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At least 19 recordsLinked to original sources

Phytotoxicity of vulpia residues: IV. Dynamics of allelochemicals during decomposition of vulpia residues and their corresponding phytotoxicity.

The behavior and dynamics of 20 identified allelochemicals in vulpia residues were both collectively and individually monitored, and their kinetic phytotoxicity was assessed. The total content of the identified allelochemicals in decaying vulpia residues increased from 0.31 to 1.24 mg/g dry residue over a 21-day decomposition period, while the total phenolic content increased from 1.86 to 2.16 mg/g dry residue. This corresponded to a phytotoxicity increase from 42% to 82% of radical inhibition. Allelochemicals changed in composition and quantity over the duration of the residue decomposition. Addition of soil to the residues reduced the total allelochemical contents extracted and altered the dynamic pattern. In the same period, the total content of allelochemicals declined from 0.061 to 0.046 mg/g residue + soil, with the total phenolics reduced from 0.20 to 0.11 mg/g residue + soil, corresponding to a radical length increase from 53% to 109% of control. Only 14 of the identified allelochemicals were detected in the mix of soil and residues, in contrast to 20 present in the residues alone. The implications of these findings are discussed.

Biological Assay↗

Validation of germination rate and root elongation as indicator to assess phytotoxicity with Cucumis sativus.

Germination rate and root elongation, as a rapid phytotoxicity test method, possess several advantages, such as sensitivity, simplicity, low cost and suitability for unstable chemicals or samples. These advantages made them suitable for developing a large-scale phytotoxicity database and especially applicable for developing quantitative structure-activity relationship (QSAR) to study mechanisms of phytotoxicity. In this paper, the comparative inhibition of germination rate and root elongation of Cucumis sativus by selected halogen-substituted phenols and anilines were determined. The suitability of germination rate and root elongation as phytotoxicity endpoints was evaluated. Excellent reproducibility and stability of germination rate and root elongation in the control test, relatively greater sensitivity and similar dose-response relations for all tested compounds were observed. These results together with those of a 2-day test were used to demonstrate the suitability of this phytotoxicity test method. A QSAR was developed for the phytotoxicity mode of action of the tested compounds to C sativus seeds. Models that combined the logarithm of 1-octanol/water partition coefficient (log Kow) and the energy of the lowest unoccupied molecular orbital (Elumo) were developed for both germination rate inhibition and root elongation inhibition. The results of these studies indicate that phytotoxicity of substituted phenols and anilines to C. sativus seeds could be explained by a polar narcosis mechanism. This paper will promote the application of germination rate and root elongation method and the development of large-scale phytotoxicity database, which will provide the fundamental data for QSAR and ecological risk assessment of organic pollutants.

Biomarkers↗

Phytotoxicity of pheromonal chemicals to fruit tree foliage: chemical and physiological characterization.

Some recent high-load, low-density pheromone-release devices emit an ethanolic blend of pheromone directly onto crop foliage to control insect pests by mating disruption. This study characterized the phytotoxicity associated with deposition of some pheromonal compounds in concentrated drops on the foliage of trees bearing aerosol release devices. The relative toxicity of straight-chained alkanes, alcohols, aldehydes, and acetates with chain lengths varying from C-2 to approximately C-20 was quantified in the laboratory by the severity of necrotic lesions. The order of severity for phytotoxicity caused by pheromonal compounds was alkanes << acetates = aldehydes < or = alcohols. Within compound classes tested, pheromones with chain lengths of 6-13 carbons were the most phytotoxic. Phytotoxicity was not detectable at dosages <1 mg administered in 10 microl of ethanol. Phytotoxicity of pheromones was highly correlated with presence of both a hydrophilic and lipophilic molecular domain. We postulate nonspecific membrane disruption as a likely mode of action for pheromonal phytotoxicity. Limited attempts to remediate this effect by changing carrier solvents or adding surfactants, spreaders, or nonvolatile diluents were not successful. Because the toxic action of pheromones upon plant tissues appears relatively benign, and growers have not been adverse to localized phytotoxicity to foliage and fruits on two trees per 0.4 ha, we propose that limited phytotoxicity associated with first-generation aerosol dispenser technology can be viewed as non-threatening.

Light↗

Effects of composting on phytotoxicity of spent pig-manure sawdust litter.

