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Polyethylene Glycol Treatments for Basketry on the Northwest Coast of North America
Ellen Carrlee* and Dana K. Senge
Alaska State Museum
395 Whittier Street
Juneau AK 99801 USA
Abstract: Basketry artifacts discovered in wet sites have been routinely treated with polyethylene
glycol (PEG) since the 1960’s. Although the vast literature on PEG treatment of shipwrecked
wood informs the treatment decisions for this material, basketry treatments often do not behave
in the manner expected for waterlogged wood. This is in part due to the size and geometry of the
material, as well as the parts of the tree used, such as bark and root. A group of waterlogged
archaeological baskets at the Alaska State Museum provided the basis of an investigation into
better PEG protocols for treatment of this material. Ancient baskets treated with 20% PEG 400
and 5% PEG 4000 were not adequately stabilized for exhibition and study. Testing suggests
55% PEG 3350 is a better solution for the remaining baskets in this group still in need of
treatment, and consolidation with 10% Butvar B-98® in ethanol is effective in stabilizing the
fragile baskets that had previously been treated with PEG.
Keywords: polyethylene glycol, PEG, basketry, consolidation, Butvar, waterlogged,
archaeological
1. INTRODUCTION TO PEG TREATMENT FOR BASKETRY
Basketry artifacts discovered in water saturated archaeological sites (wet sites) on the Northwest
Coast of North America have been routinely treated with polyethylene glycol (PEG) since the
1960’s. These artifacts range in age from a few centuries to more than five thousand years old.
The vast literature regarding PEG treatment decisions focuses on the needs of shipwrecked
wood. Basketry treatments utilizing PEG often do not behave in the predicted manner of
waterlogged wood. This is in part due to the size of the woven elements of the basketry
structure, as well as the parts of the tree processed for the fabrication of these artifacts, such as
bark and root. The cellular structure of some basketry material, such as inner bark, differs
enough from trunk wood to require a variation in treatment (Florian 1982, Purdy 1996).
The ideal approach to treatment of archaeological basketry would be to assess the degree of
degradation before treatment and apply the proper PEG protocol. This can be more challenging
for basketry than for wood. One simple method is to air dry a small sample fragment and
observe shrinkage and deformation. Dramatic changes in dimensions from wet to dry can be
expected to correlate to a more deteriorated the cellular structure. Since the complex small
shapes made by the basketry weave can be difficult to measure accurately for comparison before
and after drying, photographing on graph paper can be useful technique. McCawley (1977) has
reported that waterlogged wood in sound or slightly degraded condition shows variation in
shrinkage in the three major directions: 0.5% longitudinally, 3-6% radially, and 5-10%
tangentially. For more deteriorated waterlogged wood, these differences are less distinct.
Another method to determine degree of degradation involves comparing the density of the
archaeological wood to the density of sound, non-waterlogged wood. Archaeological and
waterlogged wood is expected to be less dense because of the structure lost in deterioration.
Methods of quantifying this include the computer program PEGCON (Cooke and Grattan 1990),
and moisture content readings (Boone and Wengert 1998, Hamilton 1998). However, these
methods are less accurate with basketry than with wood. Measuring density is easiest with a
solid chunk of wood. Tiny woven basketry elements are challenging to measure accurately
because of the small size and geometry of the warps and wefts. Moisture content readings
cannot be considered accurate using equipment in a typical conservation laboratory because the
sample size available is so much smaller than recommended. For example, Boone and Wengert
(1998) recommend 100g of oven-dry sample to be used for measuring moisture content. While
this may be possible for waterlogged ship’s timbers, 100g is far greater than the sample
permitted for analyzing a basket, particularly since the analysis is destructive. The weight of a
generous basketry sample that might be available for testing is a mere 0.1 g dry weight (0.5g
fully waterlogged.) In addition to the tiny size, basketry is often made of root or bark, while the
reference standard is trunk wood.
Light microscopy has been used extensively to identify deterioration mechanisms in
archaeological wood. While conservators are trained in the principles and use of the polarized
light microscope, successful analysis of archaeological basketry can be difficult without
specialized training and practice. Most of the important references in the conservation literature
are authored by scientists with considerable backgrounds in plant anatomy and pathology. In
order to examine archaeological wood, familiarity with the structures present in sound wood of
the same species and part of the tree (root, branch, trunk) is needed (Friedman 1978, Florian et
al. 1990). Techniques used by experienced microscopists, such as examination under half
polarized light or fluorescence, and the use of staining may also be helpful (Florian et al. 1990,
Bjordal and Nilsson 2002).
