Landslide assessment through integrated geoelectrical and seismic methods: A case study in Thungsong site, southern Thailand.

Many landslides can cause significant damage to infrastructure, property, and human life. To study landslide structure and processes, geophysical techniques are most productive when employed in combination with other survey and monitoring tools, such as intrusive sampling. Here, the integration of electrical resistivity tomography (ERT) and seismic refraction tomography (SRT) methods is used to assess landslides in Thungsong district, Nakhon Si Thammarat, the south of Thailand, where is a hilly and seasons of prolonged rainfall region. The 2D cross-plot analysis of P-wave velocity and resistivity values obtained by these two methods is introduced to identify potential landslide-prone zones in this region. The results of the 2D cross-plot model reveal detailed image of the subsurface conditions, highlighting areas of low P-wave velocity (lower than 600 m/s) and low resistivity (lower than 600 Ωm). These areas are indicative of weak zone and are potential to be sliding materials. Moreover, an intrusive sampling data from boreholes is also used for the calibration and validation geophysical data with geological data. This can improve the accuracy of landslide assessment and develop effective mitigation strategies to reduce the risk of landslides in this area. In addition of the 2D cross-plot, the volume of sliding material is also determined from the difference of the surface and slipping plane elevations. The volume calculation of sliding material is roughly 33447.76 m3. This approach provides a preliminary tool for landslide studies and monitoring landslides in this region, thus enabling an improved understanding of slope failure processes in this context, and the basis of a landslide mitigation strategy in the future.

Activation and degradation of the phosphorothionate insecticides parathion and EPN by rat brain.

Cytochrome P-450-dependent monooxygenases are known to activate phosphorothionate insecticides to their oxon (phosphate) analogs by oxidative desulfuration. These activations produced potent anticholinesterases, decreasing the I50 values to rat brain acetylcholinesterase almost 1000-fold (from the 10(-5) M range to the 10(-8) M range). Since the usual cause of death in mammals from organophosphorus insecticide poisoning is respiratory failure resulting, in part, from a failure of the respiratory control center of the brain, we investigated the ability of rat brain to activate and subsequently degrade two phosphorothionate insecticides, parathion (diethyl 4-nitrophenyl phosphorothioate) and EPN (ethyl 4-nitrophenyl phenylphosphonothioate). Microsomes from specific regions (cerebral cortex, corpus striatum, cerebellum, and medulla/pons) of the brains of male and female rats and from liver were incubated with the phosphorothionate and an NADPH-generating system. Oxon production was quantified indirectly by the amount of inhibition resulting in an exogenous source of acetylcholinesterase added to the incubation mixture as an oxon trap. The microsomal activation specific activity was low for brain when compared to liver [0.23 to 0.44 and 5.1 to 12.0 nmol.min-1.(g tissue)-1 respectively]. The mitochondrial fraction of the brain possessed an activation activity for parathion similar to that of microsomes [about 0.35 nmol.min-1.(g tissue)-1 for each fraction], but mitochondrial activity was slightly greater than microsomal activity for EPN activation [0.53 to 0.58 and 0.23 to 0.47 nmole.min-1.(g tissue)-1]. Whole homogenates were tested for their ability to degrade paraoxon and EPN-oxon (ethyl 4-nitrophenyl phenylphosphonate), quantitated by 4-nitrophenol production. Specific activity for oxon degradation in liver was greater than that in brain [31 to 74 and 1.1 to 10.7 nmole.min-1.(g tissue)-1 respectively]. Overall, the brain and liver had about 1.5- to 12-fold higher specific activities for degradation than activation depending on the compound used. These findings demonstrate that the brain possesses both phosphorothionate activation and oxon degradation abilities, both of which may be significant during exposures to organophosphorus insecticides.

Identification and isolation of two rat serum proteins with A-esterase activity toward paraoxon and chlorpyrifos-oxon.

