Laura
Norfolk
*a,
Klaudia
Kapusta
a,
David
Cooke
b and
Sarah
Staniland
a
aDepartment of Chemistry, The University of Sheffield, Dainton Building, Brook Hill, Sheffield, S3 7HF, UK. E-mail: s.s.staniland@sheffield.ac.uk
bDepartment of Chemical Sciences, The University of Huddersfield, Huddersfield, HD1 3DH, UK
First published on 24th June 2021
Magnetite nanoparticles play a key role in the nano-industry, with crucial importance in the developing nanomedicine sector. Such particles must be homogeneous, with a consistent shape and size, due to the growing need to tailor particles to more defined faceted morphologies. Here an ethylenediamine series (H2N-(–CH2CH2N–)nH2, n = 2 (DETA), 3 (TETA), 4 (TEPA), and 5 (PEHA)), of additives have been successfully used to control the morphology of nanomagnetite produced via a green ambient co-precipitation method. Whilst DETA showed less control, TETA, TEPA and PEHA mediated the near universal synthesis of faceted particles (91–97%) suggesting a near pure octahedral population (compared to only 6% of control particles). The particle size was ≈ 22 nm for all the samples and was not affected by the addition of additives. Computational molecular dynamic modelling shows the binding to the octahedral [111] face to be preferred for all additives with binding to the [100] face unfavourable for TETA, TEPA and PEHA, showing a preference to bind and direct an octahedral morphology for these 3 additives. This is further explained by the increased numbers of interactions of the longer additives with the [111] surface through O and Fe in the magnetite surface bonding to H and N in the additive which is better able to lie flat on the [111] surface. An optimum concentration of a 1:
125 additive
:
iron ion ratio was determined which shows that a relatively small quantity of a cheap, organic bioinspired amine-rich additive can have a massive impact on the morphological quality of the magnetite nanoparticles. This powerful, additive-directed, green synthesis approach could be universally applied to a vast range of nanomaterial syntheses to great impact.
For any application, control over the size, shape, composition, mono-dispersity and reproducibility is beneficial, but it is critical with MNPs for nanomedicine, with the ability to precisely tune the particles to specific requirements – a much sought-after feature of production. Monodispersity is key to ensure uniform, consistent and predicable magnetic properties, anatomical uptake, anatomical distribution and therapeutic dosing/effects.
Control over the size is essential (1) to understand the surface area and thus dosing levels; (2) to direct the anatomical location (as different sized MNPs concentrate in different parts of the body); and (3) to tune the magnetic response, with smaller MNPs exhibiting superparamagnetism with profound effects on hyperthermic heating.10
Control over the shape also varies the properties of the nanomedicine. Due to particle nuclei formation requiring a low surface area to volume ratio, the smallest MNPs will be spherical. While being highly dependent on the reaction conditions, as the MNP grows, magnetite's low index crystal faces (γ[111] < γ[100] < γ[110]) tend to be favoured in the final crystal form.11 As such, a typical equilibrium morphology is cubo-octahedral (a truncated cube which appears spherical) incorporating a reduced surface area and the most stable [111] and [100] facets.12 However, more faceted (non-spherical) MNPs have been shown to offer the most promise across a range of nanomedicines. For example, cubic nanoparticles have been found to be preferable for contrast agents compared to spherical particles (with similar volumes),13,14 while angular “nanoflower” shaped MNPs have been found to have higher hyperthermic heating compared to spherical MNPs.15,16 This is thought to be due to the physical effect of the points and edges.15,16 As such, the demand for non-spherical faceted MNPs in the biomedical industry is on the rise with synthetic control over the size, shape, and crystal quality of particles being crucial.
Whilst many syntheses exist to carefully tailor the morphology (shape and size) of MNPs, most of these techniques require environmentally unsustainable reaction conditions, increasing the negative environmental impact of the syntheses. The manufacture of cubic or nanoflower MNPs currently requires high temperature,17,18 alongside a range of organic reagents, or microwaves,19 while octahedral MNPs require an elevated temperature to allow the kinetically favoured [111] facet to dominate.20 These synthetic routes are not green, demonstrating a general problem with inorganic nanomaterial synthesis: precisely faceted nanomaterial production requires highly wasteful and less environmentally friendly synthesis.
