Torii, Sigeru, Okumoto, Hiroshi, Sadakane, Masahiro, Hai, A. K. M. Abdul, and Tanaka, Hideo (1993). Carbonylative [2+2] cycloaddition for the construction of [beta]-lactam skeleton with palladium catalyst. Tetrahedron Letters 34: 6553-6556.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.
Carbonylation/ Palladium Catalyst/ [2+2] Cycloaddition/ [beta]-Lactam/ Stereoselective
TORRES CM, PICO, Y., MARIN, R., and MANES, J. (1997). Evaluation of organophosphorus pesticide residues in citrus fruits from the Valencian Community (Spain). JOURNAL OF AOAC INTERNATIONAL; 80 1122-1128.
Chem Codes : Chemical of Concern: DZ Rejection Code: FATE.
BIOSIS COPYRIGHT: BIOL ABS. Approximately 200 citrus samples from markets of the Valencian Community (Spain) were analyzed to establish their residue levels in 12 organophosphorus pesticide residues during the 1994-1995 campaign. The organophosphorus pesticides carbophenothion, chlorpyriphos, chlorfenvinphos, diazinon, ethion, fenitrothion, malathion, methidation, methylparathion, phosmet, quinalphos, and tetradifon were simultaneously extracted by matrix solidphase dispersion and determined by gas chromatography-mass spectrometry using selected ion monitoring mode. A total of 32.25% contained pesticide residues and 6.9% exceeded the European Union Maximum Residue Levels (MRLs). The pesticides found in the samples with residues above MRLs were carbophenothion, ethion, methidathion, and methyl parathion. Lower level residues of these and the other pesticides studied (except diazinon) were frequently found. The estimated daily intake of the 12 organophosphorus pesticide residues during the studied p Biochemistry/ Biophysics/ Food Technology/ Poisoning/ Animals, Laboratory/ Herbicides/ Pest Control/ Pesticides
Tory, Monica C. and Rod Merrill, A. (2002). Determination of membrane protein topology by red-edge excitation shift analysis: application to the membrane-bound colicin E1 channel peptide. Biochimica et Biophysica Acta (BBA) - Biomembranes 1564: 435-448.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.
A new approach for the determination of the bilayer location of Trp residues in proteins has been applied to the study of the membrane topology of the channel-forming bacteriocin, colicin E1. This method, red-edge excitation shift (REES) analysis, was initially applied to the study of 12 single Trp-containing channel peptides of colicin E1 in the soluble state in aqueous medium. Notably, REES was observed for most of the channel peptides in aqueous solution upon low pH activation. The extent of REES was subsequently characterized using a model membrane system composed of the tripeptide, Lys-Trp-Lys, bound to dimyristoyl-sn-glycerol-3-phosphatidylserine liposomes. Subsequently, data accrued from the model peptide-lipid system was used to interpret information obtained on the channel peptides when bound to dioleoyl-sn-glycerol-3-phosphatidylcholine/dioleoyl-sn-glycerol-3-phosphatidylglycerol membrane vesicles. The single Trp mutant peptides were divided into three categories based on the change in the REES values observed for the Trp residues when the peptides were bound to liposomes as compared to the REES values measured for the soluble peptides. F-404W, F-413W, F-443W, F-484W, and W-495 peptides exhibited small and/or insignificant REES changes ([Delta]REES) whereas W-424, F-431W, and Y-507W channel peptides possessed modest REES changes (3 nm<=[Delta]REES<=7 nm). In contrast, wild-type, Y-367W, W-460, Y-478W, and I-499W channel peptides showed large [Delta]REES values upon membrane binding (7 nm<[Delta]REES<=12 nm). The REES data for the membrane-bound structure of the colicin E1 channel peptide proved consistent with previous data for the topology of the closed channel state, which lends further credence to the currently proposed channel model. In conclusion, the REES method provides another source of topological data for assignment of the bilayer location for Trp residues within membrane-associated proteins; however, it also requires careful interpretation of spectral data in combination with structural information on the proteins being investigated. Tryptophan fluorescence/ Membrane interaction/ Channel structure
Trappe, J. M., Molina, R., and Castellano, M. (1984). Reactions of Mycorrhizal Fungi and Mycorrhizae Formation to Pesticides . Ann.Rev.Phytopathol. 22: 331-359.