In addition to a firm grasp of wood anatomy, an understanding of the various factors contributing
to archaeological degradation is needed to successfully interpret the images under the
microscope. Micromorphological changes include deterioration of layers in the cell wall, fungal
decay, bacterial attack, impregnation with foreign substances or staining from the burial
environment, missing or eroded structural elements, and even problems with sampling and
mounting techniques (Florian 1990, Hedges 1990, Blanchette et al. 1990, Blanchette and
Hoffmann 1994). It is difficult for a conservator who does not regularly work with wood
anatomy and archaeological material to make a confident analysis of archaeological basketry
with light microscopy. For example, secondary cell wall can sometimes look present when in
fact only amorphous granular residue remains (Hoffman and Jones 1990, Bjordal and Nilsson
2002). Caution is in order for determining degree of deterioration from light microscopy alone.
The conservation literature on the use of PEG to stabilize waterlogged wood indicates several
variables affect PEG treatment: deterioration of the basketry elements due to age, use and burial
environment, species, anatomical structure of the wood (bark, trunk, root etc), concentration of
PEG used, molecular mass of PEG used, duration of soaking, and heating during impregnation.
Low molecular mass PEG (PEG 200-600) is thought to penetrate more deeply into the secondary
cell wall and the smaller spaces in the wood than higher molecular mass PEG. It is also more
mobile and hygroscopic. If too much is used, the surface of the artifact will look wet, feel moist
and soft, attract dust, and be humidity-sensitive. High molecular mass PEG (PEG 1500-6000)
does not penetrate the secondary cell wall because the molecule is too large, but it acts like a
filler, impregnating the lumens and interstices between the cells. Too much high molecular
mass PEG can leave white crusts on the surface, result in a heavy artifact, and be more difficult
to dry. Higher molecular mass PEG is thought to cause structural damage if used on wood with
fairly intact cell wall structure, perhaps from the osmotic pressure as the hygroscopic PEG pulls
water out of the smaller structures where the larger PEG molecule cannot penetrate. (Grattan
1986, Hoffmann 1990). A combination of high and low molecular masses of PEG is often the
solution (Hoffmann1986, Johns 1998, Hoffmann et al. 2004) but it can be tricky to determine the
right mixture for solid wood, and basketry is even more challenging.
A review of the PEG literature and previous treatments at the Alaska State Museum suggests a
bias that basketry materials surviving in the archaeological context have intact secondary cell
wall structure that is available to be bulked. This bias would lead to treatment with low
molecular mass PEG. However, the results indicate that use of predominantly low molecular
mass PEG was not enough to impart the stability needed for study and exhibition.
2. PEG TREATMENTS AT THE ALASKA STATE MUSEUM
Much of the past PEG based treatment for waterlogged basketry on the Northwest Coast has
followed the lead of Gerald Grosso’s 50% PEG 1500 used on Ozette site material. PEG 1500 is
a combination of 41/59 weight percent mixture of PEG 300 and PEG 1450, with an average
molecular mass of 500-600. The name of the product was changed to PEG 540 Blend after
1976. At the Alaska State Museum, several PEG combinations have been attempted, and
comparison is informative, but limited. Caution is needed when comparing the results of
basketry that may be made of different materials, have differing degrees of deterioration, or
suffering from the all-too-frequent challenge of poorly documented treatments.
Fig 1: Castle Hill Basket slowly air-dried without impregnation with PEG
The Castle Hill Basket (Figure 1, 49-SIT-002) is thought to be spruce root and was excavated
damp but not fully waterlogged from a site dating to the Russian-American period (at least 150
years BP) in Sitka, Alaska in 1998. It was not impregnated but slowly air-dried in a refrigerator
with good results. It has an easily readable surface, slightly flexible woody feel and can be
easily handled or flipped for study.
Fig 2: Tawah Creek Basket treated with 50% PEG 540 at 60°C for one month
The Tawah Creek Basket (Figure 2, 49-YAK-019) is thought to be spruce root and was removed
from a waterlogged freshwater site in 2004 in the Yakutat area with fish weir stakes that were
radiocarbon dated approximately 130 years BP. It had a three-dimensional structure when
found, and retained that shape though treatment with 50% Carbowax PEG 540 Blend at 60°C for
one month. It was slowly dried at -35°C in a non-vacuum freezer. Surface appearance and
flexibility are adequate, although the broken edges could benefit from some additional
consolidation.
Fig 3: Spruce root lashings, 0.5cm wide, on the Montana Creek Fish Trap. Likely impregnated
with low concentrations of low, medium and very high molecular masses of PEG. Five of the
diagonal strips are painted Tyvek® reinforcing bands adhered with Acryloid B-72®.
The Montana Creek Fish Trap (Figure 3, 49-JUN-453) was found eroding from a riverbank near
Juneau, Alaska and excavated in 1989-1991. It was radiocarbon dated at 400-600 years BP. The
trap has sizable hemlock and spruce elements, but also basketry-like spruce root lashings.
