Open Access Article
Mayson Whipple
a,
Barbara Christianb,
Kendell M. Pawelec
cd,
Netsanet Waal
a,
D. Adam Lauver
b and
Robert C. Ferrier Jr.
*a
aDepartment of Chemical Engineering and Materials Science, Michigan State University, East Lansing, MI, USA. E-mail: ferrier5@msu.edu
bDepartment of Pharmacology and Toxicology, Michigan State University, East Lansing, MI, USA
cDepartment of Radiology, Michigan State University, East Lansing, MI, USA
dInstitute of Quantitative Health Science and Engineering, Michigan State University, East Lansing, MI, USA
First published on 24th December 2025
Medical imaging techniques like X-ray, magnetic resonance imaging (MRI), and computed tomography (CT) rely on contrast agents to enhance the visibility of blood vessels, tissues, and organs, making them crucial for medical diagnoses. Contrast agents used clinically for CT are typically small molecules containing iodine, which are associated with nephrotoxicity, often require large doses that can disrupt thyroid function, have short half-lives, and are sometimes immunogenic. Loading/functionalization of larger molecules with iodine may attenuate X-rays similarly to small molecules, but at much lower concentrations, potentially mitigating the adverse effects of current contrast agents. To test this, iodinated poly(ethylene oxide) (PEO) was synthesized with varying amounts of iodine and structural features and examined for use as a contrast agent. First, 5 kg mol−1 PEG containing one terminal hydroxyl was reacted with trimethylaluminum to form a macroinitiator from which block-co-polymers consisting of PEO-co-poly(epichlorohydrin) (PECH) were synthesized with PECH blocks of 5, 15, and 30 kg mol−1. The polymers were subsequently iodinated and characterized with 1H NMR and 13C NMR spectroscopy, size exclusion chromatography (SEC), and differential scanning calorimetry (DSC). X-Ray attenuation was found to be similar to that of iohexol, a conventional contrast agent. Further, we found that high molecular weight polymers were completely non-cytotoxic, unlike iohexol, with polymer size the dominating factor for cytotoxicity rather than iodine concentration. As such, these new materials hold promise as medical contrast agents.
Elements of higher atomic number (Z) attenuate X-rays at high levels and, historically, iodine (Z = 53) has been incorporated into contrast media for clinical CT.4 Today, nearly all available contrast agents are based on the modification of a tri-iodinated benzene ring with hydrophilic functional groups to facilitate solubility, classified as iodinated contrast agents (ICA).5 Existing ICAs are either ionic or nonionic and monomeric or dimeric, with monomeric agents containing one tri-iodinated benzene ring and dimeric containing two.6 ICAs with low (nonionic monomer ex. iohexol) or similar (nonionic dimer ex. iodixanol) osmolarity compared to human blood plasma have proven less toxic than high osmolarity agents.6 Dimeric structures can fit higher concentrations of iodine per osmole, allowing for optimal radiopacity at lower concentrations and thus lower osmolarity and toxicity.7
Existing contrast agents have been associated with adverse reactions, namely thyroid dysfunction, immune reactions, and nephrotoxicity. The mechanisms prompting adverse reactions are not fully understood; however, the high doses required for effective contrast is likely a contributing factor.4 X-Ray attenuation increases linearly with iodine concentration and traditional small molecule ICAs require high dosing volumes to achieve effective contrast.8 Existing ICAs introduce iodine in concentrations several hundred thousand times the recommended daily dose of iodine. High levels of free iodine in the body are associated with thyroid dysfunction and while contrast-induced thyroid dysfunction is relatively rare, excess exposure to iodine can induce permanent hyperthyroidism in some patients.4 Further, direct toxicity on renal cells from existing, small molecule ICAs can cause contrast-induced nephropathy, a potentially life-threatening condition. The risk is highest in patients with prior renal dysfunction, diabetes, and intensive care patients.9 Consequently, patients requiring critical diagnosis for treatment planning and monitoring of disease progression are unable to utilize contrasted CT, which may delay diagnosis and lead to poor treatment outcomes.
There is a clear need for novel contrast agents that (1) exhibit high X-ray attenuation at lower concentrations and (2) are non-cytotoxic, particularly to renal cells. Polymer-based contrast agents may be advantageous due to the unique properties afforded by polymers, such as biocompatibility, facile synthesis, and versatility in structural modification and functionalization.10 Recent advances in polymeric drug delivery systems have been explored to improve biocompatibility, circulation time, and more efficient targeting through encapsulation and delivery of existing ICAs.11,12 Other polymeric approaches aimed to form iodinated macromolecules via polymerization of iodinated monomers or functionalization of polymer backbones with iodine or iodinated compounds.13–15 These strategies have highlighted the potential for polymeric contrast agents to overcome the drawbacks of existing ICAs; however, complex synthesis, low iodine content, moderate contrast, or low biodegradability and/or biocompatibility have limited their advancement to clinical use.
