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Metabolism of the arylamide herbicide propanil. II. Effects of propanil and its derivatives on hepatic microsomal drug-metabolizing enzymes in the rat.

Propanil (3,4-dichloropropionanilide) is an arylamide herbicide that has been reported to be contaminated with the cytochrome P450 enzyme inducers 3,3',4,4'-tetrachloroazobenzene (TCAB) and 3,3',4,4'-tetrachloroazoxybenzene (TCAOB), which are structural analogs of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). We determined if treatment of rats with TCAB, TCAOB, propanil, 3,4-dichloroaniline, TCDD, or phenobarbital induced the hepatic microsomal metabolism of propanil and 3,4-dichloroaniline. Acylamidase-catalyzed hydrolysis of propanil to 3,4-dichloroaniline was not induced by any of the pretreatments; however, hydroxylation of propanil at the 2'-position was induced by TCDD, TCAB, TCAOB, propanil, and 3,4-dichloroaniline pretreatments. Ring- and N-hydroxylations of 3,4-dichloroaniline were induced by TCDD, TCAB, TCAOB, and 3,4-dichloroaniline pretreatments. Microsomal 7-ethoxyresorufin-O-deethylase (EROD) and 7-benzoxyresorufin-O-dealkylase (BROD) activities and electrophoretic mobility of microsomal proteins suggested that cytochromes P450c and P450d were induced by TCAB and TCAOB pretreatment. EROD, BROD, and 7-pentoxyresorufin-O-dealkylase activities were slightly increased in microsomes from propanil- and 3,4-dichloroaniline-pretreated rats, which suggests that these compounds may be weak inducers of cytochrome P450 isozymes.

Anilides↗

Propanil (3,4-dichloropropionanilide) particulate concentrations within and near the residences of families living adjacent to aerially sprayed rice fields.

Propanil is widely used as a postemergence herbicide in rice. Because it is typically applied aerially, there is a potential for propanil to drift into and around homes of those living adjacent to rice fields. Propanil has been shown to be immunotoxic in rodent models. The objective of this study was to measure the levels of propanil to which families living adjacent to aerially sprayed rice fields may be exposed. Air levels were sampled by actively and passively collecting propanil in and around the homes of volunteer families living in close proximity to rice fields sprayed with propanil. Homes ranged from 73 m to 113 m from treated rice fields. Sampling was conducted in the home, adjacent to the home (within 5 m of the home), 30 m from the home, and at the edge of the rice field. Concentrations were determined via gas chromatography/mass spectroscopy. Propanil levels adjacent to the homes ranged from nondetectable to 1,106.4 microg per 400 cm2 collection surface (2.0 microg detection limit). Wind direction and wind velocity were the primary determinants of propanil drift. At sites where the prevailing wind was blowing away from the home, no propanil was detected except at the edge of the field. Distance from the edge of the rice field also influenced the amount of drift with higher levels measured at 30 m from the house than adjacent to the house. No propanil vapor was detected on absorbent media sampled in and around the homes. The results indicate that individuals living adjacent to rice fields aerially sprayed with propanil are potentially exposed to variable amounts of propanil, and wind speed and direction are the most important factors that influence the concentration of aerially applied pesticide.

Agriculture↗

Comparison of the immunotoxicity of propanil and its metabolite, 3,4-dichloroaniline, in C57Bl/6 mice.

