproxyfen); 96182-53-5 (Tebupirimphos); 96489-71-3 (Pyridaben); 96491-05-3 (Thenylchlor); 96525-23-4 (Flurtamone); 97780-06-8; 97886-45-8 (Dithiopyr); 98886-44-3 (Fosthiazate); 99105-77-8 (Sulcotrione); 99129-21-2 (Clethodim); 100646-51-3; 101007-06-1 (Acrinathrin); 101200-48-0 (Tribenuron-methyl); 101205-02-1; 101463-69-8 (Flufenoxuron); 102851-06-9 (Tau-fluvalinate); 104040-78-0 (Flazasulfuron); 104098-48-8 (Imazapic); 104770-29-8 (NC-330); 105024-66-6 (Silafluofen); 107360-34-9 (NC-170); 107713-58-6 (Flufenprox); 109293-97-2 (Diflufenzopyr); 111479-05-1 (Propaquizafop); 111578-32-6 (Metobenzuron); 111872-58-3 (Halfenprox); 111991-09-4 (Nicosulfuron); 112143-82-5 (Triazamate); 112226-61-6 (Halofenozide); 112410-23-8 (Tebufenozide); 112636-83-6 (Dicyclanil); 113036-88-7 (Flucycloxuron); 114311-32-9 (Imazamox); 114420-56-3 (Clodinafop); 117337-19-6 (Fluthiacet-methyl); 117718-60-2 (Thiazopyr); 119126-15-7 (Flupoxam); 119168-77-3 (Tebufenpyrad); 119738-06-6; 120068-37-3 (Fipronil); 120162-55-2 (Azimsulfuron); 122008-85-9 (Cyhalofop-butyl); 122453-73-0 (Chlorfenapyr); 122836-35-5 (Sulfentrazone); 122931-48-0 (RIMSULFURON); 123249-43-4 (Thidiazimin); 123312-89-0 (Pymetrozine); 125401-75-4 (Bispyribac); 126535-15-7 (Triflusulfuron-methyl); 128639-02-1 (Carfentrazone-ethyl); 129630-19-9 (Pyraflufen-ethyl); 131086-42-5 (Ethoxyfen-ethyl); 131929-63-0 (Spinosyn D); 134098-61-6 (Fenpyroximate); 135410-20-7 (Acetamiprid); 138164-12-2 (Butroxydim); 138261-41-3 (Imidacloprid); 141776-32-1 (Sulfosulfuron); 142459-58-3 (Flufenacet); 144651-06-9 (Oxasulfuron); 144740-53-4 (Flupyrsulfuron-methyl); 147838-04-8 (XR-100); 149877-41-8 (Bifenazate); 150824-47-8 (Nitenpyram); 153233-91-1 (Etoxazole); 160791-64-0 (Flubrocythrinate); 161050-58-4 (Methoxyfenozide); 168088-61-7 (Pyribenzoxim); 173584-44-6 (Indoxacarb) Role: AGR (Agricultural use), PRP (Properties), BIOL (Biological study), USES (Uses) (use of surface-area parameters for agrochem. screening of herbicides and insecticides)