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87
VII/1/2016
INTERDISCIPLINARIA ARCHAEOLOGICA
NATURAL SCIENCES IN ARCHAEOLOGY
homepage: http://www.iansa.eu
Unrecognized Taphonomy as a Problem of Identifcation and the Scale of
Contamination of Archaeobotanical Assemblages – the Example of Prague –
Zličín Migration Period Burial Ground
Tereza Šálková
a,b,f*
, Alena Dohnalová
c
, Jan Novák
b
, Tomáš Hiltscher
d
, Jaroslav Jiřík
d,e
, Jiří Vávra
f
a
University of South Bohemia, Faculty of Philosophy, Institute of Archaeology, Branišovská 31a, 370 05 České Budějovice, Czech Republic
b
University of South Bohemia, Faculty of Science, Na Zlaté stoce 3, Laboratory of Archaeobotany and Palaeoecology, 370 05 České Budějovice, Czech Republic
c
Masaryk University, Faculty of Science, Department of Geological Sciences, Kotlářská 2, 611 37 Brno, Czech Republic
d
Prácheň Museum in Písek, Velké náměstí 114, 397 24 Písek, Czech Republic
e
Charles University in Prague, Faculty of Arts, Institute of Prehistory and Early History, Celetná 20, 116 36 Praha 1, Czech Republic
f
Labrys, o. p. s., Hloubětínská 16/11, 198 00, Praha 9 – Hloubětín, Czech Republic
1. Introduction
The role of plants in the burial rites of diferent societies
can be studied through analyses of their remains recovered
from grave deposits (Hansson, Bergström 2002). However,
the problems of intrusion and residuality in archaeobotany
are most acute in periods in which plant assemblages are
generally less abundant than in others (Pelling
et al.
2015).
For example, a low density of carbonized and mineralized
macroremains (with contaminants) has been demonstrated
in open settlement sites with a long history of human
occupation, cultivation, grazing, and bioturbation. The
spectra of macroremains found there are often, at least
partially, “mixed” or contaminated due to depositional and
post-depositional processes (Borojevic 2011).
By studying an assemblage of plant remains from partially
wet sediments in the Migration Period graves at Prague
Zličín (Jiřík
et al
. 2015), we have shown that the same can
also be true for burial sites situated in an area with a history
of long-term occupation. The archaeobotany of Migration
Period burial grounds in central Europe is very rare (
e.g.
Hopf 1979; Theune-Großkopf 2010), and our research at
the large burial ground in Prague Zličín is therefore unique.
Rigorous sampling of excavated sediments has been applied
(Figure 1), and three types of archaeobotanical materials
studied: plant diaspores, charred and uncharred wood, and
pollen with non-pollen polymorphs.
The aim of this research is to:
•
determine the relationship between various types of
plant remains, and their positions in graves (
e.g.
cofn,
looting shaft, various layers of the infll);
•
reconstruct the process of plant intrusion and
residuality at the site;
Volume VII ● Issue 1/2016 ● Pages 87–110
*Corresponding author. E-mail: terezasalkova@seznam.cz
ARTICLE INFO
Article history:
Received: 7
th
December 2015
Accepted: 28
th
November 2016
Key words:
archaeobotany
contamination
plant macroremains
wood
charcoal
pollen
graves
Migration Period
ABSTRACT
This research aimed to compare diferent sources of botanical material obtained from the infll of
Migration Period graves (Vinařice group, 5
th
century and the turn of 5
th
and 6
th
century AD) in Prague
Zličín during 2005–2008. From a total number of 173 excavated graves with 176 burials, 74 were
sampled for archaeobotanical analyses, and these are the subject of this contribution. All of the
researched graves were robbed shortly after the time of burial. The archaeobotanical approach was
applied through three methods: macroremains analysis; anthracology – xylotomy; and pollen analysis.
The samples had low densities of plant macroremains, and contained many residuals and contaminants
which had penetrated the graves’ infll. Only a fragment of the pollen samples was positive. Knowledge
about the penetration of intact features by earlier and later plant remains was of major importance in
the development of the methodology used for this research in the graves.
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
88
•
reconstruct the burial rite, with a focus on the role of
plants;
•
reconstruct the vegetation of the area during the “life”
of the burial ground.
2. Background information about the site
Rescue excavations in Prague Zličín (2005–2008) uncovered
a multi-period site with a number of settlement features
from farming pre- and protohistory, and 176 burials in
173 graves – dated to the 5
th
century AD and the turn of
the 5
th
and 6
th
century – belonging to the Migration Period
Vinařice group (Vávra
et al.
2012, 3, Figure 2). The burial
ground represents the largest inhumation cemetery from the
early phase of the Migration Period excavated in Bohemia
up to now (Svoboda 1965, especially list of grave yards at
pp. 237–295), and it is also one of the largest cemeteries in
central Europe (Figure 1). The assemblage of the grave goods
from the Prague Zličín graves refects a material culture
from the greater part of the 5
th
century, a dating which is also
supported by radiocarbon dates on human skeletal material.
The wide spectrum of the fnds demonstrates extensive
contacts with various parts of the Barbaricum, as well as
the (former) Roman provinces (
i.e.
“barbarian kingdoms”
on Roman territory). Within the relative chronology, the
dating of the site can be attributed to the phases D2–D3/E1
sensu
J. Tejral (Vávra
et al
. 2012, 1–3). Accordingly, it was
hoped that the site would ofer a unique set of information
about burial processes and the life of the inhabitants of the
Bohemian Basin during the Migration Period.
Settlement features from other than the Migration Period,
located among the graves (Vávra
et al.
2012, Figure 2), can
be attributed to the Bronze Age and/or to a wide category
of “farming prehistory”. The artefacts recovered from all
depths of the features of the Migration Period graves date
the occupation of the site more closely. They point to the use
of the area during the Neolithic, Late Neolithic, Late Bronze
Age and La Tène Period (Vávra, Kuchařík 2015, 123).
Occupation of the area from the Late Iron Age to the Early
Figure 1.
Prague Zličín; plan of the excavation. Blue – graves with foated samples, green – graves with pollen analysis, yellow – graves with both foated
samples and pollen analysis.
0 100 m
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
89
Roman Period could be attested by a fragment of animal
bone from grave no. 142 dated by AMS (see results).
It is very important to stress that almost all of the graves
in Prague Zličín had been reopened and robbed in ancient
times, as is often the case (Vávra, Kuchařík 2015, 130–147).
