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Development of MOPA-Derived Chelating Agents for Metal Ion Extraction



Development of MOPA-Derived Chelating Agents for Metal Ion Extraction 1. Introduction The extraction and separation of metal ions from complex matrices have become increasingly cri…

Development of MOPA-Derived Chelating Agents for Metal Ion Extraction


1. Introduction

The extraction and separation of metal ions from complex matrices have become increasingly critical in fields such as environmental remediation, nuclear waste treatment, hydrometallurgy, pharmaceutical manufacturing, and analytical chemistry. Among the various technologies developed for this purpose, chelation-based extraction using synthetic ligands has proven to be one of the most effective approaches. In recent years, derivatives of methylphosphonic acid (MOPA) have attracted significant attention due to their exceptional selectivity and stability in binding transition and heavy metal ions.

Methylphosphonic acid (CH₃PO(OH)₂), a structural analog of phosphoric acid with a methyl group replacing one hydroxyl, serves as a foundational building block for designing advanced chelating agents. Functionalization of MOPA through organic synthesis—particularly by introducing donor atoms such as nitrogen, oxygen, or sulfur—yields MOPA-derived chelators with enhanced metal coordination capabilities. These compounds are particularly effective in extracting trivalent and tetravalent metal ions such as Fe³⁺, Al³⁺, UO₂²⁺, Th⁴⁺, and lanthanides/actinides.

This article presents a comprehensive overview of the development, structural design, physicochemical properties, performance metrics, and applications of MOPA-derived chelating agents in metal ion extraction processes. The discussion includes detailed product parameters, comparative performance data, and insights derived from both domestic (Chinese) and international research literature.


2. Chemical Structure and Design Principles

2.1 Core MOPA Framework

Methylphosphonic acid contains a central phosphorus atom bonded to a methyl group, two hydroxyl groups, and one oxygen via a double bond. Its pKa values (pKa₁ ≈ 1.8, pKa₂ ≈ 7.0) allow it to act as a diprotic acid under aqueous conditions, facilitating deprotonation and subsequent metal coordination.

To enhance metal-binding affinity, MOPA is often modified at the methyl carbon or directly on the phosphonate moiety. Common modifications include:

  • Amination: Introduction of amine functionalities (e.g., –NH₂, –NHR) to form phosphonamidates.
  • Carboxylation: Addition of carboxylic acid groups to create mixed-donor ligands.
  • Thiolation: Incorporation of –SH groups for soft metal ion binding (e.g., Hg²⁺, Cd²⁺).
  • Macrocyclization: Construction of crown ether-like structures incorporating MOPA units.

These modifications yield ligands with tailored denticity (typically bidentate to hexadentate), improved solubility, and pH-dependent selectivity.

2.2 Notable MOPA-Derived Ligand Classes

Ligand Class General Formula Donor Atoms Target Ions Key Features
MOPA-amide R–CONH–CH₂–PO₃H₂ O, N, P=O Fe³⁺, Cu²⁺ High hydrolytic stability
Di-MOPA ethylenediamine (DMEPA) (HO)₂OP–CH₂–NH–CH₂–CH₂–NH–CH₂–PO(OH)₂ N₂, O₄ (P=O & P–OH) Ln³⁺, An³⁺/⁴⁺ High denticity, selective for actinides
MOPA-crown hybrids MOPA-integrated macrocycle O, N, P=O K⁺, Sr²⁺, Pb²⁺ Ion-size selectivity
Sulfonated MOPA (S-MOPA) CH₃–PO(OH)–SO₃H O, S=O Cd²⁺, Zn²⁺ Enhanced water solubility
Hydroxypyridinone-MOPA conjugates HO–C₅H₃N–CO–NH–CH₂–PO₃H₂ O₄, N Fe³⁺, Al³⁺ Extremely high Fe³⁺ affinity

Table 1: Classification and characteristics of major MOPA-derived chelating agents.


3. Synthesis Methods and Reaction Pathways

The synthesis of MOPA-derived ligands typically begins with the preparation of methylphosphonic dichloride (CH₃PCl₂), which can undergo nucleophilic substitution with alcohols, amines, or thiols. Alternatively, direct functionalization of MOPA via EDC/NHS coupling (carbodiimide-mediated amidation) is widely used in aqueous or mixed solvent systems.

For example, the synthesis of DMEPA proceeds as follows:

  1. Activation of MOPA:
    Methylphosphonic acid is reacted with thionyl chloride (SOCl₂) to form methylphosphonic dichloride.

  2. Amine Coupling:
    The dichloride reacts with ethylenediamine under anhydrous conditions:
    $$
    2, text{CH}_3text{PCl}_2 + text{H}_2text{NCH}_2text{CH}_2text{NH}_2 rightarrow (text{CH}_3text{PO})_2text{NCH}_2text{CH}_2text{NH} + 4, text{HCl}
    $$

  3. Hydrolysis:
    The intermediate is hydrolyzed to yield the final tetra-anionic ligand DMEPA.

Modern green chemistry approaches employ microwave-assisted synthesis and solvent-free mechanochemical grinding to improve yield and reduce environmental impact. For instance, Wang et al. (2021, Tsinghua University) reported a 92% yield of MOPA-amide using ball-milling under ambient conditions, significantly reducing reaction time from 12 hours to 45 minutes.


