Phytotoxicity of single and combined polycyclic aromatic hydrocarbons toward economic crops

Toxicity of anthracene, fluoranthene, fluorene, phenanthrene, and the mixtures of these polycyclic aromatic hydrocarbons (PAHs) to three economic crops in Thailand was compared. Seeds of sweet corn, waxy corn, and rice were planted in soils contaminated with each PAH alone, binary mixtures, and total four PAH mixture. Rice seedlings were most sensitive to PAHs. Germination of sweet corn, waxy corn, and rice seeds was delayed by single PAH and their mixtures, especially at their high concentrations. More than 20 mg/kg of anthracene and 2 mg/kg of phenanthrene significantly retarded the seed germination rate in waxy corn. Root and shoot elongation were more sensitive to toxic PAHs than other growth indices. Fluorene was more toxic to all the tested plants than other PAHs. (Anthracene + fluoranthene) was most toxic to plants when compared with other PAH mixtures. There was synergistic combine effect of PAHs on corn root length, but there were antagonistic combine effects on fresh weights of both plants and rice root length. PAH mixtures did not affect dry weights of all plants.     

The polycyclic aromatic hydrocarbon phenanthrene causes oxidative stress and alters polyamine metabolism in the aquatic liverwort Riccia fluitans L

The polycyclic aromatic hydrocarbon (PAH) phenanthrene (PHEN) is a highly toxic pollutant, commonly found in aquatic environments, the effects of which on aquatic plants have not been studied in depth. As PAHs are known to induce oxidative stress and recent studies have shown that polyamines (PAs) participate in the defence reactions protecting plants against environmental stresses, PA metabolism and oxidative damage were investigated in the aquatic form of the liverwort Riccia fluitans L. exposed to PHEN. Exposure of Riccia fluitans plants to PHEN at concentrations of 0.5 microm or less induced oxidative stress, but at a level from which plants could recover. Despite increased levels of enzymatic and non-enzymatic antioxidants, recovery appeared, at least in part, due to increased synthesis of PAs, achieved via increased activities of the enzymes arginine decarboxylase (ADC) and S-adenosylmethionine decarboxylase (SAMDC). Chemical inhibition of these enzymes inhibited plant recovery, while treatment with PAs aided recovery. Finally, as chloroplasts and the plasma membrane appeared to be key targets for PHEN-induced damage, the potential roles of PAs in protecting these cellular components were considered. How PAs could protect plant cells from serious environmental pollutants such as PHEN and could prevent oxidative stress is discussed.     

Distribution of polycyclic aromatic hydrocarbons in subcellular root tissues of ryegrass (Lolium multiflorum Lam.)

Background

Because of the increasing quantity and high toxicity to humans of polycyclic aromatic hydrocarbons (PAHs) in the environment, several bioremediation mechanisms and protocols have been investigated to restore PAH-contaminated sites. The transport of organic contaminants among plant cells via tissues and their partition in roots, stalks, and leaves resulting from transpiration and lipid content have been extensively investigated. However, information about PAH distributions in intracellular tissues is lacking, thus limiting the further development of a mechanism-based phytoremediation strategy to improve treatment efficiency.

Results

Pyrene exhibited higher uptake and was more recalcitrant to metabolism in ryegrass roots than was phenanthrene. The kinetic processes of uptake from ryegrass culture medium revealed that these two PAHs were first adsorbed onto root cell walls, and they then penetrated cell membranes and were distributed in intracellular organelle fractions. At the beginning of uptake (< 50 h), adsorption to cell walls dominated the subcellular partitioning of the PAHs. After 96 h of uptake, the subcellular partition of PAHs approached a stable state in the plant water system, with the proportion of PAH distributed in subcellular fractions being controlled by the lipid contents of each component. Phenanthrene and pyrene primarily accumulated in plant root cell walls and organelles, with about 45% of PAHs in each of these two fractions, and the remainder was retained in the dissolved fraction of the cells. Because of its higher lipophilicity, pyrene displayed greater accumulation factors in subcellular walls and organelle fractions than did phenanthrene.