Treatment notes suggest the trap was impregnated unheated over several months with 10% PEG
200, 5% PEG 1000 and 10% Carbowax Compound 20M. Polyethylene glycol Compound 20M
has an average molecular mass between 15,000 to 20,000 and is not typically used in
conservation. Its use at the Alaska State Museum was experimental based on a recommendation
and free sample from Dow Chemical Company. Due to its size, the trap was slowly air-dried
after impregnation. The trap materials fared very well, with no darkening, but the spruce root
was rather brittle and broken in many places. Small wads of Japanese tissue saturated with a
mixture of wheat starch paste and a small amount of polyvinyl acetate emulsion provided support
and adhesion for the spruce root lashings (Carrlee 2005).
Fig. 4: Detail of the Thorne River Basket under-treated with 20% PEG 400 and 5% PEG 4000 in
need of supplementary consolidation.
The Thorne River Basket (Figure 4, 49-CRG-433) was found as one large fragment in a
waterlogged site on Prince of Wales Island, Alaska in 1994 and radiocarbon dated 5450 years
BP. It was confirmed spruce root and treated with unheated 20% PEG 400 and 5% PEG 4000
over 6 months, then slowly dried at -35°C in a non-vacuum freezer. The basket has a pleasing
appearance but a soft, spongy rubbery quality. It sheds fibers readily and cannot be handled
without risk of breakage or unraveling the weave at the edges.
Fig. 5: Detail of one of the South Baranof Island baskets under-treated with 20% PEG 400 and
5% PEG 4000 in need of supplementary consolidation.
The South Baranof Island baskets from a waterlogged site in Southeast Alaska (49-XPA-78)
were radiocarbon dated at 4,550 years BP. Only one of the six baskets (Figure 5) from this site
has been treated; the other five remain waterlogged pending results of this study. The treated
basket was impregnated with the same protocol as the Thorne River Basket, with similar results.
Surprisingly, this basket was identified by plant anatomist Mary-Lou Florian as mountain
hemlock Tsuga heterophylla root instead of the expected spruce root. There is no known
tradition of weaving with hemlock root (Henrikson and Criswell 2009). The basket is in two
large fragments and about a dozen smaller fragments. Three of the smaller fragments were used
in this investigation to determine an appropriate consolidant for the under-treated Thorne River
and South Baranof Island baskets. Another waterlogged item from the 49-XPA-78 group, a
semi-rigid knotted netting artifact, provided sample material for exploration into a better
impregnation protocol.
3. TESTING HIGHER MOLECULAR MASS PEG FOR BASKETRY
3.1 Objectives of Testing
The shortcomings of the PEG treatment used for the Thorne River and South Baranof Island
baskets revealed the need for a better PEG treatment technique for the remaining baskets found
at the South Baranof Island site. A knotted spruce root netting artifact recovered in hundreds of
fragments provided sample material for testing various concentrations of high molecular mass
PEG. Reconstruction of this artifact is unlikely, and the large number of similar small fragments
give good comparative study samples. All fragments had been stored in distilled water in a
refrigerator since their discovery in 1995. Limited biological growth had occurred in the past.
Water was rarely changed. Since 2006, little biological growth has been noted. All fragments
were fragile. Extreme shrinkage and distortion to an air-dried fragment (figure 7) suggested
advanced deterioration. The testing aimed to answer the following questions:
Can we develop a PEG protocol that will make the waterlogged artifacts in group 95-12 stable
enough for study and exhibition?
What are the optimum concentrations of PEG for this basketry?
What are the optimum molecular masses of PEG for this basketry?
Will increasing the amount of high molecular mass PEG help?
Does heating during treatment provide a benefit?
Will the treated artifact be vulnerable to high humidity?
One set of samples was impregnated in a lab oven at 60°C to evaluate the potential advantages
and disadvantages of heating. Heating may speed and enhance penetration as well as the
solubility of high molecular mass PEG (Grattan and Clark 1987). However, heating was thought
to contribute to undesirable darkening for the objects treated at the Ozette site (Cooke, Cooke
and Grattan 1994). Heat is an accelerant to deterioration and PEG treatments for leather in the
literature have mostly eliminated heat altogether for that reason. Heat is also thought to break
down the PEG molecule, and some sources have advised against heating PEG during the
impregnation (Bilz et al 1994). Christensen (1970) found less osmotic collapse of oak using
PEG 4000 at room temperature than he did with heating. In both cases, no impregnation of the
oak core took place, but collapse only occurred in the hot bath. The Tawah Creek basket at the
ASM was heated with good results. (Carbowax PEG 540 Blend at 50% concentration for a
month at 60°C).