Aside from intravenous contrast agents, CT imageable probes have been incorporated into polymer-based biomedical devices to improve clinical assessment. While not generally iodine-based, these CT probes nonetheless consist of high Z materials and are often in the form of nanoparticles. For example, Pawelec et al. incorporated biocompatible tantalum oxide (TaOx) nanoparticles into biocompatible polymer-based scaffolds.16,17 They were able to monitor the degradation of the devices over time both in vitro and in vivo due to the contrast from the TaOx. Other examples of nanoparticles for CT imaging are extant and they provide strong contrast.18,19 However, there are concerns about the long- and short-term impacts to the patient of exposure to high Z nanoparticles, as well as scale-up and other clinically relevant factors.20 Furthermore, compatibilizing nanoparticles with polymers, biomedical or otherwise, can be challenging21,22 and may add additional modification and/or processing steps.
In this work, we set out to explore polyether materials as potential contrast agents. Polyethers, especially poly(ethylene oxide) (PEO), are commonly used for biomedical applications. However, PEO is largely non-functional. We sought to combine PEO with a functional polyether material, polyepichlorohydrin (PECH) to enable a tunable, high-contrast, and biocompatible polymer platform. This work explores this platform for biomedical imaging applications. Specifically, we created iodinated polymers from functional polyethers, which provide high tunability, high iodine content, and are non-cytotoxic. Block copolymers consisting of PEO and PECH were synthesized by chain extension polymerization from 5 kg mol−1 PEO and functionalized with iodine moieties. Iodinated polymers (PEO–PEI) were synthesized with iodine concentrations ranging from 29% to 90% by targeting increasing PECH block sizes of 5 kg mol−1, 15 kg mol−1, and 30 kg mol−1. Polymer structures were characterized with nuclear magnetic resonance (NMR) spectroscopy, differential scanning calorimetry (DSC), and gel permeation chromatography (GPC). Micro-CT (μCT) imaging demonstrated high levels of X-ray attenuation can be achieved at 20× lower sample concentrations of PEO–PEI (low Mn & lowest iodine content) compared to conventional iohexol. ICP-MS analysis revealed iodine concentrations in the PEO–PEI case at similar levels to iohexol, even with the low concentration of the PEO–PEI molecules themselves, confirming the presence of iodine on the polymer chain. A predictive model for X-ray attenuation given polymer concentration at particular Cl to I conversion was generated to inform future design of iodinated polymers. Finally, cytotoxicity of PEO–PEI was assessed in human renal cells. Higher molecular weight PEO–PEI exhibited no cytotoxicity while lower molecular weight PEO–PEI was cytotoxic and exhibited behavior similar to that of iohexol. This work is a first step in developing these radiopaque polymer materials for biomedical imaging applications.
Size exclusion chromatography (SEC) was performed using a Tosoh EcoSEC Elite on THF with refractive index used for molecular weight determination. Calibration was performed using polystyrene standards in THF rather than PEG due to solvent incompatibility.
Differential scanning calorimetry (DSC) was performed on a TA250 instrument with a heating rate of 10 °C min−1 under an N2 atmosphere.
Inductively coupled plasma mass spectroscopy (ICP-MS) was used to measure iodine content in solutions and was conducted at the quantitative bio element analysis and mapping (QBEAM) Center (Michigan State University). Samples were digested for 4 hours in HNO3. After digestion, a liquid sample was added to a matrix consisting of 0.1% w/v EDTA, 2% v/v NH4OH and 0.01% v/v Triton X-100 in water, with Gadolinium (Gd) ISTD.
Micro-computed tomography (CT) imaging. All tomography images were obtained using a PerkinElmer Quantum GX at 90 keV, 88 µA, with a 36 mm field of view at a 50 µm resolution. Scans were taken with 2 min scan time, corresponding to a step size: 0.11 degrees and exposure time per projection: 36 m s. Solutions of iodinated and non-iodinated polymers were prepared in DI water or DCM. Iohexol solutions were used as a positive control.