Conclusions

Transpiration and the lipid content of root cell fractions are the main drivers of the subcellular partition of PAHs in roots. Initially, PAHs adsorb to plant cell walls, and they then gradually diffuse into subcellular fractions of tissues. The lipid content of intracellular components determines the accumulation of lipophilic compounds, and the diffusion rate is related to the concentration gradient established between cell walls and cell organelles. Our results offer insights into the transport mechanisms of PAHs in ryegrass roots and their diffusion in root cells.     

抑制剂和安全剂对高羊茅根中酶活性和菲代谢的影响

以高羊茅(Festuca arundinacea)为供试植物,利用水培体系研究了抑制剂和安全剂对植物根中过氧化物酶(POD)和多酚氧化酶(PPO)活性以及菲代谢的影响。供试安全剂为浓度0.3%的NaCl,抑制剂为浓度2.00 mg/L的Vc。结果表明,2.00 mg/L的Vc作用下,1—16d,高羊茅根的菲含量显著高于对照处理,而供试安全剂对植物根中菲含量的影响不显著。抑制剂作用下植物根部的PPO和POD活性显著降低;16d,抑制剂作用下的植物根部PPO和POD活性为对照组的1/6和1/9,表现出强抑制效应。而安全剂作用下植物根部PPO和POD活性则略高于对照组,但差异不显著（P＜0.05）。植物体内酶的初始活性是影响植物代谢PAHs菲的关键因素。抑制剂主要通过调节酶活性来影响根系代谢菲,其对植物根中PPO和POD活性的抑制效率与根部菲代谢抑制效率显著正相关。     

REDUCTION IN SOIL POLYCYCLIC AROMATIC HYDROCARBONS BY ARBUSCULAR MYCORRHIZAL LEEK PLANTS

The effect of arbuscular mycorrhizal fungi (AMF) on the reduction of soil polycyclic aromatic hydrocarbon (PAH), nutrient uptake, and growth of leek (Allium porrum L. cv. Musselburgh) plants was studied under greenhouse conditions. This experiment was a 3 × 2 × 2 × 4 factorial design including three mycorrhizal treatments (non-AMF, Glomus intraradices, and G. versiforme strains), two microorganism statuses (with and without soil bacteria), two PAH chemicals (anthracene and phenanthrene), and four PAH concentrations (three concentrations added and one control). Leek growth was reduced significantly in soils spiked with anthracene or phenanthrene. Inoculation with either Glomus intraradices or G. versiforme not only increased N and P uptake and plant growth, but also enhanced PAH disappearance in soil. After 12 weeks of potcultures, the anthracene and phenanthrene concentrations in soils were decreased as compared to their initial level, 9%–31% versus 43%–88%, respectively. Reductions in concentration were larger for phenanthrene than anthracene. The addition of a soil microorganism (SM) extract in potcultures accelerated the disappearance of PAHs. The decrease of PAHs in soil was mainly attributed to the enhanced nutrient uptake by AMF, leading to improved plant growth, which, in turn, may stimulate soil microbial activity. This study shows the interrelationships between AMF, plants, other SMs, and PAH disappearance in soil. The phytoremediation of soil contaminated with PAHs can be accelerated through inoculation with AMF and other SMs.     

Colonization on Root Surface by a Phenanthrene-Degrading Endophytic Bacterium and Its Application for Reducing Plant Phenanthrene Contamination

A phenanthrene-degrading endophytic bacterium, Pn2, was isolated from Alopecurus aequalis Sobol grown in soils contaminated with polycyclic aromatic hydrocarbons (PAHs). Based on morphology, physiological characteristics and the 16S rRNA gene sequence, it was identified as Massilia sp. Strain Pn2 could degrade more than 95% of the phenanthrene (150 mg·L⁻¹) in a minimal salts medium (MSM) within 48 hours at an initial pH of 7.0 and a temperature of 30°C. Pn2 could grow well on the MSM plates with a series of other PAHs, including naphthalene, acenaphthene, anthracene and pyrene, and degrade them to different degrees. Pn2 could also colonize the root surface of ryegrass (Lolium multiflorum Lam), invade its internal root tissues and translocate into the plant shoot. When treated with the endophyte Pn2 under hydroponic growth conditions with 2 mg·L⁻¹ of phenanthrene in the Hoagland solution, the phenanthrene concentrations in ryegrass roots and shoots were reduced by 54% and 57%, respectively, compared with the endophyte-free treatment. Strain Pn2 could be a novel and useful bacterial resource for eliminating plant PAH contamination in polluted environments by degrading the PAHs inside plants. Furthermore, we provide new perspectives on the control of the plant uptake of PAHs via endophytic bacteria.     