There is factual uncertainty about the flling mechanism
used for the looting shafts. This probably difered in each
case. Assumptions as to the flling of the shafts can only
be made in connection with the physical evidence at the
site. This is due to the fact that the depths of the graves are
variable (see above), and if left open (which seems more
probable-given the humous character of the infll, which is
clearly diferent in comparison to the backfll of the grave
itself-than the possibility that the looters found the time to
refll the open grave) then the time necessary for the shaft
to be flled would difer according to the individual extent
of the secondary intervention, and also perhaps the slope of
the terrain. Without radiocarbon dating of specially-selected
plant macroremains, which would indicate contamination by
earlier residua as well as later intrusions, interpretation of the
assemblage of plant remains is virtually impossible.
Regardless of these circumstances, the material from Prague
Zličín represents an important body of data on the plant use
and vegetation in diferent time periods, as well as information
about cofn manufacture, possible looting equipment directly
connected to the robbing of these graves, and the dating of
these events (see Vávra
et al.
2012, 3, 10–13, Table 1).
The graves, varying in depth (0.12–2.6 m), disposition
and presence of grave goods, provided variable chemical
conditions for the preservation of their organic material. The
analyses of the archaeological fnds from the graves revealed
a wide range of organic, usually perishable, fnds in several
dozens of cases. Apart from the bones of the deceased, they
included bone or antler artefacts (
e.g.
grave no. 54, 113), hair/
fur/scalp (grave no. 11), leather (
e.g.
graves no. 132, 152),
textile or its imprint (
e.g.
grave no. 143 and 172), fragments
of wooden handles of knives, and an arrow shaft. All of
these fnds were preserved due to the increased humidity
of the sediment (wet, but not waterlogged), or by metal
corrosion products (
e.g.
oxides and sulphides of copper), if
connected to the metal fnds. The frst group, preserved due
to the higher soil moisture, included non-carbonized wood
(interpreted as remains of the cofns, grave goods such as
wooden dishes or furniture, and tools-like hoes, shovels and
torches-used for looting). A similar scale of artefacts was
reported, for example, from the unique grave-chamber of
Poprad-Matejovce, dated to the late 4
th
/early 5
th
century AD
(Lau, Pieta 2014), where the exceptionally good preservation
of the grave chamber was possible due to the waterlogged
conditions. In the second group, carbonized diaspores and
wood which was connected with the use of fre in the area
of the burial ground, or in its hinterland, at the time of
human activities at the site, were found. A direct connection
between the burial rite and the remains of carbonized plants
was impossible without a radiocarbon dating of all fnds.
3. Material and methods
3.1 Material
The evaluated assemblage is comprised of various
types of plant remains obtained from two main types of
contexts: funerary and settlement deposits of diferent
age. Macroremains are represented by seeds of cultivated
and wild plants, cereal chaf, leaves of conifers,
etc.
, and
fragments of wood, preserved in charred, waterlogged, and
mineralised form. Pollen grains represent the microremains.
3.1.1 Graves
Plant macroremains were recovered from sediment samples
collected at diferent parts of the infll of the various graves:
all together 614 samples from 53 graves. Samples were
taken to obtain both botanical macroremains and small
artefacts. Due to the low density of plant remains per sample,
and for better evaluation and interpretation of results, they
were divided into 5 groups. These groups are: infll of the
cofns and/or the bottom parts of graves (R); upper infll
of the graves (J); plunderers’ shafts (S); and “transitional”
or uncertain contexts of unknown or mixed depth within
upper grave infll or plunderers’ shafts (JS); and, cofns or
plunderers’ shafts (RS; Table 2; Figure 2). In three graves
(nos. 9, 11, 12), larger remains of wooden cofns were
documented
in situ.
From cleaned surfaces of the profles of the 34 graves,
95 samples were placed in small boxes and analysed for
pollen (Table 1).
Figure 2.
Prague Zličín; model grave with
base contexts. (R and blue – cofns, J and
green – graves infll, S and orange – looting
shafts, RS and JS – borders between cofn/
looting shaft or between cofn/grave infll).
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Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
90
Table 1.
Prague Zličín; list of graves with samples analysed by method of macroremains analysis, charcoal/wood analysis and pollen analysis. (In parentheses
is the number of pollen samples with more than 100 determinations).
Grave numberSamples volume
(fotation)
Macroremains
samples count
Charcoal/wood
samples count
Pollen sample
count
Positive pollen
samples count
Negative pollen
samples count
4
18061
11
15064
17
111
20
111
31
3011
67
3
12
97
30112
2
107
8 8
108
5
14
109
5
23
112
3
21
113
3
3
114
4
31
115
2
2
116
1
1
117
5
23
118
1
1
119
5
23
120
11
11 (1)
121
3
21
122
4
13
123
6
3 (2)3
124
1
1
127
3
12
128
3
21
130
3011321
131
2
11
132
80029131
1
133
335133
134
390174
135
270103
136
1,1183518
137
15562
138
395125
139
301
1
1
140
7
16
141
9253515
142
8
2
1
1
143
44515151
1
144
12542
145
354122
146
4901651
1
147
5522
148
370122
149
3701052
2
150
30415101
1
151
362145
152
175113
153
4901910
154
28510322 (1)
155
360116
156
450154
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
91
Grave numberSamples volume
(fotation)
Macroremains
samples count
Charcoal/wood
samples count
Pollen sample
count
Positive pollen
samples count
Negative pollen
samples count
157
2
11
158
30091
159
3871914
160
390152
161
323132
162
33022
8
163
516195
164
7993215
165
190
7
166
331174
167
173105
168
180136
169
9752
170
110421
1
171
4162215
172
395203
173
163
7
6
174
245
8
3
175
294156
176
377164
177
14042
178
3011
74 graves15,351 litre53 graves/
614 sampels
49 graves/
252 sampels
34 graves/
95 samples
25 graves/
33 samples
30 graves/
62 samples
Table 2.
Prague Zličín; list of individual types of contexts and their properties (number of samples and their volume, number of carbonized, non-carbonized/
waterlogged macroremains and their concentration – average number per litre of sediment).
Number of
samples
Sediment
volume (l)
CarbonizedNoncarbonized/
waterlogged
Carbonized
concentration
Noncarbonized/
waterlogged
concentration
cofns and bottom of graves (R)
1874,1811025480.0240.131
graves backflling (J)
962,7711114810.0390.169
plundering shaft (S)
2015,105673980.0240.144
cofns and bottom of graves/
plundering shaft (RS)
1142,841133
888
0.0260.174
graves backflling/ plundring
shaft (JS)
15426201250.0470.293
roads (C)
91500
7
0.0000.047
other features (X)
22569245890.0421.035
summary644 samples16,043 litre
4573036
0.0290.285
Table 1.
