Abstract
Copper-containing materials such as verdigris are commonly found in historic and artistic works of art, often at advanced states of decay. Applied on paper as inks and watercolors, many of which needed a binder such as gum arabic, the intrinsic instability of this pigment was known since the medieval period. The decay of verdigris (a mixture of copper acetates) as a pigment, as watercolor, and as a dye, was studied using a combination of vibrational (Fourier transform infrared) and X-ray photoelectron spectroscopy (XPS) and X-ray diffraction (XRD) instrumental techniques. Changes in the copper oxidative states and the formation of copper oxide were monitored during accelerated degradation as powdered solids and applied on mockup samples (with and without binder). Accelerated aging of both commercially available and synthesized verdigris pigments showed the presence of an intermediate species, Cu(CH3COO)2•3Cu(OH)2•2H2O, which points to the beginning of the decay processes, that culminates in the formation of Cu(II) oxide. However, the presence of gum arabic seems to delay deterioration, by temporarily reducing Cu(II) to Cu(I), even when the final product includes Cu(II). This novel application of XPS and supporting techniques has significant implications in art conservation, as the identified behavior helps explain the better preservation state of some works of art.
Keywords
Introduction
There is a growing fascination with the research of historic and artistic materials, as well as their decay. Areas of interest include the artists' creation processes and techniques (technical art history),1,2 the development and evaluation of art conservation methodologies,3–5 and research into constituent materials' decay.4,6–10 Degradation of pigment is particularly interesting, given that new findings can challenge conservation professionals' course of action. 11 Verdigris is one of the pigments falling into this category. Commonly present in works of art dating back as far as antiquity, this copper-based pigment has been identified in various states of degradation in leather and parchment,12,13 fabric, 14 waxy paint, 15 (oil and canvas) paintings,7,9,16–18 and paper.8,19–22
The term verdigris is now applied to a blue-green pigment composed of (a mixture of) copper(II) acetates. However, throughout history, the term could also refer to copper carbonates (malachite, azurite), chlorides (atacamite, brochantite), 2 and sulfates (posnjakite, langite). 23 Being a synthetic pigment, verdigris' chemical composition is the direct result of its synthesis; its various degradation mechanisms are strictly associated with the media in which it was applied. Its application can be as a pure pigment or as a mixture. To all these considerations, conservation professionals must add the conditions in which the object was and will be treated, stored, and/or displayed to evaluate it.
For the purpose of this paper, we will be referring to verdigris as the blue-green pigment obtained by reacting copper and acetic acid. Studies have shown that obtaining a single phase of this pigment is challenging.24,25 Therefore, finding more than one form of verdigris in both works of art and in experiments is expected. Chemically, verdigris can predominantly be divided in neutral and basic, with the most common compounds being (Cu(CH3COO)2• H2O) and (Cu(CH3COO)2•Cu(OH)2•5H2O), respectively. 26 The pigment has been identified in numerous oil paintings and its degradation has been the subject of detailed studies. For instance, it was reported that ligand exchange reactions take place between fatty acids and verdigris. 27 Degradation products include copper oxalates, carboxylates, and even formates, which were previously thought to be intermediate products from fatty acids carboxylates to oxalates. 7 Similarly, research into the discoloration observed when verdigris was mixed with linseed oil, suggested a light-induced mechanism that favors decarboxylation and reduction from Cu(II) to Cu(I). 9
Every artifact containing verdigris can be affected by its established reactivity; its deleterious effects are particularly concerning with more fragile materials, such as those on paper, e.g., illuminated manuscripts and maps.12,19,21–23,28–31 Although many seem in good condition, it has been demonstrated that soluble copper ions, present in inks and watercolors with pigments such as verdigris, are particularly active towards the so-called “corrosion” of paper. 32 That is, copper ions induce hydrolysis, oxidation, and radical-driven reactions that contribute to the subsequent degradation of cellulose.5,33–35 Much of the research on this pigment and the effects copper ions have on paper has focused on treatment and it has been commonly in par with iron gall ink research.34–37 Detailed studies on the development and use of antioxidants, complexing agents, and deacidification processes has shown various degrees of success in slowing down copper ion-induced paper decay.3–5,8 However, similar studies to those made on verdigris with oil media remain scant. Herein, we report on the results that build onto preliminary work 38 and discuss detailed accelerated degradation studies of verdigris using gum arabic on cellulose, a common binding agent and media in writing and illumination. The present article reports on the application of a multi-analytical approach, including X-ray photoelectron spectroscopy (XPS), for tracking oxidation state changes that lead to the decay of verdigris in cultural heritage applications; ongoing investigations focus on substrates other than cellulose.