Propanil (3,4-dichloropropionaniline), used extensively as a postemergence herbicide in rice and wheat, has as its major metabolite, 3,4-dichloroaniline (DCA). Propanil has previously been shown to affect the T cell-dependent antibody response. To determine the immunotoxicity of DCA, as well as extend the previous immunotoxicity studies, several T cell-dependent and -independent immune responses were determined after DCA or propanil exposure. Unlike propanil, DCA caused a significant reduction in T-dependent antibody production (anti-SRBC response) only at a high dose (150 mg/kg). DCA or propanil at 150 or 200 mg/kg, respectively, caused a significant reduction in the number of anti-DNP antibody producing cells. However, doses of 37 or 50 mg/kg of DCA or propanil, respectively, caused an increase in the number of anti-DNP antibody producing cells. These data indicate that both propanil and DCA have a differential effect on the T-independent antibody response depending on the dose. Similar to propanil, DCA (at 150 mg/kg) caused a significant increase in spleen weight and cellularity. The effect of DCA or propanil on selected cellular immune functions was also determined. DCA caused a significant decrease in the natural killer (NK) cell activity at doses of 75 or 150 mg/kg, and propanil caused a significant decrease at 100 or 200 mg/kg. Cytotoxic T lymphocyte activity, however, was unaffected even at 150 or 200 mg/kg DCA or propanil, respectively. Thus, it appears that T cells are relatively resistant to the effects of propanil and DCA, whereas, other immune cell types, e.g., NK cells are sensitive to its effects.

Aniline Compounds↗

The immunomodulatory effects of the herbicide propanil on murine macrophage interleukin-6 and tumor necrosis factor-alpha production.

Intraperitoneal (i.p.) exposure to propanil (3,4-dichloropropionanilide) has previously been shown to affect macrophage cytotoxicity. In this study, we compared the immunotoxic effects of propanil, after different routes of in vivo administration, on cytokine production by thioglycollate-elicited peritoneal macrophages. C57B1/6 mice were treated with either vehicle or 200 mg/kg propanil i.p., or with vehicle, 40, or 400 mg/kg propanil orally. Three or 7 days later, ex vivo production of interleukin-6 (IL-6) and tumor necrosis factor-alpha (TNF-alpha) by macrophages after lipopolysaccharide (LPS) stimulation was determined. Both oral and i.p. propanil exposure resulted in up to a 60-70% reduction in IL-6 and TNF-alpha production by the LPS-stimulated macrophages, depending on the route, postexposure time, and dose of propanil administered. Oral exposure to propanil also caused splenomegaly and thymic atrophy in animals in much the same manner as animals exposed via the i.p. route. In vitro exposure to propanil also significantly reduced macrophage cytokine production. Thioglycollate-elicited macrophages from normal mice were cultured in the continuous presence of 0, 10, or 20 microM propanil plus LPS. This exposure caused a significant reduction in IL-6 and TNF protein production by these macrophages in a concentration-dependent manner. Northern blot analysis demonstrated that the message levels of these cytokines were reduced by approximately the same percentage as the protein levels in propanil-treated macrophages, indicating a possible transcriptional or pretranscriptional target(s) for propanil.

Administration, Oral↗

Alteration of macrophage cytotoxicity through endogenous interferon and tumor necrosis factor alpha induction by propanil.

The effect of propanil on mouse peritoneal macrophages (m phi) was measured by determining cytotoxicity via the P815 cell line, which is resistant to tumor necrosis factor alpha (TNF-alpha). Although control animals showed a typical pattern of requiring both interferon (IFN)-gamma and lipopolysaccharide (LPS) for m phi activation, m phi from propanil-treated animals were cytotoxic when induced with LPS alone. This suggested that propanil influenced endogenous IFN levels. This was confirmed by the abrogation of cytotoxicity upon addition of anti-IFN to the cultures. When cells were assayed for IFN transcript, mRNA in resident m phi was present in higher concentrations in propanil-treated animals. IFN mRNA was present in even higher concentrations in m phi from propanil-treated animals after 30 min of culture with LPS, whereas control m phi required 4 hr in culture with LPS to produce similar levels. IFN protein levels were also higher in propanil-treated m phi after culture in the presence of LPS. Thus, propanil induces increased levels of endogenous IFN which probably works in conjunction with LPS to induce P815 cytotoxicity. Because of the known influence IFN has on the increased secretion of TNF-alpha, we tested the tumoricidal activity of m phi from propanil-treated animals against TNF-alpha-sensitive cell lines. When using WEHI-164 or L929 cells, m phi from propanil-treated animals revealed tumoricidal activity with just the addition of LPS or IFN-gamma. This implies that the additional endogenous levels of IFN, combined with other propanil-induced effects, caused increased secretion of TNF-alpha from m phi.