Chem Codes: EcoReference No.: 72426
Chemical of Concern: PNB,DZ,Captan,Cu,CTN Rejection Code: REVIEW.
Treistman, Steven N., Moynihan, Margaret M., and Wolf, David E. (1987). Influence of alcohols, temperature, and region on the mobility of lipids in neuronal membrane. Biochimica et Biophysica Acta (BBA) - Biomembranes 898: 109-120.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.
Fluorescence recovery after photobleaching was used to examine lipid diffusibility in different regions of Aplysia neurons. Differences in diffusion of 1-acyl-2-(6-[N-(7-nitrobenz-2-oxa-1,3-diazol-4-yl)]aminohexanoyl)phosphatidylcholine (NBD-C6-PC) in the cell body, axon hillock, and axon were not apparent. Lipid diffusibility during temperature variations and exposure to alcohols was also examined by photobleaching techniques. For these studies, all measurements were made on the cell body. Alcohols were found to be selective in their effects upon the diffusibility of lipid probes. Neither ethanol nor butanol affected the diffusibility of NBD-PC. However, at the same concentrations, both of these alcohols caused a significant increase in the diffusion coefficient (D) for rhodamine-phosphatidylethanolamine (Rho-PE). The diffusion coefficient for NBD-PC in the cell body plasma membrane did not increase with warming, between 4[deg]C and 25[deg]C. The fraction of lipid probe free to diffuse (per cent recovery; %R) however, increased as temperature increased, within this range. The nonconventional relationship between temperature and D was even more pronounced for Rho-PE. As temperature increased, D became smaller for this probe, concurrent with an increase in %R. These results suggest that immobile viscous lipid is recruited into a mobile fraction as temperature increases, resulting in the maintenance of constant diffusibility. The effects of temperature on D and %R, and the selective effects of alcohols on lipid diffusibility suggest that the membrane is heterogeneously organized, on a submicroscopic scale, into domains. The implications of this organization for nerve function and responses of nervous systems to temperature and anesthetics are discussed. Fluorescence/ Lipid/ Photobleaching/ Fluorescence photobleaching recovery/ Temperature/ Alchol/ (Aplysia)
Trevisan, M., Montepiani, C., Ragozza, L., Bartoletti, C., Ioannilli, E., and Del Re, A. A. M. (1993). Pesticides in rainfall and air in Italy. Environmental Pollution 80: 31-39.
Chem Codes: Chemical of Concern: DZ Rejection Code: SURVEY.
The presence of pesticide residues in rain, throughfall, stemflow and in ambient air in two Italian forests affected by the forest damage phenomenon were investigated. Pesticides measured were: alachlor, atrazine, carbaryl, 2,4-, diazinon, dichlobenil, fluazifop-butyl, MCPA, parathion, phorate and trifluralin. Rainwater samples were collected from May to October 1988 at Vallombrosa and Renon, air and atmospheric particulates were sampled during April-June 1989, only at Vallombrosa. A total of 146 samples of rainfall and 20 samples of ambient air were analysed and 49 out of 166 samples contained at least one active ingredient. Herbicides were more frequent than insecticides, and their concentrations were also higher (max 3[middle dot]44 [mu]g litre-1).
Tronsmo, A. (1989). Effect of Fungicides and Insecticides on Growth of Botrytis cinerea, Trichoderma viride and T. harzianum. Norw.J.Agric.Sci. 3: 151-156.
EcoReference No.: 75156
Chemical of Concern: DMT,BMY,MZB,IPD,VCZ,TDF,MLN,BTN,Captan,Cu,DOP,TFR,AZ,DCF,DMT,FNTH,FNT,DZ,PRN,MCPP1; Habitat: T; Effect Codes: POP; Rejection Code: NO CONTROL(ALL CHEMS).
Tsezos, M. and Bell, J. P. (1989). Comparison of the biosorption and desorption of hazardous organic pollutants by live and dead biomass. Water Research 23: 561-568.
Chem Codes: Chemical of Concern: DZ Rejection Code: FATE.