Statistics were performed using GraphPad Prism (v. 10.0.2). All data were analyzed via ANOVA, followed by Fisher's LSD test. Cytotoxicity results were analyzed by comparing the percent cell viability relative to the control. Nonlinear regression was performed to create best-fit curves. In all cases, α < 0.05 was considered significant, with a 95% confidence interval. Data are presented as mean ± standard error.
1H NMR (500 MHz, CDCl3) δ 2.80 (q, 6H), 1.18 (t, 9H), −0.89 (s, 9H). 13C NMR (126 MHz, CDCl3) δ 47.78, 9.20.
1H NMR (500 MHz, CDCl3) δ 3.80–3.66 (bm, CH–CH2Cl), 3.64–3.56 (bm, CH2CH2 and CH2CH–CH2Cl).
13C NMR (500 MHz, CDCl3) δ 79.08 (t, –O–CH2–CH(CH2Cl)–O–), 70.59 (s, CH2CH2), 69.89–69.30 (bm, CH2–CH–CH2Cl), 43.65 (s, CH2Cl).
1H NMR (500 MHz, CDCl3) δ 3.80–3.66 (bm, CH–CH2I), 3.64–3.56 (bm, CH2CH2 and CH2 CH–CH2I), 3.46–3.24 (bm, CH2CH–CH2I).
PEO–PEI or iohexol (positive control) stock solutions were prepared by dissolving powder in RPTEC/TERT1 media, which was subsequently serially diluted 2-fold to generate a range of concentrations.
On the day of treatment, the culture medium was aspirated from each well and replaced with media containing PEO–PEI or iohexol at the indicated concentrations in triplicate. After 30 minutes of incubation, MP Biomedicals™ Gly-Phe-7-Amino-4-Trifluoromethylcoumarin (Cat. no. 03AFC03310) was added to the wells, followed by an additional incubation period.
Cell viability was assessed by measuring fluorescence using a BioTek Synergy Neo plate reader at one- and two-hours post-PEO exposure.
Block-co-polymers consisting of PEO and PECH were synthesized as precursors for tuning the polymer iodine content. Chain extension polymerization of epichlorohydrin (ECH) was performed using an NAl catalyst23–25 and an aluminum alkoxide PEO macroinitiator, as shown in Scheme 1. Briefly, the macroinitiator was formed by reacting a commercially obtained PEO (average Mn of 5000 g mol−1) containing one hydroxyl end group (commonly referred to as mPEG) with trimethylaluminum and stirring at room temperature overnight. NAl catalyst and epichlorohydrin were then added in amounts to target PECH blocks of 5000 g mol−1, 15
000 g mol−1, and 30
000 g mol−1. 1H and 13C NMR spectroscopy were used to confirm copolymer structure and determine molecular weight. The resultant spectra and a detailed example calculation can be found in the SI (Fig. S1–S6). Ratios of PECH to PEO were determined based on the 1H NMR spectra by setting the integration of the PEO peak at 3.64 ppm to 4 (accounting for the OCH2CH2 backbone), integrating both backbone peaks, subtracting by 4, and dividing by 5 (the number of protons in the PECH block). The relative amount of PECH could then be calculated based on the ratio of PECH to PEO. For example, the PECH:PEO ratio for target 5 kg mol−1 was 0.46 so relative PECH was calculated to be 0.32 (0.46/(1 + 0.46)). Mn of the PECH block was then calculated by finding the total number of repeat units (N), subtracting the N of PEO, and multiplying by the molecular weight of PECH repeat unit. PECH Mn were found to be 4872 g mol−1, 15
556 g mol−1, and 30
402 g mol−1 in good agreement with the target Mn. Polymerization details can be found in Table 1.