3.2 Selection of Concentrations and Molecular Masses
Samples fell into three main groups: samples treated at room temperature, samples treated at
60°C, samples treated briefly in a 160°C oven and then at 60°C. (This third grouping was the
result of an error that led the samples to be overheated for approximately 12 hours). Each group
had five fragments treated with various concentrations and molecular masses:
20% PEG 400, then 20% PEG 3350
Rationale: PEG 400 should enter the secondary cell wall and bond there, while the 3350 will fill
in the larger voids and give strength. This is slightly higher than the concentration of 3350 PEG
used previously on the South Baranof Island material, but that treatment did not give enough
strength. PEG 400 is kept at 20% to hopefully prevent excess from oozing out. Ozette site
material that was re-treated with 15% PEG 200 and 10% PEG 4000 was the subject of additional
consolidation tests with POLYOX® coagulant, suggesting the PEG treatment was not adequate
(Cooke et al. 1994).
20% PEG 400, then 35% PEG 3350
Rationale: High molecular mass PEG is supposed to perform well on highly degraded wood
(Hoffmann, 1984). The South Baranof Island basketry is very old and treatment with mostly low
molecular mass PEG was not fully successful. This suggests the basketry may be more degraded
than predicted, and may respond better to high molecular mass PEG.
20% PEG 400, then 55% PEG 3350
Rationale: Some references suggest avoiding the eutectic, but others (Jensen et al. 2002) seem to
suggest that aiming for the eutectic is desirable for even distribution. Theoretically, ice crystals
form in a way that blocks even distribution of the PEG unless the eutectic is used. Apparently,
concentrations lower than the eutectic also expand on freezing, causing cracks. At the eutectic,
the 9% expansion of ice is counterbalanced by 7% volumetric contraction of PEG. A medieval
log house in Oslo was treated successfully with 50-55% PEG 4000 (Astrup 1994). The
successful Tawah Creek basket treatment by Scott Carrlee (unpublished, Alaska State Museum)
used PEG 540 near the eutectic.
55% PEG 3350 alone
Rationale: Since the Jensen et al. article (2002) seems to suggest PEG near the eutectic is
optimal if an even distribution is the aim, even though other articles specifically indicate the
eutectic should be avoided, it would be worthwhile to isolate the PEG 3350 to test this. Perhaps
it simplifies the freezing process to only use one molecular mass of PEG. In addition, Astrup
(1994) and Hoffman (1990) found some success in their treatments with around 50% PEG 4000
in degraded softwoods. Strætkvern (2001) reported compression strength of wood is greater for
high molecular mass PEG treatments done without low molecular mass PEG.
20% PEG 400, then 75% PEG 3500
Rationale: Several sources report success with high concentrations of high molecular mass PEG
for highly degraded wood (DeJong 1978, Keene 1982, DeWitte et al. 1984, Jover 1994, Kaenel
1994).
3.3 Testing Protocol
Fragments of similar size with no obvious joins to other fragments were selected for testing and
photographed. Each sample was sewn between layers of nylon mesh screening with polyester
thread to hold the fragment securely, allow good circulation of solution around the fragment, and
permit handling. Each PEG concentration was increased incrementally approximately every two
weeks. PEG 400 was increased in 5% increments, PEG 3350 was increased in 5 or 10%
increments. In each case, the concentrations were increased gradually to minimize the risk of
osmotic shock from pressure differentials between the fluid inside the fragile wood and the fluid
in the container. The time to reach desired concentration took between 3 and 6 months. PEG
3350 was supplied as a powder and was dissolved in a bit of the test solution using a hotplate
before adding it to the unheated and heated sample containers. For the unheated samples, the
addition of the warm PEG 3350 caused them to be cloudy for two to three minutes before
becoming clear again. All samples were removed from solution at the same time. Each sample
was dipped in a beaker of distilled water to rinse excess PEG from the surface and gently tamped
with KimWipes® to remove as much water as possible before freezing. Fragments were
weighed and placed in a non-vacuum freezer (-35°C) to drive off the excess water through
sublimation (solid ice directly to vapor). Air drying without the freezer would send liquid water
to water vapor, and the strong surface tension of liquid water contributes to collapse of cell
structure as the water evaporates (Grattan 1986). Samples were regularly weighed to determine
the end point of drying (when weight no longer decreased,) and fragments were all removed
from the freezer at the same time. Concern about shrinkage or distortion during final air drying
required a method to compare the fragments at this stage to the final result. After removal from
the freezer, fragments were taken out of the nylon mesh and photographed on graph paper
immediately. They were photographed on graph paper again a week later to check for possible
distortion from the evaporation of residual water at room temperature (Figure 6). One month
after they were removed from the freezer, they were subjected to several 12 hour cycles of 80%
humidity to determine if the treatment rendered the fragments vulnerable to changes at high RH.