The adsorption and desorption of lindane, diazinon, pentachlorophenol and 2-chlorobiphenyl by living and dead cells of the fungus R. arrhizus and activated sludge was studied. A generalization concerning the relative magnitude of biosorptive uptake between live and dead biomass cannot be made using the experimental data. Uptakes by live and dead cells are similarly correlated to the octanol/water partition coefficient of the organic pollutants. The desorption of the organic pollutants is not always complete. A part of the observed biosorptive uptake can be attributed to the cell walls of the microbial biomass. biosorption/ adsorption/ organic/ pollutants/ activated sludge/ desorption/ fate
Tsuda, T., Aoki, S., Inoue, T., and Kojima, M. (1995). Accumulation of diazinon, fenthion and fenitrothion by killfish from mixtures of the three pesticides. Toxicological and Environmental Chemistry [TOXICOL. ENVIRON. CHEM.]. Vol. 47, no. 3-4, pp. 251-255. 1995.
Chem Codes: Chemical of Concern: DZ Rejection Code: MIXTURE, METABOLISM.
ISSN: 0277-2248
Descriptors: pesticides
Descriptors: fish
Descriptors: bioaccumulation
Descriptors: water pollution effects
Descriptors: aquatic life
Descriptors: diazinon
Descriptors: insecticides
Descriptors: water pollution
Descriptors: pollution effects
Descriptors: Oryzias latipes
Abstract: Differences in the accumulation of diazinon, fenthion and fenitrothion by killifish (Oryzias latipes) at three concentration levels of mixtures of the pesticides were studied. For diazinon and fenthion, the higher the concentration levels, the longer the time required to reach plateaus. The bioconcentration factors (BCF) had a tendency to increase with an increase in concentration level for all pesticides. One-way analysis of variance was carried out to detect significant differences in the BCF of each pesticide among the concentration levels. There were significant differences (p < 0.05 or p < 0.01) after 6-48 hr except diazinon at 6 hr and fenitrothion at 48 hr.
Language: English
English
Publication Type: Journal Article
Environmental Regime: Freshwater
Classification: SW 3030 Effects of pollution
Classification: P 6000 TOXICOLOGY AND HEALTH
Classification: Q5 01504 Effects on organisms
Classification: X 24133 Metabolism
Subfile: Toxicology Abstracts; ASFA 3: Aquatic Pollution & Environmental Quality; Pollution Abstracts; Water Resources Abstracts
Tsuda, T., Aoki, S., Inoue, T., and Kojima, M. (1995). Accumulation of Diazinon, Fenthion and Fenitrothion by Killifish from Mixtures of the Three Pesticides. Toxicol.Environ.Chem. 47: 251-255.
Chem Codes: EcoReference No.: 16174
Chemical of Concern: DZ Rejection Code: MIXTURE.
Tsuda, T., Aoki, S., Kojima, M., and Fujita, T. (1992). Pesticides in Water and Fish from Rivers Flowing into Lake Biwa (II). Chemosphere 24: 1523-1531.
Chem Codes: EcoReference No.: 45856
Chemical of Concern: DZ Rejection Code: NO DURATION/SURVEY.
Tsuda, T., Aoki, S., Kojima, M., and Fujita, T. (1992). Pesticides in water and fish from rivers flowing into Lake Biwa (II). Chemosphere 24: 1523-1531.
Chem Codes: Chemical of Concern: DZ Rejection Code: SURVEY, MIXTURE.
Surveys of pesticides (diazinon, IBP, malathion and MEP) were performed for water and fish samples obtained from seven rivers flowing into Lake Biwa in 1990. The field data on accumulation of pesticides by pale chub ( ) and ayu sweetfish ( ) were compared with the laboratory experimental data on willow shiner ( ) and topmouth gudgeon ( ). The bioconcentration factors (BCF) of pesticides in the field could not be satisfactorily estimated from the experimental data. This is not only due to the difference of fish species but also the reason that the concentrations of these pesticides in the river water are changeable and those in the fish body do not reach plateaus instantly.
Tsuda, T., Aoki, S., Kojima, M., and Harada, H. (1991). Pesticides in water and fish from rivers flowing into Lake Biwa. Toxicological and Environmental Chemistry [TOXICOL. ENVIRON. CHEM.]. Vol. 34, no. 1, pp. 39-55. 1991.
Chem Codes: Chemical of Concern: DZ Rejection Code: SURVEY.
