Redistribution of boron in leaves reduces boron toxicity

High soil boron (B) concentrations lead to the accumulation of B in leaves, causing the development of necrotic regions in leaf tips and margins, gradually extending back along the leaf. Plants vary considerably in their tolerance to B toxicity, and it was recently discovered that one of the tolerance mechanisms involved extrusion of B from the root. Expression of a gene encoding a root B efflux transporter was shown to be much higher in tolerant cultivars. In our current research we have shown that the same gene is also upregulated in leaves. However, unlike in the root, the increased activity of the B efflux transporter in the leaves cannot reduce the tissue B concentration. Instead, we have shown that in tolerant cultivars, these transporters redistribute B from the intracellular phase where it is toxic, into the apoplast which is much less sensitive to B. These results provide an explanation of why different cultivars with the same leaf B concentrations can show markedly different toxicity symptoms. We have also shown that rain can remove a large proportion of leaf B, leading to significant improvements of growth of both leaves and roots.Key words: Bor genes, boron tolerance, boron toxicity, efflux pumping, leaf necrosis, membrane transportB-toxic soils are widespread throughout agricultural areas of the world where they cause significant and often substantial reductions in crop quality and yield. The mechanism by which B is toxic to plants is not well understood¹ but toxicity symptoms include reduced root growth which affects uptake of water and nutrients, and the development of necrotic patches on leaves which impairs photosynthesis. Tolerance to B toxicity has been recognized in a number of crops, notably in cereals. In most cases, tolerance is achieved by reduced uptake of B into the root, which then leads to reduced uptake into the shoot. Genetic studies established that in barley, a locus associated with reduced tissue B occurred on chromosome 4 and that this locus could be transferred to other barley cultivars with desirable agronomic traits.²Hayes and Reid³ made a careful study of the characteristics of B uptake in a highly tolerant landrace barley cultivar Sahara, and found that although B was highly permeable, the root B concentration in this cultivar could be maintained at only half that in the external medium, whereas in sensitive cultivars, B was the same in both intracellular and extracellular phases. It was concluded that tolerant cultivars must have a membrane active transporter that exports B from the root. A B exporter, AtBor1 had previously been discovered in Arabidopsis where it was involved in B loading into the xylem⁴ but it was later found to be degraded under high B conditions⁵ and therefore would not be useful in B tolerance.However, other Bor1 homologues were subsequently discovered in Arabidopsis and in rice. Based on homology with rice, Reid⁶ cloned genes from barley and from wheat (HvBor2 and Tabor2 respectively) which were shown to be strongly upregulated in roots of tolerant cultivars, and virtually undetectable in sensitive cultivars. Thus, a simple mechanism to explain tolerance was established; efflux of B from the root reduced the intracellular concentration of B in the root cells, thereby reducing toxicity and improving root growth. At the same time, the lower root content meant that less B was transferred to the shoot, resulting in lower shoot toxicity.Yet there remained several unanswered questions regarding B toxicity. Firstly, it was commonly observed that toxicity symptoms were not reliably correlated with leaf B concentration, and that often after rain, toxicity symptoms became less severe. Nable et al.⁷ had investigated the effect of rain on shoot B concentrations and concluded that although rain did reduce the B concentration in leaves, it did not affect growth and yield. Secondly, field trials with cultivars in which the B tolerance traits were expressed, did not show the improvements in growth and yield that could be observed in glasshouse trials.^8,9Our recent work¹⁰ has provided new insights into these phenomena. Sensitive and tolerant cultivars of both wheat and barley were grown in varying levels of B. Then, ignoring the level of B in the growth solution, leaves of the different cultivars that displayed the same degree of leaf necrosis were selected. This revealed that in the tolerant cultivars, necrosis began to appear at leaf B levels that were two-to five-fold higher than in sensitive cultivars. Since no internal tolerance mechanism had been reported, it was hypothesised that in the tolerant cultivars, internal toxicity was reduced by pumping B from the cytoplasm into the cell wall where B is much less toxic. To prove this hypothesis three types of experiment were conducted. Firstly protoplasts were isolated from leaves of tolerant and sensitive cultivars of barley, and it was shown that when incubated in the same concentration of B, the tolerant cultivar was able to reduce the intracellular B concentration to approximately half that of the sensitive cultivar. Secondly, it was reasoned that if more B was accumulated in the apoplast of the tolerant cultivar, then it should be more quickly released by washing of the leaf; this was confirmed. Thirdly, it was shown that the same efflux transporters that were responsible for B export from the root were also highly expressed in leaves of tolerant cultivars of wheat and barley. The combination of these three experiments provided compelling evidence that redistribution of B in the leaf was a significant factor in B tolerance.The elution experiment also highlighted the fact that because B is highly soluble and has high membrane permeability, it can easily be washed from leaves. Obviously in the field B could be removed from leaves by rain, but no positive effect of this on growth had been quantified. In our experiments, we simulated the average rainfall during the early growing season in a high B region of Southern Australia by spraying plants with calibrated amounts of water for 16 d. At high B concentrations, rain reduced leaf B by around 50% while simultaneously improving growth of shoots by up to 90%. Rather surprisingly, the rain treatment, which had no significant effect on root B concentrations, caused a two-fold increase in root growth, presumably by improving the supply of photosynthate from the shoot.This study has enabled an evaluation of the importance of three main factors in determining the severity of B toxicity; two genetically determined processes, efflux pumping of B in roots and leaves, coupled with the variable leaching of B from leaves by rain (Fig. 1). The results also provide an explanation for the poor correlations observed between toxicity and shoot B concentrations in cereals.^7,11Open in a separate windowFigure 1Summary of processes contributing to reduced B toxicity in wheat and barley. The intensity of shading indicates the level of B in different regions of the plant. Boron (B) enters the leaf via the xylem and continues to accumulate as the leaf grows. When plants are grown in high concentrations of B, the older parts of the leaf become necrotic first while the younger basal tissues continue to expand. In tolerant cultivars, B efflux transporters in leaves pump B from the cytoplasm where it is toxic into the cell walls where it can be tolerated at high concentrations. Sensitive cultivars have a very low capacity for B efflux and therefore retain much higher concentrations inside the cell than in tolerant cultivars. rain can remove large amounts of B from leaves, thereby alleviating toxicity. In roots of tolerant cultivars, the same B efflux transporters that occur in leaves are used to pump B from the cells into the external medium. This reduces the toxicity to roots and limits the amount of B entering the xylem and reaching the leaves.     