Magnetite can be easily synthesized on a large scale using a room-temperature co-precipitation (RTCP) reaction (Fig. 1a). The addition of a base such as NaOH, KOH, or Et4NOH to an aqueous solution of ferric and ferrous iron under an inert atmosphere at room temperature produces iron oxides without the use of toxic solvents/reagents.21 This is a fast and straightforward green synthesis, with no use of high energy processes such as heating or vacuum pressure allowing for large volumes of particles to be produced. The disadvantage of this green synthesis is that there is very little control over the final product, with a broad size distribution (5–40 nm) of an undefined/pseudo-spherical shape with little opportunity to tailor the morphology.
Within the green chemistry remit (ambient conditions), some control can be offered by changing the reaction conditions, using such systems as micro-22 and milli-fluidic flow synthesis23 or pH-regulated synthesis;24 however, these methods are not currently scalable to large-scale production and offer less control over the particle shape.
The use of additives in a green RTCP is an established method to offer control over nanoparticle synthesis.25 Grafted co-polymer additives have been used to control the size of magnetite MNPs26 while there are many examples of green/natural additives being used such as unrefined seaweed27 and plant leaf extracts in the synthesis of MNPs,28–30 as well as citrate,31 oxalic acid32 and chitosan.33 Green additives such as fruit juice and sea buckthorn have also been used to control the size of gold34 and silver35,36 nanoparticles. However, all these examples produce spherical particles or particles of undefined morphology. Clearly, shape is more difficult to control with additive synthesis, with the green synthesis of tailored faceted MNPs offering a greater challenge.
Highly uniform, morphologically controlled MNPs are observed in nature, for example within magnetotactic bacteria. These unique bacteria foster the ability to precisely control the synthesis of MNPs using magnetosome membrane specific (Mms) biomineralisation proteins such as Mms637–41 and MmsF.42 This has translated to the successful use of several Mms proteins as biological additives to mediate the formation of enhanced MNPs in simple RTCP syntheses. Purified Mms6, MmsF and an MmsF protein mimic60 have been used in vitro to control particle formation in RTCP reactions, with increased control over the size (Mms6) and morphology (MmsF) and magnetite mineral purity (both) compared to protein free reactions.38,39,41,42,60
Recently, by screening an (Adhiron) affimer protein phage-display library against cubic [100] magnetite (labelled MIA (Magnetite Interacting Adhiron)), we identified a protein additive that specifically directs the formation of cubic MNPs. The resulting MIAs were found to contain high levels of basic residues, particularly lysine.43 Molecular dynamics simulations showed the amino acid lysine to have the lowest adsorption energy to the magnetite [100] surface through amine interactions with the surface.43 Adsorption of MIA additives to the magnetite [100] surface of a developing crystal results in stabilizing and propagating that surface allowing it to dominant the final (cubic) particle structure. This was seen in RTCP reactions where cubic MNPs were formed when mediated by an MIA protein additive, a morphology previously only accessible using organic solvents and high-temperature methods. From this work, we saw that the amine rich additive controlled the MNP morphology through adsorption to the magnetite surface.43
Whilst complex proteins are green additives capable of specific crystal face binding to control morphology, they are very expensive to produce compared to the other additives cited above. For example, a commonly used arginine based synthetic protein costs £49 per mg,44 with more bespoke and membrane proteins costing multiple times more. In this study, we take a systematic approach to understand morphology controlling protein additives and use this to develop cheaper bioinspired additives to mediate the RTCP of faceted MNPs.
We identify the importance of amine groups for interacting with magnetite surfaces to control their morphology. In this study, we screen an ethylenediamine series (amines linked with aliphatic CH2CH2 spacers of various lengths) as bioinspired additives for RTCP of faceted MNPs. Ethylenediamines are small, simple and cheap additives for a green RTCP synthesis that pose a more realistic commercially viable proposition for scale-up and green manufacture at a millionth of the cost of a protein additive (tetraethylenepentamine is £55.30 per kg (ref. 45)), demonstrating that this method could be used for the green production of magnetite on an industrially viable scale.