Mechanisms of inhibitory effects of polycyclic aromatic hydrocarbons in photosynthetic primary processes in pea leaves and thylakoid preparations

• Inhibitory effects of polycyclic aromatic hydrocarbons (PAHs) on plants were studied in pea leaves in order to elucidate the mechanisms of action of PAHs such as naphthalene (Naph) and phenanthrene (Phen) on activity of photosystem II (PSII).
• The changes in different Chl fluorescence parameters were calculated on the basis of Chl fluorescence induction curves. H₂O₂ content was measured in leaf homogenates with the luminol‐dependent chemiluminescence method.
• We demonstrated that following PAH treatment, total energy dissipation (DI₀/ABS) and amount of Q_B‐non‐reducing complexes of PSII significantly increased. Non‐photochemical quenching (NPQ) also increased, when weak oxidative stress after PAH application developed. In leaves, a two‐step increase in H₂O₂ was found with time of incubation in the presence of PAHs, which may be associated with damage to the lipid bilayer of the plasma membrane and then violation of lipid bilayer membranes of cell organelles.
• A hypothesis for the mode of action of PAHs is provided that involves the role of ROS, membrane permeability and associated functional changes in PSII.

     

Phytoremediation of polycyclic aromatic hydrocarbons (PAH) by cv. Crioula: A Brazilian alfalfa cultivar

This work aimed to evaluate the phytoremediation capacity of the alfalfa cultivar Crioula in soils contaminated with polycyclic aromatic hydrocarbons (PAHs), primary pollutants with mutagenic and carcinogenic potential. Alfalfa was grown from seed for 40 days on soil amended with anthracene, pyrene, and phenanthrene. Soil and plant tissue was collected for biometric assay, dry mass analysis, and PAH analysis by liquid chromatography. Increased total PAH concentration was associated with decreases in plant biomass, height, and internode length. The Crioula cultivar had a satisfactory phytoremediation effect, reducing total PAH concentration (300 ppm) in the experimental soil by 85% in 20 days, and by more than 95% in 40 days. The PAH showed a tendency to be removed in the temporal order: phenanthrene before pyrene before anthracene, and the removal ratio was influenced by the initial soil concentration of each PAH.     

Biochemical and physiological peculiarities of the interactions between <Emphasis Type="Italic">Sinorhizobium meliloti</Emphasis> and <Emphasis Type="Italic">Sorghum bicolor</Emphasis> in the presence of phenanthrene

The effect of phenanthrene, a polycyclic aromatic hydrocarbon (PAH) at concentrations of 0, 10, and 100 mg/kg and the bacterium Sinorhizobium meliloti P221 on root exudation of Sorghum bicolor L. Moench was studied in laboratory vegetative experiments. Inoculation of the bacterium promoted plant resistance to the pollutant stress and increased their acclimation rate and biomass formation. The ability of this microorganism to produce a phytohormone, indolyl-3-acetic acid, and to degrade phenanthrene, resulted in morphological changes of the plant root system and in the changed intensity of root exudation. In root exudates of sorghum, enzyme activities towards the metabolites formed during microbial degradation of PAH were revealed, which is indicative of a direct involvement of plants in PAH degradation in the rhizosphere as well as of the coupled plant-microbial metabolism in the course of xenobiotic degradation in the root zone. In phenanthrene-contaminated soil, sorghum was found to support selectively the development of the S. meliloti P221 population.     