| Sample | PECH Mtheon (kg mol−1) | PECH Mna (kg mol−1) | PECH Mnb (kg mol−1) | Đ | Iodine conversion (%) |
|---|---|---|---|---|---|
| a Determined from 1H NMR.b Determined from SEC. | |||||
| PEO–PECH5 | 5 | 4.9 | 4.7 | 1.3 | — |
| PEO–PECH15 | 15 | 15.6 | 16.3 | 2.2 | — |
| PEO–PECH30 | 30 | 30.4 | 29.6 | 2.4 | — |
| PEO–PEI5 | 5 | 6.2 | — | — | 27 |
| PEO–PEI15 | 15 | 20.0 | 20.4 | 2.1 | 26 |
| PEO–PEI30 | 30 | 60.3 | 32.3 | 1.9 | 92 |
Copolymers were analyzed by SEC for further confirmation of molecular weights and determination of polydispersity (Đ). RI spectra can be found in the SI (Fig. S7). SEC revealed copolymers with Mn of 9693 g mol−1 and Đ = 1.3 for the target PECH block of 5 kg mol−1, 21
300 g mol−1 and Đ = 2.2 for the target PECH block of 15 kg mol−1, and 34
615 g mol−1 and Đ = 2.4 for the target PECH block of 30 kg mol−1. These results compare favorably to the molecular weights targeted and calculated by 1H NMR spectra. The polydispersity increased with molecular weight, which was also observed in previous work from Keever et al., albeit the PEO and PECH blocks were smaller than in this work.26 Furthermore, this high Đ at higher molecular weight may be due to the better solubility of the PECH block compared with the PEO block in THF (the GPC solvent). This is supported by the fact that when we replaced most of the Cl with I, we see a drop in the Đ, indicating this could be a solvent effect. Despite the relatively high Đ from a synthetic polymer chemistry standpoint, biomedical polymers at similar Đ are utilized medically.
Copolymers will be referenced throughout the rest of this manuscript according to the relative Mn of the PECH block (PEO–PECHX). For example, the copolymer with target PECH Mn of 5 kg mol−1 is referred to as PEO–PECH5. Iodinated copolymers will be referenced similarly except with PEO–PEIX, where X is the molecular weight of the PECH block.
DSC was performed on each polymer and truncated traces can be found in Fig. 1. Full DSC traces for each polymer can be found in the SI (Fig. S8–S10). The DSC revealed one Tg for each copolymer, namely −43.2 °C for PEO–PECH5, −33.64 °C for PEO–PECH15 and −32.84 °C for PEO–PECH30. This observation of a single Tg is consistent with the fact that PEO and PECH are miscible at all volume fractions.27,28 Furthermore, the shift in Tg with relative PECH size to higher Tg (i.e., closer to PECH Tg) is consistent with the increased fraction of PECH in the copolymer. At lower molecular weights (and smaller PECH block size), the copolymer appears semi-crystalline (Tc = 0 °C and Tm = 50 °C), with a calculated %crystallinity of 23.5% consistent with the literature.28 At higher PECH Mn, no crystallization was observed likely due to the plasticization effect of the PECH, again consistent with the literature. To further analyze these thermal data, the Tg shift as a function of weight fraction of PEO (wPEO) was calculated using the Fox equation. Fig. 1(B) contains the results from the Fox equation, as well as our data and data from Don Paul and co-workers of PEO–PECH blends. It should be noted that for Paul's work, they used a much higher molecular weight PEO, resulting in a higher Tg for wPEO = 1. We adjusted our wPEO for the PEO–PECH5 point based on the measured PEO crystallinity. Our measured values fall between the Fox equation prediction and Paul's experimental data and are generally close to both lines for all points.
The reaction scheme and truncated 1H NMR spectra for PEO–PECH30 and its iodinated counterpart can be seen in Fig. 2. Full 1H NMR spectra for each iodinated polymer can be found in the SI (Fig. S11–S13). The 1H NMR spectra post-iodine functionalization confirmed the substitution of chlorine as a new peak emerged around 3.4 ppm representing the CH2–I peak with upfield shifting due to the decrease in shielding from the iodine moieties, consistent with literature.29 Conversion of Cl to I was calculated from 1H NMR spectra. An example of this calculation can be found in the SI. Conversions were 27% for PEO–PECH5, 26% for PEO–PECH15 and 92% for PEO–PECH30. While iodination reactions were performed in identical experimental conditions, the conversions were significantly lower for lower Mn polymers, however the range of substitution is consistent with the literature.29 This difference in iodine conversion could be due to the higher relative ratio of ECH units pushing the reaction to conversion as has been observed in other examples of Finkelstein reactions.30 Nonetheless, PEO with increasing and distinct iodine concentrations were synthesized.
![]() | ||
| Fig. 2 (top) Reaction scheme for iodinating copolymers and 1H NMR spectra of PEO–PECH30 (left) and PEO–PEI30 (right). | ||
PEO–PEI15 and PEO–PEI30 were analyzed via SEC to ensure there was no degradation of the polymer. A report of polyepiiodohydrin synthesis from the Finkelstein reaction of PECH with NaI from 1978 reported a reduction in Mn at increased iodine conversion.29 They attributed this to cleavage of ether linkages and noted a drastic drop in molecular weight on the SEC. In our case, it is unlikely ether cleavage is occurring given the (modest) increases in Mn of our polymer noted from our SEC data. SEC traces can be found in the SI (Fig. S17 and S18). The measured Mn of PEO–PEI15 was 25.4 kg mol−1 and the Mn of PEO–PEI30 was 37.3 kg mol−1. As such, we found small increases in polymer Mn after substitution as determined by SEC due to the limited volume change of the polymer after iodine substitution. This is expected as the absolute volume of our polymer would not change much with iodine incorporation, meaning there would be a small effect on elution time and therefore calculated molecular weight. Here, the SEC is being utilizing to confirm that our polymer is not degrading rather than to provide a way to quantify iodine substitution.