Prague Zličín; list of graves with samples analysed by method of macroremains analysis, charcoal/wood analysis and pollen analysis. (In parentheses
is the number of pollen samples with more than 100 determinations). (
Continuation
)
3.1.2 Settlement features
An assemblage of 31 samples was also collected and
analysed from other than funerary deposits. Of these,
22 samples came from settlement features, and nine from
excavated remnants of a road (the “trackway”). Ten samples
were studied by anthracology and xylotomy: two samples
from the road, and eight samples from settlement features.
Roads (features 816, 1588 and 1553; in Tables and Figures
marked as C) were flled by humid soils before the cemetery
was founded in the 5
th
century AD, and evaluated overall.
The road was dated to “agricultural prehistory”, but feature
no. 816 was of an earlier date than the excavated graves,
indicated by its superposition relative to three of them. One
settlement feature (no. 1542) was dated based on ceramic
typology to the Late Bronze Age; other features (nos. 1584,
1606, 1607 and 1608; in Tables and Figures marked as X)
were dated based on material culture only as “agricultural
prehistory” (Table 2). Three samples were obtained from
settlement features numbers 794 and 813 and analysed by
pollen analysis methods.
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Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
92
3.2 Methods
Plant macroremains and wood and charcoal fragments were
extracted from archaeological sediments by water fotation.
A fotation tank (modifed ANAKARA type; Pearsall 1989)
was used for fotation at the time of excavation (573 samples,
15,303 litres; 21 samples of visible plant remains were hand-
picked directly during excavation). The manual technique of
fotation was used in the laboratory for extraction of samples
from the close proximity of bones and artefacts (48 samples,
48 litres). The light fraction was collected on sieves with mesh
sizes of 0.25, 0.4, 1.0, 2.0 mm, and mineral residuum on the
mesh of 1 mm. Both foat and heavy fractions were sorted in
full, and analysed under a stereomicroscope. Determination
of all plant macroremains is based on a wide range of standard
literature,
e.g.
Berggren (1981); Anderberg (1994); Cappers
et al.
(2006; 2009) and a comparative seed collection. In this
analysis, NISP (Number of Identifed Specimens) was used
as the primary method of quantifcation.
Analysis of charcoals and wood was performed only on
fragments from the large fraction (>2 mm) and only randomly
selected samples were analysed. Smaller charcoal pieces, that
were not taxonomically identifable, were excluded because
they seldom provide useful palaeoecological information
(
e.g.
Robin
et al.
2014). Charcoal and waterlogged wood
were analysed with the use of an episcopic interference
microscope with 200–500× magnifcation. Identifcation
Figure 3.
Prague Zličín; AMS radiocarbon
dating. Calibration: H – human bones, A –
animal bones. Calibration 95.4% (Bronk
Ramsey 2013, Reimer
et al.
2013).
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
93
according to taxa was done with the help of a reference
collection and standard identifcation literature (Greguss
1972; Schweingruber 1990). Charcoals were quantifed as
the number of analysed fragments.
Pollen samples were prepared by laboratory treatment of
the sediment (1 cm
3
) using the standard method of HCl, HF,
KOH and acetolysis (Erdtman 1960). The resulting macerated
product was, due to a higher yield of palynomorphs,
concentrated in a heavy liquid (ZnCl
2
) and observed in
this medium on a biological specimen slide (26×76 mm)
covered with a glass slip (22×22 mm). Identifcation of
palynomorphs and non-pollen objects was based on a
wide range of publications, including Beug (2004), Boros,
Járai-Komlódi (1975), Ellis, Ellis (1985), Erdtman (1957),
Erdtman
et al.
(1961), Komárek, Jankovská (2001), Moore
et al.
(1991), Reille (1995), Thomma (2003), Van Geel,
Aptroot (2006). The total pollen diagram was created using
the POLPAL program (Walanus, Nalepka 1999). The basic
sum of all the woody species (arboreal pollen – AP) as well
as herbs (non-arboreal pollen – NAP) representing 100%
(total sum – TS) was used for calculation of the percentage
of individual types. A portion of ferns was not included into
the calculation, but it was evaluated.
Ten samples of organic remains – two samples of wood
from cofns, three animal bones, two human bones, one
carbonized caryopsis of barley, and two noncarbonized seeds
(of fg and cofee) were radiocarbon dated using accelerator
mass spectrometry at the Centre for Applied Isotope Studies,
University of Georgia and Poznań Radiocarbon Laboratory
(Figure 3; Table 3). Data were calibrated by OxCal v4.2.4
(Bronk Ramsey 2013) using the IntCal13 calibration curve
(Reimer
et al.
2013).
In order to consider the main patterns in the
archaeobotanical datasets-in terms of position within the
graves-multivariate statistical methods were used (Canoco
v. 5; ter Braak, Šmilauer 2002). Logarithmic transformation
of the percentage data and centering by species was used for
all ordinations. Detrended Correspondence Analysis (DCA)
was performed on the whole dataset, as the preliminary DCA
showed that length of the gradient was sufcient (6.69 for
macroremains and 3.79 for wood and charcoal). Canonical
Correspondence Analysis (CCA) was used to test how much
variability in the archaebotanical datasets can be explained
by the position of the sample in the grave.
4. Results
Radiocarbon data obtained from the graves showed
the complicated development of sediments inside them
(Figure 3 and Table 3). An earlier occupation of the site was
also refected by residuals of ceramic vesels (Neolithic, Late
Neolithic, Late Bronze Age and La Tène Period).
4.1 Plant macroremains
In total, 644 samples from the site were analysed for plant
macroremains. Of these, 614 samples came from 53 graves
(volume 15,351 litres) (Tables 1 and 2), 22 samples
from seven settlement pits (volume 150 litres), and nine
samples from the infll of the road (569 litres). More than
16,000 litres of sediments were foated. A total of 3,493
macroremains were counted (457 carbonized; 3,036 non-
carbonized/waterlogged; Table 2). About 67 carbonized and
103 non-carbonized taxa were recorded (Tables 4, 5 and 6).
Settlement features were dated to the Late Bronze Age or to
“agricultural prehistory”, and graves to the Migration Period,
but many intrusions were also documented. The density of
plant macroremains per litre of sediment in all samples was
very low, but within groups of contexts (R, RS, J, S, JS, C,
X) it was similar (Table 2).
4.1.1 Graves
The average values of carbonized macroremains were
similar for samples from cofns, from the bottoms of graves
(R), grave backflls (J) and plunderers’ shafts (S). In samples
from boundary groups (RS and JS) the values were higher
(Figure 4). Average values of non-carbonized macroremains
were similarly low for samples from cofns and the bottoms
of graves (R) and grave backflls (J). In samples from
plunderers’ shafts (S) and from the boundaries of plunderers’
shafts (RS and JS), average values were higher (Figure 4).