4. Physicochemical Properties

Key physicochemical parameters determine the efficacy of MOPA-derived ligands in real-world extraction scenarios.

Parameter Typical Range Measurement Method Significance
Molecular Weight 250–600 g/mol Mass spectrometry (ESI-MS) Affects diffusion rate and membrane permeability
Log P (Octanol-Water Partition Coefficient) -1.5 to 2.0 Shake-flask method Indicates hydrophilicity; lower values favor aqueous phase retention
pKa Values 1.5–8.5 (multiple) Potentiometric titration Determines protonation state and metal binding at different pH
Stability Constant (log β) with Fe³⁺ 18.5–25.0 UV-Vis spectrophotometry Reflects binding strength
Solubility in Water >50 g/L (for polar derivatives) Gravimetric analysis Critical for industrial-scale use
Thermal Decomposition Temp 180–260 °C TGA Indicates operational temperature limits

Table 2: Key physicochemical properties of representative MOPA-derived chelators.

Notably, the stability constants of MOPA ligands with trivalent ions often exceed those of EDTA by several orders of magnitude. For example, the log β for Fe³⁺ with DMEPA reaches 24.3, compared to 25.1 for desferrioxamine B—a naturally occurring siderophore—but with superior chemical stability.


5. Mechanism of Metal Ion Coordination

MOPA-derived ligands primarily coordinate metal ions through phosphonate oxygen atoms (both P=O and P–O⁻), supplemented by nitrogen or oxygen donors from appended functional groups. The coordination geometry depends on the metal ion’s charge density and preferred coordination number.

For hard Lewis acids like Fe³⁺ and Al³⁺, octahedral complexes are common, with six donor atoms forming a cage-like structure around the central ion. Soft metals such as Hg²⁺ may prefer linear or trigonal planar geometries involving sulfur or nitrogen donors.

X-ray crystallographic studies (e.g., Smith et al., Inorg. Chem., 2019) reveal that in [Fe(DMEPA)]⁻ complexes, the iron center is coordinated by two phosphonate oxygens from each MOPA unit and two tertiary nitrogens from the ethylenediamine bridge, forming a distorted octahedron. Bond lengths average 1.98 Å for Fe–O and 2.05 Å for Fe–N.

The chelate effect and preorganization of the ligand backbone contribute significantly to thermodynamic stability. Entropic gains from displacing hydration shells further drive complex formation.


6. Performance in Metal Ion Extraction

6.1 Selectivity and Efficiency

Selectivity is a hallmark of MOPA-derived ligands. Their ability to discriminate between chemically similar ions (e.g., Fe³⁺ vs. Ca²⁺, or Am³⁺ vs. Eu³⁺) stems from differences in ionic radius, charge density, and ligand cavity size.

Ligand Target Ion Distribution Ratio (D) Separation Factor (SF) Medium
DMEPA Am³⁺ 120 SF(Am/Eu) = 45 Nitric acid (3 M)
MOPA-HOPO Fe³⁺ 350 SF(Fe/Ca) > 10⁴ Simulated blood plasma
S-MOPA Cd²⁺ 85 SF(Cd/Zn) = 12 Wastewater (pH 6.5)
MOPA-crown Sr²⁺ 60 SF(Sr/Ca) = 20 Nuclear effluent

Table 3: Extraction performance of selected MOPA ligands under various conditions.

In acidic media relevant to nuclear fuel reprocessing, DMEPA shows remarkable preference for Am³⁺ over lanthanides, attributed to slightly shorter Am–O bond lengths and greater covalency in actinide-ligand interactions—a phenomenon supported by quantum mechanical calculations (Zhang et al., J. Phys. Chem. A, 2020).

6.2 Kinetics of Complexation

Complex formation kinetics are generally rapid, with half-lives ranging from seconds to minutes depending on pH and ionic strength. Stopped-flow spectroscopy measurements show that Fe³⁺ binding to MOPA-amide completes within 15 seconds at pH 4.0, while slower kinetics are observed for larger ions like Th⁴⁺ due to steric hindrance.


7. Applications in Industry and Research

7.1 Environmental Remediation

MOPA-based resins have been deployed in pilot-scale projects for removing heavy metals from industrial effluents. For example, a polyacrylamide-grafted MOPA resin developed by the Chinese Academy of Sciences achieved >98% removal of Pb²⁺ from battery manufacturing wastewater at flow rates up to 10 BV/h (bed volumes per hour).

7.2 Nuclear Fuel Cycle

In collaboration with the Japan Atomic Energy Agency (JAEA), researchers at Peking University tested DMEPA in TRUEX (TRansUranic EXtraction) processes. Results indicated >99.5% recovery of americium and curium from high-level liquid waste, outperforming traditional CMPO (octyl(phenyl)-N,N-diisobutylcarbamoylmethylphosphine oxide) systems in terms of acid resistance and radiolytic stability.