If the nanomaterial industries, particularly biomedical, are to continue to expand and precisely faceted MNPs are required on a larger scale, it is critical to develop synthetic methods that offer substantial reductions in energy usage and manufacturing carbon footprint whilst still offering precise control over the nanomaterial properties. Here we demonstrate that ethylenediamine additives in green RTCP have the ability to control morphology with the precision of proteins at a fraction of the cost.
TGA was performed on these dry particles between 20 and 800 °C at a heating rate of 10 °C per minute under a 2/3 N2 and 1/3 O2 atmosphere.
The structures of the ethylenediamine molecules were generated using the AMBERTOOLS package TLEAP, and magnetite slabs terminating with the (100) and (111) surfaces perpendicular to the x-axis and approximately 25 Å thick were generated from the pre-relaxed (1 ns of MD simulation at 300 K using the NPT ensemble) bulk structure using the METADISE code.32 pH was incorporated into the modelling by considering several charged examples of each ethylenediamine molecule and using published pKa values (Hazardous Substances Data Bank) a weighted average could be determined to reflect the results in the chosen conditions.
Except for the initial relaxation of the bulk structure, the MD simulations were performed using the canonical, NVT, ensemble at 300 K, employing the Nose Hoover thermostat with a relaxation time of 0.5 ps. The trajectories were generated using the Verlet leapfrog algorithm58 using a time step of 1.0 fs. The long-range coulombic interactions were calculated using the Ewald summation,59 and the short-range inter- and intramolecular interactions were described using the potential parameters discussed above. Each production run was performed for 5 ns, during which all the atoms within the system were free to relax. The energetics of the system were recorded every 0.1 ps, and the coordinates were written to the general trajectory file every 1 ps. To better scan the configuration space, 42 simulations were run for each molecule on each surface, where the orientation and position of the molecule at the start of the simulation differed. Thus, the results reported represent statistics collected over 210 ns of MD simulation.
We have screened a full ethylenediamine series of H2N-(–CH2CH2N–)nH2 (with n = 2, diethylenetriamine (DETA); 3, triethylenetetramine (TETA); 4, tetraethylenepentamine (TEPA); and 5, pentaethylenehexamine (PEHA)) (Fig. 2b–e) to assess their effectiveness in controlling the morphology of MNPs compared to additive-free control. These additives were selected due to their relatively low cost, the only factor varied in these reactions was the additive used. The amount of additive used per reaction was relative to the number of amine groups present, i.e. twice the amount of DETA was used relative to PEHA to maintain 0.08 mmol of active amine groups. As the reaction contained 1 mmol of iron ions, the ratio of functional groups:
iron ions was thus 1
:
12.5. As such, the final ratios of additive
:
iron ions varied depending on the additive used: DETA (1
:
37.5), TETA (1
:
50), TEPA (1
:
62.5), PEHA (1
:
75).
Fig. 2a–e shows representative TEM images of the nanoparticles formed (ESI Fig. S3† for larger TEM images). From visual inspection, it is clear the additives have had a profound effect on particle morphology. The control particles (Fig. 2a) were found to be consistent with previous magnetite MNPs from the literature formed via an RTCP route (mean size 22.2 nm, standard deviation (6.5 nm)).60 The sizes of MNPs from TEM analysis (Fig. 2a–e) and crystallite sizing calculated with the Scherrer equation from the full width maximum of the XRD pattern are in agreement and are shown in Table 1. The addition of the amine additives does not have a significant effect on the MNP/crystallite size and the size distributions are similar for all the reactions with only TETA appearing minimally smaller in size (Fig. 2f, (ESI Fig. S4† for individual histograms)), suggesting that the amine additives do not affect the MNP size.