Experimental
Preparation of Pigments
Verdigris pigments were prepared by adapting historical recipes reported by Pliny et al.,39,40 Scott,41 and Thompson. 42 Two verdigris crystals (neutral and basic) were formed and collected; see Wiggins et al. for more details regarding their preparation and characterization. 38
Preparation of Samples
We studied the degradation of verdigris pigments dependent and independent of an organic substrate. First, both the independent powder pigments and mixtures of pigment powders with cellulose powder were aged. The degradation related to the presence of cellulose was studied by mixing each pigment and microcrystalline cellulose (ACROS Organics, particle size 50 μm) in a 1 : 1 (w/w) ratio. Mixtures of pigment and powdered cellulose complement our study of paper colored with the pigments, as we could evaluate an organic substrate (cellulose) with pigment, without the influence of any binding media. This sample set was prepared by placing approximately 0.3 g of each pigment or pigment–cellulose mixture in 2 mL gas chromatography vials with caps (Sun SRi). Septa from these caps were replaced with porous, non-woven, polyester fabric (Reemay) to allow equilibrium with the environmental conditions, while minimizing mass loss due to air circulation within the chamber.
To study the effects of an organic substrate on the pigments, verdigris was applied to cellulose paper (Whatman filter paper no. 1), both as a dye and as a watercolor. Commercially available (Kremer) and our neutral and basic verdigris pigments were dissolved in water at 5% (w/w). Various concentrations of gum arabic were added to each solution. X-ray diffraction (XRD) and Fourier transform infrared (FT-IR) showed the Kremer verdigris were neutral verdigris crystals. The basic verdigris pigment was not readily soluble in water, so a small aliquot of 0.75 mL of 5% acetic acid was added to 15 mL of solution to aid in dissolution by slightly neutralizing the pigment, while still maintaining its basic character. Gum arabic mixtures of each pigment (commercially acquired, neutral, and basic) were prepared at 1%, 5%, and 10% (w/w) against the total weight of the verdigris solution.
Solutions of the verdigris pigments with no gum arabic were drop-cast onto five strips of Whatman filter paper no. 1 (13 × 3 cm) in 20 μL aliquots and repeated five times, which were allowed to dry between applications to concentrate the pigment. This process was repeated with the 1%, 5%, and 10% (w/w) gum arabic concentrations for a total of 20 paper strips (4 × 5 replicates). Within the environmental chamber, these strips were hung from the grates by commercially purchased, metal binder clips attached to the edges of the verdigris-colored papers. Mylar strips were used as support and buffers along the edges of the papers to avoid contamination from the clips. One sample strip of each type was withheld from aging to act as controls, and the subsequent replicates were removed after one, three, five, and seven days (see Fig. 1).
Paper samples treated with commercial (C, top), neutral (N, middle), and basic (B, bottom) verdigris applied with 10%, 5%, 1%, and 0% gum arabic (left to right), which had been aged for (a) 0, (b) 3, and (c) 7 days.
Aging Studies
Pigments were studied both as a pure powder pigment and as part of organic matrices (mixed in cellulose powdered and applied to cellulose paper) using an ESPEC BTL 433 test chamber. The accelerated degradation cycle ramped the chamber parameters to 60 ± 2 ℃ and 85 ± 2% relative humidity (RH) (15 min), then held at these conditions for up to 21 days. Samples of the paper were taken at one, three, five, and seven days (Fig. 1). The pigment–cellulose mixtures were sampled at three and seven days. Independent pigment powder samples were sampled at three, seven, and twenty-one days.