ISSN: 0277-2248
Descriptors: water pollution
Descriptors: pollution surveys
Descriptors: bioaccumulation
Descriptors: pesticides
Descriptors: freshwater fish
Descriptors: Pisces
Descriptors: Zacco platypus
Descriptors: Plecoglossus altivelis
Descriptors: Gnathopogon caerulescens
Descriptors: Pisces
Abstract: Surveys of pesticides were performed for water and fish samples obtained from seven rivers flowing into Lake Biwa. The field data on accumulation and excretion of pesticides by pale chub (Zacco platypus ) and ayu sweetfish (Plecoglossus altivelis ) were compared with the laboratory experimental data on willow shiner (Gnathopogon caerulescens ) in our previous reports. The bioconcentration factors (BCF) of pesticides in the field could not be satisfactorily estimated from the experimental data due to the difference of fish species. However, the order of BCF calculated from the field data (CNP > oxadiazon > benthiocarb > diazinon > IBP > simetryne) was almost same to that for willow shiner (CNP > oxadiazon > diazinon > benthiocarb > IBP > simetryne). Further, it has become apparent from the field data that these pesticides are rapidly excreted from pale chub and ayu sweetfish after stopping their use. These results were consistent with the experimental data for willow shiner showing rapid excretion rates of these pesticides.
Language: English
English
Publication Type: Journal Article
Environmental Regime: Freshwater
Classification: Q5 01504 Effects on organisms
Classification: P 2000 FRESHWATER POLLUTION
Classification: X 24136 Environmental impact
Subfile: Toxicology Abstracts; Pollution Abstracts; ASFA 3: Aquatic Pollution & Environmental Quality
Tsuda, T., Inoue, T., Kojima, M., and Aoki, S. (1996). Pesticides in water and fish from rivers flowing into Lake Biwa. Bulletin of Environmental Contamination and Toxicology. Vol. 57, no. 3, pp. 442-449. Sep 1996.
Chem Codes: Chemical of Concern: DZ Rejection Code: SURVEY.
ISSN: 0007-4861
Descriptors: pesticides
Descriptors: water pollution
Descriptors: bioaccumulation
Descriptors: Pisces
Descriptors: freshwater fish
Descriptors: agricultural pollution
Descriptors: agricultural runoff
Descriptors: fish
Descriptors: Japan, Biwa L.
Descriptors: water pollution sources
Descriptors: Pisces
Descriptors: Japan, Honshu, Shiga Prefect., Biwa L.
Abstract: We have already reported various pesticide contamination of water and fish (pale chub, ayu sweetfish and dark chub) from rivers flowing into Lake Biwa from April in 1988 to March in 1992. In this report, the same surveys were more extensively performed for twenty one pesticides (salithion, diazinon, IBP, tolclofosmethyl, chlorpyriphos, fenthion, malathion, fenitrothion, isofenphos, phenthoate, prothiophos, propaphos, methidathion, butamifos, isoprothiolane, edifenphos, EPN, pyridaphenthion, phosmet, benthiocarb and simetryne) from April in 1992 to March in 1993, and for nine pesticides (fenobucarb, carbofuran, simazine, chlorothalonil, pretilachlor, isoprothiolane, flutolanil, benthiocarb and simetryne) from April in 1993 to March in 1994.
Language: English
Publication Type: Journal Article
Environmental Regime: Freshwater
Classification: X 24136 Environmental impact
Classification: D 04802 Pollution characteristics and fate
Classification: P 2000 FRESHWATER POLLUTION
Classification: Q5 01504 Effects on organisms
Classification: SW 3020 Sources and fate of pollution
Classification: Q5 01503 Characteristics, behavior and fate
Subfile: Water Resources Abstracts; ASFA 3: Aquatic Pollution & Environmental Quality; Pollution Abstracts; Ecology Abstracts; Toxicology Abstracts
Tsuda, T., Kojima, M., Harada, H., Nakajima, A., and Aoki, S. (1997). Relationships of Bioconcentration Factors of Organophosphate Pesticides Among Species of Fish. Comp.Biochem.Physiol.C 116: 213-218.
EcoReference No.: 19012
Chemical of Concern: CPY,DS,DZ,MDT,FNTH,FNT,IFP; Habitat: A; Effect Codes: ACC; Rejection Code: NO CONTROL(ALL CHEMS).
TSUDA, T., KOJIMA, M., HARADA, H., NAKAJIMA, A., and AOKI, S. (1997). Relationships of bioconcentration factors of organophosphate pesticides among species of fish. COMPARATIVE BIOCHEMISTRY AND PHYSIOLOGY C PHARMACOLOGY TOXICOLOGY & ENDOCRINOLOGY; 116 213-218.