Animals↗

Acute, chronic and sublethal effects of the herbicide propanil on Daphnia magna.

Acute and chronic toxicity tests with propanil were conducted on Daphnia magna. The 24 and 48 h LC50 were 43.74 and 5.01 mg/l respectively. Chronic toxicity tests were carried out using sublethal propanil concentrations (0.07, 0.10, 0.21 and 0.55 mg/l) during 21 days. The effect of propanil on survival, reproduction and growth of D. magna organisms was monitored. The parameters used to evaluate herbicide effect on reproduction were: mean total young ones per female, mean brood size, time to first reproduction, mean number broods per female and intrinsic rate of natural increase (r). Survival and growth (body length) were also determined after 21 days of exposure to the herbicide. Reproduction was significantly reduced when propanil concentration increased in the medium. The intrinsic rate of natural increase (r) decreased with increasing concentrations of propanil especially in those animals exposed to 0.55 mg/l. However, growth as well as survival of the exposed organisms only decreased in daphnids exposed to the highest propanil concentration tested. The maximum acceptable toxicant concentration (MATC) was calculated for D. magna exposed to the herbicide using as parameter of evaluation the intrinsic rate of natural increase (r). The interpolation of these results gave MATC values of 0.08 mg/l herbicide. We have derived the EC50 values for some selected parameters on D. magna exposed to propanil. EC50 values indicated that reproductive parameters were very sensitive of the effect of propanil on daphnids. Finally, the daphnids were exposed to the same sublethal herbicide concentrations as in the chronic study and the effect of the toxicant on filtration and ingestion rates was determined. Feeding rates of D. magna declined with increasing propanil concentrations. The effective propanil concentrations at which feeding rates were reduced to 50% of that in controls (EC50) were also calculated.

Animals↗

Propanil inhibits tumor necrosis factor-alpha production by reducing nuclear levels of the transcription factor nuclear factor-kappab in the macrophage cell line ic-21.

Tumor necrosis factor-alpha (TNF-alpha) is an essential proinflammatory cytokine whose production is normally stimulated by bacterial cell wall components, such as lipopolysaccharide (LPS), during an infection. Macrophages stimulated with LPS in vitro produce several cytokines, including TNF-alpha. LPS-stimulated primary mouse macrophages produced less TNF-alpha protein and message after treatment with the herbicide propanil (Xie et al., Toxicol. Appl. Pharmacol. 145, 184-191, 1997). Nuclear factor-kappaB (NF-kappaB) tightly regulates TNF-alpha transcription. Therefore, as a step toward understanding the mechanism of the effect of propanil on TNF-alpha transcription, IC-21 cells were transfected with a TNF-alpha promoter-luciferase construct, and the effect of propanil on luciferase activity was measured. Cells transfected with promoter constructs containing a kappaB site showed decreased luciferase activity relative to controls after propanil treatment. These observations implicated NF-kappaB binding as an intracellular target of propanil. Further studies demonstrated a marked reduction in the nuclear levels of the stimulatory p65 subunit of NF-kappaB after propanil treatment, as measured by fluorescence confocal microscopy and Western blot analysis. The p50 subunit of NF-kappaB was not found to be reduced after propanil exposure by Western blot. Electrophoretic mobility gel shift assays showed decreased DNA binding of both p65/p50 heterodimers and p50/p50 homodimers to the kappaB3 site of the TNF-alpha promoter of propanil-treated cells. The marked reduction in nuclear p65/p50 NF-kappaB levels and diminished binding to the TNF-alpha promoter in propanil-treated cells are consistent with reduced TNF-alpha levels induced by LPS.

Animals↗

Evidence for a novel endocrine disruptor: the pesticide propanil requires the ovaries and steroid synthesis to enhance humoral immunity.