The structure of individual categories of samples was similar
(Figure 5). Among carbonized macroremains, useful plants
were dominant. Remains of weeds and ruderals were also
Table 3.
Prague Zličín; AMS radiocarbon data.
SampleLab. codeGrave/feature numberMaterialBCBC/AD cal.
521_woodPoz-64638gr. 12cofn1600±30 BP399–539 AD, 95.4%
519_woodPoz-64639gr. 11cofn1570±30 BP416–557 AD, 95.4%)
1524_dogPoz-64641f. 1524
bone, dog
1550±30 BP423–574 AD, 95.4%
573_hPoz-64642gr. 55
bone, human
1630±30 BP346–36 AD, 95.4%
573_aPoz-64644gr. 55
bone, animal
1505±30 BP431–635AD, 95.4%)
1555_hPoz-64645gr. 142
bone, human
1570±30 BP416–557 AD, 95.4%
1555_aPoz-64646gr. 142
bone, animal
1970±30 BP45 BC–85 AD, 95.4%
1333_barleyPoz-64640gr. 175
caryopsis, barley
75±30 BP1690–1925 AD, 95,4%
1491_cofeeUGAMS 20578gr. 31cofee bean
recentrecent
1204_fgUGAMS 20579gr. 164seed, fg210 BP±251646 AD – recent, 93%
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Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
94
frequently refected. Remains of plants which grow in
diferent types of grasses were common. Remains of wood
plants were rare in all categories. Among non-carbonized
macroremains, weeds and ruderals were dominant. Remains
of plants typical for forests and grasslands were present.
The category of neophytes, or imports, is problematic and
minimal. Remains of useful plants are rare.
Remains of
carbonized useful plants
are similar in
each category (Table 4). The remains of cereals (
Hordeum
vulgare
,
Panicum miliaceum
,
Triticum aestivum
, cf.
Triticum
dicoccum
,
Triticum spelta
,
Secale cereale
,
Avena
sp.)
are more numerous then remains of pulses, except for the
boundary area between grave backflling and plunderers’
shafts, where pulses prevail (Figure 6). Pea (
Pisum sativum,
Vicia/Pisum
) is most numerous, followed by lentil (
Lens
culinaris
), but their frequency in individual categories is
similar. Seeds of Faba bean (cf.
Vicia faba
) were found only
in one sample from a plunderer’s shaft.
Damage to cereal grains due to poor preservation was
high. In assemblages from R, RS and J 50% of cereal grains
(
Cerealia
) could not be determined
(Figure 7). The grains
of barley (
Hordeum vulgare
/
Hordeum vulgare
var.
vulgare
)
were the most abundant in all contexts. Also present in
all contexts, though in smaller quantities, were grains of
Figure 4.
Prague Zličín; concentration of carbonized/non-carbonized plant macroremains (average number per litre of sediment) in individual parts of the
graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between cofn/looting shaft or between cofn/grave infll).
Figure 5.
Prague Zličín; reconstruction of individual eco-groups among the carbonized (c)/non-carbonized (n) plant macroremains in individual parts
of the graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between cofn/looting shaft or between cofn/grave infll; depicted in
percentages).
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
95
Table 4.
Prague Zličín; remains of carbonized useful plants and non-carbonized useful plants, and neophytes of imports, in individual parts of the graves
(R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between cofn/looting shaft or between cofn/grave infll).
CarbonizedNon-carbonized
UsefulUsefulNeofyt/import
R
Avena
sp. 1, Cerealia 16, Cerealia/Fabaceae (pulses) 1,
Hordeum
vulgare
4,
Hordeum vulgare
var.
vulgare
8,
Lens culinaris
2,
Panicum miliaceum
7,
Panicum/Setaria
1,
Pisum sativum
2, cf.
Secale cereale
1,
Triticum
sp. 1,
Triticum aestivum
3,
Triticum
cf.
spelta
2,
Vicia/Pisum
10
Brassica campestris
1,
Carum carvi
2,
Cerealia (straw) 1,
Hordeum vulgare
var.
vulgare
1,
Hordeum vulgare
var.
vulgare
(rachis) 2,
Humulus lupulus
1,
Panicum/Setaria
1,
Papaver somniferum
1
Amaranthus
sp. 24,
Helianthus
sp. 2
RS
Cerealia 22,
Hordeum vulgare
5,
Hordeum vulgare
var.
vulgare
10,
Lens culinaris
1,
Panicum miliaceum
5,
Pisum sativum
1, cf.
Secale
cereale
1,
Triticum
cf.
aestivum
1,
Triticum spelta
1,
Triticum spelta
(spikelet fork) 1,
Vicia/Pisum
22
Carum carvi
2, Cerealia 1, Cerealia (straw) 2,
cf.
Humulus lupulus
1
Amaranthu
s sp. 39,
Cofea
cf.
arabica
1,
Helianthus
sp. 9,
Prunus persica
J
Avena
sp. 1, Cerealia 15
, Hordeum vulgare
(rachis) 1,
Hordeum
vulgare
5,
Hordeum vulgare
var.
vulgare
6,
Triticum
sp. 1,
Triticum
cf.
aestivum
1, cf.
Triticum dicoccum
4,
Lens culinaris
1,
Pisum
sativum
4,
Vicia
cf.
faba
1,
Vicia/Pisum
4
Carum carvi
1,
Hordeum vulgare
var.
vulgare
(rachis) 1
Amaranthus
sp. 57,
Ficus
carica
1,
Helianthus
sp. 1,
Pistacia vera
1
S
Avena
sp. 1, Cerealia 39,
Pisum/Vicia
1,
Hordeum vulgare
(rachis)
1,
Hordeum vulgare
8,
Hordeum vulgare
var.
vulgare
1,
Lens
culinaris
2,
Panicum miliaceum
9,
Panicum/Setaria
1,
Pisum
sativum
3,
Triticum
sp. 1,
Triticum aestivum
3,
Triticum compactum
1, cf.
Triticum dicoccum
1,
Vicia/Pisum
5
Avena
sp. 1,
Hordeum vulgare
var.
vulgare
1
Amaranthus
sp. 61,
Helianthus
sp. 6,
Thuja
plicata
1
JS
Cerealia 1,
Hordeum vulgare
1,
Pisum sativum
2,
Triticum
sp . 1,
Vicia/Pisum
3
Amaranthu
s sp. 2
Figure 6.
Prague Zličín; relation among
remains of cereals and pulses in individual
parts of the graves (R – cofns, J – graves
infll, S – looting shafts, RS and JS – borders
between cofn/looting shaft or between
cofn/grave infll).
