Full free study available at http://www.aaem.pl/pdf/11149.pdf
Ann Agric Environ Med. 2004;11(1):149-53.
Pesticide exposure in dwellings near
bulb growing fields in The Netherlands: an explorative study.
Hogenkamp A, Vaal M, Heederik D.
Astrid Hogenkamp, Science Shop for Biology, Utrecht University,
Padualaan 8, 3584 CH Utrecht, The Netherlands.
An explorative field study was conducted to assess residential
exposure to pesticides, regularly applied in bulb farming. House
dust floor samples were taken from homes of bulb farmers (n
= 12) and from homes in close proximity to a bulb field (i.e.
non-farmers) (n = 15). Samples were analysed for 7 pesticides
used by bulb growers in the sampling period. Of these pesticides,
chloropropham, flutolanil and vinchlozolin
could be detected in non-farmers homes.
All pesticides were detected in farmers' homes, except
metamitron. Median concentrations for chloropropham were significantly
higher in farmers' homes (0.05 vs. 0.20 microg/m(2), p = 0.03).
Logistic regression analyses showed that the odds for detecting
pesticides were higher in farmers' compared to non-farmers'
homes and remained higher after correction for potential confounders.
Results showed no significant effect of
proximity of a residence to a bulb field for median concentrations
of pesticides; however, logistic regression analysis
showed a borderline statistically significant effect for detecting
chloropropham above the detection limit (OR = 10, p = 0.08).
These findings demonstrate that, as expected, risk of exposure
is higher for bulb farmers than for non-farmers. They also indicate
that exposure to pesticides is not limited
to bulb farmers only, and this warrants further investigation.
Full free study available at http://jeq.scijournals.org/cgi/content/full/30/1/18
J Environ Qual. 2001 Jan-Feb;30(1):18-23.
In vitro pesticide degradation in turfgrass
soil incubated under open and sealed conditions.
Suzuki T, Yaguchi K, Suzuki S, Suga T.
Tama Branch Lab, Tachikawa, Tokyo, Japan. tsuzuki@tokyo-eiken.go.jp
Degradation of selected pesticides was conducted in a turfgrass
soil from a golf course
under open (i.e., allowing gas exchange with atmosphere) and
sealed systems. The time required for 50% of the initial dose
of fenitrothion (O,O-dimethyl O-4-nitro-m-tolyl phosphorothioate),
diazinon (O,O-dimethyl O-2-isopropyl-6-methylpyrimidin4-yl phosphorothioate),
iprodione [3-(3,5-dichlorophenyl)-N-isopropyl-2,4-dioxo-imidazolidine-1-carboxamide],
mecoprop [(RS)-2-(4-chloro-otolyloxy)propionic acid], and asulam
(4-aminophenylsulfonyl-carbamate) to dissipate (half-life, t
1/2) was less than 2 wk under both conditions. The t 1/2 values
of dithiopyr (S,S'-dimethyl 2-difluoromethyl-4-isobutyl-6-trifluoro-methylpyridine-3,5-dicarbothioate)
were 324 and 185 d under the open and sealed conditions, respectively.
The t 1/2 values of isoprothiolane (di-isopropyl 1,3-dithiolan-2-ylidene-malonate),
flutolanil (alpha,alpha,alpha-trifluoro-3'-isopropoxy-o-toluanilide),
and benefin (N-butyl-N-ethyl-alpha,alpha,alpha-trifluoro-2,6-dinitro-p-toluidine)
under the open conditions were 154, 336,
and 47 d, respectively. The t 1/2 values of these pesticides
increased slightly under the sealed conditions. The t 1/2 values
of terbutol (2,6-di-tert-butyl-4-methylphenyl N-methycarbamate)
and one of the major degradation products, N-demethyl-terbutol
(2,6-di-tert-butyl-4-methylphenyl carbamate), were 182 and 291
d under the open conditions and increased by six- and threefold
under the sealed conditions, respectively. The degradation system
under the sealed conditions could characterize the persistence
of terbutol and N-demethyl-terbutol, which were the most persistent
in the field.
http://www.ncbi.nlm.nih.gov/entrez/query.fcgi?cmd=Retrieve&db=pubmed&dopt=Abstract&list_uids=10507161
Sci Total Environ. 1999 Aug 30;234(1-3):223-31.
