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E1On the effect of 6-methyluracil on mice damaged by 2,4,6-triethylene-imino-1,3,5-triazine or by X-irradiation (author's transl).

Survival time of mice after i.v. injections of 2,4.6-triethylene-imino-1,3,5-trazine (TEM) or total body-X-irradiation (TBI) was increased by 6-methyluraclil (6-MU) when given in food (200 ppm). Under the same conditions, 6-MU decreased the involution of spleen and thymus (as measured by DNA-content and DNase II activity) under the infuence of TEM and enhanced the regeneration of the spleen after TBI. Elevation of DNase I- and protein content of the kidneys and a (short-dated) increase of incorporation of 14C-phenylalamine into microsomes of liver of 14C-orotic acid into RNA of liver and kidney suggest that the influence of 6-MU is mediated at least partly by a specfically anabolic effect.

Animals↗

[Embryotropic action of the triazine herbicide polyzin 50].

The embryotropic effect of the new Bulgarian simtriazine herbicide polyzin 50 was studied in an experiment upon 90 pregnant albino rats - Wistar, via inhalation effect in concentrations 2 mg/m3 and 0.2 mg/m3, daily during the whole pregnancy and at a level of 2 mg/m3 during the first trimester of gestation. With both regimes, the preparation has a teratogenic and a more lightly manifested embryotoxic activity. In the absence of general toxic effect upon the pregnant organism, polyzin induces external malformations (hypognathus, oedema), anomalies in the development of the internal organs (hydrocephalus, intracerebral hematoma, hemorrhages in the abdominal cavity, infarctus-like foci in liver) and defects in the ossification of the cranial bones of fetus. The preparation has an embryotoxic activity (increased incidence of subcutaneous hematomas of the fetus), only with the daily penetration in organism of the pregnant animals in a concentration of 2 mg/m3. With both concentrations of antenatal effect of polyzin studied, a functional insufficiency of the liver of the progeny develops during the postnatal development period. On the grounds of the data obtained about the embryotoxic and teratogenic effect of polyzin with its inhalation effect in low concentrations - 2 mg/m3 and 0.2 mg/m3, a recommendation is proposed-prohibition of women's participation in its production at a fertile age.

Animals↗

Interactions between aldehyde derivatives and the aldehyde binding site of bacterial luciferase.

The interaction of triazine aldehydes with the aldehyde binding site of bacterial luciferases was investigated using a series of triazine aldehydes with different aldehyde chain length, and substituents on the s-triazine ring. Substrate activity was determined using luciferase from Photobacterium fischeri and Vibrio harveyi in a dithionite-based luciferases assay. The chain length optimum was determined for two triazine aldehyde classes to be C-10 and C-11, respectively. Only the substrate activity of 10-(4-chloro-6-methylthio-s-triazine-2-yl)aminodecanal (5) was as high as n-decanal, the reference aldehyde. All other triazine derivatives reduced light emission, probably by hindered binding of the substrates. The degree of activity reduction correlated with the volume of the triazine ring moiety. The triazine moiety volume of compound 5 was estimated to be 200 x 10(-30) m3. Triazine aldehydes which showed reduced light emission had an estimated volume of 228 x 10(-30) m3 or greater. All triazine aldehydes showed approximately 10-fold lower activities for Vibrio harveyi than for Photobacterium fischeri luciferase. Substrate specificity was the same for both luciferases. A schematic superposition of quinone aldehydes and triazine aldehydes which showed substrate activities equivalent to n-decanal, indicated potential interaction sites of aldehyde substrates with the aldehyde binding site of bacterial luciferases. The in vivo relevance of the results is discussed.

Aldehydes↗

Control of workers' exposure to airborne endotoxins and formaldehyde during the use of metalworking fluids.