The Nonessentiality of Glycine and the Essentiality of L-Proline in the Chick Nutrition

2-Methylpiperazino[1, 2-a]indole-6, 9-diones were synthesized as the analogues of mitomycin antibiotics. The compounds prepared from 2-carbethoxy-5-methoxyindole showed antibacterial activities.     

A critical analysis of the causes of boron toxicity in plants

This study investigated the main factors contributing to boron toxicity in plants. Growth was rapidly inhibited by internal B concentrations in the range 1–5 m m across a range of plant types that included monocot, dicot and algal species. In contrast, mature cells were able to withstand up to 60 m m B for several days. In wheat, rapid inhibition of root growth occurred if high B was applied to the root tip, but not if high B was applied to mature sections of the root. In leaves, there were gradations in B concentrations that correlated with visible symptoms of toxicity. However, there was no evidence to support the hypothesis that toxicity in leaves is due to osmotic stress induced by the accumulation of B. Analysis of the sensitivity to B of a range of metabolic processes including photosynthesis, respiration and protein synthesis leads to the conclusion that growth is not restricted by effects of B on energy supply and not directly by inhibition of protein synthesis. At higher B concentrations, many cellular activities were found to be partially inhibited and the toxicity to mature tissues was therefore considered not to arise from the disruption of a single process, but from the accumulated retardation of many cellular processes, exacerbated in light by photo‐oxidative stress.     

Effects of boron toxicity on root and leaf anatomy in two Citrus species differing in boron tolerance

Key message

Typical toxic symptom only occurred in B-toxic C. grandis leaves. B-toxicity induced PCD of C. grandis leaf phloem tissue. The lower leaf free B might contribute to the higher B-tolerance of C. sinensis.