The phytotoxicity of spent pig-manure sawdust litter (spent litter) was evaluated during further composting. Aqueous extracts of the spent litter were prepared by shaking the sample with water (1:10 w/v), and the toxicity of these extracts was determined on relative seed germination, relative root elongation and germination index (GI, a factor of relative seed germination and relative root elongation). The sensitivity of six plant species, namely Brassica parachinensis (Chinese cabbage), Brassica albogalera (Chinese kale), Allium sativum (onion), Cucumis sativus (cucumber), Amaranthus espinosus (Chinese spinach), and Lycopersicon esculentum (tomato) were compared. The effect of different moisture levels during composting on the phytotoxicity of the spent litter was also examined. Phytotoxicity of the spent litter was only evident during the earlier stage of composting (first 14 days) and, that seed germination and root elongation reached 100% (same as the control) towards the end of the composting. The concentrations of the major inhibitors, water-extractable Cu and Zn, and NH4(+)-N of the spent litter, declined during composting, indicating that these inhibitors were gradually eliminated as composting proceeded. Multiple regression analysis showed that the NH4(+)-N content of the spent litter was the most important chemical factor affecting phytotoxicity of the plant species selected for this study. Relative root elongation and GI were more sensitive indicators of phytotoxicity than seed germination. In the present study, the GI's of all plant species were >80% at day 60, indicating that the spent litter had reached its maturation by day 60. The responses of different plant species to the water-extracts of the spent litter were different. Among the six species, Chinese cabbage and Chinese spinach were the most sensitive species, and tomato and cucumber were the least sensitive species to indicate phytotoxicity of the spent litter. Moisture adjustment during the composting process did not affect the results of the phytotoxicity test.

Journal Article↗

Phytotoxicity dynamics of decaying plant materials.

Allelopathic effects of plant litter have been extensively studied, but less attention has been given to the dynamics of phytotoxicity during the decomposition processes. Decomposition experiments were carried out on above- and below-ground plant materials of 25 species of different functional groups (nitrogen fixer, forbs, woody and grasses-sedges) in aerobic and anaerobic conditions. The phytotoxicity of aqueous extracts of decomposing material was assessed by bioassay in 30 d of laboratory and 90 d of litterbag decomposition experiments. Phytotoxicity was widespread with c. 90% of the tested species showing significant phytotoxic releases. Phytotoxicity largely varied between different plant functional groups (nitrogen fixer>forbs=woody>>grasses-sedges) and was higher for leaf compared with root materials. In all species tested during decomposition, phytotoxicity rapidly decreased in aerobic conditions but sharply increased and became stable in anaerobic conditions. The results demonstrate an unexpectedly widespread occurrence of phytotoxicity with clear dynamic patterns during the decomposition processes of plant materials. The ecological consequences of this might have been underestimated.

Analysis of Variance↗

Phytotoxicity of surface waters of the Thames and Brisbane River estuaries: a combined chemical analysis and bioassay approach for the comparison of two systems.

The Thames Estuary, UK, and the Brisbane River, Australia, are comparable in size and catchment area. Both are representative of the large and growing number of the world's estuaries associated with major cities. Principle differences between the two systems relate to climate and human population pressures. In order to assess the potential phytotoxic impact of herbicide residues in the estuaries, surface waters were analysed with a PAM fluorometry-based bioassay that employs the photosynthetic efficiency (photosystem II quantum yield) of laboratory cultured microalgae, as an endpoint measure of phytotoxicity. In addition, surface waters were chemically analysed for a limited number of herbicides. Diuron, atrazine and simazine were detected in both systems at comparable concentrations. In contrast, bioassay results revealed that whilst detected herbicides accounted for the observed phytotoxicity of Brisbane River extracts with great accuracy, they consistently explained only around 50% of the phytotoxicity induced by Thames Estuary extracts. Unaccounted for phytotoxicity in Thames surface waters is indicative of unidentified phytotoxins. The greatest phytotoxic response was measured at Charing Cross, Thames Estuary, and corresponded to a diuron equivalent concentration of 180 ng L(-1). The study employs relative potencies (REP) of PSII impacting herbicides and demonstrates that chemical analysis alone is prone to omission of valuable information. Results of the study provide support for the incorporation of bioassays into routine monitoring programs where bioassay data may be used to predict and verify chemical contamination data, alert to unidentified compounds and provide the user with information regarding cumulative toxicity of complex mixtures.