Application of short-term bioassay guided
chemical analysis for water quality of agricultural land run-off.
Okamura H, Omori M, Luo R, Aoyama I,
Liu D.
Research Institute for Bioresources, Okayama University, Kurashiki,
Japan. hokamura@rib.okayama-u.ac.jp
The effect of agricultural land run-off on the water quality
of Lake Kojima, Japan, was investigated using a short-term bioassay-guided
chemical analysis. Water samples were collected for 1 year starting
from June 1995 to June 1996. Toxicity of the dissolved and adsorbed
extracts in the water samples was evaluated using the Daphnia
immobilization test and the concentrations of pesticides and
putative toxic substance in the extracts were determined by
high performance liquid chromatography. Most of the dissolved
extracts caused immobilization of the test Daphnia magna at
low concentrations during the period of paddy pesticide application.
Some extracts were found to contain pesticides such as dymron,
mefenacet and flutolanil, but their
concentrations were too low to have a toxic effect on the daphnia.
An unknown toxic compound, Peak C, was isolated from some river
water samples, but it produced only a relatively weak toxicity
to Daphnia. To better understand the impact of agricultural
run-off on a receiving water body, the relationship between
the observed toxicity and the concentrations of pesticides and
Peak C in the water samples was studied both temporally and
spatially.
PMID: 10507161 [PubMed - indexed for MEDLINE]
From Toxline at Toxnet
ENVIRONMENTAL SCIENCE & TECHNOLOGY; 32 (7). 1998.
920-929.
Estimation of leachability and persistence
of pesticides at golf courses from
point-source monitoring and model to predict pesticide leaching
to groundwater.
SUZUKI T, KONDO H, YAGUCHI K, MAKI T,
SUGA T
Tama Branch Lab., Tokyo Metropolitan Res. Lab. Public Health,
3-16-25 Shibazaki-cho, Tachikawa, Tokyo 190, Japan.
The monitoring of 19 pesticides in drainage and groundwater
at a golf course was performed when there was no runoff water.
The loading rates of most pesticides via leaching water were
lower than 4% of application amount, except for more than 23%
for terbutol. The times of pesticides loading into the drainage
reducing to 50% of initial (t1/2(loading)) were 40.3 months
for terbutol, 9.4 months for isoprothiolane, 6.6
months for flutolanil, and within 1 month for the other
pesticides. On the basis of several published models for predicting
pesticides leaching to groundwater at agricultural land, the
pesticides having the GUS score greater than 0.4 or exhibiting
Koc less than 7000 cm3 g-1, and t1/2(soil) greater than 3 days
were classified as the pesticides leaching to groundwater at
golf courses. The golf course is a high pollution potential
area compared with agricultural land. For the persistence of
terbutol at golf courses, the concentrations of terbutol in
subsoils at [abstract truncated]
CAS Registry Numbers:
66332-96-5
66332-96-5
50512-35-1
1918-11-2
From Toxline at Toxnet
FOOD AND CHEMICAL TOXICOLOGY; 34 (11-12). 1996
(1997). 1091-1096.
Effects of pesticide mixtures at the
acceptable daily intake levels on rat carcinogenesis.
ITO N, HAGIWARA A, TAMANO S, FUTACUCHI
M, IMAIDA K, SHIRAI T
Nagoya City Univ., 1 Kawasumi, Mizuho-cho, Mizuho-ku, Nagoya
467, Japan.