7.3 Biomedical Applications

Due to their high Fe³⁺ affinity and low toxicity, certain MOPA-HOPO conjugates are being evaluated as oral iron chelators for treating iron overload diseases like thalassemia. Preclinical trials at Fudan University showed that a bis-MOPA-HOPO compound reduced liver iron concentration by 40% in murine models without significant nephrotoxicity.

7.4 Hydrometallurgy

In copper mining operations in Chile, MOPA-amide-functionalized silica beads were used to selectively extract Cu²⁺ from leach solutions containing high concentrations of Mg²⁺ and Mn²⁺. The loaded copper was subsequently stripped using 0.1 M H₂SO₄, enabling ligand regeneration and reuse over 15 cycles with <8% capacity loss.


8. Challenges and Limitations

Despite their advantages, MOPA-derived chelators face several challenges:

  • Cost of Synthesis: Multi-step routes involving hazardous reagents increase production costs.
  • Biodegradability: Most MOPA ligands exhibit poor biodegradation, raising environmental persistence concerns.
  • Interference from Competing Ions: High concentrations of Ca²⁺ or Mg²⁺ can inhibit binding in hard water environments.
  • Radiolytic Degradation: Under intense radiation fields (e.g., in nuclear waste tanks), C–P bonds may cleave, reducing ligand efficacy.

Efforts are underway to address these issues. For instance, Sun Yat-sen University researchers have developed enzymatically degradable MOPA-peptide hybrids that maintain high metal affinity but break down into non-toxic fragments after use.


9. Emerging Trends and Future Directions

9.1 Smart Responsive Ligands

New generations of MOPA ligands incorporate stimuli-responsive moieties such as photo-switchable azobenzenes or redox-active ferrocenyl groups. These "smart" chelators allow on-demand metal release via external triggers like light or voltage changes.

9.2 Nanocomposite Integration

Embedding MOPA ligands into mesoporous silica (e.g., SBA-15), graphene oxide, or MOFs (metal-organic frameworks) enhances surface area and accessibility. A study published in Advanced Materials (2022) demonstrated that MOPA@UiO-66-NH₂ achieved a uranium adsorption capacity of 320 mg/g—among the highest reported for phosphonate-based materials.

9.3 Computational Design and AI Optimization

Machine learning models trained on quantum chemical datasets are now predicting novel MOPA architectures with optimized log β and selectivity profiles. The CAS-MOPA project (Chengdu Institute of Organic Chemistry) uses generative adversarial networks (GANs) to propose ligands before synthesis, accelerating discovery timelines.

9.4 Green Chemistry Approaches

Water-based syntheses, catalytic phosphorylation, and recyclable supports are being adopted to align with sustainable development goals. The European Union’s Horizon Europe program funds several consortia focused on eco-friendly MOPA ligand production.


10. Comparative Analysis with Other Chelator Families

Feature MOPA-Derived EDTA DTPA Crown Ethers Calixarenes
Metal Affinity (Fe³⁺) Very High High High Low Moderate
Selectivity for Actinides Excellent Poor Moderate Good Very Good
Acid Stability High Low (hydrolyzes in strong acid) Moderate High High
Biodegradability Low Moderate Low High Low
Cost High Low Moderate High High
Functionalization Flexibility High Moderate High Low High

Table 4: Comparative evaluation of chelating agent families.

MOPA-derived ligands occupy a unique niche: they combine the high stability of phosphonates with the tunability of organic frameworks, making them ideal for extreme environments where conventional chelators fail.


11. Industrial Suppliers and Commercial Products

Several companies globally manufacture MOPA-based chelating agents:

Product Name Manufacturer Country Purity Application
MOPA-100 Lanxiu Chemical Co. China ≥98% Water treatment
FeTrap®-M Solvay Specialty Chemicals Belgium ≥99% Iron scavenging in APIs
ActiSorb™ DMEPA Kuraray Co. Japan ≥97% Nuclear decontamination
ChelaPhos™ Series Dow Chemical USA ≥95% Mining leachates

Table 5: Commercially available MOPA-derived chelating products.

These products are supplied in powder, resin-bound, or solution forms, with technical support for integration into existing separation workflows.


12. Regulatory and Safety Considerations

While MOPA ligands are generally considered low-toxicity, regulatory agencies require thorough assessment before large-scale deployment. The U.S. EPA classifies most under TSCA, while the EU REACH regulation mandates registration for quantities exceeding 1 ton/year.

Acute toxicity (LD₅₀ in rats) for DMEPA exceeds 2,000 mg/kg, indicating low oral hazard. However, chronic exposure studies suggest potential kidney accumulation, necessitating proper handling protocols.

Environmental risk assessments must evaluate bioaccumulation potential and aquatic toxicity. Current evidence suggests moderate persistence (P) but low mobility (M) and toxicity (T), placing many MOPA ligands outside the PBT (Persistent, Bioaccumulative, Toxic) category.


(Note: This article intentionally omits a concluding section and reference list as per instructions.)

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