Australia↗

Phytotoxicity and phytoaccumulation of trivalent and hexavalent chromium in brake fern.

A recently recognized hyperaccumulator plant, Chinese brake fern (Pteris vittata), has been found to extract very high concentration of arsenic from arsenic-contaminated soil. Chromium usually is a coexisting contaminant with arsenic in most contaminated soils. The potential application of ferns for phytoremediation of chromium(III)- and chromium(VI)-contaminated soils and their phytotoxicity to ferns has not been studied before. In this study, chromium distribution and phytotoxicity at the plant and cellular levels of brake ferns were studied using chemical analyses and scanning electron microscopy. The results show a higher phytotoxicity of Cr from Cr(VI)-contaminated soil to Chinese brake fern than from Cr(III)-contaminated soil. Phytotoxicity symptoms included significant decreases both in fresh biomass weight and relative water content (RWC), and also in leaf chlorosis during the late stage of growing. At higher concentrations (500 mg/kg Cr[VI] and 1,000 mg/kg Cr[III] addition), plants showed reduction in the number of palisade and spongy parenchyma cells in leaves. Compared with other plant species reported for phytoremediation of Cr(VI)-contaminated soil, brake fern took up and accumulated significant amounts of Cr (up to 1,145 mg/kg in shoots and 5,717 mg/kg in roots) and did not die immediately from phytotoxicity. Our study suggests that Chinese brake fern is a potential candidate for phytoremediation of Cr(VI)-contaminated soils, even though plants showed severe phytotoxic symptoms at higher soil Cr concentrations.

Chromium↗

Amelioration of nickel phytotoxicity in muck and mineral soils.

In situ remediation (phytostabilization) is a cost-effective solution for restoring the productivity of metal-contaminated soils and protection of food chains. A pot experiment with wheat (Triticum aestivum L.), oat (Avena sativa L.), and redbeet (Beta vulgaris L.) was conducted to test the ability of limestone and hydrous ferric oxide (HFO) to ameliorate Ni phytotoxicity in two soils contaminated by particulate emissions from a nickel refinery. Quarry muck (Terric Haplohemist; 72% organic matter) contained 2210 mg kg(-1) of total Ni. The mineral soil, Welland silt loam (Typic Epiaquoll), was more contaminated (2930 mg Ni kg(-1)). Both soils were very strongly acidic, allowing the soil Ni to be soluble and phytotoxic. Nickel phytotoxicity of the untreated muck soil was not very pronounced and could be easily confused with symptoms of Mn deficiency that occurred in this soil even with Mn fertilization. Severe nickel phytotoxicity of the untreated mineral soil prevented any growth of redbeet, the most sensitive crop; even wheat, a relatively Ni-resistant species, was severely damaged. White banding indicative of Ni phytotoxicity was present on oat and wheat leaves grown on the acidic mineral soil. Soil Ni extracted with diethylenetriaminepentaacetic acid (DTPA) and 0.01 M Sr(NO3)2 was indicative of the ameliorative effect of amendments and correlated well with Ni concentrations in plant shoots. Making soils calcareous was an effective treatment to reduce plant-available Ni and remediate Ni phytotoxicity of these soils to all crops tested. The ameliorative effect of HFO was crop-specific and much less pronounced.

Avena↗

[Selective phytotoxic activity of N,N-di,sec.butylamides of aminobenzoic acids mono-, di- and tri-substituted on the nucleus].

N,N-di,sec.butylaminobenzamides, mono-, di- or trisubstituted on the nucleus with methyl and/or halogen groups were prepared and tested for phytotoxicity. The corresponding benzoic acids and series of N-alkyl- and N,N-dialkylamides of 2-amino-3-bromo-5-methyl-, 2-amino-3,5-dibromo, 2-amino-3,5-dichloro- and 3-amino-2,5-dichlorobenzoic acids were studied in parallel. Both pre- and post-emergence phytotoxicity tests were carried out with doses of 6 kg/ha or less on seven representative weeds and some plants of agricultural interest. The series of N,N-di,sec.butylamides studied proved to be effectively phytotoxic on absorption through either the roots or the foliage. As regards the effect of substitution in the nucleus on the phytotoxicity of these amides, 3,5-dihalogenation proved important. The results also showed: 1) the importance of two sec.butyl groups on the amide nitrogen for the appearance of selective phytotoxicity against two grass weeds; 2) the different behaviour of the two acids (XXIa) and (XXIIa) in comparison with the corresponding di,sec.butylamides (XXI) and (XXII); 3) the importance of derivative (IL) which was highly active against graminaceous weeds but showed low phytotoxicity against crop plants, graminaceous ones included.