Possible modifying effects of pesticide mixtures on tumorigenesis
were investigated with medium-term carcinogenesis protocols
for rapid detection of carcinogenic agents using male F344 rats.
In the 8-wk liver model, administration of 20 pesticides (19
organophosphorus compounds and one organochlorine), added to
the diet each at acceptable daily intake (ADI) levels, did not
enhance rat liver preneoplastic lesion development initiated
by diethyltyrosamine. In contrast, a mixture of these 20 pesticides
at 100 times the ADI significantly increased the number and
area of liver lesions. In the second experiment using a multi-organ
carcinogenicity protocol of 28 wk, mixtures of 40 pesticides
(high production examples) or 20 pesticides (suspected carcinogens)
added to the diet at their respective ADI levels did not modulate
carcinogenesis in any organ initiated by five known potent carcinogens
in combination. These results thus provide direct support for
the safety factor [abstract truncated]
Included in a long list of CAS Nos: 66332-96-5
From Toxline at Toxnet
NIPPON SUISAN GAKKAISHI; 62 (3). 1996.
414-419.
Evaluation of pesticides used in golf
links by acute toxicity test on rainbow trout.
KIKUCHI M, MIYAGAKI T, WAKABAYASHI M
Tokyo Metropolitan Research Inst. Environmental Protection,
Shinsuna, Koto, Tokyo 136, Japan.
To assess the effects of pesticides sprayed in golf links on
aquatic organisms, twenty pesticides were assayed by acute toxicity
test using rainbow trout Oncorhynchus mykiss. Susceptibility
to several pesticides, i.e. captan, chlorothalonile, chlorpyrifos,
diazinon, and fenitrothion, was measured at different developmental
stages: embryo, sac fry, and fry. No remarkable difference in
susceptibility was observed among developmental stages on four
pesticides except for chlorpyrifos, which showed a remarked
difference in susceptibility among the different stages. Of
the 20 chemicals tested, the 96 hour median lethal concentration
(96 h-LC50) of less than 0.1 mg/l was obtained in captan, chlorothalonile,
thiuram, chlorpyrifos, and oxine-copper. On
the other hand, 96 h-LC50 exceeding 10 mg/l was obtained in
flutolanil, mepronil, benfluralin, and mecoprop. The
96 h-LC50 values of several pesticides were lower than the current
effluent guideline values for golf links, suggest
CAS Registry Numbers:
66332-96-5
66332-96-5
66063-05-6
55814-41-0
50512-35-1
40487-42-1
36335-67-8
25311-71-1
18854-01-8
15299-99-7
10380-28-6
2921-88-2
1897-45-6
1861-40-1
741-58-2
333-41-5
137-26-8
133-06-2
122-14-5
119-12-0
93-65-2
52-68-6
From Toxline at Toxnet
BIOSCIENCE BIOTECHNOLOGY AND BIOCHEMISTRY; 60 (4). 1996.
557-566.
Similarities in bioanalogous structural
transformation patterns among various bioactive compound series.
FUJITA T
EMIL Project, Fujitsu Kansai Systems Laboratory, 2-2-6 Shiromi,
Chuo-ku, Osaka 540, Japan.
Successful structural transformations of bioactive compounds
into newer skeletal structures by replacing the substructure
with others, the features of which are not necessarily similar
to but more or less drastically varied from the original one,
were proposed to be called being made
"bioanalogously" instead of "bioisosterically".