While the Alaska State Museum has stable RH, there are less stable locations in Alaska that may
wish to exhibit the artifacts after treatment. Exhibition and storage in uncontrolled humidity is a
reality for many PEG treated archaeological baskets.
Fig. 6 Fragment treated with 55% PEG 3350 at room temperature. Photographed on graph
paper immediately out of the freezer (left) and one week later (right) to check for distortion.
3.4 Results and Interpretation:
In this experiment, the percent weight loss in the freezer is used to interpret water loss and
possible impregnation with PEG (Table 1). Theoretically, in comparison to the air-dried control,
lower percent weight loss during drying means less water left in the system, indicating PEG
molecules replaced water molecules during treatment, reducing the amount of water that could
be lost from the structure during drying. According to this theory, all the room temperature
fragments had about the same amount of water loss after drying, and therefore a similar amount
of PEG penetration. At higher concentrations, the heated fragments had less water loss,
indicating better penetration of PEG 3350 than the room temperature samples. Possible
explanations of this greater penetration of molecules that may include: size variation through
thermal breakdown, better diffusion, possible expansion of wood structure with heat to allow
better penetration, or the enhanced solubility of heated PEG. Weight loss in the freezer for the
treated fragments ranged from 10% to 33%, compared to the air-dried untreated fragment which
lost 40% of its weight.
The samples with lowest concentrations were distinctly spongier to the touch than those
concentrations of 55% 3350 and higher, in spite of similar amounts of weight loss. Surprisingly,
results for 20% PEG 400 with 55% PEG 3350 were nearly the same as the results for 55% 3350
alone. Most of the samples showed very little dimensional change after final drying as revealed
by before and after photographs on graph paper. All were within a range acceptable for
successful treatment.
The waterlogged basketry elements (identified as spruce root) were dark brown in color when
waterlogged before treatment. After treatment, the samples treated at room temperature all
appeared a very pale beige-gray or driftwood-like color, with no obvious color difference with
higher concentrations. The samples treated at 60°C were all pale yellow ochre-grayish in color,
but still much paler than most historical basketry. The samples treated at 160°C then 60°C were
a rich brown burnt umber color, ironically more like historical spruce root basketry in color, and
samples treated with higher concentrations of PEG were darker in color. The untreated air-dried
control sample was the darkest of all (dark burnt umber in color) and extremely brittle, shrunken,
and deformed (Figure 7). Almost all samples had some whitish powdery PEG residue/crusts in
the crevices. This did not seem to increase with concentration, but was more pronounced on the
samples impregnated at room temperature. The waxy PEG could not easily be brushed from the
surface (the brush tended to drag it around) but localized application of ethanol with a brush
under magnification seemed to drive the PEG below the surface and improve the appearance.
All impregnated samples were placed in the humidity chamber and raised to 80% RH for 12
hours to evaluate effect of high RH on the concentrations and molecular weights of PEG used.
No oozing or surface changes were observed on the samples or on the blotter paper below them
during this first test. However, when the RH test was repeated, the unheated and the heated to
160°C samples that had been treated with the 75% PEG solution in water turned dark and waxy,
oozing PEG-like material. This did not revert back upon stabilization of the RH, and did not
seem to get worse with repeated RH tests. The sample treated with 75% PEG heated to 60°C did
not ooze or get dark, even on repeated RH fluctuations.
TABLE 1
PEG Concentration Results of treatment at
room temperature
Results of treatment at
60°C
Results of treatment at
160°C (12hours) and
60°C
20% PEG 400
20% PEG 3350
20 days at -35°C
22% weight loss in non-
vacuum freezer
65 days at -35°C
22% weight loss in
non-vacuum freezer
40 days at -35°C
33% weight loss in non-
vacuum freezer
20% PEG 400
35% PEG 3350
40 days at -35°C
23% weight loss in non-
vacuum freezer
90 days at -35°C
21% weight loss in
non-vacuum freezer
40 days at -35°C
25% weight loss in non-
vacuum freezer
20% PEG 400
55% PEG 3350
65 days at -35°C
23% weight loss in non-
vacuum freezer
90 days at -35°C
23% weight loss in
non-vacuum freezer
20 days, at -35°C
22% weight loss in non-
vacuum freezer
55% PEG 3350
90 days at -35°C
23% weight loss in non-
vacuum freezer
65 days at -35°C
18% weight loss in
non-vacuum freezer
20 days at -35°C
22% weight loss in non-
vacuum freezer
20% PEG 400
75% PEG 3350
90 days at -35°C
20% weight loss in non-
20 days at -35°C
10% weight loss in
65 days at -35°C
18% weight loss in non-
vacuum freezer non-vacuum freezer vacuum freezer
Fig: 7: These waterlogged archaeological basketry samples test increasing concentrations of
PEG 3350. Concentrations increase from left to right, with top row representing unheated,
middle row heated to 160°C then 60°C, and bottom row heated to 60°C. Untreated air-dried
sample in upper right.