Effect of the polycyclic aromatic hydrocarbon phenanthrene on root exudation of Sorghum bicolor (L.) Moench

The objective of this work was to study the effect of two concentrations (10 and 100 mg kg⁻¹) of phenanthrene, a ubiquitous polycyclic aromatic hydrocarbon (PAH), on root exudation of the remediating plant Sorghum bicolor (L.) Moench under controlled conditions in a pot experiment. It was found that the phenanthrene concentration of 10 mg kg⁻¹ did not cause significant effects on plant survival and growth but had little stimulating effect on carbohydrate exudation. The contamination with phenanthrene at 100 mg kg⁻¹ inhibited accumulation of plant shoot and root biomass, decreasing the carboxylic acid, carbohydrate, and amino acid amounts released by sorghum root into the rhizosphere. However, root exudation per unit of root surface was not changed significantly with increasing phenanthrene concentration. There were no differences in qualitative composition of root exudates under the influence of PAH were found. The observed alterations in the ratio between the main root-exuded components are assumed to manifest adaptive alterations occurring in the plant as a response to pollutant stress. The activity of three oxidoreductases (oxidase, peroxidase, and tyrosinase) released by sorghum roots was clearly progressive to the increasing phenanthrene concentration in the substrate. Under the influence of phenanthrene, the population of phenanthrene-degrading microorganisms in sorghum root zone increased, and their share in the total number of culturable heterotrophs increased as well. The main promotional factor was the pollutant; however, the stimulating effect of the plant root exudates was also involved. The increased pollutant-degrading microbial population and activity of the extracellular root enzymes are presumed to be important for the rhizodegradation of PAH.     

植物对水中菲和芘的吸收

以菲和芘为多环芳烃（PAHs）代表物,采用水培体系研究了黑麦草（Lolium multiflorum Lam）对水中PAHs的吸收作用,重点研究了植物吸收菲和芘的时间动态.水中菲和芘起始浓度分别为1.00mg/L和0.12mg/L.0～288h内,黑麦草根和茎叶中菲和芘含量均先快速增加而后降低,积累量不断增大,植物根系和茎叶富集系数则先快速升高而后趋于稳定.茎叶中菲和芘含量、茎叶对菲和芘的富集系数比根低1～3数量级,积累量也明显小于根系.黑麦草根系对水中芘有更强的富集能力,其根系富集系数比菲大85%～179%;而其茎叶对菲的富集作用则略强.菲和芘在植物体内有明显的传导作用.0～288h,传导系数（TF）先显著升高而后趋于恒定;但实验条件下,菲和芘的TF值均很小,分别不高于0.031和0.009,且芘的TF值明显小于菲,表明供试植物对芘的传导能力更弱.     

Effect of the polycyclic aromatic hydrocarbon phenanthrene on root exudation of Sorghum bicolor (L.) Moench

The objective of this work was to study the effect of two concentrations (10 and 100 mg kg⁻¹) of phenanthrene, a ubiquitous polycyclic aromatic hydrocarbon (PAH), on root exudation of the remediating plant Sorghum bicolor (L.) Moench under controlled conditions in a pot experiment. It was found that the phenanthrene concentration of 10 mg kg⁻¹ did not cause significant effects on plant survival and growth but had little stimulating effect on carbohydrate exudation. The contamination with phenanthrene at 100 mg kg⁻¹ inhibited accumulation of plant shoot and root biomass, decreasing the carboxylic acid, carbohydrate, and amino acid amounts released by sorghum root into the rhizosphere. However, root exudation per unit of root surface was not changed significantly with increasing phenanthrene concentration. There were no differences in qualitative composition of root exudates under the influence of PAH were found. The observed alterations in the ratio between the main root-exuded components are assumed to manifest adaptive alterations occurring in the plant as a response to pollutant stress. The activity of three oxidoreductases (oxidase, peroxidase, and tyrosinase) released by sorghum roots was clearly progressive to the increasing phenanthrene concentration in the substrate. Under the influence of phenanthrene, the population of phenanthrene-degrading microorganisms in sorghum root zone increased, and their share in the total number of culturable heterotrophs increased as well. The main promotional factor was the pollutant; however, the stimulating effect of the plant root exudates was also involved. The increased pollutant-degrading microbial population and activity of the extracellular root enzymes are presumed to be important for the rhizodegradation of PAH.     

Effects of co-occurring aromatic hydrocarbons on degradation of individual polycyclic aromatic hydrocarbons in marine sediment slurries

Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.     