DSC was performed on all iodinated polymers to examine changes in thermal properties and further investigate the modification of polymer structure. Tg shifted to higher temperatures after iodination, which can be seen for the PEO–PECH5 copolymer in Fig. 3 and for the other copolymers in the SI (Fig. S14–S16) Tg = −36.9 °C for PEO–PEI5, −31.12 °C for PEO–PEI15, and −16.88 °C for PEO–PEI30. More significant shifts in Tg were observed after iodinating PEO–PECH5 (+6.3 °C) and PEO–PECH30 (+16.8 °C); however, only a small shift was observed in the PEO–PECH15 polymer (+1.72 °C).
To better understand this thermal data, we calculated the glass transition temperature of PEO–PEI polymers. A previous report produced iodinated PECH at various conversions and determined the Tg.29 A reproduction of their glass transition data as a function of conversion can be seen in SI (Fig. S19 or Fig. 5 in ref. 29). A linear regression reveals the Tg of pure polyepiiodohydrin (i.e., PECH at 100% iodine conversion) to be 10 °C. Utilizing this linear regression model, we hypothesize that the Tg at a given conversion of iodine for PECH can be predicted. This is combined with the Fox equation to predict the Tg at the calculated iodine conversion for the PEO–PEI polymers. It should be noted that the Fox equation utilizes weight fractions of the polymers and so these fractions need to be adjusted due to the increased weight of the iodinated polymers compared with neat PECH. Table 2 summarizes the data for these calculations. Here, the calculated Tg are within a few °C for PEO–PEI5 and PEO–PEI15 but is 15 °C off for PEO–PEI30. This could be due to an over-adjustment of the wPEO given the increased mass of the iodinated polymers or it could be due to an overestimation of the iodination in our system from the NMR spectrum. For completeness, we used this model to calculate the iodine conversion for each of our polymers given the measured Tg, which can be seen in Table 2. As expected, the iodine conversion is calculated to be a little higher for PEO–PEI5 and a little lower for PEO–PEI30. Our current hypothesis for this discrepancy is uncertainty in the dependence of Tg on iodine incorporation in our block-co-polymer structure, which is a fundamentally different material than the one from the report in 1978. In future work, we will make rigorous changes to iodine conversion and investigate the connection between composition and thermal properties.
We recontextualized the data as a half minimal cytotoxic concentration (CC50) to better understand the cytotoxic effects of the polymers/iohexol. CC50 was determined from a fit to the fluorescence response data. The CC50 for the PEO–PECH/PEI15/30 is not very meaningful given the lack of inhibition of fluorescence (i.e., survivability of the cells). As such, the CC50 determined from a fit to the data is either unrealistically high or incalculable. On the other hand, the CC50 for the PEO–PECH/I5 and iohexol is meaningful. First, the CC50 for PEO–PECH5 and PEO–PEI5 are almost identical to one another, calculated to be 0.46 mM and 0.49 mM, respectively. This means that incorporation of the iodine is not appreciably affecting the toxicity of the cells, further highlighting the relation of polymer size to cytotoxicity. The iohexol had a calculated CC50 of 19.72 mM. Given that the iodinated polymers show a negligible difference in behavior in CC50 from the non-iodinated polymers, it is difficult to compare the polymer CC50 to the iohexol CC50. For instance, what concentrations do we compare? Since PEO is generally viewed as non-cytotoxic, we could recalculate the CC50 of PEO–PECH5 in terms of ECH units. In this case, the CC50 of ECH is 24.86 mM, similar to iohexol. This comparison is likely dubious given at higher ECH concentrations (i.e., PEO–PECH15/30) we see limited cytotoxicity. Further studies need to be done to better understand the source of cytotoxicity with the smaller polymers.