The active metabolites (oxons) of phosphorothionate insecticides can be detoxified via A-esterase hydrolysis. Two enzymes with A-esterase activity have been isolated from rat serum. Whole serum was applied to anion exchange gel (DEAE Sepharose Fast Flow) and incubated (1 hr). Tris-HCl buffer (0.05 M; pH 7.7, at 5 degrees) containing 0.25 M NaCl was added to the slurry and incubated. The decant, containing low A-esterase activity but a high protein concentration, was discarded. Further displacement of A-esterase from DEAE gel was achieved with 1.0 M NaCl in 0.05 M Tris-HCl buffer (Ph 7.7 at 5 degrees). Following desalting and concentration, further separation was achieved by gel filtration (Sephacryl S-100 HR) and two sequential preparative scale isoelectric focusings. Final fractions contained two proteins of high molecular mass (one about 200 kDa and one between 137 and 200 kDa). The apparent range of isoelectric points for the two enzymes was 4.5 to 5.6. Following native-PAGE analysis, activity stains with beta-naphthyl acetate and Fast Garnet GBC in the presence of paraoxon (10-5 M) verified that A-esterase activity was associated with both proteins. Spectropho-tometric assay detected A-esterase activity toward paraoxon, chlorpyrifos-oxon, and phenyl acetate in the final preparation.

Transferable residues from dog fur and plasma cholinesterase inhibition in dogs treated with a flea control dip containing chlorpyrifos.

We studied chlorpyrifos, an insecticide present in a commercial dip for treating ectoparasites in dogs, to estimate the amount of transferable residues that children could obtain from their treated pets. Although the chlorpyrifos dip is no longer supported by the manufacturer, the methodology described herein can help determine transferable residues from other flea control insecticide formulations. Twelve dogs of different breeds and weights were dipped using the recommended guidelines with a commercial, nonprescription chlorpyrifos flea dip for 4 consecutive treatments at 3-week intervals (nonshampoo protocol) and another 12 dogs were dipped with shampooing between dips (shampoo protocol). The samples collected at 4 hr and 7, 14, and 21 days after treatment in the nonshampoo protocol averaged 971, 157, 70, and 26 microg chlorpyrifos, respectively; in the shampoo protocol the samples averaged 459, 49, 15, and 10 microg, respectively. The highest single sample was about 7,000 microg collected at 4 hr. The pretreatment specific activities in the plasma of the dogs were about 75 nmol/min/mg protein for butyrylcholinesterase (BChE), and 9 nmol/min/mg protein for acetylcholinesterase (AChE). BChE was inhibited 50-75% throughout the study, and AChE was inhibited 11-18% in the nonshampoo protocol; inhibition was not as great in the shampoo protocol. There was no correlation (p

Changes in rat brain cholinesterase activity and muscarinic receptor density during and after repeated oral exposure to chlorpyrifos in early postnatal development.

The effects of repeated oral exposures to the organophosphorus insecticide chlorpyrifos (CPS) on brain muscarinic receptor densities, together with cholinesterase (ChE) activity, were studied in early postnatal rats. Initially, the effects on esterases from lactational exposure to CPS were investigated in young rats by administering CPS (100, 150, or 200 mg/kg subcutaneously in corn oil) to dams 1 day postpartum, yielding a significant body burden of CPS in the dams for possible excretion in the milk. Brain ChE inhibition in pups was less severe than in dams, whereas liver carboxylesterase (CbxE) inhibition in pups was at the same level as in dams. Because of the limited brain ChE inhibition obtained following lactation, pups were exposed to CPS directly by gavage, using 3 dosing regimens to yield a dose response. The rats were gavaged with CPS in corn oil on alternate days from postnatal day (PND) 1 through PND 21. Rats in the low-dosage group received 11 treatments at 3 mg/kg, those in the medium-dosage group received 3 treatments at 3 mg/kg and 8 at 6 mg/kg, and those in the high dosage group received 3 treatments at 3 mg/kg, 4 at 6 mg/kg, and 4 at 12 mg/kg. ChE activity in brain homogenates were inhibited significantly by 29% and 63% in the low- and high-dosage groups, respectively, on PND 22 and by 17% in the high dosage group on PND 40. Muscarinic receptor densities in brain synaptosomes were reduced using 3H-N-methylscopolamine (NMS) and 3H-quinuclidinyl benzilate (QNB) as ligands, with the effects more prominent from 3H-NMS. Densities of both ligands recovered to the control level several days after terminating treatment. The results indicate that pups are apparently exposed to only limited amounts of chlorpyrifos and/or its oxon through the milk when dams are exposed to extremely high chlorpyrifos levels. In addition, repeated direct oral exposures of early postnatal rats to CPS will result in persistent brain ChE inhibition and will transiently reduce muscarinic receptor density.