Steroid hormones are known to affect the humoral immune response to a variety of antigens. However, the mechanisms regulating these effects are poorly understood. The immunotoxic chemical propanil and estrogen have similar effects on the immune system including augmentation of humoral immune responses. Propanil enhances the number of phosphorylcholine (PC)-specific IgG2b, IgG3, and IgM antibody-secreting cells (ASCs) in the spleen four- to sixfold 7 days after vaccination of female C57BL/6 mice with heat-killed Streptococcus pneumoniae. Several experiments were performed to test the hypothesis that propanil increases the response via an estrogenic pathway. Ovariectomy abrogated the effect of propanil on the PC-specific ASC response. Both in vitro and in vivo assays indicate that propanil does not bind either estrogen receptor (ER) alpha or beta. Exogenous estradiol administration in ovariectomized mice failed to restore the effect of propanil on the PC response. Treatment of female mice with a pure ER antagonist, ICI 182,780, or the progesterone antagonist RU486 did not inhibit the increase in ASCs. These data suggest that estrogen and progesterone do not regulate the effect of propanil. However, complete inhibition of steroid synthesis with the gonadotropin-releasing hormone (GnRH) antagonist antide abrogated the increased response in propanil-treated mice, indicating a necessary role for steroid synthesis. Experiments in male mice demonstrated that propanil increased the number of ASCs comparable to female mice. However, orchiectomy did not inhibit this effect, suggesting that androgens do not regulate the amplification of the humoral response. These data suggest a novel role for the ovarian hormones in the regulation of the PC-specific antibody response.

Animals↗

Evaluation of immune parameters in propanil-exposed farm families.

The rice herbicide propanil induces alterations in the mouse immune system, causing significant decreases in T cell-dependent and T cell-independent antibody responses. This postemergent herbicide is used extensively in rice production in the Mississippi River delta region of the southern United States. The aerial application and airborne drift of propanil may pose health concerns to exposed farm families living adjacent to sprayed rice fields. To determine if aerial spraying of propanil increases risks of altered immune responses in families bordering rice fields, immune parameters were assessed during a 2-year study. Families living within 100 yards of rice fields were compared in a case control study to farm families whose homes exceeded 1 mile from any rice field. Blood was analyzed in adults (n = 56) and children (n = 52) at three time intervals: (1) preseason, prior to propanil application; (2) 5-7 days after aerial application of propanil to rice fields; and (3) postseason, following harvest. Exposed adults and children were compared with controls for a number of immune parameters. Total cell count and the percentage of various lymphocytes (T cells, B cells, CD4+ helper cells, and CD8+ suppressor cells) and natural killer (NK) cells, mitogen-induced cell proliferation, cytokine (IL-2+) production, and NK cell function were assessed. A comparison of immune function between exposed and nonexposed farm families showed no significant differences, possibly related to propanil exposure. However, some immune test parameters changed as a function of season rather than propanil exposure. The data indicate that individuals living next to rice fields are not at increased risk of altered immune function due to propanil exposure.

Adolescent↗

Propanil-induced methemoglobinemia and hemoglobin binding in the rat.

Administration of [ring-U-14C]propanil (3,4-dichloropropionanilide) to male Sprague-Dawley rats (30, 100, and 300 mg/kg, ip) increased the formation of methemoglobin at the two highest doses. Following a propanil dose of 100 mg/kg, methemoglobin formation attained a maximum level of 5% by 1.5 hr and declined to normal levels (approximately 2.5%) by 12 hr. Hemoglobin binding attained a maximum level of 50 pmol/mg protein by 12 hr, and remained constant for 24 hr. Following a propanil dose of 300 mg/kg, methemoglobin formation attained a maximum level of 24% by 4.5 hr, and declined to a level of 5% by 24 hr. Hemoglobin binding attained a maximum level of 425 pmol/mg protein by 12 hr, and remained constant for 24 hr. Hemoglobin binding was also detected at the lowest propanil dose (10 pmol/mg protein) even though methemoglobin formation was not observed. HPLC analysis of alkaline-treated hemoglobin from propanil-treated rats indicated the presence of one radiolabeled compound with the same HPLC retention time as 3,4-dichloraniline. These data are consistent with the concept that propanil is converted to N-hydroxy-3,4-dichloroaniline in the liver. Subsequently, this metabolite enters the erythrocyte and is oxidized by hemoglobin to 3,4-dichloronitrosobenzene with concomitant conversion of oxyhemoglobin to methemoglobin. The 3,4-dichloronitrosobenzene binds to cysteine residues on hemoglobin as the corresponding sulfinic acid amide adduct. These data suggest that human exposure to propanil may be monitored in the absence of observable toxicity by the analysis of propanil metabolites bound to hemoglobin.