Instrumentation
Fourier transform infrared was used to monitor changes to the pigment and cellulose aging through functional groups. The spectra were collected using a Bruker Optic Vertex 70 FT-IR spectrometer and Hyperion 2000 Microscope with a single-point attenuated total reflectance (ATR) attachment. Spectra were collected using OPUS 6.0 (v.6.0.72) software, averaging 128 scans in the 4000–600 cm−1 region with a resolution of 4 cm−1.
X-ray diffraction was used to identify the crystalline materials and their changes over the aging process. It was performed using a Rigaku D/max Rapid II diffractometer with a copper anode X-ray tube and 0.3 mm collimator. Samples adhered to a glass loop by Parabar 10312 (Hampton Research) were secured to the sample stage in spin mode (0–360 ° rotation), 10 °/s, 40 kV, 30 mA, and a total collection time in the range of 15–30 min. Pigment paper fibers used 45 kV, 40mA, and a total collection time in the range of 60–90 min. Rigaku RAPID/XRD software (v.2.4.2) was used to operate the instrument and collect the data, while Rigaku 2DP software (v.2.0.1.1) was used to select and process the diffraction pattern. Rigaku PDXL 2 software (v.2.3.1.0) was used to interpret and compare to a reference database, the Powder Diffraction File from the International Center for Diffraction Data (ICDD).
X-ray photoelectron spectroscopy (XPS) was used to determine the composition and oxidation states of elements, specifically studying copper changes. It was performed on cuttings (1 × 1 mm) from the artificially aged filter papers adhered to carbon tape (Nisshin EM Co., Ltd.) for analysis with a Thermo Scientific K-Alpha + XPS instrument. This instrument was equipped with a monochromatic Al Kα source (hυ = 1486.6 eV) and it operated at a base pressure of 8 × 10−9 mbar. For each sample, measurements were taken in three different spots with a 400 μm X-ray spot size and the counts were summed. An electron flood gun was used to reduce charging effects. Copper 2p high-resolution spectra were collected with 25 scans across the 965–925 eV range. The pass energy was 20 eV at 0.1 eV/step and a 50 s dwell time. Data were collected with Thermo Avantage (v5.962) and analyzed with CasaXPS (version 2.3.18PR1.01), where the spectra were calibrated using the C1s peak at 284.6 eV.
Results and Discussion
Experiments with Pure Powder Pigments and Pigment–Cellulose Mixtures
X-ray diffraction and FT-IR analysis of verdigris pigments, prepared following a simple historical recipe that consists of letting vinegar fumes slowly react with copper,39–42 showed two products: neutral (Cu(CH3COO)2•H2O) and basic (Cu(CH3COO)2•Cu(OH)2•5H2O) verdigris. 26 As expected, neutral verdigris is a green-turquoise product, while basic verdigris is light blue color. These two verdigris species represent two possible starting materials used by artists for their different coloring.13,28,43–45
While studying verdigris' impact on cellulose is extremely important, we focused our current efforts solely in understanding the pigment in the presence of cellulose, with and without gum arabic. Accelerated degradation tests were performed first on powdered pigments with no organic substrate/media; second, on a mixture of the pigment and powdered cellulose; and third, on paper applied as watercolors (with gum arabic) and as dyes (dissolved in water). Studying the pigments' degradation on paper was critical to contribute to the understanding of a near real-case scenario degradation. Studying mixtures of powdered verdigris and cellulose, on the other hand, allowed for experiments in the absence of any binder, with a comparatively higher ratio of pigment to organics, and with comparatively greater surface areas than on a paper sheet.
The pure powdered pigments and the mixture of powdered pigments with powdered cellulose were aged for seven days at 50 ℃ and 60% RH in open vials (more details in the Experimental section). Figure 2 shows XRD patterns of pigments' aging: control (with no organics present) of basic (left) and neutral (right) verdigris. After seven days of aging, new peaks at 9.41 ° and 18.73 ° suggest the formation of the less common basic verdigris species Cu(CH3COO)2• 3Cu(OH)2•2H2O as an intermediate before showing any visual changes pointing to degradation.41,46,47
X-ray diffraction patterns of basic, Cu(CH3COO)2•Cu(OH)2•5H2O (left), and neutral, Cu(CH3COO)2•H2O (right), verdigris pigments at 0 (black) and 7 (blue and green) days of aging (50 ℃, 60% RH). Conversion from both starting forms to Cu(CH3COO)2•3Cu(OH)2•2H2O is evidenced in both the absence (blue) and presence (green) of cellulose: new peaks at 9.41 ° and 18.73 ° (red lines).