Effects of co-occurring aromatic hydrocarbons on degradation of individual polycyclic aromatic hydrocarbons in marine sediment slurries.

Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.     

Uptake and active efflux of polycyclic aromatic hydrocarbons by Pseudomonas fluorescens LP6a

The mechanism of transport of polycyclic aromatic hydrocarbons (PAHs) by Pseudomonas fluorescens LP6a, a PAH-degrading bacterium, was studied by inhibiting membrane transport and measuring the resulting change in cellular uptake. Three cultures were used: wild-type LP6a which carried a plasmid for PAH degradation, a transposon mutant lacking the first enzyme in the pathway for PAH degradation, and a cured strain without the plasmid. Washed cells were mixed with aqueous solutions of radiolabelled PAH; then the cells were removed by centrifugation, and the concentrations of PAH in the supernatant and the cell pellet were measured. The change in the pellet and supernatant concentrations after inhibitors of membrane transport (azide, cyanide, or carbonyl cyanide m-chlorophenyl hydrazone) were added indicated the role of active transport. The data were consistent with the presence of two conflicting transport mechanisms: uptake by passive diffusion and an energy-driven efflux system to transport PAHs out of the cell. The efflux mechanism was chromosomally encoded. Under the test conditions used, neither uptake nor efflux of phenanthrene by P. fluorescens LP6a was saturated. The efflux mechanism showed selectivity since phenanthrene, anthracene, and fluoranthene were transported out of the cell but naphthalene was not.     

Influence of the carcinogenic pollutant benzo[a]pyrene on plant development: fern gametophytes

Polycyclic aromatic hydrocarbons (PAHs), ubiquitous environmental pollutants, are known to be biologically active in mammalian systems and are accumulated by plants. A few reports suggest that PAHs stimulate growth in plants and induce morphogenesis in plant tissue in culture. To investigate the growth altering abilities of PAHs in plants, polypodiaceous fern gametophytes were grown under sterile conditions on media containing a biologically active PAH, benzo[a]pyrene (BaP), at doses ranging from 0.1 to 10.0 micrograms/ml. The growth pattern of polypodiaceous fern gametophytes enables alterations in growth and morphogenesis to be observed at the cellular level in an intact plant. Doses of BaP in the range 0.1--3.2 micrograms/ml enhanced the onset of the morphological transitions from 1-dimensional (1D) to 2-dimensional (2D) growth. This transition for BaP treated plants occurred after fewer cell divisions than the corresponding solvent and untreated controls. The low (0.1 and 0.32 micrograms) and high (1.0 and 3.2 micrograms) doses of BaP were found to accelerate and inhibit cell proliferation, respectively. The 10.0 microgram dose was toxic and resulted in decreased germination of spores and reduced survival of plants. A slight but significant decrease in survival was also observed in ferns treated with 3.2 micrograms. This is the first example of PAH influencing cell differentiation in a whole plant system.     

Uptake and Active Efflux of Polycyclic Aromatic Hydrocarbons by Pseudomonas fluorescens LP6a

The mechanism of transport of polycyclic aromatic hydrocarbons (PAHs) by Pseudomonas fluorescens LP6a, a PAH-degrading bacterium, was studied by inhibiting membrane transport and measuring the resulting change in cellular uptake. Three cultures were used: wild-type LP6a which carried a plasmid for PAH degradation, a transposon mutant lacking the first enzyme in the pathway for PAH degradation, and a cured strain without the plasmid. Washed cells were mixed with aqueous solutions of radiolabelled PAH; then the cells were removed by centrifugation, and the concentrations of PAH in the supernatant and the cell pellet were measured. The change in the pellet and supernatant concentrations after inhibitors of membrane transport (azide, cyanide, or carbonyl cyanide m-chlorophenyl hydrazone) were added indicated the role of active transport. The data were consistent with the presence of two conflicting transport mechanisms: uptake by passive diffusion and an energy-driven efflux system to transport PAHs out of the cell. The efflux mechanism was chromosomally encoded. Under the test conditions used, neither uptake nor efflux of phenanthrene by P. fluorescens LP6a was saturated. The efflux mechanism showed selectivity since phenanthrene, anthracene, and fluoranthene were transported out of the cell but naphthalene was not.