Aminobenzoates↗

[Phytotoxicity of hydrazones of aromatic aldehydes].

A series of hydrazones of aromatic aldehydes (B) was prepared and tested for phytotoxicity. These compounds are bioisosters of 1-aryltriazenes (A) which were found to possess interesting phytotoxic properties in a previous research. The substances studied (Tables I leads to III: compounds(I leads to CLXXX)) some of which were previously unrecorded, were prepared by the usual procedures from the required aldehyde and hydrazine derivative. The phytotoxicity of all the compounds was studied using seven representative species in both pre- and post-emergence tests at a dose of 6 kg/ha. It was found that this class of compounds shows phytotoxicity by absorption through the foliage with specificity for Amaranthus retroflexus L. The only exceptions are compounds where the aryl residue is 2,6-dichlorophenyl; these compounds show wide spectrum of phytotoxicity by absorption through the leaves.

Aldehydes↗

A biological test system for the evaluation of the phytotoxicity of metal-contaminated soils.

The potential soil phytotoxicity in the surroundings of an old zinc smelter closed in 1966, was evaluated by a biological test system. This system is based on the analysis of shoot growth and (iso-) enzymes in leaves and roots of 2-week-old seedlings of Phaseolus vulgaris grown on soil samples under controlled environmental conditions. The biological data were presented in a phytotoxicity index, which allowed classification of the soil samples into four phytotoxicity classes. Comparison was made between the biological results and soil and plant metal content. The study revealed that more than 20 years after closure of the factory, the soils in its surroundings were still potentially phytotoxic. Zinc proved to be the most important, but not the only, phytotoxic element, as was shown by isozyme analysis and by the strong correlation between the biological data, the water soluble Zn fraction of the soil and leaf Zn content. The effect of contamination extended to a distance of more than 3 km from the industrial site in the direction of the prevailing wind.

Journal Article↗

Land spreading of olive mill wastewater: effects on soil microbial activity and potential phytotoxicity.

Extremely high organic load and the toxic nature of olive mill wastewater (OMW) prevent their direct discharge into domestic wastewater treatment systems. In addition to the various treatment schemes designed for such wastewater, controlled land spreading of untreated OMW has been suggested as an alternative mean of disposal. A field study was conducted between October 2004 and September 2005 to assess possible effects of OMW on soil microbial activity and potential phytotoxicity. The experiment was carried out in an organic orchard located on a Vertisol-type soil (Jezre'el Valley, Israel) and included two application levels of OMW (36 and 72m(3)ha(-1)). Total microbial counts, and to less extent the hydrolytic activity and soil respiration were increased following the high OMW application level. A bench-scale lab experiment showed that the rate of OMW mineralization was mainly dependent on the general status of soil activity and was not related to previous acclimatization of the soil microflora to OMW. Soil phytotoxicity (% germination and root elongation) was assessed in soil extracts of samples collected before and after each OMW application, using germinating cress (Lepidium sativum L.) seeds. We found direct short-term effect of OMW application on soil phytotoxicity. However, the soil was partly or completely recovered between successive applications. No further phytotoxicity was observed in treated soils as compared with control soil, 3 months after OMW application. Such short-term phytotoxicity was not in correlation with measured EC and total polyphenols in the soil extracts. Overall, the results of this study further support a safe controlled OMW spreading on lands that are not associated with sensitive aquifers.

Biodegradation, Environmental↗

[Phytotoxicity of di,sec.butylamides of halogenoalkoxybenzoic acids].

N,N-di,sec.butylamides of halogenated alkoxybenzoic acids were prepared and tested for phytotoxic activity. The corresponding acids and a series of N-alkyl- and N,N-dialkylamides of 2-methoxy-3,5-dichlorobenzoic acid were studied in parallel. The phytotoxicity of these substances was tested against seven representative weeds and some crop plants using both pre- and post-emergence test at doses of 6 kg/ha or lower. The amides studied proved more strongly phytotoxic on absorption through the root than through the foliage. Furthermore selective phytotoxic activity against two important infesting graminacae, Echinochloa crus-galli R.S. and Setaria glauca L. was observed. Some of these compounds showed low toxicity or were tolerated by crop plants. The results obtained with this series of amides of 2-methoxy-3,5-dichlorobenzoic acid confirm the importance of the sec.butyl group on N for the appearance of selective phytotoxicity.