Precedents of the bioanalogous replacements of substructures
composed of the amide, urea, and related components with others
were explored. Anilides, N-phenylureas, and N-phenylcarbamates
are bioanalogous as herbicides and topical antiseptics. The
bioanalogy can be expanded to include substructures containing
ester as well as ether components when local anesthetics are
considered together. The polar hydrogen-bonding groups such
as (thio)urea, cyanoguanidine, and nitroethenediamine substructures
found in histamine H2-receptor antagonists are also bioanalogous
in various other bioactive compound series. The open-chain amides
and the correspondin [abstract truncated]
CAS Registry Numbers:
160430-64-8
160430-64-8
89764-44-3
80844-07-1
66332-96-5
55814-41-0
51630-58-1
50471-44-8
36734-19-7
32809-16-8
25475-73-4
23950-58-5
20354-26-1
3766-81-2
2307-68-8
2164-09-2
1967-16-4
1918-18-9
1918-11-2
709-98-8
330-55-2
330-54-1
122-42-9
From Toxline at Toxnet
ACTA UNIVERSITATIS CAROLINAE GEOLOGICA; 39 (2). 1995.
359-370.
EXPERIMENTS ON POLLUTANTS RUNOFF IN
A GOLF COURSE UNDER LAND SITE DEVELOPMENT
OJIMA M
Abstract: RRM RESEARCH ARTICLE AGRICULTURAL CHEMICALS WATER
QUALITY PRECIPITATION SOIL
CAS Registry Numbers:
66332-96-5
66332-96-5
17778-88-0
14797-55-8
7723-14-0
122-14-5
Language: English
From Toxline at Toxnet
JAPANESE JOURNAL OF CROP SCIENCE; 63 (3). 1994.
442-451.
Water pollution caused by agricultural
chemicals and fertilizers in the drainage from golf
links.
TOMIMORI S, NAGAYA Y, TANIYAMA T
Faculty Bioresources, Mie Univ., Tsu 514, JAP.
An investigation of agricultural chemicals and chemical fertilizer
used by golf links were carried out from June 1991 to May 1992.
Immediately after or during the rainfall, sampling for drainage
was started at 6 points of 3 golf links. About 15 agricultural
chemicals, nitrogen, phosphorus and potassium were analyzed.
The following results were obtained. Nine agricultural chemicals
including 3 herbicides (Propyzamide, Simazine, Napropamide),
4 bactericides (Flutoluanil Isoprothiolane,
Captan, Tolclophos-methyl) and 2 insecticides (Diazinon, Fenitrothion)
were detected. Detectable frequency was different at the 3 golf
links and the 6 sampling points. The highest levels of agricultural
chemicals were detected in June, and high
levels of Flutoluanil, Isoprothiolane and Captan were detected.
These concentrations were higher in September, and high
levels of Propyzamide and Simazine were detected, and each maximum
level was over 8 and 3 mugL-1. Many concentrations were from
0.1 [abstract truncated]
CAS Registry Numbers:
66332-96-5
66332-96-5
57018-04-9
50512-35-1
36734-19-7
25311-71-1
23950-58-5
18854-01-8
17778-88-0
15299-99-7
7723-14-0
2921-88-2
1897-45-6
333-41-5
133-06-2
122-34-9
122-14-5
From Toxline at Toxnet
JOURNAL OF PESTICIDE SCIENCE; 19 (1). 1994. 1-10.
Runoff and leaching of pesticides in
golf course.
ODANAKA Y, TANIGUCHI T, SHIMAMURA Y, IIJIMA
K, KOMA Y, TAKECHI T, MATANO O
Mitsukaido Inst., Inst. Environmental Toxicol., Uchimoriya-cho,
Mitsukaido 303, JAP.
An investigation of runoff property of pesticides applied
in a golf course was conducted by using lysimeters and at actual
golf courses. In lysimeter experiment, a
remarkable leaching was observed in only 5 pesticides
(trichlorfon (DEP), metalaxyl, isoprothiolane,
flutolanil and iprodione) with at least 100 mm of precipitation.