4. TESTING CONSOLIDANTS FOR UNDER-PEGGED BASKETS
4.1 Objectives of Testing
Identifying a good consolidant for the undertreated baskets was challenging because materials
that might consolidate wood well are not the same as ones that are expected to bond well to a
waxy surface such as PEG. A review of the literature indicated that many of the adhesives said
to bond well with PEG are not conservation-friendly. These included casein glues, hide glues,
hot-set phenolic resin, cold-set urea resin and resorcinol resin (Stamm 1959, Mitchell 1972).
Empirical testing was carried out to examine various potential consolidants commonly available
to conservators and archaeologists.
4.1.1 Testing Protocol
The testing done was empirical in nature, meant to narrow down the possibilities to test on
fragments of the underPEGged basketry. Rice (1990) thinks that PEG chemically interferes with
the formation of bonds between the wood and the adhesive and that PEG gets in the way of
further consolidation with polymers such as acrylics. Testing the bond of potential consolidants
with PEG was one aspect of the empirical testing. PEG 3350 was placed in a disposable
aluminum weighing pan on a hotplate over low heat. Patches of molten PEG 3350 were brushed
onto the ends of two glass microscope slides and allowed to cool. The two patches were then
adhered with a drop of test adhesive. The free end of the top slide was supported by a blank
slide. After drying overnight, the supporting slide was pulled out to cause slight stress on the
join and identify the weakest bonds. Then one slide was picked up and shaken manually to test
the strength of the bond. Finally, the slides were manually pulled apart. Under magnification,
each adhesive was picked at with a sharp tool to test how easily it might peel off the PEG. The
test on glass slides was repeated a second time. An identical test was done with molten PEG
3350 on the surface of flat wooden sticks. Several products were tested that are not ideal for
conservation but may be tempting to archaeologists. Hide glue, cyanoacrylate, wood glue, and
cellulose nitrate were tested because they are mentioned in the hobbyist literature concerning
PEG and green wood and they are more widely available than adhesives which have good aging
properties and are readily reversible. Of those four adhesives, only cellulose nitrate (Duco®)
performed at the level of the final samples.
Results narrowed the field of choices to seven: Acryloid B-72®, AYAT®, Butvar B-98®, BEVA
D-8 dispersion®, Acrysol WS-24®, Lascaux Medium for Consolidation®, and POLYOX®
WSR coagulant. These seven were then tested on silk crepeline and gossamer nylon fabrics by
both pipette dropper and brush application to see how the consolidants might penetrate small
spaces in the textile weave and to reveal qualities of flexibility and glossiness. The final five
consolidants were applied by brush on five small fragments of the South Baranof Island basket
that had been under-treated with PEG. Samples needed to be flipped frequently during drying to
avoid pooling of consolidant on the underside.
4.1.2 Results and Interpretation
Samples that failed at the bond between the two patches of PEG on the glass slides and the
wooden sticks were interpreted as weaker than samples that failed at the PEG/substrate bond.
Samples that did not penetrate into the PEG but formed a skin were considered poor candidates.
Consolidants tested on the fabric were examined for gloss, penetration, and flexibility. On the
archaeological basketry, samples were examined for gloss, darkening, and flexibility in addition
to stabilizing the fragile structure.
4.2 Promising Consolidants Tested on Basketry Fragments
4.2.1 Butvar B-98®
Several sources (Grattan 1980, Sakuno and Schniewind 1990, Schniewind 1990, Spirydowicz et
al. 2001) suggested Butvar B-98® might be successful on archaeological wood not treated with
PEG. Tímár-Balázsy et al. (1998) reports that on textiles, polyvinyl alcohols and polyvinyl
butyrals can get stiffer and the textiles are said to suffer frictional damage from the sharp edges
of the particles when the adhesive become aged, rigid, and cracked. Sakuno and Schniewind
(1990) found the adhesive strength of Butvar B-98® higher than Acryloid B-72® and AYAT®
but less than PVA emulsion. Schniewind and Carlson (1990) also mention that Butvar B-98® is
better than Acryloid B-72® for strength. In the Alaska State Museum testing, 10% Butvar B-
98® in ethanol was the best consolidant choice (Figure 8). It had among the strongest bonds of
all adhesives tested, although weaker on the wooden stick than on the glass slide. It did seem
stronger than Acryloid B-72® when manipulated with the fingers. It penetrated the fabric well,
looked slightly glossy, and was flexible without being brittle, but not as flexible as Lascaux
Medium or Polyox. No noticeable darkening occurred, and the physical appearance of the
basketry was the best of the five consolidants tested on basketry. Butvar B-98® is a polyvinyl
butyral resin manufactured by Monsanto and available through Talas in the U.S.