Effects of repeated oral postnatal exposure to chlorpyrifos on open-field behavior in juvenile rats.

Organophosphorus (OP) insecticides have the potential to cause behavioral effects in children. This study was designed to determine if repeated oral exposure of preweanling rats to chlorpyrifos would produce behavioral changes at both pre- and postweanling ages. Treatment occurred every second day beginning on post-natal day (PND) 1, and continued through PND 21. The rats received one of the following regimens: a low-dosage (3 mg/kg) from PND 1-21; a medium dosage (mg/kg from PND 1-5, and then 6 mg/kg from PND 7-21; or a high-dosage schedule of 3 mg/kg on PND 1-5, then 6 mg/kg from PND 7-13, and 12 mg/kg from PND 15-21. There were no differences in body weights among the control-, low-, and medium-dosage groups but the high-dosage group had significantly lower body weights on PND 13-21. An open field was used to measure locomotor activity on PND 10, 12, 14, 16, 18, 20, 25, and 30. There were no differences in locomotor activity levels or treatment effects between males and females. On PND 10, 12, 14, 16, 18, and 20 there was no effect on locomotor activity with any dosage. On days 25 and 30, locomotor activity was significantly decreased with the medium- and high-dosage groups. Brain cholinesterase (ChE) inhibition was about 25-38% on PND 25 and 14-34% on PND 30. On PND 25 but not 30, lung and diaphragm ChE and serum butyrylcholinesterase (BChE), with the high-dosage animals, and heart ChE with the medium- and high-dosage groups were significantly inhibited. There was no significant inhibition of skeletal muscle ChE or serum acetylcholinesterase (AChE) on PND 25 and 30. These data suggest that early postnatal chlorpyrifos exposures will depress locomotor activity in juvenile rats, with the effects most pronounced after brain ChE activity has substantially recovered.

Common mechanism of toxicity: a case study of organophosphorus pesticides.

The Food Quality Protection Act of 1996 (FQPA) requires the EPA to consider "available information concerning the cumulative effects of such residues and other substances that have a common mechanism of toxicity ... in establishing, modifying, leaving in effect, or revoking a tolerance for a pesticide chemical residue." This directive raises a number of scientific questions to be answered before the FQPA can be implemented. Among these questions is: What constitutes a common mechanism of toxicity? The ILSI Risk Science Institute (RSI) convened a group of experts to examine this and other scientific questions using the organophosphorus (OP) pesticides as the case study. OP pesticides share some characteristics attributed to compounds that act by a common mechanism, but produce a variety of clinical signs of toxicity not identical for all OP pesticides. The Working Group generated a testable hypothesis, anticholinesterase OP pesticides act by a common mechanism of toxicity, and generated alternative hypotheses that, if true, would cause rejection of the initial hypothesis and provide criteria for subgrouping OP compounds. Some of the alternative hypotheses were rejected outright and the rest were not supported by adequate data. The Working Group concluded that OP pesticides act by a common mechanism of toxicity if they inhibit acetylcholinesterase by phosphorylation and elicit any spectrum of cholinergic effects. An approach similar to that developed for OP pesticides could be used to determine if other classes or groups of pesticides that share structural and toxicological characteristics act by a common mechanism of toxicity or by distinct mechanisms.

Biochemical mechanisms contributing to species differences in insecticidal toxicity.

Comparison of published LD50 or LC50 levels for a variety of insecticides in several vertebrate species indicate that a wide range of toxicity levels exist, and these cannot be easily predicted within either a chemical group or within a species. There is a relatively limited data base documenting interactions between insecticides and other chemicals, either agricultural or non-agricultural; however, the fact that all major insecticide groups perturb nervous system function as their primary mechanism of acute toxicity suggests the potential for interactions. Studies in our laboratories on a select group of phosphorothionate insecticides in rats indicated that brain acetylcholinesterase sensitivity to inhibition by the oxons, the active metabolites of the phosphorothionates, does not correlate with acute toxicity levels. The activities and properties of hepatic cytochrome P450-mediated activation (desulfuration) and detoxication (dearylation) of the phosphorothionates as well as of A-esterase-mediated hydrolysis of oxons contribute substantially to understanding the acute toxicity levels in rats, as does the sensitivity of the protective aliesterases to phosphorylation. However, in the channel catfish, the acetylcholinesterase sensitivity to oxon inhibition reflects the acute toxicity level of these same insecticides, and may be largely responsible for determining the acute toxicity level in this species. Thus, metabolism of insecticides appears to be far more influential in some species than others in determining the toxicity elicited.