The leaching was scarce in other 12 pesticides (bensulide (SAP),
isofenphos, fenitrothion (MEP), fenarimol, triflumizole, tetrachlorvinphos
(CVMP), pyridaphenthion, oxine-copper, isoxathion, prothiofos,
tolclofosmethyl, pendimethalin) with sum of 440 mm of precipitation
for 51 days. The leaching pattern of the 5 pesticides showed
a single broad peak. There was a tendency that pesticides with
a high water solubility had a potential to move downward. In
putting green experiment, all the 3 pesticides
applied (isofenphos, flutolanil and metalaxyl) were detected
in leaching water with only 10 mm of precipitation. There
was no significant difference am [abstract truncated]
From Toxline at Toxnet
JAPANESE JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH; 39
(6). 1993. 543-548.
Environmental pollution by pesticides
from golf courses in Kanagawa prefecture.
FUSHIWAKI Y, HAMAMURA T, HASEGAWA A,
URANO K
Environmental Res. Cent., Kanagawa Prefecture, 842 Nakaharashimojuku,
Hiratsuka 254, JAP.
Recently, the environmental pollution by pesticides applied
to golf courses has been paid attention as a social problem
in Japan. Therefore the concentrations of nineteen pesticides
in water and atmosphere samples were measured around golf courses
in Kanagawa prefecture from 1990 to 1992. Diazinon, simazine,
isoprothiolane, flutolanil, propyzamide were detected in many
sampling points at a higher level, although the concentrations
in water samples did not exceed the guideline values which were
published by Environmental Agency. Moreover, isoprothiolane
and flutolanil, whose solubilities in
water were high, were easily detected in water environment.
On the other hand, benfluralin and fenitrothion, whose volatilization
rates were large, were easily detected in atmospheric environment.
The concentration of tolclophosmethyl in effluent increased
rapidly due to the rain fall after it was sprayed.
From Toxline at Toxnet
WATER SCIENCE AND TECHNOLOGY; 28 (3-5).
1993. 549-559.
THREE TYPES OF APPROACHES TO CONTROLLING
NON-POINT SOURCE POLLUTION OF AGROCHEMICALS FROM GOLF
LINKS IN WATER RESOURCES MANAGEMENT
MORIOKA T
CAS Registry Numbers:
66332-96-5
66332-96-5
50512-35-1
23950-58-5
15299-99-7
2921-88-2
1897-45-6
333-41-5
122-34-9
122-14-5
From Toxline at Toxnet
J PESTIC SCI; 18 (2). 1993. S69-S77.
Development of a systemic fungicide,
flutolanil.
ARAKI F, YABUTANI K
Dev. Div., Nihon Nohyakau Co. Ltd., Chuo-Ku, Tokyo 103, Japan.
In the course of our research work for a novel systemic fungicide
to control rice sheath blight disease caused by Rhizoctonia
solani, various derivatives having amide linkage, especially
benzanilide derivatives were synthesized for biological screening.
Trifluoromethyl at the ortho position of the acid moiety of
benzanilide was selected as the most favorable substituent with
a certain level of steric bulk and lipoid solubility. Alkoxy
groups introduced at the meta position of the aniline moiety
enhanced the fungitoxic activity. Ultimately, flutolanil (alpha,
alpha, alpha-trifluoro-3'-isopropoxy-2-toluanilide) was selected
as the most potent compound for our purpose. Flutolanil
is the first registered fungicide able to control rice sheath
blight with application of granules into paddy water as well
as foliar spray application in Japan. Approximately 2
ppm of flutolanil in rice leaf sheaths contributed to about
80% suppression of the disease development by inhibiting hyph
[abstract truncated]
From Toxline at Toxnet
COMP BIOCHEM PHYSIOL C COMP PHARMACOL TOXICOL; 101 (1). 1992.
63-66.
Accumulation and excretion of pesticides
used in golf courses by carp (Cyprinus
carpio) and willow shiner (Gnathopogon caerulescens).
TSUDA T, AOKI S, KOJIMA M, FUJITA T
Shiga Prefectural Inst. Public Health Environmental Science,
13-45 Gotenhama, Ohtsu, Shiga 520, Jpn.