The study evaluated the effects of triazine use and machine enclosure on workers' exposure to bacteria, endotoxins, and formaldehyde in the use of metalworking fluids (MWF). Concentrations of triazine and bacterial contaminants were monitored in bulk samples of MWF from two machines in one workplace. One of the machines was used normally; triazine was added to the other when needed. Air sampling was used to estimate workers' exposure to endotoxins at 18 workplaces near enclosed and open machines. Concentrations of triazine in MWF and formaldehyde in the air were measured. Some recirculating local exhaust ventilation systems were also tested. The endotoxin and bacteria concentrations in the biocide test of MWF rapidly increased when the biocide levels decreased below 500 ppm. Airborne concentrations of endotoxins were substantially lower near enclosed machines than near open ones. Concentrations of airborne formaldehyde were below the Finnish occupational exposure limit at the existing levels of triazine in MWF. Concentrations of triazine in MWF correlated well with those of formaldehyde in the air near the machines (correlation coefficient r=.69). The results showed that the triazine levels in MWF should continuously be kept high enough (>500 ppm) to prevent workers' exposure to endotoxins and bacteria. Overdosing with triazine, however, should be avoided, so that the levels of airborne formaldehyde remain low. Triazine levels in MWF can be followed by the method described in this article. Workers' exposure to contaminants of MWF can be reduced substantially by enclosing the machines and equipping them with local exhausts.

Aerosols↗

Identification of enzymes involved in the metabolism of atrazine, terbuthylazine, ametryne, and terbutryne in human liver microsomes.

Compounds of the s-triazine family are among the most heavily used herbicides over the last 30 years. Some of these derivatives are suspected to be carcinogens. In this study the identity of specific phase-I enzymes involved in the metabolism of s-triazine derivatives (atrazine, terbuthylazine, ametryne, and terbutryne) by human liver microsomes was determined. Kinetic studies demonstrated biphasic kinetics for all pathways examined (S-oxidation, N-dealkylation, and side-chain C-oxidation). Low K(m) values were in a range of about 1-20 microM, whereas high K(m) values were up to 2 orders of magnitude higher. For a correlation study, 30 human liver microsomal preparations were screened for seven specific P450 activities, and these were compared to activities for the metabolites derived from these s-triazines. A highly significant correlation in the high-affinity concentration range was seen with cytochrome P450 1A2 activities. Chemical inhibition was most effective with alpha-naphthoflavone and furafylline at low s-triazine concentrations and additionally with ketoconazole and gestodene at high substrate concentrations. Studies with 10 heterologously expressed P450 forms demonstrated that several P450 enzymes are capable of oxidizing these s-triazines, with different affinities and regioselectivities. P450 1A2 was confirmed to be the low-K(m) P450 enzyme involved in the metabolism of these s-triazines. A potential participation of flavin-containing monooxygenases (FMOs) in sulfoxidation reactions of the thiomethyl derivatives ametryne and terbutryne in human liver was also evaluated. Sulfoxide formation in human liver microsomes as a function of pH, heat, and chemical inhibition indicated no significant involvement of FMOs. Finally, purified recombinant FMO3, the major FMO in human liver, exhibited no significant activity (< 0.1 nmol (nmol of FMO3)-1 min-1) in the formation of the parent sulfoxides of ametryne and terbutryne. Therefore, P450 1A2 alone is likely to be responsible for the hepatic oxidative phase-I metabolism of the s-triazine derivatives in exposed humans.

Adult↗

Ametryne and prometryne as sulfur sources for bacteria.

Bacteria were isolated that could utilize quantitatively the s-triazine herbicide prometryne [N,N' -bis(1-methylethyl)-6-(methylthio)-1,3,5-triazine-2,4-diamine] or ametryne [N-ethyl-N'-(1-methylethyl)-6-(methylthio)-1,3,5-triazine- 2,4-diamine], or both, as a sole source of sulfur for growth. The success of enrichments depended on previous exposure of the soil inoculum to s-triazine herbicides. Deaminoethylametryne [4-(1-methylethyl)amino-6-(methylthio)-1,3,5-triazine-2-(1H)-one], methylsulfonic acid, and sodium sulfate could also be used as sulfur sources. Utilization of a compound was quantified as the growth yield per mole of sulfur supplied. Yields were about 6 kg of protein per mol of sulfur. The product of the desulfuration of an s-triazine was identified as the corresponding hydroxy-derivative. This is the first substantiated report of the utilization of these s-triazines as sulfur sources by bacteria.