Sample | Particle size TEM (nm) | Crystallite size XRD (nm) | % Faceted particles |
---|---|---|---|
Control | 22.2 ± 6.5 | 20.4 | 6 |
DETA | 22.6 ± 6.1 | 19.3 | 42 |
TETA | 18.4 ± 5.0 | 17.5 | 96 |
TEPA | 23.3 ± 7.2 | 17.5 | 97 |
PEHA | 22.9 ± 7.0 | 18.4 | 91 |
The XRD patterns (Fig. 2g) of MNPs synthesised with additives are consistent with magnetite being the major crystalline component of each sample (semi-quantitative analysis suggests >80% for all samples). Minor contaminants of other iron oxides (wüstite hematite and maghemite) are present. The control sample contains all 3 contaminants, while small quantities of maghemite and hematite (estimated < 6%) are seen in the reactions mediated by the longer chain PEHA and TEPA additives, and wüstite (estimated < 20%) is seen in the reactions mediated by the short chain DETA and TETA additives. The TEPA mediated sample was found to contain the purest magnetite.
From the analysis of TEM images, the particle shape was assigned (Fig. 2h and 3). Remarkably, the addition of all the ethylenediamine additive resulted in an increased formation of faceted particles (diamond, square, hexagonal). The methodology by which a particle's shape is assigned is demonstrated in Fig. 3 (also see Methods and ESI S2†). It should be noted that TEM images are 2D projections of 3D shapes and as such there can be an overlap and error in the assignment (e.g. octahedra commonly project a diamond shape in 2D but can also project hexagonal and square shapes if viewed at a different angle.41 Similarly, cubes commonly look square but can project a hexagon). The populations here show a particular dominance of the octahedral morphology, with mainly diamonds with some square and hexagons. Faceted particles are clearly distinguishable from undefined particles.
A control reaction produced 6% faceted particles, increasing to 42% on addition of DETA, the shortest amine additive tested. The proportion of faceted particles increased with the additive length up to TEPA, with TETA and TEPA producing 96% and 97% of particles with a defined morphology respectively. As the additive chain length increased further for PEHA, 91% of faceted particles were formed. All three TETA, TEPA, and PEHA show highly significant quantities of faceted MNPs with each mediating the production of >60% of diamond particles, assigned to an octahedral morphology. The octahedral nature of these assigned particles was confirmed by the lattice fringe measurement of HRTEM images (Fig. 4). The d-spacing of 4.8 Å is indicative of a [111] octahedral plane, confirming a predominantly octahedral morphology in the TEPA additive mediated particle population.
![]() | ||
Fig. 4 (a) Selected area electron diffraction of octahedra assigned particles from the TEPA mediated MNP sample, (b) HRTEM of octahedral particles, (c) lattice fringe measurements. |
Eads = Eslab+molecule − (Eslab + Emolecule) |
With the exception of DETA, we find the adsorption is endothermic at the [100] surface and exothermic at the [111] surface (Fig. 5), showing a definite preference for the interaction with the [111] face over the [100] face for these molecules. After this quantity has been normalised, to take into to account the varying number of amine groups in the molecule and the overall charge on the molecule, we find that that adsorption at the [111] surface is favoured by 100–140 kJ mol−1 per unit charge per amine group. There is no significant difference between the calculated values for TETA, TEPA and PEHA but the difference is greater at pH 7 than at pH 8 (Fig. 5).
![]() | ||
Fig. 5 Calculated changes in the surface energy due to the adsorption polyamine chains of varying lengths. Solid lines at pH 7 and dotted lines at pH 8. |
The surface energy, after adsorption (γads), is defined as the difference in energy per unit area between a magnetite slab with an adsorbed molecule and the sum of a bulk system containing the same number of Fe3O4 formula units as the slab and an isolated molecule:
γads = [Eslab+molecule − (Ebulk + Emolecule)]/A |
As a Wulff construction62 assumes that a crystal will arrange itself such that its surface Gibbs free energy is minimized by assuming a shape of low surface energy the reduction in the energy of a particular surface at the expense of another will be directly related to the observed morphology of the resulting particles. This is shown in Fig. 5 and clearly illustrates that the adsorption of the TETA, TEPA or PEHA molecule leads to a small stabilisation of the [111] surface, whereas adsorption destabilises the [100] surface with the effect increasing with chain length and goes some way to explaining the results shown in Fig. 2h, where octahedral particles are the most abundant when TETA, TEPA and PEHA are present. Note there is negligible difference for both adsorption energies to each magnetite surface and thus less preference for octahedral particles when DETA is present.