Figure 7.
Prague Zličín; relation among
determined and undetermined remains of
cereals in individual parts of the graves (R
– cofns, J – graves infll, S – looting shafts,
RS and JS – borders between cofn/looting
shaft or between cofn/grave infll).
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
96
Figure 8.
Prague Zličín; structure of cereals in individual parts of the graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between
cofn/looting shaft or between cofn/grave infll, depicted in percentages).
Table 5.
Prague Zličín; carbonized and non-carbonized remains of weeds and ruderals in individual parts of the graves (R – cofns, J – graves infll, S –
looting shafts, RS and JS – borders between cofn/looting shaft or between cofn/grave infll).
CarbonizedNoncarbonized
Weeds and ruderal
R
Agrostemma githago
1,
Chenopodium
album
11,
Chenopodium hybridum
1,
Malva
cf.
neglecta
1,
Brassica
sp. 1,
Galium
sp. 1,
Lamiaceae
1
Aethusa cynapium
5,
Arenaria serpyllifolia
2,
Atriplex
sp. 19,
Avena fatua
(spikelet) 1,
Echinochloa crus-galli
5,
Fallopia convolvulus
19,
Fumaria ofcinalis
10,
Galium
sp.
2,
Chenopodium album
213,
Chenopodium fcifolium
3,
Chenopodium
sp. 2,
Persicaria
hydropipe
r 1, Polygonaceae 2,
Polygonum aviculare
51,
Setaria
sp. 1,
Setaria viridis
3,
Silene alb
a 1,
Silene
cf.
noctifora
3,
Silene
sp. 11,
Sinapis arvensis
1,
Stellaria media
1,
Tripleurospermum maritimum
2,
Veronica hederifolia
27,
Veronica
sp. 8
RS
Galium
sp. 1,
Galium spurium
2,
Chenopodium album
8,
Chenopodium
sp.
8, P
olygonum aviculare
1,
Setaria
sp. 2,
Silene
cf.
alba
2
Aethusa cynapium
6,
Anthriscus caucalis
1,
Atriplex
sp. 17,
Echinochloa crus-galli
14,
Fallopia convolvulus
16,
Fumaria ofcinalis
16,
Galium spurium
1,
Chenopodium
album
164,
Chenopodium fcifolium
1,
Chenopodium
sp. 4,
Lactuca seriola
1,
Neslia
paniculat
a 2,
Panicum/Echinochloa/Setaria
fragment 1, Polygonaceae 2,
Polygonum
aviculare
32,
Setaria
sp. 2,
Setaria viridis
1,
Silene
sp. 3, S
tellaria media
2,
Thlaspi
arvense
2, T
ripleurospermum maritimum
9,
Veronica hederifolia
16
J
Fallopia convolvulus
1,
Chenopodium
album
6,
Chenopodium
sp. 1,
Silene
cf.
alba
1,
Solanum nigrum
1
Aethusa cynapium
4,
Atriplex
sp. 24,
Ballota nigra
1, Brassicaceae 1,
Echinochloa
crus-galli
1,
Fallopia convolvulus
9,
Fumaria ofcinalis
9,
Chenopodium album
132,
Chenopodium fcifolium
2,
Chenopodium
sp. 8,
Lactuca
sp. 1,
Neslia paniculata
1,
Papaver rhoeas
2,
Polygonum aviculare
13, Polygonaceae 2,
Setaria
sp. 1,
Silene alba
1,
Silene
sp. 8,
Stellaria media
2,
Thlaspi arvens
e 1,
Urtica dioica
1,
Veronica hederifolia
12,
Veronica
sp. 1
S
Anagallis arvensis
1,
Galium
sp. 2,
Galium spurium
2,
Chenopodium
album
1,
Chenopidium fcifolium
1,
Chenopodium hybridum
1,
Chenopodium
sp. 2,
Neslia paniculata
3,
Polygonum
aviculare
1,
Polygonum lapathifolium
1,
Solanum nigrum
1,
Solanum dulcamara
1,
Veronica hederifolia
2
Aethusa cynapium
13,
Arenaria serpyllifolia
1, 1,
Atriplex
sp. 24,
Echinochloa crus-galli
5,
Fallopia convolvulus
28,
Fumaria ofcinalis
22,
Galium
sp. 2,
Chenopodium album
407,
Chenopodium fcifolium
3,
Chenopodium hybridum
1,
Chenopodium
sp. 3,
Lactuca
seriola
1,
Polygonum aviculare
57,
Polygonum aviculare
(mineralised) 2,
Polygonum
lapatifolium
1,
Setaria viridis
1,
Setaria/Echinochloa
sp. 1,
Silene
sp. 29,
Stellaria media
2,
Thlaspi arvense
4,
Tripleurospermum maritimum
2,
Veronica hederifolia
51,
Veronica
sp. 2
JS
Fallopia convolvulus
1,
Chenopodium
album
3,
Viola
sp. 1
Echinochloa crus-galli
1,
Euphorbia helioscopia
1,
Fallopia convolvulus
10,
Fumaria
ofcinalis
2,
Chenopodium album
63,
Polygonum avicular
e 19,
Setaria
sp. 1,
Silene
sp.
1,
Veronica hederifoli
a 6,
Veronica
sp. 1
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
97
naked wheat (
Triticum aestivum/compactum
), as well as oat
(
Avena
sp.). Millet (
Panicum miliaceum
) was concentrated
in samples from cofns and the bottoms of graves (R), in
the boundary area between cofns and plunderers’ shafts
(RS), and from shafts (S), whereas rye (cf.
Secale cereale
)
and spelt (
Triticum
cf.
spelta
) were found only in side cofns
(R and RS), and emmer (cf.
Triticum
dicoccum
) was only in
grave inflls and in shafts (J and S; Figure 8).
Remains of
non-carbonized useful plants
were not
numerous: amounting to about 2% of the samples from the
cofns (R and RS). In other samples the ratio of useful plants
was under 1% of non-carbonized remains (Table 4). Remains
of barley (
Hordeum vulgare
/
Hordeum vulgare
var.
vulgare
)
were found in all categories (R, S, J), Cerealia found in the
cofn samples (R and RS), and remains of oats (
Avena
sp.)
found in the shafts (S). Seeds of
Carum carvi
were found
in cofns (R and RS) and in inflls (J). Seeds of
Humulus
lupulus
(R and RS), as well as
Brassica campestris
and
Papaver somniferum
(R), were only found inside cofns.
Some remains from the category of
imports/neophytes
are considered as useful plants.