At seven days of aging, the pure basic verdigris, without organics, is almost entirely converted to the above-mentioned intermediate structure. The conversion reaction for neutral verdigris seems to be slower, as Cu(CH3COO)2•H2O is still present, along with the intermediate, after seven days. The pigments mixed with cellulose showed similar trends. X-ray diffraction of both basic and neutral verdigris mixtures showed a partial conversion to the intermediate species Cu(CH3COO)2•3Cu(OH)2•2H2O, albeit slightly more pronounced for basic verdigris.
The FT-IR spectra of both pigments, displayed in Fig. 3, further supports the alteration suggested by XRD, which, to the naked eye, is associated with a shift to paler hues of both basic and neutral pigments. Unreacted basic verdigris showed carbonyl bands at 1564, 1537, and 1420 cm−1, which shifted to 1527 and 1415 cm−1 when aged with cellulose powder. Unreacted neutral verdigris, on the other hand, exhibited the carbonyl bands at 1595, 1442, and 1421 cm−1, and shifted to 1547 and 1412 cm−1 when aged with cellulose powder.7,41,46,47
Fourier transform infrared spectra of basic, Cu(CH3COO)2•Cu(OH)2•5H2O (left), and neutral, Cu(CH3COO)2•H2O (right) verdigris pigments. Red lines indicate a shift of the carbonyl bands, associated with aging.
Altogether, FT-IR and XRD evidence suggest both basic, Cu(CH3COO)2•Cu(OH)2•5H2O, and neutral, Cu(CH3COO)2•H2O, verdigris degrades into the same intermediate form: Cu(CH3COO)2•3Cu(OH)2•2H2O. This intermediate, identified as such because its presence becomes noticeable in the samples during the aging process and it is not detected once the final product, copper oxide, is predominant. The intermediate was detected in the absence as well as in the presence of cellulose. However, its presence seems to promote and increase the production of the alteration product. The deleterious effects of copper-containing species with paper have been the focus of attention for paper conservators and heritage conservation scientists alike; however, in contrast to our research, the research has been heavily focused on treatment development and evaluation.4,8,44,48,49 While there are several established chemical structures for Cu(II) acetates or verdigris, the present study documented that two starting species (basic and neutral) will transform into a different verdigris species, the intermediate Cu(CH3COO)2• 3Cu(OH)2•2H2O during their degradation, as pigment, and in the presence of cellulose. This species has been documented previously, but the impact of other common constituent documents (gum arabic) has not been well-documented.41,47,50
Experiments on Paper
To help establish an overall degradation pathway for verdigris on cellulose, the preliminary work published in 2018 was continued. 41 Previous results suggested both basic and neutral verdigris pigments degrade into an intermediate state of verdigris (Cu(CH3COO)2•3Cu(OH)2•2H2O) that continues to degrade into copper oxide.
An independent set of aging experiments (50 ℃, 60% RH, seven days) was performed on unisized paper (Whatman filter paper no. 1), where commercially available (Kremer) and lab prepared verdigris (basic and neutral) were applied as dye (mixed in water). X-ray diffraction and FT-IR results of freshly applied pigments on paper showed the presence of neutral (Cu(CH3COO)2•H2O) and basic (Cu(CH3COO)2• Cu(OH)2•5H2O) verdigris species, respectively.7,41,47 Figures S1 and S2 (Supplemental Material) show FT-IR spectra for pigments (lab-synthesized and commercially available) and Whatman filter paper with and without basic verdigris before degradation, respectively. In addition, samples of the basic verdigris already contained the intermediate species (Cu(CH3COO)2•3Cu(OH)2•2H2O) before aging (Fig. 4). Figure 4 shows the intermediate species (9.41 ° and 18.73 °) at 0 days of aging, which seems to be connected to the rapid transformation of the basic pigment into to Cu(II) oxide (35.5 ° and 38.6 °).51,52 Since copper oxide is a common degradation product in cultural heritage objects where copper salts have reacted with organic materials (e.g., parchment, binders, etc.), its presence was expected.36,53,54 The XRD pattern following seven days of aging showed a broad feature of the baseline (see first half of Fig. 4). This is a result of both amorphous cellulose fibers included in the analysis sample and possibly amorphous alteration products, as previously suggested in degradation studies by Bette et al.