Chem Codes: Chemical of Concern: DZ Rejection Code: MODELING.
BIOSIS COPYRIGHT: BIOL ABS. A study was made of correlations between fish species in a logarithm of bioconcentration factor (logBCF) of 15 organophosphate pesticides in guppy (Lebistes reticulatus), killifish (Oryzias latipes), goldfish (Carassius auratus), and white cloud mountain fish (Tanichthys albonubes). The correlation coefficient (gamma) between the fish species (0.9458-0.9937) was considerably higher than that (0.6208-0.7642) between a logarithm of noctanol-water partition coefficient (logPow) and logBCF for the same 11 pesticides. If an appropriate reference fish can be selected as test fish, estimation of BCF in various species of fish by the BCF in the reference fish will be more accurate than that by Pow, because the former estimation considers the ionic characteristics, metabolism, molecular weights, etc., which are the reason for the low correlation between logPow and logBCF. Biochemistry/ Poisoning/ Animals, Laboratory/ Fishes
Tsuji, S., Tonogai, Y., Ito, Y., and Kanoh, S. (1986). The Influence of Rearing Temperatures on the Toxicity of Various Environmental Pollutants for Killifish (Oryzias latipes). J.Hyg.Chem.(Eisei Kagaku) 32 : 46-53 (JPN) (ENG ABS).
EcoReference No.: 12497
Chemical of Concern: Captan,CBL,DZ,HCCH,CuS,CuCl,CrAC, NaLS, CdCl, AgN, PL, BNZ, PbN, PbAc, FML, AND, 3CE, CF, MnCl, ZnCl2, DDT, FeCl3, CrO3, HgCl2, PRN, CTC,Se,Zn,C8OH; Habitat: A; Effect Codes: MOR; Rejection Code: NO FOREIGN.
Tsutsumi, Toshihiko, Tokumura, Akira, and Kitazawa, Shikifumi (1998). Undifferentiated HL-60 cells internalize an antitumor alkyl ether phospholipid more rapidly than resistant K562 cells. Biochimica et Biophysica Acta (BBA) - Lipids and Lipid Metabolism 1390: 73-84.
Chem Codes: Chemical of Concern: DZ Rejection Code: METHODS.
In this study, we confirmed a previous finding that 1-O-octadecyl-2-O-methyl-rac-glycero-3-phosphocholine (methyl-PAF) expresses higher antineoplastic activity against the promyelocytic leukemia cell line HL-60, than against the erythroleukemic cell line K562, and intended to clarify the reason for this. Using an albumin back-exchange method, we measured the rates of binding and internalization of methyl-PAF by HL-60 and K562 cells. We found that methyl-PAF associated very rapidly and to similar extents with the two types of cells at low concentrations of extracellular bovine serum albumin, but that when bound to the cell surface, it was internalized into HL-60 cells faster than into K562 cells. The internalization of methyl-PAF by HL-60 cells was concentration-independent, intracellular ATP-independent and susceptible to thiol group-modifying reagents and cytochalasin B. Thus the inward transbilayer movement of methyl-PAF seems to occur by cytochalasin B-sensitive protein-mediated mechanism based on passive diffusion not requiring energy, in which SH-groups of protein play a critical role. We also found that the internalization of 1-hexadecanoyl-2-(4,4-difluoro-5,7-dimethyl-4-bora-3a,4a-diaza-s-indacene-3-pentanoyl)-sn-glycero-3-phosphocholine (Bodipy-C5-PC), whose structure resembles that of methyl-PAF, into HL-60 cells was faster than that into K562 cells. Using a combination of an albumin back-exchange method and observation by confocal laser scanning microscopy, we next examined the intracellular distribution of this fluorescent phospholipid probe after its internalization. Intracellular membranes, especially those peripheral to nuclei, were fluorescence-labeled in both HL-60 and K562 cells, but fluorescence of the nuclear membranes was weak, suggesting that this probe seems mainly to accumulate in intracellular granules, and may interact directly with several key enzymes for phospholipid metabolism, leading to cell injury. Because the difference between the internalization rates of methyl-PAF in HL-60 and K562 cells was correlated with their different susceptibilities to the cytotoxic effect of methyl-PAF, we suggest that the capacities for uptake of methyl-PAF and its accumulation in intracellular membranes are critical factor for its induction of apoptosis. Methyl-PAF (ET-18-OCH3)/ HL-60 cell/ K562 cell/ Phospholipid internalization/ Bodipy-C5-PC
Tu, C. M. (1991). Effect of Some Technical and Formulated Insecticides on Microbial Activities in Soil. J.Environ.Sci.Health Part B 26: 557-573.
