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Microelements behavior:
Salts vs Chelates

in system with sensitive (oligotrophic) plant species

The behavior of Fe and Mn in a system with the following factors: high oxygen (+400 mV redox), low pH (~5.0), no buffering, CO₂ saturation, and light exposure.

1. Fe/Mn Behavior: Unchelated (FeCl₃, MnSO₄) vs. Chelated (Fe-DTPA, Mn-EDTA)

Unchelated Metals (FeCl₃, MnSO₄): "Naked Ions in a Storm"

  • Fe³⁺ (from FeCl₃):
    • Oxidation/Precipitation: At pH 5.0 + high O₂, Fe³⁺ hydrolyzes instantly:
      Fe³⁺ + 3H₂O → Fe(OH)₃ ↓ + 3H⁺
      • Forms insoluble ferric hydroxide (rust-colored particles).
      • Kinetics: >90% precipitates within minutes to hours at pH 5.0.
    • Plant Availability: <10% remains dissolved. Plants must use inefficient Fe³⁺-reduction mechanisms.
    • Colloidal Radicals: Yes! Partially oxidized Fe forms nanoscale colloids (FeOOH). These generate ROS (Reactive Oxygen Species) via Fenton reactions:
      Fe²⁺ + H₂O₂ → Fe³⁺ + OH• + OH⁻ (toxic hydroxyl radical)
      Analogy: Throwing iron filings into seawater—they rust and sink fast, but some rusty dust (colloids) stays suspended, causing damage.
  • Mn²⁺ (from MnSO₄):
    • Oxidation: Slower than Fe. Mn²⁺ oxidizes to Mn³⁺/Mn⁴⁺, forming MnO₂ (brown-black solids):
      Mn²⁺ + ½O₂ + H₂O → MnO₂ ↓ + 2H⁺
    • Kinetics: At pH 5.0 + high O₂, ~50% precipitates in hours to days.
    • Plant Availability: ~30-50% remains soluble short-term.
    • Toxicity Risk: Low at 50 ppb, but MnO₂ colloids can cause oxidative stress.

Chelated Metals (Fe-DTPA, Mn-EDTA): "Armored Delivery"

  • Fe-DTPA/Mn-EDTA: Chelators act as protective cages, preventing oxidation.
    • Stability in High O₂:
      • Fe-DTPA remains soluble for weeks even at +400 mV.
      • Mn-EDTA is stable but weaker (Mn²⁺ can "escape" slowly).
    • pH Sensitivity:
      • Fe-DTPA stable at pH 5.0–7.0 (ideal for oligotrophic system).
      • Mn-EDTA dissociates below pH 6.0, releasing Mn²⁺.
    • Plant Availability:
      • Plants absorb intact Fe-DTPA/Mn-EDTA via transporters.
      • At pH 5.0, >80% remains available long-term.

2. Kinetic Comparison: "Race Against Time"

FormTime to 50%
Precipitation/Loss
Dominant Forms in Water
FeCl₃Minutes to hoursFe(OH)₃ (solid), FeOOH (colloids)
Fe-DTPAWeeksSoluble Fe³⁺-DTPA complex
MnSO₄Hours to daysMn²⁺ (aq), MnO₂ (solid)
Mn-EDTADays to weeksSoluble Mn²⁺-EDTA, some free Mn²⁺

3. Toxicity & Deficiency Risks

Unchelated Salts

  • Deficiency: Rapid precipitation → plants starve despite dosing.
  • Toxicity: Colloidal Fe/Mn generate ROS, damaging cells (e.g., leaf chlorosis).
    Example: Your 100 ppb FeCl₃ dose may deliver <10 ppb available Fe but generate toxic colloids.

Chelated Forms

  • Deficiency Risk: Low (high stability).
  • Toxicity Risk:
    • Overdosing: Chelated Fe/Mn resist precipitation but can be over-absorbed.
    • ROS from Light: Under PAR light, Fe-DTPA can undergo photoreduction, releasing free Fe²⁺ that fuels Fenton reactions:
      Fe³⁺-DTPA + light → Fe²⁺ + DTPA⁻ (then Fe²⁺ + H₂O₂ → OH•)
      Analogy: Armored truck (chelate) protects cargo, but sunlight can crack the armor, releasing hazardous material.

4. Chelates vs. Salts: Which is Safer for Sensitive (Oligotrophic) Species?

Hyper-accumulation behavior of some [oligotrophic] plant species changes the risk calculus:

FactorUnchelated Salts (FeCl₃/MnSO₄)Chelates (Fe-DTPA/Mn-EDTA)
Bioavailability spikeShort, intense burst (minutes-hours)Sustained low-level release (days-weeks)
Plant responseSudden metal flood → rapid overloadContinuous trickle → gradual accumulation
Toxicity triggerAcute poisoning (necrosis in days)Chronic buildup (toxicity in weeks)
Worst for…Species with fast-responding transportersSpecies lacking excretion mechanisms

Key Mechanisms Driving Toxicity:

  • For salts: Plants detect the brief soluble Fe/Mn spike → activate high-affinity transporters → massive metal influx before precipitation occurs.
    Example: FeCl₃ dosed at 0.1 ppm may deliver 0.08 ppm soluble Fe for 1-2 hours—enough for oligotrophic plants to absorb 2-3 days' worth.
  • For chelates: Slow degradation (pH/light-driven) releases Fe/Mn steadily. Plants absorb metals faster than chelates degrade → sustained uptake.
    Example: Fe-DTPA degrades 5% per day, but plants absorb 10% of available Fe daily → net accumulation.

5. Why Chelates May Be More Dangerous in System with Sensitive (Oligotrophic) Species

  1. Continuous "Appetite Stimulation":
    • Chelated Fe/Mn remain detectable by root sensors → high-affinity transporters stay activated.
    • Salts precipitate → signal dissipation → transporters downregulate.
  2. Colloidal Middlemen:
    • Degraded chelates form FeOOH/MnO₂ colloids that oligotrophic plants efficiently scavenge (via specialized reductases).
  3. Bicarbonate Synergy:
    • HCO₃⁻ displaces chelators → releases metals and forms bioavailable bicarbonate complexes.
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