Abstract

Seedlings of ‘Xuegan’ (Citrus sinensis) and ‘Sour pummelo’ (Citrus grandis) differing in boron (B)-tolerance were irrigated with nutrient solution containing 10 (control) or 400 (B-toxic) μM H₃BO₃ for 15 weeks. Thereafter, the effects of B-toxicity on leaf photosynthesis, chlorophyll, plant B absorption and distribution, root and leaf anatomy were investigated to elucidate the possible B-tolerant mechanisms of Citrus plants. Typical toxic symptom only occurred in B-toxic C. grandis leaves. Similarly, B-toxicity only affected C. grandis photosynthesis and chlorophyll. Although total B concentration in B-toxic roots and leaves was similar between the two species, leaves from B-toxic C. grandis plant middle had higher free B and lower bound B as compared with those from C. sinensis. Effects of B-toxicity on leaf structure were mainly limited to the mesophyll cells and the phloem of leaf veins. Although irregular cell wall thickening was observed in leaf cortex cells and phloem tissue of B-toxic C. grandis and C. sinensis leaves, exocytosis only occurred in the companion cells and the parenchyma cells of B-toxic C. sinensis leaf phloem. Also, B-toxicity induced cell death of phloem tissue through autophagy in C. grandis leaf veins. B-toxicity caused death of root epidermal cells of the two Citrus species. B-toxicity restrained degradation of middle lamella, but did not alter ultrastructure of Golgi apparatus and mitochondria in root elongating zone cells. In conclusion, C. sinensis was more tolerant to B-toxicity than C. grandis. The lower leaf free B and higher bound B might contribute to the higher B-tolerance of C. sinensis.     

An investigation of boron toxicity in barley using metabolomics

Boron (B) is an essential micronutrient that affects plant growth at either deficient or toxic concentrations in soil. The aim of this work was to investigate the adaptation of barley (Hordeum vulgare) plants to toxic B levels and to increase our understanding of B toxicity tolerance mechanisms. We used a metabolomics approach to compare metabolite profiles in root and leaf tissues of an intolerant, commercial cultivar (cv Clipper) and a B-tolerant Algerian landrace (cv Sahara). After exposure to elevated B (200 and 1,000 microM), the number and amplitude of metabolite changes in roots was greater in Clipper than in Sahara. In contrast, leaf metabolites of both cultivars only responded following 1,000 microM treatment, at which B toxicity symptoms (necrosis) were visible. In addition, metabolite levels were dramatically altered in the tips of leaves of the sensitive cultivar Clipper after growth in 1,000 microM B compared to those of Sahara. This correlates with a gradual accumulation of B from leaf base to tip in B-intolerant cultivars. Overall, there were always greater differences between tissue types (roots and leaves) than between the two cultivars. This work has provided insights into metabolic differences of two genetically distinct barley cultivars and information about how they respond metabolically to increasing B levels.     

A relationship between toxicity and chemical nature

The maximum allowable concentration of any chemical substance can be estimated with some degree of confidence solely on the basis of the chemical groups and structure it contains. The derivation of this methodology from the U. S. Dept. of Labor Occupational Health and Environmental Control Air Contaminants List (1972) is described.     

Taxonomy and morphology of dematiaceous fungi isolated from nature

The Hughes system of classification was applied to the identification of dematiaceous fungi isolated from nature. The majority of the isolates encountered could be identified with this system using brightfield microscopy. However, phase contrast microscopy was needed to determine the mode of conidial ontogeny with some species of Phialophora, Exophiala and Wangiella. The identifications based upon phase contrast microscopy were confirmed using the scanning electron microscope (SEM). Scanning electron photomicrographs are presented for Bispora betulina, Cladosporium trichoides, Exophiala jeanselmei, Phialophora revens, P. verrucosa and Wangiella dermatitidis. SEM observations of W. dermatitidis support the present classification of this organism as proposed by other workers. It is suggested that the Hughes system of classification and phase contrast microscopy be used to facilitate identification of isolates of dematiaceous fungi encountered in the clinical laboratory.     