Journal Article↗

Sonolytic, photolytic, and photocatalytic decomposition of atrazine in the presence of polyoxometalates.

Aqueous solutions of atrazine [2-chloro-4-(isopropylamino)-6-(ethylamino)-s-triazine] (CIET) decompose upon illumination with a low-pressure Hg-arc lamp (254 nm). However, no decomposition takes place with lambda > 300 nm. On the other hand, addition of polyoxometalates (POM), PW12O40(3-) or SiW12O40(4-), into a solution of atrazine photodecomposes the substrate within a few minutes (cutoff fiter 320 nm). Ultrasound (US) treatment also decomposes aqueous solutions of atrazine within a few minutes. Both methods, sonolysis and photolysis with POM, give common intermediates, namely, 2-hydroxy-4-(isopropylamino)-6-amino-s-triazine (OIET), 2-chloro-4-(isopropylamino)-6-amino-s-triazine (CIAT), 2-chloro-4-amino-6-(ethylamino)-s-triazine (CAET), 2-hydroxy-4,6-diamino-s-triazine (OAAT), and 2-hydroxy-4-hydroxy-6-amino-s-triazine (OOAT) among others. The final products for both methods, US and photolysis with POM, were cyanuric acid (OOOT), NO3-, Cl-, CO2, and H2O. OOOT showed no signs of decomposition by sonication and/or photolysis with POM. It also resisted degradation upon photolysis with plain UV light (254 nm). However, it has been reported to decompose upon photolysis with lambda > 200 nm. Combination of US and photolysis with POM produces only a cumulative effect.

Atrazine↗

Changes in rat liver cytochrome P450 enzymes by atrazine and simazine treatment.

1. We examined the effect of two chloro-s-triazines (atrazine and simazine) on hepatic microsomal cytochrome P450 enzymes in rat. Rats were treated intraperitoneally with atrazine or simazine daily for 3 days with 100, 200 and 400 mumol/kg. 2. Among the P450-dependent monooxygenase activities, testosterone 2 alpha-hydroxylase (T2AH) activity in rat, which is associated with CYP2C11, was significantly decreased at all doses of atrazine and simazine. The levels relative to control activities were 59-46 and 60-32% respectively. Similarly, oestradiol 2-hydroxylase (ED2H) activity was also significantly decreased by 28-51% by atrazine and simazine at all doses. However, no change in CYP2C11 protein level by either chloro-s-triazine was observed. K(m) for T2AH was significantly increased only by simazine (200 mumol/kg), whereas the Vmax and Cl(int) for T2AH were significantly decreased by atrazine and simazine at all doses. 3. 7-Ethoxyresorufin O-deethylase (EROD), 7-methoxyresorufin O-demethylase (MROD) and 7-pentoxyresorufin O-depentylase (PROD) activities were significantly increased by 1.4-1.6-, 1.7-3.2- and 1.5-2.2-fold respectively, by both chloro-s-triazines at 200 or 400 mumol/kg. Lauric acid omega-hydroxylase (LAOH) was also increased by 1.4-fold by simazine at 200 and 400 mumol/kg. Immunoblotting showed that only simazine induces CYP1A2 and CYP4A1/2 protein expression. 4. The activities of 7-ethoxycoumarin O-deethylase (ECOD), bufuralol 1'-hydroxylase (BF1'H), chlorzoxazone 6-hydroxylase (CZ6H), testosterone 6 beta-hydroxylase (T6BH) and testosterone 7 alpha-hydroxylase (T7AH) were not affected by either chloro-s-triazine. 5. These results suggest that the pattern of changes in P450 isoforms by chloro-s-triazines differs between atrazine and simazine, that these herbicides change the constitutive and/or male specific P450 isoform(s) in rat liver, and that these changes closely relate to the toxicity of chloro-s-triazines.

Animals↗

Atrazine metabolism in resistant corn and sorghum.