The nature of the adsorption, and hence the difference in the calculated surface energies can be understood by considering the nature of the bonding at the surface. This is simply achieved by considering the radial distribution functions (RDF) between the iron and oxygen in the magnetite and the nitrogen and hydrogen atoms in the amine groups. Fig. 6 shows this data for a system at pH 8. The sharp peak at ∼1.8 Å in Fig. 6a and c indicates that strong hydrogen bonds form between surface oxygen and the hydrogens in the amine groups for both [100] and [111] surfaces.
As would be expected, the peaks are sharpest for the shortest molecules as there fewer degrees of freedom available during the adsorption and thus the range of bond lengths explored will be smaller. More interesting, and also explaining why the adsorption is stronger at the [111] surface, is the lack of an Fe–N bonding peak at 2 Å in Fig. 6d, which is present in Fig. 6b, illustrating that at the [111] surface both adsorption modes are present, whereas only hydrogen bonding is present at the [100] surface. The link of increased binding with increased binding modes is further demonstrated by the fact the adsorption peak for the Fe–N bonding at [111] is missing only for DETA (Fig. 6b) and DETA shows no difference in surface energy absorption (Fig. 5).
Integrating the first peak of the RDF gives the average number of bonds formed between the adsorbed molecule and the surface.63 As would be expected, the number of bonds increases with chain length however, more importantly, the number of bonds is significantly greater for the [111] surface than that for [100]. This implies that the longer molecules are better able to lie flat on the [111] surface, forming a stronger interaction with the surface and reducing the surface energy at the [111] surface. Fig. 7 shows PEHA is able to lie flat on the [111] surface (Fig. 7b), which is not the case for the [100] surface (Fig. 7a). Fig. 7b shows additional interactions between surface Fe and the amine groups and N to surface O interactions. However, the data appear to be independent of both chain length and pH for the [111] surface, whereas increasing chain length and reducing pH have a detrimental effect on the [100] surface energy (Fig. 6 and 7).
![]() | ||
Fig. 7 Atomistic simulations of TEPA interacting with a magnetite surface (a) [100] and (b) with the [111] surface. |
To further probe the nature of the adsorption, two angular order parameters were defined that describe the orientation of the molecule on the surface.64 The first is the acute angle formed by a vector, parallel to the surface and a vector connecting the two terminal amine groups and second, the acute angle formed by the vector, parallel to the surface and a vector joining a terminal amine with the centre of mass of the molecule. The results are shown in Table 2.
End to end | End to centre | |
---|---|---|
[100] | ||
DETA | 4 (1.8) | 28 (4.1) |
TETA | 20 (26.8) | 38 (10.8) |
TEPA | 24 (24.8) | 20 (17.8) |
PEHA | 45 (32) | 29 (29.7) |
[111] | ||
DETA | 15 (18.5) | 30 (25.3) |
TETA | 16 (15.3) | 30 (28.4) |
TEPA | 14 (15) | 29 (29.4) |
PEHA | 15 (15.1) | 29 (30.7) |
The end–end angle increases steadily with chain length, when considering adsorption at the [100] surface, whereas it remains approximately constant (∼15°) when considering adsorption at the [111] surface. With the exception of DETA the angle is always greater for the [100] surface. This, together with variance in the end to centre parameter shows that the molecules are more mobile on the [100] surface, whereas they adsorbed strongly to the [111] surface and remain flat, i.e. parallel to surface, further suggesting the molecules’ role in promoting the growth of the [111] surface.
TEM images (Fig. 8a–d) show particles of various sizes and morphologically defined populations (larger images available in ESI Fig. S5†). Fig. 8e and Table 3 (and ESI Fig. S6†) demonstrates that size and size distribution remained consistent at the lower concentrations between the 1:
1250–1
:
12.5 ratios. At the 1
:
1.25 ratio, there is a significant shift in the profile with respect to both the size and morphology of the particles formed. The mean size of the particles increases from ∼22 nm for lower concentrations to 49.4 nm, and the standard deviation increasing from 6.0 to 19.6.