Amaranthus
sp. and
Helianthus
sp. were found in samples from all categories
(R, RS, J, S, JS). Remains of
Cofea
cf.
arabica
and
Prunus
persica
were found in the RS category, while remains of
Ficus carica
(Figure 9) and
Pistacia vera
were only found
in the infll of graves (J), while the remains of
Thuja plicata
were documented in plunderers’ shafts (S).
Carbonized remains of
weeds and ruderal plants
were
frequently refected. Among non-carbonized macroremains, the
category of weeds and ruderal plants was dominant (for details,
see Table 5). Among the carbonized macroremains, in many
determinations it was only possible to estimate to the genus
because of the degradation of individual seeds and fruits.
A list of plant remains which can grow in diferent types
of
grasslands
is in Table 6. The concentration of carbonized
remains was generally higher than non-carbonized remains
(categories R, J, S and JS).
Non-carbonized remains of
woody plants
were present
more frequently than carbonized macroremains (for details
see Table 6). Fragments of non-carbonized needles (
Abies
alba
,
Picea abies,
Abies alba
) were present in all categories
except JS. Seeds of
Betula pendula
were frequently present
among non-carbonized remains, but were rare among
carbonized remains (only R). A non-carbonized nut of
Tilia
sp. was found in grave infll. A carbonized seed of
Rubus
sp.
and non-carbonized seeds of
Sambucus nigra
,
S. racemosa
and
Sambucus
sp., as well as remain of
Galeopsis tetrahit/
bifda
, were found in samples from plunderers’ shafts.
Many plant remains were not able to be included in any
eco-groups due to unclear identifcation – mostly because
Table 6.
Prague Zličín; remains of carbonized and non-carbonized remains of grasslands, forest, and non-categorized remains in individual parts of the
graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between cofn/looting shaft or between cofn/grave infll).
CarbonizedNon-carbonized/waterlogged
GrasslandForest
Non-categorizedGrasslandForestNon-categorized
R
Asteraceae 1, Poaceae
1, Poaceae (straw) 3,
Trifolium
cf.
dubium
1,
Trifolium/Medicag
o 1,
Vicia cracca
1,
Vicia
sp. 3
Betula pendula
1
Apiaceae 1,
Asperula cynanchica
1, cf.
Carex
sp. 2, cf.
Juncus
sp. 1,
Poaceae 4, Poaceae (chaf) 1, Poaceae
(straw) 1,
Taraxacum
sp. 1,
Trifolium/
Medicago
1,
Vicia cracca
1
Betula pendula
59,
Picea abies
(needle)
2,
Piněus sylvestris
(needle) 1
indeterminata 10,
leaf fragment 10,
resin 1, rhizome
fragment 15,
stalk 5
RS
Hypericum
sp. 1,
Medicago lupulina
1,
Myosoton aquaticum
1,
cf.
Poa
sp. 1, Poaceae
(straw) 1,
Trifolium
cf.
repens
1
bud 1
indeterminata 15,
leaf fragment 1
Asteraceae 6,
Carduus
sp.1,
Cirsium arvens
e 2,
Epilobium
sp.
2,
Hypericum
sp. 1,
Medicago
lupulina
2,
Myosotis
sp. 1,
Myosoton
aquaticum
1, Poaceae 4, Poaceae
(internodium) 2, Poaceae (straw)
3,
Rumex
sp. 1,
Taraxacum
sp.
3,
Trifolium repen
s 1,
Trifolium/
Medicago
1
Abies alba
(needle)
1,
Betula pendula
31,
Picea abies
(needle) 1
Bryopsida 4,
Equisetum
sp.
1, indeterminata
12, leaf fragment
4, rhizome
fragment 9, stalk
7,
Potamegeton
sp. 2
J
Asteraceae 1, Poaceae
(straw) 1,
Rumex sp. 1,
Silene
sp. 1,
Trifolium
cf.
arvense
1,
Trifolium
repens
1,
Vicia
sp. 3
indeterminata 4
Apiaceae 1,
Carduus/Cirsum
1,
Cirsium oleraceum
1,
Medicago
lupulina
1, Poaceae 1, Poaceae
(straw) 4,
Rumex
sp. 1,
Taraxacum
sp. 3,
Trifolium repens
1
Betula pendula
32,
Picea abies
(needle) 33, Pinaceae
(strobilus fragment)
1,
Tilia
sp. 1
indeterminata 9,
leaf fragment 7,
stalk 2
S
Carex
sp. 1,
Phleum
pratense
1, Poaceae 4,
Poaceae (straw) 13,
Vicia
cf.
cracca
1,
Vicia
sp. 6
cf.
Abies alba
(needle) 1,
Rubus
sp. 1,
bud 5
indeterminata 1
Asteraceae 4,
Cirsium oleraceum
1,
Medicago lupulina
1,
Picris
hieracioides
1, Poaceae 11, Poaceae
(internodium) 1, Poaceae (leaf
fragment) 1, Poaceae (chaf) 1,
Poaceae (straw) 13,
Ranunculus
sp. 1,
Taraxacum
sp. 6
Abies alba
(needle)
1,
Betula pendula
36,
Galeopsis tetrahit/
bifda
1,
Picea
abies
(needle) 4,
Pinus sylvestris
1,
Sambucus nigra
1,
Sambucus racemosa
2,
Sambucus
sp. 1
indetreminata 1,
leaf fragment 1
JS
Poaceae (straw) 1,
Vicia
sp. 1
indeterminata 1Poaceae 1,
Taraxacum
sp. 2
Betula pendula
8
indeterminata 1,
leaf fragment 5
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
98
Figure 9.
Prague Zličín; selected plant macroremains. A –
Cofea
cf.
arabica
, B –
Ficus carica
, C –
Prunus persica.
Figure 10.
Prague Zličín; Canonical
Correspondence Analysis (CCA) of charcoal/
wood dataset.
of the fragmentation and degradation of individual remains.
Among these were indeterminate seeds/fruits, fragments of
leaves, stalks and rhizomes (Table 6).
4.1.2 Non-funerary deposits
Only 24 specimens of carbonized macroremains, dated
to “agricultural prehistory”, were present in the samples
from the non-funerary settlement deposits. Useful plants –
caryopsis of barley (
Hordeum vulgare
var.
vulgare, Hordeum
vulgare
)
,
indeterminate
Cerealia,
seeds of lentil
(
Lens
culinaris
)
and pea
(
Pisum sativum
,
Vicia/Pisum
) – formed
half of the assemblage. Wild plants were represented by two
(ruderal) taxa –
Chenopodium album
and
Sambucus
sp.