Critical time periods and the effect of tryptophan in malathion-induced developmental defects in Xenopus embryos.

Xenopus laevis embryos were exposed to the organophosphorus insecticide malathion or its metabolite malaoxon during the first four days of development. The compounds produced the following defects in a dose dependent manner: reduced size, abnormal pigmentation, abnormal gut, enlargement of the atria and aorta, bent notochord and lowered NAD+ levels. Notochords were bent downward between the third and sixth somites with concurrent compression of the somites. Anterior intestine diameter was increased with a concurrent reduction in the number of intestinal loops. When tryptophan was administered along with malathion, NAD+ was measured at control levels or above, yet neither severity nor incidence of defects were reduced. The reduction of NAD+ does not seem to be responsible for the defects seen in Xenopus as occurs for some defects in avian species. In experiments to determine critical time of exposure, the final 48 h, which follow organogenesis and are primarily devoted to growth and development, seem most critical.

Role of detoxication pathways in acute toxicity levels of phosphorothionate insecticides in the rat.

Phosphorothionate insecticides and their active oxon metabolites can be detoxified by a variety of hepatic mechanisms. Cytochrome P450-mediated dearylation activity was higher in males than in females. While dearylation was induced by phenobarbital in both sexes, it was induced by beta-naphthoflavone in females only. Detoxication of oxons in the presence of EDTA was inducible by phenobarbital, was higher in males than in females, and paralleled aliesterase activity. In vitro Ca(++)-dependent A-esterase-mediated hydrolysis of chlorpyrifos-oxon but not of paraoxon occurred at biologically relevant nM concentrations. This hydrolysis was also inducible by phenobarbital. Glutathione-mediated conjugation did not appear to be relevant to the disposition of the phosphorothionates studied here. Hepatic detoxication via dearylation, aliesterase phosphorylation and A-esterase-mediated hydrolysis (for some organophosphates) all appear to be relevant reactions in the attenuation of acute toxicity.

Target site bioactivation of the neurotoxic organophosphorus insecticide parathion in partially hepatectomized rats.

Target organ bioactivation of phosphorothionate insecticides to their potent anticholinesterase oxon metabolites (for example, parathion to paraoxon) may be extremely important in toxicity because liver and blood provide so much potential protection by a variety of mechanisms, such as the aliesterases which serve as alternate phosphorylation sites. To determine whether the brain can produce sufficient oxon in vivo to contribute to toxicity, male rats were partially hepatectomized and injected i.v. with 1.5 mg/kg parathion. After 30 minutes, brain AChE was inhibited 68% whereas liver and plasma aliesterases were unaffected. Because aliesterases are far more sensitive to paraoxon inhibition than is brain AChE, these results indicate that neither the liver nor extra-hepatic tissues were contributing oxon into the blood stream. Thus target site activation of parathion occurred in vivo at sufficient levels to contribute substantially to toxicity.

Effects of paraoxon, p-nitrophenol, phenyl saligenin cyclic phosphate, and phenol on the rat interleukin 2 system.

Two organophosphorus compounds, paraoxon and phenyl saligenin cyclic phosphate, as well as p-nitrophenol and phenol which are structurally related to paraoxon, were tested for their effects on interleukin 2 (IL2) production and responsiveness by rat splenocytes in vitro. Three of the four compounds inhibited mitogen-induced lymphocyte proliferation as well as IL2 production and responsiveness. However, phenyl saligenin cyclic phosphate produced maximal inhibition at a much lower concentration (0.5 microM) than p-nitrophenol (200 microM) or paraoxon (200 microM). Phenol was not inhibitory at any concentration tested (up to 250 microM). Since the production of and response to IL2 are key events in immune responses, compounds which suppress these events can be identified as potential suppressors of host resistance to disease.

Effect of mirex, dechlorinated mirex derivatives and chlordecone on microsomal mixed-function oxidase activity and other hepatic parameters.