55
X-ray diffraction patterns of basic (Cu(CH3COO)2•Cu(OH)2•5H2O) verdigris pigment applied to Whatman filter paper no. 1 as dye (aqueous solution). Measurements were taken after 0 (black), 3 (blue), and 7 (green) days. Peaks at 35.5 ° and 38.6 ° indicate formation of copper(II) oxide (red lines).
This new set of experiments puts verdigris' decay on paper into a greater conservation context. It has been well established that both basic and neutral verdigris pigments degrade into copper oxides. Additionally, the evidence presented here allowed identification of the intermediate (Cu(CH3COO)2•3Cu(OH)2•2H2O) as part of the oxidative alterations of the pigment. More importantly its presence seems to be the indicator of a subsequent rapid degradation process, as decay was more pronounced when applied to paper as a dye (aqueous solution) and not as the cellulose–pigment (in the previous section) mixture. Using XRD, the crystalline changes to these pigments were determined during the degradation process, in the presence and absence of cellulose.
Experiments on Paper with Gum Arabic
Gum arabic was a common binder in works of art on paper, including illuminated manuscripts, where verdigris was used.44,56–58 To evaluate the role of this substance in the degradation pathway, aging experiments (50 ℃, 60% RH, seven days) were performed on unisized paper (Whatman filter paper no. 1). Commercially available (Kremer, neutral) and lab-synthesized verdigris (basic and neutral) were applied both as dye (mixed in water) and as watercolor (mixed in an aqueous solution of gum arabic) in a range of gum arabic concentrations (0%, 1%, 5%, and 10%). See the Experimental section for sample details.
Surface analysis of the samples was performed using XPS, which allowed for accurate tracking of the changes in oxidation states of copper-containing species. Because this technique provides information about the chemical environments, but not of the exact species, the XPS discussion will be limited to oxidation states only. Given its high spatial resolution, attempting to sample the same site to run complementary analysis like XRD was impossible. However, other areas of the same mockup sample were analyzed using XRD and FT-IR. Monitoring of the cellulosic changes with FT-IR did not show any conclusive trends. Alterations to these cellulose substrates could not be readily distinguished with IR spectroscopy and complementary studies are ongoing.
X-ray photoelectron spectroscopy analysis of commercially available (neutral) and lab-synthesized (basic and neutral), both as unaged pigments and applied to paper as aqueous solutions, showed mixtures of Cu(I) and Cu(II) states. This is consistent with previous results in Wiggins et al. 38 Although this result could be interpreted as a mixed-valence compound being present, it is possible the ultrahigh vacuum required to run XPS dehydrated the samples, resulting in a partial reduction.
The presence of gum arabic seems to be associated with the reduction of copper to Cu(I). Even at 0 days of aging, basic verdigris is predominantly in a Cu(II) state without gum arabic. Neutral verdigris (Fig. S1, Supplemental Material), on the other hand, is approximately an even mixture of Cu(I) and Cu(II). The XPS high-resolution scan of the copper 2p region (Fig. 5) suggests a correlation between higher concentrations of gum arabic and more Cu(I). Higher concentrations of gum yield an increase in peaks at 953.3 eV (2p1/2) and 933.1 eV (2p3/2), meaning a reduction to Cu(I). In addition, there are more Cu(I) species in the sample.
51
X-ray photoelectron spectra of the copper 2p region for basic verdigris (Cu(CH3COO)2•Cu(OH)2•5H2O) mixed with different amounts of gum arabic before degradation. Red lines highlight Cu(I) increasing as gum arabic concentration increases.