Fig 8: South Baranof Island basket fragments under-treated with PEG. Top fragment
consolidated with Butvar B-98® 10% in ethanol and bottom fragment unconsolidated.
4.2.2 Acryloid B-72®
Fig. 9: South Baranof Island basket fragments under-treated with PEG consolidated with 10%
Acryloid B-72® in 50:50 acetone and ethanol.
Acryloid B-72® has been recommended as a consolidant for deteriorated archaeological wood
not treated with PEG by several sources (Grattan 1980, Wang and Schniewind 1985, Sakuno and
Schniewind 1990, Schniewind 1990). It also performed well in the reconstruction of an
archaeological fish trap treated with PEG (Carrlee 2005). 10% Acryloid B-72® in 50:50 acetone
and ethanol was tested empirically at the Alaska State Museum and seemed to be the strongest of
all consolidants tested on the PEG-treated basketry (Figure 9). It penetrated the fabric well,
looked slightly glossy, and was flexible without being brittle, but not as flexible as Lascaux
Medium or POLYOX. Some darkening occurred and the surface of the basketry was slightly
glossy. Acryloid B-72® is an ethyl methacrylate (70%) and methyl acrylate (30%) copolymer
manufactured by Rohm and Haas and available through Talas in the U.S.
4.2.3 AYAT
Grattan (1980) did not test AYAT®, but listed AYAC® as his third choice of consolidant for dry
and degraded wood (not PEG treated) after polyvinyl butyrals and acryloid resins. Schniewind
(1990) tested AYAT® on degraded archaeological wood (not PEG treated) and felt it was not
hard enough, only penetrated the surface layer, and caused a notable deepening of color. In the
Alaska State Museum testing, 10% AYAT® in ethanol was one of the better consolidant choices
(Figure 9) and had the best handling properties, flowing smoothly off the brush and wicking
visibly into the basketry fibers during application. On the glass and wood mock-ups, it was
almost as strong as Acryloid B-72® or Butvar B-98® and penetrated into the PEG. It also
penetrated the fabric well, looked slightly glossy, and was flexible without being brittle, but not
as flexible as Lascaux Medium® or POLYOX®. No noticeable darkening occurred, and the
physical appearance of the basketry was similar to the excellent appearance of Butvar B-98®
tested on the basketry. The AYAT® tested was part of the series of polyvinyl acetate resins
manufactured by Union Carbide until recently, and the same as the product mentioned by
Grattan (1980) and Schniewind (1990). However, the products marketed today through
Conservation Support Systems and Talas in the U.S. may not be the same AYAT® available in
the past (Alderson 2008). Investigating the performance of the new AYAT® may be an avenue
of future research.
Fig. 10: South Baranof Island basket fragment under-treated with PEG consolidated with
AYAT® 10% in ethanol
4.2.4 Lascaux Medium for Consolidation®
Lascaux Medium for Consolidation® has not been mentioned in the literature for this
application, but behaved well during the empirical tests. It was used in full concentration as
supplied, and penetrated the fabrics very well. It dried with slight gloss, and was one of the few
samples to fail at the PEG-glass bond instead of the PEG-adhesive bond. However on the
basketry samples it was unacceptably dark and glossy with a rubbery, plastic-like quality when
manipulated with the fingers (Figure 10). It also formed a skin in some interstices of the
basketry, and formed some areas of glossy pooled excess in spite of frequent flipping of the
fragments during drying. Lascaux Medium for Consolidation® is an aqueous dispersion of
acrylic co-polymers based on acrylic ester, styrene, and methacrylate ester manufactured by
Lascaux Colours and Restauro in Switzerland and available through Talas in the U.S.
Fig 11: South Baranof Island basket fragment under-treated with PEG and consolidated with
Lascaux Medium for Consolidation®.
4.2.5 POLYOX® WSR Coagulant
POLYOX® has been used on archaeological material with good results (Bilz et al. 1991, Cooke
et al. 1993). During testing, POLYOX WSR coagulant 2% aqueous solution formed a stringy
mess with very poor handling properties. It was not sticky but made long slimy strings that
could not easily be broken. However, it seemed to penetrate well into the PEG and form a
moderate bond on both wood and glass samples. It also penetrated the fabric very well and dried
with little gloss. On the basketry, POLYOX® darkened the surface slightly, had a slight gloss
and formed a distracting skin in some interstices of the weaving (Figure 12). The POLYOX®
fragment was still very flexible and felt the most fragile of the three fragments tested on basketry
fragments when manipulated with the fingers. The product literature suggests mixing in a 1%
solution, which may have better handling properties, but as a 2% solution was still too fragile a
1% solution was not attempted. POLYOX® WSR coagulant is a non ionic polyethylene oxide
with a molecular mass of 5,000,000 g/mol manufactured by Dow Chemical and provided as a
free sample.