Animals↗

Cytokine production by C57BL/6 mouse spleen cells is selectively reduced by exposure to propanil.

Numerous immunomodulatory effects are caused by propanil, an extensively used postemergent herbicide. The T-dependent antibody response is suppressed after exposure to propanil, raising the question of propanil's effect on T-helper-cell populations. In the present study, we show that the production of several T-cell cytokines is affected by propanil after in vivo or in vitro exposure. In vivo exposure to propanil caused the reduction of interleukin (IL)-2, IL-6, granulocyte-macrophage colony-stimulating factor (GM-CSF), and interferon (IFN)-gamma production in concanavalin A-stimulated spleen cell cultures established 2 d after exposure. IFN-gamma and GM-CSF production had recovered by d 4 postexposure; however, IL-2 and IL-6 levels continued to be depressed through d 7 postexposure. Continuous in vitro treatment of normal spleen cells with propanil decreased IL-2, IL-6, GM-CSF, and IFN-gamma production after concanavalin A activation. Pulsing normal spleen cell cultures with propanil for up to 8 h before T-cell activation resulted in reduced IL-6 but not IL-2 or IFN-gamma production. These data indicate that propanil can selectively inhibit spleen cell cytokine production, which could contribute to the immunomodulatory effects previously described.

Adjuvants, Immunologic↗

Selective myelotoxicity of propanil.

Propanil, a commonly used herbicide, has been previously shown to be immunotoxic for selected immune functions as well as specific cell types, such as the macrophage. Propanil has also been shown to cause a methemoglobulinemia and anemia through direct action on the erythrocyte. Demonstrated toxicity to both macrophages and erythrocytes raised concern for the possible myelotoxicity of propanil which could contribute to the observed effects of exposure. Therefore, the effect of propanil on several stem and progenitor cell types was assessed 7 days after acute propanil exposure. The results described herein show that propanil, at doses of 50-200 mg/kg body wt, resulted in reduction in the number of myeloid stem cells and early myeloid and erythroid progenitor cells. No reduction in the numbers of more differentiated myeloid and erythroid progenitor cells was noted at even the highest dose used (200 mg/kg). In addition, no statistically significant difference in number of leukocytes per femur was noted. These data suggest that propanil is myelotoxic to early hemapoietic stem cells, but that this reduction is apparently compensated by proliferation of more differentiated progenitor cells for the myeloid and erythroid lineages. It remains unknown whether chronic exposure leads to progressive depletion of additional myeloid and erythroid cells.

Animals↗

Role of metabolites in propanil-induced hemolytic anemia.

Hemolytic anemia and methemoglobinemia induced by exposure to certain arylamines, such as aniline and dapsone, are known to be mediated by their N-hydroxylamine metabolites. The arylamide propanil (3,4-dichloropropionanilide), a herbicide used extensively in rice fields, is also thought to induce methemoglobinemia through the action of metabolites. However, the hemolytic potential of this compound has not previously been reported. The present studies were undertaken to determine the hemolytic potential of propanil, and, if positive, the role of metabolites in this hemotoxicity. The survival of previously administered 51Cr-labeled erythrocytes in rats was reduced in a dose-dependent manner by ip administration of both propanil and its deacylated metabolite, 3,4-dichloroaniline (ED50 for both ca. 1.8 mmol/kg). When labeled erythrocytes were exposed in vitro to propanil or 3,4-dichloroaniline and then readministered to rats, no decrease in erythrocyte survival was observed, which indicated that these compounds were not direct-acting hemolytic agents. In contrast, erythrocyte survival was markedly reduced by ip administration or in vitro exposure to N-hydroxy-3,4-dichloroaniline. In addition, N-hydroxy-3,4-dichloroaniline was detected in the blood of propanil-treated rats in amounts sufficient to account for the hemolytic activity of the parent compound. These data indicate that N-hydroxy-3,4-dichloroaniline mediates propanil-induced hemolytic anemia, and that occupational exposure to propanil may result in an increased risk of hemolytic episodes.