1. The average bioconcentration factors (BCF) in whole body
of willow shiner (Gnathopogon caerulescens) were 3.9 for simazine,
18 for chlorothalonil and 350 for captan.
2. The average BCF values in whole body of carp (Cyprinus carpio
L.) were 220 for tolclofos-methyl, 460 for chlorpyriphos,
20 for flutolanil, 27 for isoprothiolane, 25 for chlorothalonil,
100 for captan, 440 for isoxathion and 360 for iprodione.
3. The correlations between n-octanol-water partition coefficients
(Pow) and BCF in willow shiner and carp were investigated for
the pesticides studied here and already reported. Correlation
factors (r) except captan were 0.939 1 (N = 10) for willow shiner
and 0.7747 (N = 15) for both fishes.
4. The excretion rate constants (k) from whole body of willow
shinner were 0.77 hr-1 for simazine, 0.04 hr-1 for chlorothalonil
and 0.02 hr-1 for captan.
5. The k values from whole body carp were 0.04 hr-1 for tolclofos-methyl,
0.02 hr-1 for chlorpyriphos, 0.12 hr-1
for fluto [abstract truncated]
CAS Registry Numbers:
66332-96-5
66332-96-5
57018-04-9
50512-35-1
36734-19-7
18854-01-8
2921-88-2
133-06-2
From Toxline at Toxnet
WATER SCIENCE AND TECHNOLOGY; 30 (7). 1994.
137-144.
RUNOFF PATTERN OF PESTICIDES FROM PADDY
FIELDS IN THE CATCHMENT AREA OF RIKIMARU RESERVOIR JAPAN
NAGAFUCHI O, INOUE T, EBISE S
Abstract: RRM RESEARCH ARTICLE IRRIGATION WATER MANAGEMENT
POLLUTION CONSERVATION GROUNDWATER CHEMISTRY WATER QUALITY
CAS Registry Numbers:
66332-96-5
66332-96-5
57369-32-1
50512-35-1
28249-77-6
17109-49-8
5598-13-0
122-34-9
55-38-9
From Toxline at Toxnet
AGRIC BIOL CHEM; 55 (3). 1991.
763-768.
Photolysis of flutolanil fungicide and
the effect of some photosensitizers.
TSAO R, ETO M
Lab. Pesticide Chem., Dep. Agric. Chem., Kyushu Univ., Higashi-ku,
Fukuoka 812, Jpn.
Photolysis of the fungicide flutolanil, 3'-isopropoxy-2-(trifluoromethyl)benzanilide,
was investigated both in an aqueous solution and on solid surfaces
(silica gel and glass) by irradiating with UV light under laboratory
conditions. In an ethanolic aqueous solution, irradiation
resulted in the formation of a major product (2-(trifluoromethyl)benzamide)
and some other products (2-(trifluoromethyl)benzoic acid, N-ethoxycarbonyl-2-(trifluoromethyl)benzamide,
etc.). The latter is considered to have been formed
by the reaction with an organic solvent. On
the solid surfaces, the main photoproduct was 2'-amino-4'-isopropoxyphenyl-2-(trifluoromethyl)phenyl
ketone, a product from the photo-Fries rearrangement reaction.
Another photoproduct, 3'-hydroxy-2-(trifluoromethyl)benzanilide
was obtained only on the glass surfaces, this desisopropylated
compound not being detected under any other conditions. The
photolysis of this fungicide, was accelerated more by carbonyl
compounds such [abstract truncated]
From Toxline at Toxnet
J PESTIC SCI; 13 (1). 1988. 153-156.
AN OUTLINE OF TOXICITY TESTS USING FLUTOLANIL
From Toxline at Toxnet
J PESTIC SCI (NIHON NOYAKU GAKKAISHI); 8 (4). 1983.
529-536.
Degradation of flutolanil in soils under
flooded and upland conditions in the laboratory.