Fig. 12: South Baranof Island basket fragment under-treated with PEG consolidated with 2%
POLYOX® WSR coagulant.
4.3 Other Consolidants Examined
Acrysol WS-24® took a long time to fully dry, but had moderate penetration of PEG and a
moderate bond. When tested on fabrics, it was glossy, formed bubbles that dried in place, and
formed a stiff film that cracked when flexed. Acrysol WS-24® is often used on archaeological
bone.
BEVA D-8® dispersion made a moderate-to-weak bond, and formed a skin that separated
readily from the PEG. Further testing on fabric revealed good flexibility but poor penetration,
with drops made by the pipette drying in place as droplets on the surface.
Carbowax PEG 3350 failed to bond well on both glass and wood tests, although molten high
molecular mass PEG has been frequently mentioned as a surface treatment for artifacts stabilized
with PEG (Grattan 1982, Grattan and Clarke 1987, Singley 1988, Muncher 1991, Rodgers 1992).
CM Bond M-4® formed a moderate bond and seemed to partially penetrate into the PEG but
also formed a skin that separated readily from the PEG.
Jade 403® PVA emulsion was part of the treatment used by Carrlee (2005) for spruce root
lashings of a fish trap treated with PEG. In the current testing, it formed a moderate bond and
seemed to partially penetrate the PEG, but did not dry well.
Klucel G® penetrated well but was weak in all tests at both 2% and 20% in ethanol. It has been
mentioned in treatment of archaeological wood not treated with PEG by Caple and Murray
(1994) and Park (1997).
Lascaux 498 HV® penetrated into the PEG and did not form a separate skin but had a moderate-
to-weak bond.
Rabbit skin hide glue gave a poor bond, did not penetrate well, and was noticeably yellow. Hide
glues had been mentioned in the literature by Stamm (1959) and Rice (1990).
Super Glue® (cyanoacrylate) did not penetrate well and formed a separate skin. It made a
moderate but brittle bond. Has been mentioned in the literature by Zumpe (1981).
Titebond II® wood glue penetrated little, had a poor bond, was slow to dry fully, formed a
separate skin that readily slid off the PEG and was noticeably yellow. Mitchell (1972) did not
think PVA’s worked well to bond wood treated with PEG and Stamm (1959) thought they gave
decreasing strength with increasing PEG concentration. Grattan and Clarke (1987) suggested
PVA emulsions with a little bit of PEG aided bonding PEG treated wood.
Duco® (cellulose nitrate) made a moderate bond on the glass and wood samples and penetrated
well, but lacks good aging properties (Stark 1976).
5. CONCLUSIONS
For the ancient waterlogged basketry from the South Baranof Island site, 55% PEG 3350 is the
best solution for stabilization. The idea that high molecular mass PEG at around 55%
concentration is useful for highly degraded softwoods is in harmony with the conclusions found
by others (Astrup 1994 and Hoffmann 1990). This may indicate that these basketry pieces are
more degraded than previously thought, with little secondary cell wall available for bonding with
low molecular mass PEG. The survival of this material may be due in part to the tenacity of the
lignin. Lignin is often the predominant structural element in archaeological wood (Hedges
1990). In addition, lignin content is typically higher in softwoods than in hardwoods (Bidlack et
al. 1992) and softwood lignin is less easily degraded (Hedges 1990). Ideally, degree of
deterioration ought to be determined before treatment in order to guide the proper protocol, but
this can be difficult and treatment is often done based on previous examples from other sites.
The diminutive size, irregular geometry, and very light weight of basketry fragments make
accurate measurement of density and moisture content difficult. In cases where PEG treatment
has not afforded adequate stability, 10% Butvar B-98® seems to offer enhanced stability without
brittleness or changes in surface appearance. Acryloid B-72® and AYAT® resins may also hold
promise. One of the few references on adhesives for PEG (Rice 1990) recommends solvent-
borne systems that can dissolve into the surface of the PEG, and solvent borne systems did
perform better in the testing on the basketry fragments than aqueous systems. Ongoing research
by the authors seeks to determine if examination of archaeological spruce root and cedar bark
basketry with light microscopy is adequate to determine degree of degradation and predict
correct treatment strategies with PEG. The authors are also compiling a reference of
archaeological basketry treatments one the Northwest Coast of North America to help inform
future treatment of this material. This work will be presented at the 2010 annual conference of
the American Institute for Conservation. An annotated bibliography of articles relevant to PEG
basketry conservation is available at http://ellencarrlee.wordpress.com
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