Higher concentrations of gum arabic imply higher concentrations of polysaccharides and reducing sugars. The results showed gum arabic mixed with all forms of verdigris reduce some verdigris species from Cu(II) to Cu(I), with higher concentrations of gum arabic leading to more Cu(I). Cu(I) species produce more hydroxyl radicals than Fe(II), and Cu(II) species produce more hydroxyl radicals than other common transition metal ions on cellulose (in Fenton-like reactions frequently associated with paper decay).34,59 Reducing sugars with Cu(II) acetate in water (Barfoed's reaction) 60 suggests objects such as illuminated manuscripts are inherently prone to degrade, as they contain all starting reagents that lead to Cu(I) species as byproducts. For instance, chelating treatments used to stop the catalytic effects of Fe(II), present in historical inks, are non-specific and can bond to transition metals59,61–63 Therefore, the role of copper ions and their oxidation state need to be considered when selecting conservation procedures, as copper acetates (verdigris) can be found as part of these inks as well.
Interestingly, pigments seem to react with gum arabic to (temporarily) oxidize copper during the accelerated degradation process, as Cu(I) oxidizes into Cu(II) species. Figure 6 shows lab-synthesized neutral verdigris in 10% gum arabic, which showed the highest Cu(I) species at the start. Over the course of aging (three and seven days), the peaks at 955.1 eV (2p1/2), 944.7–941.1 eV (satellite), and 934.9 eV (2p3/2) slightly increased, possibly indicating some conversion to a Cu(II) compound, such as Cu(II) oxide.
51
X-ray photoelectron spectra of the copper 2p region for neutral verdigris with of 10% gum arabic during accelerated degradation. The red lines indicate the increase of copper(II) species as the copper is oxidized.
Commercially available neutral verdigris showed an oxidative change as well. Samples that started with higher amounts of Cu(II) (lower amounts of gum arabic) remained in that state throughout the experiment, possibly reaching stoichiometric equilibrium or perhaps evidencing a different pathway to copper oxide (ongoing research). This shows XPS evidence of the oxidation of the copper species during the artificial aging process, which in turn informs the oxidative decay occurring for the pigments on cellulose.
The presence of Cu(I) species, significantly present when the pigment is mixed with gum arabic, seems to be associated with a slower pigment degradation. X-ray photoelectron spectroscopy results showed Cu(I) and Cu(II) were present during the entire aging time in the presence of gum. In contrast, Cu(II)-containing species are overwhelmingly present in its absence. In addition, the XRD data on the same mockups suggest a slower reaction in the presence of gum arabic, by showing the same starting material (Cu(CH3COO)2•3Cu(OH)2•2H2O) during the seven days of aging. Figure 7 shows the XRD patterns (after seven days of aging) for basic verdigris with 10% gum arabic and a control sample, with no gum arabic. While the sample with no gum arabic only shows peaks for CuO (35.5° and 38.6°), the sample with 10% gum arabic shows the presence of the initial intermediate verdigris (9.45° and 18.96°) as well as the final product of CuO.41,46,47 Furthermore, visual assessment of these samples showed that those with more gum arabic are less discolored and brown, compared to the controls, with no gum arabic (Fig. 1). This suggests that without gum arabic, under these conditions, the reaction goes to completion, while in the presence of gum arabic, the reaction progresses slowly. In both XRD patterns in Fig. 7, intense broad baselines in the range of 10°–25° indicate amorphous materials, either cellulose fibers from the substrate or amorphous alteration products, which could not be identified.
55
X-ray diffraction patterns of paper with basic (Cu(CH3COO)2•Cu(OH)2•5H2O) verdigris after 7 days of aging with 0% gum arabic (blue) and 10% gum arabic (black). Note that verdigris angles (9.45° and 18.96°, denoted by the red lines) are still present in the sample with 10% gum arabic, but not in the control.