The effects of mirex, two monohydrogen and two dihydrogen mirex derivatives, and chlordecone on several hepatic parameters were studied 2 days following a single oral dose of 100 mg/kg in female rats. All compounds increased microsomal cytochrome P-450 content, NADPH-cytochrome c reductase activity, and hepatic ascorbic acid concentration. Microsomal protein concentration was generally increased. All compounds except chlordecone increased relative liver weight and the activities of aminopyrine N-demethylase and p-nitroanisole O-demethylase. Hepatic concentration of protein and glutathione were unaltered. The dechlorinated mirex derivatives caused effects of a magnitude similar to that of mirex, whereas chlordecone was considerably less potent.

The toxic and teratogenic effects of selected organophosphorus compounds on the embryos of three species of amphibians.

The toxic and teratogenic effects of 4 organophosphorus compounds (phenyl saliginen cyclic phosphate (PSCP), leptophos-oxon (LPTO), tri-o-tolyl phosphate (TOTP), and paraoxon (PXN] were investigated in the embryos of 3 species of frogs. Developmental abnormalities were observed in surviving embryos of each of the 3 species following exposure to PSCP at concentrations as low as 500 ppb for 24 h. LPTO, while being toxic to gray treefrog embryos at concentrations as low as 2.2 ppm, did not induce developmental abnormalities. TOTP and PXN were neither toxic nor teratogenic at concentrations of 10 ppm and 100 ppm respectively.

An investigation of activities and paraoxon sensitivities of hepatic aliesterases in beta-naphthoflavone-treated rats.

Aliesterases (carboxylesterases, EC 3.1.1.1) are serine esterases which may protect acetylcholinesterase during organophosphorus insecticide intoxication by providing alternative phosphorylation sites. Levels of hepatic aliesterase activity were investigated after the intraperitoneal administration of beta-naphthoflavone (BNF) to female rats using nine 4-nitrophenyl esters as substrates (including straight and branched chain aliphatic and aromatic esters) and 1-naphthyl acetate. In addition, the in vitro sensitivities of aliesterases to inhibition by paraoxon, the active metabolite of the common insecticide parathion, were studied. Hepatic aliesterases from BNF-treated rats displayed lower activities than those from the controls with all substrates except 4-nitrophenyl phenylbutyrate and isovalerate. The aliesterases from BNF-treated rats were more sensitive to paraoxon inhibition with 4-nitrophenyl phenylbutyrate, valerate, and butyrate. Esterases hydrolyzing 4-nitrophenyl butyrate, valerate, and branched chain esters were most sensitive to paraoxon inhibition while those hydrolyzing 4-nitrophenyl hexanoate and aromatic esters were least sensitive. The results suggested that BNF-induced changes in hepatic aliesterases could alter responses to organophosphates.

Organophosphate detoxication potential of various rat tissues via A-esterase and aliesterase activities.

Paraoxon and chlorpyrifos-oxon, active metabolites of the organophosphorus insecticides parathion and chlorpyrifos, can be detoxified via A-esterases and aliesterases. These enzyme activities were measured in various tissues of Sprague-Dawley rats. High A-esterase activities were detected in liver, serum and liver mitochondrial/microsomal fractions. Low or no A-esterase activities were detected in other tissues and tissue fractions. A-Esterase substrate:substrate activity ratios suggest that the substrates are probably not degraded by the same enzyme. Highest aliesterase activities were observed in the small intestine and liver with moderate activity in kidney, serum and lungs. Low activities were noted in brain, spleen and skeletal muscle.

Acute effects of the organophosphate paraoxon on schedule-controlled behavior and esterase activity in rats: dose-response relationships.

The effects of acute intraperitoneal administration of paraoxon on behavioral and biochemical parameters were studied in male rats. Rats were trained to press a lever under an FR10 schedule of reinforcement. Rats were injected with 3 sublethal doses of paraoxon (0.5, 0.75, and 1.0 mg/kg) and performance was monitored for four days after exposure. Response rates were depressed significantly for days 1 and 2 with 0.75 and 1.0 mg/kg, but not 0.5 mg/kg, even though there was inhibition of brain and plasma cholinesterases at all doses. Performance recovered prior to brain AChE recovery. There was no clear-cut threshold of brain AChE inhibition required to yield performance deficits, nor was there a direct correlation between significant inhibition in peripheral enzymes which could serve as markers (plasma aliesterases, butyrylcholinesterase, non-iso-OMPA-sensitive cholinesterase, and hepatic aliesterases) and performance deficits, suggesting that other noncholinergic targets may play a role in OP-induced behavioral deficits.