UCHIDA M, OHORI Y, SUGIMOTO T, AIZAWA
H
Inst. Life Sci. Res., Nihon Nohyaku Co., Ltd., Honda-cho, Kawachi-Nagano,
Osaka 586, Japan.
(Aniline ring-14C(U)) flutolanil, 3'-isopropoxy-2-(trifluoromethyl)
benzanilide, in soils was considerably stable under laboratory
conditions, showing the half life of 160-300
days in 3 soils under flooded condition and 190-320 days under
upland condition. Flutolanil decomposition proceeded
more rapidly in Tochigi soil of high organic matter content
than in Saitama and Okayama soils of low organic matter content
and was attributable mainly to the formation of bound residues
and 14CO2, which accounted for 9-27% and 3-7%, respectively,
of the applied radioactivity after 180 days. Three
degradation products in the soils under flooded condition were
detected and identified as 4'-hydroxy-3'-isopropoxy-2-(trifluoromethyl)benzanilide,
3'-(hydroxymethyl)ethoxy-2-(trifluoromethyl)benzanilide and
3'-hydroxy-2-(trifluoromethyl)benzanilide. Two
additional products such as 3'-methoxy-2-(trifluoromethyl)benzanilide
and 4'-hydroxy-3'-methoxy-2-(trifluoromethyl)benzanilide were
detected in upland soils.
From Toxline at Toxnet
BULLETIN OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY; 60
(5). 1998. 669-676.
DETERMINATION OF THE CONCENTRATION OF
PESTICIDES IN ATMOSPHERE AT HIGH ALTITUDES AFTER AERIAL APPLICATION
WATANABE T
Abstract: RRM RESEARCH ARTICLE HIGH ALTITUDES PESTICIDES DDT
PESTICIDE AERIAL PESTICIDE APPLICATION POLLUTION ATMOSPHERIC
CONCENTRATIONS
Keywords:
Ecology
Biochemical Studies-General
Public Health: Environmental Health-Air
Pest Control
CAS Registry Numbers:
80844-07-1
80844-07-1
74712-19-9
73250-68-7
69327-76-0
66332-96-5
61432-55-1
57369-32-1
55814-41-0
52645-53-1
51630-58-1
50512-35-1
42576-02-3
41814-78-2
40487-42-1
36335-67-8
28249-77-6
26087-47-8
25311-71-1
23184-66-9
22936-75-0
22248-79-9
18854-01-8
17109-49-8
5598-13-0
3766-81-2
2921-88-2
2655-14-3
2631-40-5
2597-03-7
2274-67-1
2255-17-6
2212-67-1
2104-64-5
1897-45-6
1582-09-8
1129-41-5
1014-70-6
732-11-6
333-41-5
330-55-2
298-04-4
133-06-2
122-34-9
122-14-5
121-75-5
119-12-0
101-21-3
63-25-2
62-73-7
60-51-5
55-38-9
50-29-3
From Toxline at Toxnet
BULLETIN OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY; 57
(3). 1996. 442-449.
PESTICIDES IN WATER AND FISH FROM RIVERS
FLOWING INTO LAKE BIWA
TSUDA T, INOUE T, KOJIMA M, AOKI S
Keywords:
Ecology
Biochemistry-Physiological Water Studies (1970- )
Biochemical Methods-General
Biochemical Studies-General
Toxicology-Environmental and Industrial Toxicology
Public Health: Environmental Health-Air
Pest Control
Pisces-Unspecified
CAS Registry Numbers:
66332-96-5
66332-96-5
57018-04-9
51218-49-6
50512-35-1
36335-67-8
34643-46-4
28249-77-6
26087-47-8
25311-71-1
17109-49-8
7292-16-2
3811-49-2
3766-81-2
2921-88-2
2597-03-7
2104-64-5
1897-45-6
1563-66-2
1014-70-6
950-37-8
732-11-6
333-41-5
122-34-9
122-14-5
121-75-5
119-12-0
55-38-9