Effect of boron on the expression of aluminium toxicity in Phaseolus vulgaris

The interaction of boron (B) and aluminium (Al) was investigated in 5-day-old seedlings of soybean cv. Maple Arrow. Al treatment inhibited root elongation and callose formation in root tips particularly after 4-h Al treatment. After 10 and 24 h, both parameters indicated increasing recovery from Al stress. B deficiency aggravated Al toxicity compared with B sufficiency. B deficiency did lead to an increase in unmethylated pectin in the first 3 mm of the root tip. This increase in potential binding sites is reflected in generally higher Al contents in root tips of B-deficient plants. A fractionated extraction of Al from the root tips showed that citrate-exchangeable and non-exchangeable Al steeply increased up to 4 h, but then decreased after 10- and 24-h Al treatment faster in B-sufficient than in B-deficient plants. This decrease of Al contents can be explained by an Al-enhanced release of citrate from the root tips after 10-h Al treatment. However, the citrate exudation rate was the same (after 10 h) or even lower (after 24 h) in B-sufficient plants and thus cannot explain the faster decrease in Al contents of the root tips compared with the B-deficient plants. We, therefore, propose that under B deficiency, Al is more strongly bound by the pectic network of the cell wall of the root tips, which delays or prevents the recovery from initial Al stress through exudation of citrate, and thus explains the greater Al sensitivity of B-deficient common bean roots.     

Jasmonic acid alleviates boron toxicity in Puccinellia tenuiflora,a promising species for boron phytoremediation

Plant and Soil - Although elevated [CO2] causes an increase of photosynthesis in the short-term, this increase is often attenuated over time due to decreased photosynthetic capacity of the leaf in...     

Incidence and nature of testicular toxicity findings in pharmaceutical development

BACKGROUND : Testicular toxicity (TT) is a sporadic and challenging issue in pharmaceutical drug development. Efforts to develop TT screening assays or biomarkers have been overshadowed by consortium efforts to predict drug‐induced toxicities such as hepatic injury, which are encountered more frequently. METHODS : To gauge the current state of the field and to prioritize future TT activities, the International Life Sciences Institute‐Health and Environmental Sciences Institute Developmental and Reproductive Toxicology (DART) Technical Committee sponsored a survey to better understand the incidence and nature of TT findings encountered during drug development. RESULTS : Highlights from the 16 survey respondents include: (1) Although preclinical TT was encountered relatively infrequently, half of the participants observed repeated problems with TT during pharmaceutical development, (2) despite control measures such as use of sexually mature animals to diminish confounding effects of spurious lesions, interpretation of TT remains a challenge, (3) “traditional” evaluation tools such as hormonal monitoring and newer approaches such as ‐omics are utilized to investigate testicular changes, and (4) an understanding of the risk and relevance of TT findings is achieved through joint consideration of factors such as species specificity, potential mode of action, and safety margins. CONCLUSIONS : TT remains a relatively uncommon but persistent challenge in pharmaceutical development. Although current preclinical TT approaches appear to be effective in limiting the occurrence of pharmaceutical candidate attrition in clinical trials, improved biomarker or screening platforms would allow companies to identify TT at an earlier stage, thus decreasing the time and resources expended on safety evaluation of pharmaceutical candidates. Birth Defects Res (Part B) 92: 511–525, 2011. © 2011 Wiley Periodicals, Inc.     

Response of nitrogen metabolism to boron toxicity in tomato plants

Boron (B) toxicity has become important in areas close to the Mediterranean Sea where intensive agriculture has been developed. The objective of this research was to study the effects of B toxicity (0.5 m m and 2.0 m m B) on nitrogen (N) assimilation of two tomato cultivars that are often used in these areas. Leaf biomass, relative leaf growth rate (RGR_L), concentration of B, nitrate (NO₃⁻), ammonium (NH₄⁺), organic N, amino acids and soluble proteins, as well as nitrate reductase (NR), nitrite reductase (NiR), glutamine synthase (GS), glutamate synthetase (GOGAT) and glutamate dehydrogenase (GDH) activities were analysed in leaves. Boron toxicity significantly decreased leaf biomass, RGR_L, organic N, soluble proteins, and NR and NiR activities. The lowest NO₃⁻ and NH₄⁺ concentration in leaves was recorded when plants were supplied with 2.0 m m B in the root medium. Total B, amino acids, activities of GS, GOGAT and GDH increased under B toxicity. Data from the present study prove that B toxicity causes inhibition of NO₃⁻ reduction and increases NH₄⁺ assimilation in tomato plants.     