The results discussed here seem to suggest the degradation from the intermediate verdigris (Cu(CH3COO)2• 3Cu(OH)2•2H2O) to copper(II) oxide (CuO) occurs by more than one mechanism. Figure 7 shows that after seven days of aging and in the absence of gum arabic, only the degradation product CuO was detected. In contrast, in the presence of gum arabic, both the intermediate and CuO are detected. Because we are considering CuO to be the product of a complete degradation process, we think the gum arabic slows down the degradation, leading to an incomplete degradative oxidation of the pigment. Feasible reasons include: (1) a stable equilibrium between the various saccharides present in gum arabic and verdigris variants; (2) pigment simultaneously reacting with cellulose and gum arabic; or (3) a different, specific, mechanism from that occurring in the absence of gum, yet to be studied. Our findings have significant implications for conservation, as this could help explain dissimilar degradation in artifacts and could potentially lead to novel treatments.
The presence of numerous transition metal ions in historic inks is a well-documented cause of cellulose's degradation.34,35,59,64–66 In particular, the presence of Fe(II) has been the subject of numerous studies pertaining to iron gall inks and their treatment.5,32,35,37,61,63,65,67–69 Of all ions under study, copper has been deemed the most efficient to promote auto-oxidation and depolymerization of cellulose either as Cu(I) in the pseudo-Fenton's reaction to form hydroxyl radicals,35,64,70,71 or as Cu(II) to act as an oxidation agent with cellulose carboxylates.33,54,72–75 Our findings show once more that copper is indeed a clear cause of decay, but in the presence of gum arabic, Cu(I)-promoted degradation is slower than that of Cu(II) without gum.
Conclusion
This study expands on previous work regarding the characterization and alteration of verdigris pigment, with a focus on identification of its crystalline species. This paper focused on determining the verdigris pigments' oxidative changes when applied to organic materials during accelerated degradation. Both lab-synthesized neutral and basic verdigris were found to alter into the same intermediate verdigris species, Cu(CH3COO)2•3Cu(OH)2•2H2O, with and without cellulose being present. This alteration was put into the context of the pathway of verdigris to copper oxide on paper, as identified by XRD. Expanding on this work, the role of gum arabic, a common binder for paper documentation, was evaluated as well. Gum arabic formed reduced copper species in the verdigris watercolors on paper. Those copper species appear to slow down the ultimate reaction to the degradation product, copper(II) oxide. These findings were documented by XPS and XRD with supporting FT-IR analysis.
This research documents the alteration in various forms of verdigris during the aging process on cellulose and the oxidation states the pigment undergoes with gum arabic binders on cellulose. While this stage focused on changes to only the pigment as it ages on paper, ongoing investigations focus on alterations to organic substrates as well as their changes during the oxidative process. This information benefits conservators, and conservation scientists aiming to preserve and treat historical documents, where verdigris plays a key role in their degradation. Continued work in characterizing the species that were not identified in this report and in better assessing the role of a reduction agent such as gum arabic on the overall degradation process is ongoing.
Supplemental Material
Supplemental material for Multi-Analytical Study of Copper-Based Historic Pigments and their Alteration Products
Supplemental Material for Multi-Analytical Study of Copper-Based Historic Pigments and their Alteration Products by Marcie B. Wiggins, Emma Heath, Karl S. Booksh and Jocelyn Alcántara-García in Applied Spectroscopy
Footnotes
Acknowledgments
The authors thank: the Winterthur Museum, Garden, and Library’s Scientific Research and Analysis Laboratory (SRAL) for the use of the XRD and accelerated aging systems; Brain Baade at the University of Delaware for materials and assistance in preparing many of the pigments; Jim Schneck (Winterthur Museum) for photography; the National Science Foundation (CHM 1506853) and the University of Delaware’s Office of Graduate and Professional Education for support; the University of Delaware’s Surface Analysis Facility for XPS support, as well as the NSF (CHE 1428149) and the NIH NIGMS COBRE program (P30-GM110758).
Conflict of Interest
The authors report there are no conflicts of interest.
Funding
The Andrew W. Mellon Foundation provided funding for the accelerated aging unit.
Supplemental Material
All supplemental material mentioned in the text is available in the online version of the journal.
References
Supplementary Material
Please find the following supplemental material available below.
For Open Access articles published under a Creative Commons License, all supplemental material carries the same license as the article it is associated with.
For non-Open Access articles published, all supplemental material carries a non-exclusive license, and permission requests for re-use of supplemental material or any part of supplemental material shall be sent directly to the copyright owner as specified in the copyright notice associated with the article.