EcoReference No.: 69689
Chemical of Concern: Hg,CHD,ES,CPY,DZ,PRN,PMR,CYP,HgCl2,FNF,FNV; Habitat: T; Effect Codes: POP; Rejection Code: LITE EVAL CODED(CYP),OK(ALL CHEMS).
TU JC and ZHENG, J. (1993). COMPATIBILITY OF BIOCONTROL AGENTS WITH DCT. MEDEDELINGEN FACULTEIT LANDBOUWKUNDIGE EN TOEGEPASTE BIOLOGISCHE WETENSCHAPPEN UNIVERSITEIT GENT; 58 1359-1364 .
Chem Codes: Chemical of Concern: DZ Rejection Code: MIXTURE.
BIOSIS COPYRIGHT: BIOL ABS. RRM RESEARCH ARTICLE BACILLUS-SUBTILIS PSEUDOMONAS-FLUORESCENS GLIOCLADIUM-VIRENS RHIZOCTONIA-SOLANI FUSARIUM-SOLANI PYTHIUM-ULTIMUM PHASEOLUS-VULGARIS DIAZINON CAPTAN THIOPHANATE METHYL ROOT ROT SEED TREATMENT GROWTH PROLIFERATION REPRODUCTION MOBILITY BIOLOGICAL CONTROL INTEGRATED PEST MANAGEMENT Ecology/ Plants/ Biochemistry/ Movement/ Bacteria/Physiology/ Bacteria/Metabolism/ Plants/Anatomy & Histology/ Plants/Metabolism/ Biophysics/ Plants/Physiology/ Plants/Metabolism/ Plants/Growth & Development/ Biophysics/ Plants/Physiology/ Plants/Metabolism/ Plants/Anatomy & Histology/ Reproduction/ Vegetables/ Fungi/ Plant Diseases/ Plant Diseases/ Preventive Medicine/ Herbicides/ Pest Control/ Pesticides/ Pseudomonadaceae/ Gram-Positive Endospore-Forming Bacteria/ Mitosporic Fungi/ Phycomycetes/ Legumes
TU JC and ZHENG, J. (1993). EFFECTS ON SOIL MOISTURE ON DCT EFFICACY AGAINST WHITE BEAN ROOT ROT COMPLEX. MEDEDELINGEN FACULTEIT LANDBOUWKUNDIGE EN TOEGEPASTE BIOLOGISCHE WETENSCHAPPEN UNIVERSITEIT GENT; 58 1469-1475.
Chem Codes: Chemical of Concern: DZ Rejection Code: NON-ENGLISH.
BIOSIS COPYRIGHT: BIOL ABS. RRM RESEARCH ARTICLE PYTHIUM-ULTIMUM FUSARIUM-SOLANI RHIZOCTONIA-SOLANI DIAZINON CAPTAN THIOPHANATE METHYL FUNGICIDE SEED GERMINATION SEED ROT DAMPING OFF HYPOCOTYL INFECTION PHYTOTOXICITY SEED COAT FUNGAL GROWTH Biochemistry/ Poisoning/ Animals, Laboratory/ Plants/Anatomy & Histology/ Plants/Metabolism/ Biophysics/ Plants/Physiology/ Plants/Metabolism/ Plants/Growth & Development/ Biophysics/ Plants/Physiology/ Plants/Metabolism/ Plants/Anatomy & Histology/ Reproduction/ Soil/ Vegetables/ Fungi/ Plant Diseases/ Plant Diseases/ Preventive Medicine/ Herbicides/ Pest Control/ Pesticides/ Mitosporic Fungi/ Phycomycetes/ Legumes
Tuovinen, Kai, Paakkanen, Heikki, and Hanninen, Osmo (2000). Detection of pesticides from liquid matrices by ion mobility spectrometry. Analytica Chimica Acta 404: 7-17.
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