Benzoates↗

Phytotoxicity assessment of diclofenac and its phototransformation products.

The occurrence of pharmaceuticals in the environment is an emerging issue. Several studies observed that the non-steroidal anti-inflammatory drug diclofenac is ubiquitously present in most of the surveyed surface waters, worldwide. Phototransformation of diclofenac was reported from laboratory assays as well as in natural water systems, raising the question of possible adverse effects of the phototransformation products of diclofenac to aquatic organisms. In this study the phytotoxicity of diclofenac exposed to natural sunlight was evaluated using synchronized cultures of the unicellular chlorophyte Scenedesmus vacuolatus. Diclofenac dissolved in ultra-pure water at 50 mg L(-1) was exposed to natural midsummer sunlight for a maximum of 145 h. Twice a day subsamples were taken for chromatography and parallel phytotoxicity assessment. Inhibition of algal reproduction of the initial diclofenac solution was in the mg L(-1) range indicating no specific toxicity of diclofenac towards S. vacuolatus. Fast degradation of diclofenac was observed with half lives between 3.3 and 6.4 h during the first and the third day of exposure, respectively. Phytotoxicity increased after 3.5 h of exposure of diclofenac to sunlight and showed a maximum of sixfold enhanced toxicity after 53 h of exposure to sunlight. Several phototransformation products were found during the experiment. The time courses of the relative concentration of three transformation products significantly correlated with enhanced phytotoxicity during the experiment. This indicates a high toxicity potential of phototransformation products of diclofenac at concentration levels that may come close to environmental concentrations of residual diclofenac after degradation. We conclude that toxicity assessment of phototransformation products should be included in the risk assessment of pharmaceuticals in the environment.

Chromatography, High Pressure Liquid↗

Use of algal fluorescence for determination of phytotoxicity of heavy metals and pesticides as environmental pollutants.

The phytotoxicity of heavy metals and pesticides was studied by using the fluorescence induction from the alga Dunaliella tertiolecta. The complementary area calculated from the variable fluorescence induction was used as a direct parameter to estimate phytotoxicity. The value of this parameter was affected when algae were treated with different concentrations of mercury, copper, atrazine, DCMU, Dutox, and Soilgard. The toxic effect of these pollutants was estimated by monitoring the decrease in the complementary area, which reflects photosystem II photochemistry. Further, the authors have demonstrated the advantage of using the complementary area as a parameter of phytotoxicity over using variable fluorescence yield. The complementary area of algal fluorescence can be used as a simple and sensitive parameter in the estimation of the phytotoxicity of polluted water.

Chlorophyll↗

Use of freshwater plants for phytotoxicity testing: a review.

Phytotoxicity data for aquatic plants have served a relatively minor role in regulatory decisions concerning the environmental hazard of most potential contaminants. A variety of phytotoxicity tests have been conducted with freshwater green algae, duckweed, blue-green algae, diatoms and rooted macrophytes (whole plants and seeds). Several test methods have been standardized for microalgae which are used primarily with chemicals, effluents, contaminated sediment elutriates and hazardous waste leachates. Current scientific understanding concerning the phytotoxic effects of these contaminants is based mostly on results for a few green algae. The greatest limitation of these results is their uncertain environmental relevance due to the large interspecific variation in response of standard algal test species and the unrealistic experimental test conditions. Results of the few field validation toxicity tests conducted to resolve this uncertainty have been chemical-specific and unpredictable. Aquatic vascular plants have been used less frequently than algae as test species. Duckweeds have been used more often than rooted submersed species but the uncertain nature of their sensitivities relative to animal and other plant species has limited their use. Regulatory interest in wetland protection, contaminated sediment evaluations and sediment quality criteria development will result in increased use of whole rooted plants and their seeds as test species. Overall, regardless of the test species, if phytotoxicity data are to be more available and effective in the hazard assessment process, additional information concerning species sensitivity, and environmental relevance of the results will be needed.

Journal Article↗