Anemia, Hemolytic↗

Propanil affects transcriptional and posttranscriptional regulation of IL-2 expression in activated EL-4 cells.

The amide-class herbicide, propanil, causes numerous immunomodulary effects in animal models. In the present study, we investigated the effect of propanil on IL-2 expression and production in the murine lymphoma T cell line, EL-4. When supernatants of cells stimulated with phorbol 12-myristate 13-acetate in the presence of propanil were assessed by enzyme-linked immunosorbent assay, IL-2 levels were dose-dependently decreased by 20 and 50 microM of propanil but not at 10 microM. Quantitative Northern blot analysis of peak IL-2 message levels also showed a dose-dependent decrease. The kinetic pattern of message production, however, was unaffected. To determine if the reduced message production was due to reduced signaling or message stability, nuclear run-on and mRNA stability assays were performed. Nuclear run-on assays determined that the transcription rate of the IL-2 gene was decreased approximately 50% in the presence of 20 microM propanil, indicating that it was able to interfere with signal transduction. IL-2 message stability assays also demonstrated a reduction in message stability. Thus, propanil appears to reduce IL-2 production by affecting the signal transduction pathway and IL-2 message stability.

Carcinogens↗

Degradation of propanil by bacterial isolates and mixed populations from a pristine lake.

The microbial transformation rates of propanil, a commonly used herbicide, were investigated using water from a pristine lake in northeast Georgia. Microbial degradation rates were measured using natural water microflora, the natural water microflora amended with five bacterial species (Aerobacter aerogenes, Aeromonas hydrophila, Acinetobacter calcoaceticus, Proteus mirabilis, and Aeromonas salmonicida) isolated from the same lake, and the five isolates individually. Transformation rate constants for propanil were compared for the mixed microbial assemblages and isolates at similar initial bacterial concentrations (approximately 5.0 x 10(-3) bacteria/mL). Degradation started within 60 hours and was completed by 160 hours in all experiments. The mean first-order rate constant for natural microflora was -(4.80 +/- 0.620) x 10(-3) h-1. Natural waters amended with the bacterial isolates yielded rate constants ranging from -(0.39 +/- 0.186) x 10(-3) h-1 to -(2.13 +/- 0.029) x 10(-3) h-1 with an overall mean of -(1.63 +/- 0.242) x 10(-3) h-1. After 660 hours following the first amendment of propanil, (i.e., 500 hours after propanil degradation was complete), each sample was again amended with propanil. Subsequent degradation rates ranged from -(21.3 +/- 0.186) x 10(-3) h-1 to -(64.2 +/- 0.786) x 10(-3) h-1 and the mean rate constant was -(37.5 +/- 0.922) x 10(-3) h-1. No significant differences were observed between first-order rate constants among isolates following the first or the second addition of propanil. After the second spike, however, the average of rate constants was approximately 20 times greater than that following the first spike. Rates for the individual isolates varied greatly from one isolate to another, ranging from virtually no degradation with A. calcoaceticus to -(21.6 +/- 0.332) x 10(-3) h-1 for the composite treatment of all isolates.

Acinetobacter↗

Evaluation of propanil and its N-oxidized derivatives for genotoxicity in the Salmonella typhimurium reversion, Chinese hamster ovary/hypoxanthine guanine phosphoribosyl transferase, and rat hepatocyte/DNA repair assays.