The age of non-carbonized macroremains (589 specimens),
represented mainly by ruderals, is uncertain. Most of the
assemblage was formed of seeds of the neophytic plant
Amaranthus
sp. (497) and
Chenopodium album
(43). Other
taxa – usually considered as weeds of arable land – such
as
Aethusa cynapium, Atriplex
sp.,
Fallopia convolvulus,
Fumaria ofcinalis, Poaceae, Polygonum aviculare, Rumex
sp.,
Silene
sp.,
Veronica hederifolia
were rare. Forest species
were represented exclusively by fnds of
Picea abies
(15 needle
fragments)
,
and
grassland vegetation by
Stellaria graminea.
Samples from trackways (roads) yielded only a few non-
carbonized specimens of
Amaranthus
sp. (4),
Fallopia
convolvulus
(2), and
Chenopodium album
(1) of unknown date.
Canonical Correspondence Analysis (CCA) signifcantly
supported the diferences in the spectrum of species of plant
macroremains, wood, and charcoal pieces in individual
parts of the graves (wood/charcoal dataset: p=0.021, F= 1.7;
macroremains dataset: p=0.002, F=1.9). It is noticeable
that a signifcant part of the non-carbonized macroremains
correlated with the border between cofns and grave inflls
0 3 cm
0 2 mm
0 5 mm
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
99
Figure 11.
Prague Zličín; Canonical
Correspondence Analysis (CCA) of
macroremains dataset.
Table 7.
Prague Zličín; charcoal and wood in individual parts of the graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between
cofn/looting shaft or between cofn/grave infll; CH – charcoal pieces, W – wood).
JRJSSRS
Abies CH
8
2
Fagus CH
26
2911
Acer CH
1
Betula CH
428
28
7
Corylus CH
1
1
Picea CH
24
32
Pinus CH
5248014358209
Pop/Salix CH
7
6
Quercus CH
16370815564299
Tilia CH
12
Abies W
1055
2942
Betula W
4
1
Picea W
7
71
17111
Pinus W
112
2851
Quercus W
127
7
Salix W
7
4
(RS) and, by contrast, is minimally connected with cofns
(R) and infll (S) (Figures 10 and 11). Non-carbonized
macroremains probably sedimented after the looting of the
graves, when the looting shafts were open.
4.2. Charcoal and wood
The samples from the graves yielded 3017 charcoal records
(252 samples from 49 graves, Table 10). The charcoal
samples are characterized by the dominance of
Quercus
and
Pinus
, and the less common presence of
Fagus sylvatica
(Table 7, Figure 12).
The occurrence of
Abies
,
Acer
,
Betula
,
Corylus
,
Picea
,
Salix/Populus
, and
Tilia
charcoal pieces was very rare.
The species composition of the specifc parts of graves was
recorded as relatively analogous. Among the uncharred
wood fragments recovered from graves, with a total of
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
100
539 determinations,
Picea
,
Pinus
,
Abies
and
Quercus
were
commonly recorded and
Salix
and
Betula
were sporadic
(Table 7, Figure 13). These results document the selection
of wood for various purposes. The highest quantity of
wood corresponds with cofn parts (
cf.
Novák 2009).
The characteristic indication of the cofns was the higher
abundance of
Quercus
wood (Figure 10). In graves nos. 9,
11, and 12 the larger remains of oak wooden cofns were
documented
in situ
. Unfortunately, the number of preserved
annual rings was insufcient for dendrochronological dating.
Conifer wood was recorded in much higher quantities then
the wood of deciduous trees.
From the non-funerary deposits, samples were collected
from the road and sunken features. Most of the 133 charcoal
pieces from the “road” were determined as
Pinus
(127).
Quercus
(3)
and
Corylus
(3)
were identifed sporadically.
Other settlement features yielded 110 charcoal pieces and
11 wood fragments; among these
Quercus
was
dominant (79)
and
Pinus
(24)
very often present.
Charcoal pieces of
Fagus,
Betula, Corylus
and
Picea
were recorded only sporadically.
The samples from settlement features contained just a few
uncharred wood fragments of
Picea
(
5
)
and
Salix
(6).
4.3 Pollen
The frequency of pollen in samples was low (for selected
pollen grains, see Figure 14). There are only 36 positive
samples (Table 8) and only four samples contained more
than 100 palynomorphs: grave 120 (sample 399, bottom of
the grave); grave 123 (sample 506; bottom of the grave, by
the cranium); grave 123 (sample 507, bottom of the cofn,
Figure 12.
Prague Zličín; charcoal structure in individual parts of the graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between
cofn/looting shaft or between cofn/grave infll, depicted in percentages).
Figure 13.
Prague Zličín; wood structure in individual parts of the graves (R – cofns, J – graves infll, S – looting shafts, RS and JS – borders between
cofn/looting shaft or between cofn/grave infll, depicted in percentages).
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
101
Table 8.
Prague Zličín; pollen.
Sample
275
276
321
322
338
340
368
381
382
391
399
404
405
419
423
447
448
456
457
506
507
508
544
599
627
628
651
679
728
765
802
803
1092
1093
Grave––112112114114–12112111612011711767122119119109109123123123108127130130128131140157145145154154
DescriptionRRRRRRRRRRRRRRSRRRRRRRRRRRRRJJJJRSJ
Trees (AP)
Abies
2
1
Acer
1
2
2
4
Alnus
2
21
113
911
1
1
9
2
8
1
Betula
234215
17313
7
1
204131
8
152415182
Carpinus
1
3
1
54
1
11
Cornus
1
Corylus
1
1
5
1
4
46
1
4
3
1
7
Fagus
1
1
1
Frangula
1
Picea
24
Pinus sylvestris
31
442
2136
1
1
15
8
1
1
8
2
1171
Populus
1
1
11
1
2
2
Quercus
1
1
52
1
2
2111
Salix
2
Tilia
5
1
21
1
2
4
Ulmus
1
1
1
1
1
21
11
Herbs (NAP)
Ambrosia
1
Artemisia
141
1
1
251
111
14
Asteraceae Liguliforae11131632
102
112
7
111
10
7
25
8
414
Asteraceae Tubuliforae
1
1
7
53
1
2
3
4
2331
Carduus
t.
1
2
1
Brassicaceae1
22
65
2
62
7
32
Butomus
1
Centaurea cyanus
1
Centaurea
sp.
1
1
Centaurea jacea
11
1
4
Cerealia indet.
20
8
13
1
4
3
1
101
Secale
4
12
5
1
Triticum
t.
3
2
Hordeum
t.
1
Convolvulus
1
Cuscuta
1
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
102
Sample
275
276
321
322
338
340
368
381
382
391
399
404
405
419
423
447
448
456
457
506
507
508
544
599
627
628
651
679
728
765
802
803
1092
1093
Grave––112112114114–12112111612011711767122119119109109123123123108127130130128131140157145145154154
DescriptionRRRRRRRRRRRRRRSRRRRRRRRRRRRRJJJJRSJ
Cyperaceae
1
Daucaceae
2
11
1
2
4
Conium
t.