Symbiotic germination and development of myco-heterotrophic plants in nature: ontogeny of Corallorhiza trifida and characterization of its mycorrhizal fungi

The processes of symbiotic germination and seedling development were analysed in the myco-heterotrophic orchid Corallorhiza trifida , seeds of which were buried in 'packets' either adjacent to or at varying distances from adult plants in defined communities of ectomycorrhizal tree species. Germination occurred within eight months of burial under Betula – Alnus and within seven months under Salix repens . It was always associated with penetration of the suspensor by a clamp-forming mycorrhizal fungus. Four distinct developmental stages were defined and the rates of transition through these stages were plotted. There was no evidence of a relationship between extent of germination or rate of development and the presence of naturally distributed plants of C. trifida at the spatial scale of 1 m. The best germination and the most rapid rate of development of C. trifida seedlings occurred in a Salix repens community located at a considerable distance from any extant C. trifida population. Determination of internal transcribed spacer (ITS) RFLPs and of gene sequences of the fungi involved in symbiotic germination and growth of C. trifida , revealed them to belong exclusively to the Thelephora – Tomentella complex of the Thelephoraceae. These fungi are known also to be ectomycorrhizal associates of trees. It is hypothesized that the rate of growth of the C. trifida seedlings is determined by the ability of the fungal symbionts to transfer carbon from their ectomycorrhizal co-associates.     

Identification of boron transporter genes likely to be responsible for tolerance to boron toxicity in wheat and barley

Tolerance to boron (B) toxicity in cereals is known to be associated with reduced tissue accumulation of B. Genes from roots of B-tolerant cultivars of wheat and barley with high similarities to previously reported B efflux transporters from Arabidopsis and rice were cloned. Expression of these genes was strongly correlated with the ability of tolerant genotypes to lower the concentration of B in roots. The gene from barley located to chromosome 4. Backcross lines containing a B tolerance locus on chromosome 4 showed tolerance in proportion to the level of expression of the transporter gene, whereas those lacking the locus were sensitive to B and had very low levels of gene expression. The results are consistent with a widespread mechanism of tolerance to high B based on efflux of B from root cells.     

Reproductive toxicity in boron exposed workers in Bandirma, Turkey

Boric acid and sodium borates have been considered as being “toxic to reproduction and development”, following results of animal studies with high doses. However unfavorable effects of boron exposure on reproduction and development have not been proved in epidemiological studies so far. The aim of the present study was to investigate the reproductive toxicity indicators in highly exposed workers employed in a boric acid production plant in Band?rma, Turkey. Two hundred and four workers participated in this study. The mean blood boron concentration of the high exposure group of workers was 223.89 ± 69.49 (152.82–454.02) ng/g. Unfavorable effects of boron exposure on the reproductive toxicity indicators were not observed.     

The nature of anaerobic fungi and their polysaccharide degrading enzymes

Conclusion The discovery of anaerobic fungi has added a new member to the indigenous microorganisms that inhabit the rumen ecosystem. Anaerobic fungi do not appear essential for the survival of ruminants due to their presence in very low numbers, and sometimes absence, in ruminants fed low fiber diets, but their presence may likely be very important in the digestion of fibrous diets. The anaerobic fungi have adapted well to the rumen environment. They are able to ferment a large array of soluble carbohydrates and can synthesize cellular components in an anaerobic environment. The fungi posses hydrogenosomes for the removal of reducing equivalents in the form of molecular hydrogen and the removal of trace oxygen is a accomplished via removal by NADH oxidase. Their positive synergistic interaction with methanogenic bacteria eludes to their highly evolved role in the rumen environment. The fungi also produce resistant sporangia that allows for transfer of species to a new host in an oxygen environment. The anaerobic fungi posses a highly active array of polysaccharide degrading enzymes that may provide an advantage in the highly competitive rumen ecosystem. The production of specific enzymes that hydrolyze the lignocellulosic fraction of plant walls is unique in rumen microorganisms and allows for their attachment and growth on fibrous plant particles that are not available to the rumen bacteria.     