Short-term effects of paraoxon and atropine on schedule-controlled behavior in rats.

The effects of lethal (2.0 mg/kg) and high sublethal (1.3 mg/kg) dosages of the organophosphate acetylcholinesterase (AChE) inhibitor paraoxon on FR10 performance rate was determined 1 and 2 days after intoxication. The lethal doses were antidoted with either centrally acting atropine sulfate (AS), or atropine methyl bromide (AMB) or atropine methyl nitrate (AMN), both quaternary salts and not expected to act centrally. AChE inhibition in the brain was about 35-60% on the second day after treatment. AS yielded a small transient depression in performance, while AMB and AMN yielded severe deficits, with incomplete recovery. Performance was depressed by 1.3 mg/kg paraoxon by 52% and 34% on days 1 and 2, respectively, while performance was more greatly depressed by the lethal dose, especially with the noncentrally acting antidotes: AS, 67 and 48%; AMB, 81 and 55%; AMN, 91 and 78%. However, a low dose of AS with 2 mg/kg paraoxon resulted in very severe, nonrecovering deficits. A lethal dose of the nonpersistent anti-AChE eserine sulfate, antidoted with a low dose of AS, yielded no deficits. Thus, a high level, acute intoxication with paraoxon yields behavioral deficits which are attenuated by high levels of a centrally acting muscarinic receptor antagonist. The paraoxon-induced performance deficits or their recovery do not correlate directly with AChE inhibition.

Kinetic parameters of desulfuration and dearylation of parathion and chlorpyrifos by rat liver microsomes.

Parathion and chlorpyrifos are phosphorothionate insecticides, but parathion is substantially more toxic than chlorpyrifos to rats, and both are more toxic to females than to males. A kinetic analysis of cytochrome P-450 mediated desulfuration (activation) and dearylation (detoxication) of the two insecticides indicated that rat hepatic microsomes have a higher capacity to activate and a lower capacity to detoxify parathion than chlorpyrifos; these capacities correspond to their acute toxicity levels. Greater capabilities of both activation and detoxication were found in males than in females for both insecticides, which is especially apparent by comparing the clearance terms (Vmax/Km). Since dearylation clearances, but not desulfuration clearances, correspond with the sex differences in toxicity levels of the two compounds, dearylation may be the more important factor in determining the acute toxicity level. An extrapolation of lethal dose levels of the two insecticides to concentrations that could be encountered in a severe intoxication indicated that activation of both insecticides could readily occur; however, the dearylation of chlorpyrifos, but not of parathion, would occur readily. This difference in the likelihood of dearylation could be an important contributor to the lower acute toxicity levels of chlorpyrifos.

The interaction of chlorinated alicyclic insecticides with brain GABA(A) receptors in channel catfish (Ictalurus punctatus).

Chlorinated alicyclic insecticides are believed to antagonize the action of the neurotransmitter gamma-aminobutyric acid (GABA) at its receptor in vertebrates. Binding of the specific GABA(A) receptor ligand [35S]-t-butylbicyclophosphorothionate (TBPS) to channel catfish brain P2 membranes suggested a single population of receptors with a Kd (56.6+/-2.6 nM) and Bmax (2435+/-276 fmol/mg protein) that are similar to published values for other fish species. The competition of several chlorinated compounds for TBPS binding was investigated. The most potent inhibitors of TBPS binding were 12-ketoendrin, photoheptachlor epoxide, photoheptachlor, telodrin, and endrin, respectively, with IC50s of 20-90 nM. Photooxychlordane, photo alpha-chlordane, and oxychlordane were intermediate in potency (122-219 nM), as were isodrin, dihydroisodrin, heptachlor epoxide, and alpha-chlordane, which were similar in potency (311-397 nM). Dieldrin, lindane, and dihydroaldrin were much less potent (592-1103 nM). Heptachlor, aldrin, and gamma-chlordane were weak inhibitors of TBPS binding (2073-2738 nM). Chlordene and chlordecone had the lowest potency of all compounds studied (10,201-21,178 nM) with the exception of mirex, which did not inhibit binding at a concentration of 50 microM. There is a good correlation between binding potency and the available toxicity data for several of these compounds in channel catfish. There is also a good correlation between the inhibitory potency in channel catfish by these types of compounds with that in rats.