Lower molecular weight polymers exhibited greater toxicity with behavior similar to that of iohexol. Khanh et al. found a strong correlation between PEO molecular weight and cytotoxicity, with cytotoxicity decreasing as PEO chain length was increased.31 Postic et al. investigated the effect of PEO molecular weight on cell viability and cell morphology and similarly found that high concentrations of low molecular weight PEOs were more cytotoxic and prompted significant changes in cell morphology compared to high molecular weight PEOs.32 Cell death was attributed to the mechanism of cellular uptake of low molecular weight PEOs (passive diffusion) vs. endocytosis for longer chain PEOs.33 The toxic effects observed in the aforementioned works were in PEG with molecular weights much smaller than ours (ca. 200 g mol−1) and large sets of data support the benign nature of cells towards PEG/PEO at higher molecular weights.
PECH has received limited study in relation to cytotoxicity. Our initial intuition was that PECH would be cytotoxic, and we hoped that the PEO block would mitigate this. However, the limited literature data supports that higher molecular weight PECH and PEO/PECH copolymers are benign.34,35 However, there is some evidence that low molecular weight/oligomeric PECH is cytotoxic.36 Given the results with lower MW PEO–PECH (i.e., 5 kg mol−1) being cytotoxic and higher Mn not, this is generally consistent with the literature. As such, our work further establishes the effect of PEG and PEG derivatives molecular weight on cell viability.
The iodine content in the PEO–PEI5 and iohexol was measured at each of the concentrations in the CT experiments by ICP-MS. The X-ray attenuation was then plotted as a function of the measured iodine content as can be seen in Fig. 5(B). Radiopacity scales linearly with iodine content, in agreement with literature.37 This imaging trend aligns with other studies using different radiopaque elements.38,39 The slopes for iodinated PEO (PEO–PEI5) and iohexol were 5.6 HU mM−1 iodine and 4.8 HU mM−1 iodine respectively, which were not significantly different. These results confirm the tunability of X-ray attenuation due to the block copolymer system in which this work is based on. From the fits to the above data and given the amount of iodine attached to the PECH–PEI, we generated a predictive model for the X-ray attenuation given polymer concentration at a particular Cl− > I conversion, which can be found in Fig. 6. From this data, we see a discrepancy between the conversion calculated conversion and the amount of iodine present.
The maximum number of iodine bound to the polymer sample depends on the size of the precursor PECH block and Cl− > I conversion, with higher molecular weights and conversion having higher iodine content. Thus, targeting larger PECH blocks should conceivably result in increased attenuation while the overall sample concentration is held constant. The radiopacity of higher molecular weight iodinated polymers was measured in DI water; however, poor solubility limited the concentration range evaluated. In this concentration range, the radiopacity of iodinated polymers was low, 124.2 ± 7.67 HU for PEO–PEI15 and 124.2 ± 12.8 HU for PEO–PEI30. This is lower than the predicted radiopacity from the model and is likely due to the poor solubility in hydrophilic solvents (e.g., water and PBS buffer) as they tended to crash out of solution even at low concentrations (∼5 to 12 mg mL−1).
To confirm that the poor water/PBS solubility was indeed the reason for the low attenuation, X-ray attenuation was measured for PEO–PEI15 and PEO–PEI30 in DCM. Since DCM (ca. 1600 HU) is denser than water (0 HU), so baseline attenuations of these two solvents are different. Here, we achieved high X-ray attenuation, which we define as >300 HU above baseline (i.e., 1600 HU for DCM + 300 HU ≈ 1900 HU), in polymer concentrations at or above 50 mg mL−1, highlighting the importance of solubility on X-ray attenuation. X-Ray attenuation increases linearly with increasing polymer concentration (and subsequent iodine concentration) shown in Fig. S20 in the SI. As a check, we backed out the iodine concentration for these polymers (taking into account calculated iodine conversion, molecular weight, etc.) and replot them as HU as a function of iodine concentration, as seen in Fig. S21. We find that the curves overlap, meaning the iodine in one polymer is giving the same enhancement to contrast as iodine in the other polymer, which is what we would expect. Furthermore, this lends weight to our 1H NMR spectroscopy-based calculation of iodine conversion, since if this was off, the fits would not overlap. In the future, hydrophilicity issues can be mitigated by further polymer modification. Due to the versatility of the precursor block copolymers, polymer structures can be tuned by modifying Cl pendants of the PECH block with hydrophilic moieties prior to iodinating or prepared as micelles to facilitate solubility.
Vivo Biodegradation of Nanoparticle-Laden Polymeric Devices, Adv. NanoBiomed Res., 2025, 5(6), 2500005, DOI:10.1002/anbr.202500005 (acccessed 2025/11/24).| This journal is © The Royal Society of Chemistry 2026 |