Since the herbicide propanil (3,4-dichloropropionanilide) is an aromatic amide and many other aromatic amides are genotoxic via N-hydroxy (N-OH) metabolites, N-oxidized derivatives of propanil and 3,4-dichloroaniline were synthesized and tested for genotoxicity. Propanil 3,4-dichloroaniline, and their N-OH derivatives were not mutagenic in the Salmonella typhimurium reversion assay using tester strains TA97, TA98, TA100, and TA104, in both the presence and absence of exogenous metabolic activation (S9). In addition, the test compounds were not mutagenic in the Chinese hamster ovary/hypoxanthine guanine phosphoribosyl transferase (CHO/HGPRT) assay, in both the presence and absence of S9. 3,3',4,4'-Tetrachloroazobenzene (TCAB) and its azoxy derivative (TCAOB), which are synthetic contaminants and/or degradation products of propanil, were also inactive in the S. typhimurium reversion and CHO/HGPRT assays (+/- S9). Unscheduled DNA synthesis (UDS) assays were performed to determine if propanil derivatives were able to induce DNA damage in primary rat hepatocytes. Although TCAB was the only derivative tested which induced an elevation in DNA repair, the extent was not statistically significant. Hepatocyte toxicity, as measured by the release of lactate dehydrogenase 24 hr after exposure, was induced by all the test compounds in a concentration-dependent manner. Incubations of [14C]N-OH-3,4-dichloroaniline with DNA in vitro resulted in only a low level of binding that was not affected by pH. This observation may partially explained the lack of mutagenicity observed in genotoxicity assays with propanil derivatives.

Anilides↗

Changes in primary and secondary lymphoid organ T-cell subpopulations resulting from acute in vivo exposure to propanil.

Acute exposure to the herbicide propanil is immunotoxic for selected immune functions, as well as causing changes in the weights of the thymus and spleen. Although spleen cellularity and weight increase with propanil exposure, the thymus: body weight ratio decreases with increasing doses of propanil. The present study analyzes the thymocyte subpopulations in the thymus, spleen, and mesenteric lymph nodes. C57Bl/6 mice were treated with either 0, 100, 150, or 200 mg/kg propanil, and 7 d later thymocyte populations were analyzed by flow cytometry. In the thymus, propanil exposure resulted in a dose-dependent decrease in total numbers of T cells, as would be expected with its reduced weight. Determination of the thymocyte subpopulation distribution in the thymus showed a significant reduction in the number of CD3+CD4+CD8- (CD3+4+8-), CD3+CD4-CD8+ (CD3+4-8+), and CD3+CD4+CD8+ (CD3+4+8+) cells. Percent distribution of these thymic cell subpopulations showed similar decreases only with the highest dose. Apparent dose-related decreases in the numbers of CD3-CD4+CD8+ (CD3-4+8+) cells were also noted and were attributed to the general decrease in total thymus cells. The percentage of CD3- subpopulations showed an increasing trend with dose, which suggests that at 7 d postpropanil exposure there may be a specific effect on this most immature population. Although the size and cellularity of the spleen were increased, no change in CD4+ or CD8+ cell distribution was observed. Similarly, mesenteric lymph nodes showed no changes in the cell subpopulation distribution between propanil-treated and control animals.

Analysis of Variance↗

Severe propanil [N-(3,4-dichlorophenyl) propanamide] pesticide self-poisoning.

BACKGROUND: Propanil pesticide poisoning can produce methemoglobinemia, tissue hypoxia, and depression of central nervous system and respiratory system. It has been recorded only rarely worldwide and most current poison texts consider propanil to be of low toxicity. However, propanil self-poisoning is a significant clinical problem in parts of Sri Lanka and an occasional cause of death. AIM OF STUDY: To report the clinical features and management of severe propanil poisoning. PATIENTS AND METHODS: We report a retrospective case series of patients who were treated in the intensive care unit of and/or died in Anuradhapura General Hospital between 1998 and early 2002. RESULTS: Sixteen patients were identified. Common manifestations of toxicity included confusion, reduced conscious level, cyanosis, and respiratory depression. Marked hemolysis was noted in several patients. Nine deaths occurred due to respiratory depression and cardiorespiratory arrest. Management was difficult given the lack of i.v. methylene blue, inability to measure methemoglobin levels, and paucity of intensive care unit beds. CONCLUSIONS: This series indicates that propanil poisoning can be a severe form of self-poisoning, particularly in resource-poor settings. We have now initiated the establishment of a prospective series of propanil poisoned patients to further describe its clinical features, responsiveness to therapy, and case fatality rate.

Adolescent↗