Antioxidant responses of chickpea plants subjected to boron toxicity

This study investigated oxidative stress and the antioxidant response to boron (B) of chickpea cultivars differing in their tolerance to drought. Three‐week‐old chickpea seedlings were subjected to 0.05 (control), 1.6 or 6.4 mm B in the form of boric acid (H₃BO₃) for 7 days. At the end of the treatment period, shoot length, dry weight, chlorophyll fluorescence, B concentration, malondialdehyte content and the antioxidant enzymes superoxide dismutase (SOD), peroxidase (POX), catalase (CAT), ascorbate peroxidase (APX) and glutathione reductase (GR) were measured. The 1.6 mm B treatment did not cause significant changes in shoot length of cultivars, although shoot length increased in the drought‐tolerant Gökce and decreased in the drought‐sensitive Küsmen after 6.4 mm B treatment. Dry weights of both cultivars decreased with 6.4 mm B treatment. Chlorophyll fluorescence (Fv/Fm) did not change in Gökce at either B level. Nor did it change in Küsmen with 1.6 mm B but Fv/Fm decreased with 6.4 mm B. Boron concentration in the shoots of both cultivars increased significantly with increasing levels of applied B. Significant increases in total SOD activity were observed in shoots of both cultivars given 1.6 and 6.4 mm B. Shoot extracts exhibited five activity bands, two of which were identified as MnSOD and Cu/ZnSOD. In comparison to the control group, all enzyme activities (except APX and SOD) decreased with 1.6 mm B stress. GR activity decreased, while activities of CAT, POX and APX did not change with 6.4 mm B in Küsmen. On the other hand, activities of CAT, APX and SOD increased in Gökce at both B levels. In addition, lipid peroxidation was higher in Küsmen than in Gökce, indicating more damage by B to membrane lipids in the former cultivar. These results suggest that (i) Gökce is tolerant and Küsmen is sensitive to B, and (ii) B tolerance of Gökce might be closely related to increased capacity of the antioxidative system (total SOD, CAT and APX) to scavenge reactive oxygen species and thus suppress lipid peroxidation under B stress. To the best of our knowledge, this is the first report on the antioxidant response of chickpea seedlings to B toxicity.     

Abiotic factors affecting the toxicity of lead to fungi.

The toxicity of lead (Pb) to fungi in pure culture was influenced by several abiotic factors: pH, inorganic anions, clay minerals, and particulate (humic acid) and soluble organic matter. The toxicity of Pb was potentiated under acidic conditions (pH 5 and 6), and phosphate or carbonate anions reduced the toxicity, apparently as a result of the formation of sparingly soluble Pb salts. Clay minerals (montmorillonite greater than attapulgite greater than kaolinite) and particulate humic acid protected against the toxicity of Pb, presumably as the result of sorption, by cation exchange of the Pb to the exchange complexes, which reduced its availability for uptake by the fungi. Soluble organics, such as tryptone, yeast extract, cysteine, succinic acid, and increasing concentrations of neopeptone, also reduced the toxicity of Pb.     

Abiotic factors affecting the toxicity of lead to fungi.

The toxicity of lead (Pb) to fungi in pure culture was influenced by several abiotic factors: pH, inorganic anions, clay minerals, and particulate (humic acid) and soluble organic matter. The toxicity of Pb was potentiated under acidic conditions (pH 5 and 6), and phosphate or carbonate anions reduced the toxicity, apparently as a result of the formation of sparingly soluble Pb salts. Clay minerals (montmorillonite greater than attapulgite greater than kaolinite) and particulate humic acid protected against the toxicity of Pb, presumably as the result of sorption, by cation exchange of the Pb to the exchange complexes, which reduced its availability for uptake by the fungi. Soluble organics, such as tryptone, yeast extract, cysteine, succinic acid, and increasing concentrations of neopeptone, also reduced the toxicity of Pb.