Sample TEPA![]() ![]() |
Particle size TEM (nm) | Crystallite size XRD (nm) | % Faceted particles (total) | |||
---|---|---|---|---|---|---|
Diamond | Hexagonal | Square | Rod | |||
1![]() ![]() |
21.1 ± 6.0 | 23.0 | 37 | |||
28 | 5 | 5 | — | |||
1![]() ![]() |
23.5 ± 6.0 | 24.0 | 81 | |||
71 | 3 | 7 | — | |||
1![]() ![]() |
22.7 ± 6.0 | 26.2 | 35 | |||
24 | 7 | 3 | 1 | |||
1![]() ![]() |
49.4 ± 19.6 | 23.0 | 28 | |||
13 | 1 | 2 | 12 |
The shape profile (Fig. 8g) shows the particle morphology of the 1:
1.25 sample to be the poorest too, with 72% of undefined shape (Table 3). It is interesting there are almost equal quantities of diamond and elongated rods (12%) in this poorer 1
:
1.125 sample, showing that high quantities of the additive have a detrimental effect on both the size and morphology. Rod shaped particles are typically associated with the iron oxide goethite, however the XRD (Fig. 8f) shows that for each sample magnetite is the main crystalline product, with only a small quantity of goethite impurity in all samples. In fact, the XRD data remained consistent between all the samples, suggesting the difference in particle morphology is not the result of different iron oxides species being present.
The ratio 1:
125 was found to produce the most consistently faceted particles, with 81% of the particles formed being faceted with >70% being octahedral (Table 3). The ratios above and below, (1
:
1250 and 1
:
12.5 respectively) display a similar size and shape profile to each other. 1
:
125 TEPA
:
Fe ratio showing the best shape control is consistent with the previous additive screening results. The initial screening used a concentration of 1
:
62.5 (twice the concentration of 1
:
125, and between 1
:
125 and 1
:
12.5 values). It is interesting to note that the optimum proportion of faceted particles is actually achieved in the initial screening, but this concentration study achieves a more morphologically consistent diamond-shaped population.
To better understand if and when TEPA is binding to the forming particles, FT-IR spectroscopy was performed at a range of pH from 4.5 to 12.8 (ESI Fig. S6†). The magnetite particles give a strong Fe–O peak at 542 cm−1 (and a minor one at 691 cm−1). The signal from an amine organic coating (bending frequencies occurring between 1220 and 1747 cm−1) is the most predominant in pH 7.4 and pH 9 samples while only a negligible signal is seen in the extreme pH values of 4.5 and 12.8. This suggests TEPA binds only after the particle has nucleated (above pH 4.5), thus to the surface as opposed to iron ions. Above pH 12, TEPA is exclusively neutral with no –NH3+ or –NH2–+ groups for electrostatic interaction, suggesting the TEPA completely disassociates from the particles at above pH 12. TGA (ESI Fig. S6†) suggests the presence of TEPA as an organic coating at pH7.
EDA is an inexpensive, simple, amine compound and has previously been used as well as DETA as a structure-directing agent (in non-green synthetic conditions).67,68 The addition of EDA based additives of all lengths tested (amine groups = 3–6, DETA–PEHA) had an influence on the morphology of the particles, with an increased percentage of faceted particles being observed from DETA to TETA, with TETA to PEHA showing close to pure faceted particles (optimum found at TEPA). Particle size remained consistent (∼18–23 nm) between samples synthesised with no additive and the samples produced with all additives, suggesting the additive does not play a role in nucleating the MNPs. This is to be expected as mineral nucleation is usually facilitated by acidic proteins in biomineralisation (containing multiple aspartic and glutamic acid) providing sites for metal ion binding.21 An additive that affects nucleation will generally influence the mineral type and/or the particle size, neither of which is seen here. Instead the amine molecules exclusively act to control morphology, preferentially adsorbing to and stabilising the [111] face to direct the growth of [111] faceted octahedral particles. This is consistent with what is currently understood in the literature and from our modelling studies.29
Production of octahedral MNPs via a green additive synthesis is a very important advance for biomedicine. Such faceted particles are very desirable for both therapeutics and diagnostic nanomedicine, while cheap sustainable manufacture will increase accessibility leading to more widespread uses. While it is clear the EDA series of additives primarily acts to direct the morphology of the growing crystal, in doing so the amine chains bind to the surface. This has a secondary feature of forming an organic coating. This helps to stabilise and increase the dispersion of the MNPs in solution. The amine additives could thus be modified to also functionalise the particles if desired, giving the additive a dual purpose. However, the additive does not bind at extreme pH, so can be easily removed with base by continuing the titration if desired.
