Aluminium Toxicity and Other Metals
Aluminium Toxicity in Acidic Soils
- Aluminium toxicity is a primary concern in acidic soils.
- Understanding the distribution of aluminium species relative to pH is crucial.
Distribution of Aluminium Species by pH
- At very low pH (acidic conditions), Al^{3+} is the predominant form.
- The proportion of Al^{3+} decreases as pH increases.
- At pH around 4.7, Al^{3+} is approximately 50%.
- At pH 6, Al^{3+} is nearly zero.
- As hydroxyls (OH-) are added, the charge decreases (e.g., from 3+ to 2+ to 1+), shifting the maximum proportion toward higher pH values.
- AlOH^{2+} is maximized around pH 5.
- Al(OH)_2^+ is predominant at pH values higher than 5.5.
- Aluminate ion (AlO_2^−) predominates in alkaline pH.
Toxicity Concerns by Aluminium Species
- In acidic soils, Al^{3+} is the most damaging due to its high proportion.
- AlOH^{2+} also has the potential to cause damage.
- Other forms present at low proportions in acidic conditions are less of a concern.
Impact on Root Growth
- Aluminium toxicity primarily affects root tip growth.
- Healthy roots are typically long and thin, whereas roots affected by aluminium toxicity are short and stubby (coralloid appearance).
- Lateral roots particularly are affected, ceasing growth when exposed to aluminium.
Nutrient Uptake Disturbances
- Aluminium toxicity significantly influences nutrient uptake.
- Calcium uptake decreases substantially with increasing aluminium concentrations.
- Ammonium and potassium uptake are less affected.
- Phosphate uptake may slightly increase.
Effects on Cation Uptake
- Divalent cations (like calcium) are significantly impacted by aluminium toxicity.
- Monovalent cations are less affected.
- Anions (like phosphate) may experience a slight stimulating effect.
Calcium Uptake and Aluminium Toxicity
- Increasing aluminium concentrations lead to a decline in calcium uptake.
- Wheat genotypes (Atlas - resistant, Scout - sensitive) illustrate the difference in response.
Michaelis-Menten Kinetics
- V{max} (Imax) and Km (Kilometers) are used to analyze calcium uptake in the presence of aluminium.
- Resistant genotypes (Atlas) show relatively small changes in V{max} and Km with increasing aluminium.
- Sensitive genotypes (Scout) exhibit a substantial increase in Km with little change in V{max}.
Competitive Inhibition
- The observed changes (increase in Km, little change in V{max}) indicate competitive inhibition.
- Calcium and aluminium compete for the same transporters.
- Increased aluminium concentration depresses calcium uptake.
- Higher calcium concentrations can potentially outcompete aluminium.
Ameliorative Effects of Divalent Cations
- Magnesium and calcium can ameliorate aluminium toxicity.
- Increasing calcium concentrations slightly alleviate the initial hit of aluminium toxicity.
- Magnesium provides more significant improvement in growth under medium stress levels.
- Under severe stress, both calcium and magnesium offer limited help.
Plant Resistance Mechanisms: Tolerance vs. Avoidance
- Two main resistance mechanisms:
- Avoidance: Preventing aluminium uptake.
- Tolerance: Coping with aluminium within plant tissues.
- Avoidance is preferable; tolerance is necessary when avoidance is incomplete.
Tolerance Mechanisms
- Aluminium can be taken up by plants, and some plants are very tolerant.
- Tea plants are highly tolerant, binding aluminium to organic acid anions, rendering it non-toxic.
- Drinking tea results in aluminium ingestion, but it's not a major concern due to the bound form.
Avoidance Mechanisms
- Two primary types:
- Increasing pH in the glycosphere.
- Exuding organic acid anions.
Increasing pH in the Glycosphere
- Raising soil pH shifts the proportion of Al^{3+} to less toxic forms.
Exuding Organic Acid Anions
- Organic acid anions (e.g., citrate, malate, oxalate) bind aluminium, detoxifying it.
- This results in less aluminium uptake.
Root Tip pH
- Maintaining a slightly higher pH at the root tip is crucial for aluminium resistance.
- Atlas maintains a higher pH at the root tip compared to Scout when aluminium is present.
- The difference is small (less than 0.1 pH units).
Citrate Exudation in Maize
- Maize uses citrate exudation for aluminium resistance.
- Without aluminium, there is minimal citrate efflux.
- Under aluminium stress, the resistant genotype significantly increases citrate exudation.
- The sensitive genotype does not effectively increase citrate exudation.
Malate Exudation in Wheat
- Wheat uses malate exudation for aluminium resistance.
- Exogenous malate addition helps sensitive genotypes exposed to aluminium.
- Tolerant genotypes increase malate exudation upon aluminium exposure.
- Resistance has limits; higher aluminium concentrations eventually inhibit even resistant genotypes.
Genetic Transfer and Backcrossing
- Genes for aluminium tolerance from Brazilian wheat varieties were introduced into Australian varieties (e.g., Egret).
- Backcrossing is used to eliminate unwanted genes from the donor while retaining the aluminium tolerance gene.
Malate Content and Exudation
- Malate content varies in different root segments.
- Exudation is highest at the root tip, despite relatively lower malate content there.
Root Growth in Soil and Subsoil
- Sensitive genotypes show limited root growth in acidic subsoil with high exchangeable aluminium, compared to tolerant genotypes.
- Shoot growth differences are secondary, resulting from the primary effect on root growth.
Relationship Between Malate Exudation and Root Growth
- A positive relationship exists between malate exudation and root growth.
- Increased malate efflux leads to higher relative root growth, indicating improved resistance to aluminium toxicity.
Genetic Engineering
- Genes for citrate biosynthesis have been transferred into potatoes.
- Citrate exudation is regulated by external aluminium concentration.
- Response diminishes upon removal of aluminium stress.
Exclusion of Aluminium
- Exclusion of aluminium via organic acid anions is a key resistance mechanism.
- Citrate, malate, and oxalate bind aluminium, rendering it non-toxic.
- Aside from aluminium, other metals and metalloids can be toxic.
- Cadmium is a significant non-nutrient toxic metal.
- Other metals (e.g., manganese, iron, copper, zinc, molybdenum) are micronutrients but can be toxic at high concentrations.
- Arsenic and selenium are metalloids, with arsenic being a common toxicant.
- Plants employ various mechanisms to deal with metal toxicity.
- Root avoidance of contaminated areas.
- Exudation of organic acid anions and amino acids.
- Cell wall binding.
- Compartmentalization in roots and vacuoles.
- Enzyme resistance and metal tolerance.
- Hyperaccumulators are plants that accumulate very high concentrations of toxic metals (at least 10 grams per kilo or 1%).
Advantages of Hyperaccumulation
- Potential defense against herbivory due to unpalatability.
Examples of Hyperaccumulators
- Many plants in the Brassicaceae family (e.g., Alyssum) hyperaccumulate nickel.
- Concentrations can be extremely high (e.g., 40% nickel in tissue).
Characteristics of Hyperaccumulators
- Often found in Mediterranean regions.
- Amino acids like histidine play a role in complexing metals like nickel and zinc.
Extreme Examples
- Some trees accumulate over 25% nickel in their sap.
Phytomining
- Hyperaccumulators can be used to extract metals from the soil.
- Commercial viability is still limited.