The metabolism of 2-chloro-4-ethylamino-6-isopropylamino-s-triazine (atrazine) in the resistant species, corn (Zea mays L.) and sorghum (Sorghum vulgare Pers.) was not the same. In corn, atrazine was metabolized via both the 2-hydroxylation and N-dealkylation pathways while sorghum metabolized atrazine via the N-dealkylation pathway. Atrazine metabolism in corn yielded the metabolites, 2-hydroxy-4-ethylamino-6-isopropylamino-s-triazine (hydroxyatrazine), 2-hydroxy-4-amino-6-isopropylamino-s-triazine (hydroxycompound I), and 2-hydroxy-4-amino-6-ethylamino-s-triazine (hydroxycompound II). None of these hydroxylated derivatives appeared as metabolites of atrazine in sorghum.Hydroxycompounds I and II were formed in 2 ways in corn: (1) by benzoxazinone-catalyzed hydrolysis of 2-chloro-4-amino-6-isopropylamino-s-triazine (compound I) and 2-chloro-4-amino-6-ethylamino-s-triazine (compound II) that were formed by N-dealkylation of atrazine and (2) by N-dealkylation of hydroxyatrazine, the major atrazine metabolite in corn. The interaction of the 2-hydroxylation and N-dealkylation pathways in corn results in the formation of the 3 hydroxylated non-phytotoxic derivatives of atrazine.

Journal Article↗

Inhibition of atrazine degradation by cyanazine and exogenous nitrogen in bacterial isolate M91-3.

A variety of s-triazine herbicides and nitrogen fertilizers frequently occur as co-contaminants at pesticide manufacturing and distribution facilities. The degradation of atrazine and cyanazine by the bacterial isolate M91-3 was investigated in washed-cell suspensions and crude cellular extracts. Cyanazine competitively inhibited atrazine degradation. The maximum atrazine degradation rate (Vmax) was 41 times higher and the half-saturation constant for the inhibitor (Ki) was 1.3 times higher in the crude cellular extract than in the washed-cell suspension, suggesting that cellular uptake influenced degradation of the s-triazines. Cultures that had received prior exposure to atrazine and simazine exhibited comparable atrazine degradation rates, while cells exposed to cyanazine, propazine, ametryne, cyanuric acid, 2-hydroxyatrazine, biuret, and urea exhibited a lack of atrazine-degradative activity. Growth in the presence of exogenous inorganic nitrogen inhibited subsequent atrazine-degradative activity in washed-cell suspensions, suggesting that regulation of s-triazine and nitrogen metabolism are linked in this bacterial isolate. These findings have significant implications for the environmental fate of s-triazines in agricultural settings since these herbicides are frequently applied to soils receiving N fertilizers. Furthermore, these results suggest that bioremediation of s-triazine-contaminated sites (common at pesticide distribution facilities in the cornbelt) may be inhibited by the presence of N fertilizers that occur as co-contaminants.

Atrazine↗

Resistance to herbicide and susceptibility to herbivores: environmental variation in the magnitude of an ecological trade-off.

Trade-offs can maintain genetic diversity and constrain adaptation; however, their magnitude may depend on ecological factors. I considered whether resistance to the herbicide triazine in Amaranthus hybridus (Amaranthaceae) imposed the trade-off of increasing susceptibility to herbivorous insects. I grew triazine-resistant and triazine-susceptible plants under contrasting levels of light and fertilization, and quantified susceptibility to herbivores using the specialist Disonycha glabrata (Coleoptera: Chrysomelidae) and the generalist Trichoplusia ni (Lepidoptera: Noctuidae). Resistance to triazine increased susceptibility to both species of herbivorous insects, as manifested by greater feeding preference, growth, and survival of herbivores. However, these effects were more pronounced with T. ni and for plants grown under high light. My results demonstrate the presence of a trade-off between resistance to triazine and susceptibility to herbivorous insects that may in turn impose an ecologically based fitness cost, and illustrate the potential for this cost to vary across environments.

Amaranthus↗