It is clear from the additive screening that TETA, TEPA and PEHA produce the majority octahedral particles (while DETA is less effective). Computational simulation studies explain why the ethylenediamine series directs the morphology towards octahedral particles. The modelling demonstrates a clear preferential binding to the [111] face over the [100]. Despite the identical functional groups, additive performance is affected by their length, with the shortest DETA showing only a minor effect. While TETA, TEPA, and PEHA are comparable, there is a slight reduction in performance from PEHA, the longest amine molecule. From the modelling data we see DETA shows no preference for [111] or [100] and this explains why it had the least influence over particle morphology.
Modelling also shows the energies of absorption for binding are similar for TETA, TEPA and PEHA for both the [111] and [100] magnetite surfaces. This seems to be driven by a mixture of the positive effect of chelation coupled with the negative effect of entropy for long molecules which may explain the slight fall off for PEHA. The adsorption at the [111] surface is favoured by TETA, TEPA and PEHA because the arrangement of the ions on the surface enables the molecule to adsorb flat and form, not only hydrogen bonds between the magnetite surface oxygen and hydrogens on the amine groups, but also strong interactions between surface iron and nitrogen groups in the amine. Whereas only hydrogen bonding is able to occur at the [100] surface and to a lesser extent to that predicted at the [111] surface. It should be noted that the energy changes required to favour one surface over the other can be small, thus subtle changes in the form of the additive molecule result in a substantial effect to the MNP morphology. For example, it is noteworthy that the ethylenediamine series was inspired by the basic amino acid rich morphology controlling protein, with a particularly high quantity of lysine. The lysine rich peptide loop directed magnetite MNP morphology towards cubic particles, showing a preference to the [100] face. It is interesting that because these seemingly similar molecules (differ by a carboxylate group) bind differently to the magnetite [111] and [100] surfaces, a dramatically different morphological outcome is achieved. This is something that, carefully designed, computer modelling can probe as the techniques are able to directly compare adsorption at different surfaces and consider a variety of adsorption modes.
From varying the concentration of TEPA by factors of 10, a rough ideal concentration was ascertained as ∼1:
125. This is in line with the results seen for the screening which used a 1
:
62.5 ratio. At 1
:
1250 and 1
:
12.5, similar degrees of morphological control were exerted over the MNP formed, despite the difference in conditions. This may be because below the ideal concentration there may be too little of the additive for surface coverage to have a substantial effect on particle formation, and at high concentrations the reaction conditions such as pH may be altered by the additive, effectively polluting the reaction environment. This seems to be the case at near 1
:
1 additive to iron concentrations. This study was conceived to translate a green bioinspired approach to scale-up. A chief concern with scale is cost. This study demonstrates a vastly cheaper additive compared to protein alternatives and the concentration study reveals that very small quantities of this cheap additive (1
:
125) are the optimum, which is a very positive news for scale-up.
DETA | Diethylenetriamine |
EDA | Ethylenediamine |
FCC | Face-centred cubic |
FTIR | Fourier-transform infrared spectroscopy |
FWHM | Full width half maximum |
HRTEM | High resolution transmission electron microscopy |
MIA | Magnetite interacting adhiron |
Mms | Magnetosome membrane specific |
MNP | Magnetic nanoparticle |
MRI | Magnetic resonance imaging |
NaOH | Sodium hydroxide |
PEHA | Pentaethylenehexamine |
RDF | Radial distribution functions |
RTCP | Room temperature co-precipitation |
TEM | Transmission electron microscopy |
TETA | Triethylenetetramine |
TGA | Thermal gravimetric analysis |
TEPA | Tetraethylenepentamine |
VSM | Vibrating sample magnetometry |
XRD | X-ray powder diffraction |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/d1gc01539g |
This journal is © The Royal Society of Chemistry 2021 |