1
Daucus
t.
1
Peucedanum
t.
1
411
2
1
Ericaceae
/
Vacciniaceae
(
Calluna
)
1
Fabaceae
1
1
1
Lathyrus
t.
1
Lotus
t.
1
1
Trifolium
t.
2
Chenopodiaceae
1
3
2
421
1
1
31
112
9
10
Lamiaceae
1
1
2
122
2
151
Mentha
t.
1
2
2
Liliaceae
2
Plantago lanceolata
1
1
42
3
3
8
Plantago major/media
1
11
41
Poaceae
421
3
2513843
7
2
7
41263
321211411125
3
Polygonum aviculare
49
2
Polygonum persicaria
1
Potamogeton/Typha
2
Ranunculaceae
1
2
4
22
1
Ranunculus acri
s t.
1
21
1
Rosaceae
1
1
Alchemilla
t.
1
14
311
432
1
11141
Filipendula
t.
11
2
Rubiaceae –
Galium
1
Sanquisorba ofcinalis
1
Saxifragaceae
3
Scabiosa
2
Silenaceae
1
1
2
21
1
1
1
Agrostemma githago
1
Silene
t.
31
21
Urtica
2
2
3
1
1
1
2
2
2
2
Valeriana
12
Table 8.
Prague Zličín; pollen. (
Continuation
)
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
103
Table 8.
Prague Zličín; pollen. (
Continuation
)
Sample
275
276
321
322
338
340
368
381
382
391
399
404
405
419
423
447
448
456
457
506
507
508
544
599
627
628
651
679
728
765
802
803
1092
1093
Grave––112112114114–12112111612011711767122119119109109123123123108127130130128131140157145145154154
DescriptionRRRRRRRRRRRRRRSRRRRRRRRRRRRRJJJJRSJ
Verbascum
1
Indeterminata
5214
554
25
2
2
18122
32514
225192
Sum NAP
7
96
8
12214135329293203152411221001619555354224132420518
Sum AP
7
54
7
19520219942621613067401451251242639746
Sum AP + NAP
14141015231191555491135265313
7
1189140175146804
78
430163327924
Sporophytes
Asplenium
sp.
1
Botrychium lunaria
1
Polypodium vulgare
1
1
Polypodiaceae smooth
1
1
7
1
53
1
Fungi
6
3
XXX XXX
123
13
7
2
4
1
1
31
Gelasinospora
cf.
Reticulispora
(type 2)
1
Glomus
14124
3703
1
XXX
4
12
7
10
1811
206
25321
7
101
Chelidonium
2
Sordaria
1
1
6
2
1
type 581
3
Algae
4
1
221
54
3
2
10
5
2
7
12
24
Mougeotia1
3
Zygnema
2
Nonpollen objects
Amphitrema favum
2
Anthoceros laevis
2
Anthoceros punctatus
1
13
12
1
2
Bryophyta
1
1
2
1
1
Cyanobacteria
3
Rivularia
121
Insecta
1
11
1
11
Riccia
1
13
2
3
Rhizopoda
1
animal hair
1
6
1
1
hair
1
1
fbre
112
1
1
1
11
fbre – fax
1
1
1
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
104
by the pelvis); and grave 154 (sample 1092, bottom of the
cofn, by the pelvis).
4.3.1 Grave 120 (sample 399, negative 808, the bottom
of the grave).
Of woody species, the pollen of
Pinus sylvestris
prevailed.
Picea
could probably represent a fall from higher altitudes.
Corylus
and photophilous
Betula
were present in a larger
quantity. The woody species of the oak-lime-hornbeam forest
group (
Quercus, Tilia, Carpinus, Acer
and
Fagus
) occurred.
The woody species from the foodplain forest group were
present to a lesser extent (
Alnus
,
Fraxinus, Populus, Salix
and
Ulmus
). The herbal vegetation was varied. The herbs were
prevalent among the synanthropic indicators: Brassicaceae,
Chenopodiaceae,
Polygonum aviculare
,
Artemisia
,
Urtica;
Plantago major/media
can be considered an
indicator of
trampling
.
Cereals (Cerealia indet.,
Secale
and
Triticum
t.) can be ranked among the cultural crops, along with
legumes – the pollen type
Lathyrus
may point to lentils (
Lens
culinaris
) – according to Beug (2004). The meadow species
(Asteraceae; Tubuliforae; Liguliforae, including
Centaurea
sp.; Daucaceae; Fabaceae, incl. species
Lotus
and
Trifolium
;
Lamiaceae; Poaceae; Ranunculaceae;
Alchemilla
; Silenaceae;
and
Verbascum
) were also observed within the spectrum. The
others can be ranked among the more hygrophilic types, such
as
Mentha
and
Ranunculus acris
.
In addition, the spores of undetermined fungi (Fungi
indet.), probably some Ascomycetes on bark and wood,
were observed. The spores of the genus
Glomus,
the fungi
species living in symbiosis with plant roots, was also
determined, as well as coprophilic
Sordaria
. Also interesting
was an occurrence of
Chaetomium.
It is a dark-walled mould
normally found in soil, air, cellulose and plant debris, and
can cause an infection in humans (Ellis, Ellis 1985). Algae
were present in small amounts. The water algae
Zygnema
was also caught (Komárek, Jankovská 2001). In addition to
the fndings of algae and fungi, the spores of bryophytes, the
liverwort
Riccia,
and hornwort
Anthoceros punctatus
,
were
found; the latter is an indicator of disturbed soils (Boros,
Járai-Komlódi 1975). There was likewise an occurrence
of Rhizopoda (
Amphitrema favum
) among the non-pollen
objects.
4.3.2 Grave 123, sample 506 (negative 821, the bottom of
the cofn/upper part – head area)
In this sample, the pollen of
Betula
prevailed among the
trees, while
Pinus sylvestris
was plentifully covered. A
second coniferous tree was determined as
Abies.
The group
of oak-lime-hornbeam forest involved
Quercus, Carpinus,
Tilia, and Fagus.
The hydrophilic woody species, such as
Alnus
,
Populus
and
Ulmus
occurred again.
Corylus
and
Cornus
were represented among shrubs. There was more
pollen from herbs than from trees. The meadow species
predominated: Asteraceae; Tubuliforae; and Liguliforae,
incl.
Centaurea jacea
; Daucaceae, incl.
Peucedanum
t.,
Lamiaceae; Liliaceae,
Plantago lanceolata
; Poaceae;
Ranunculaceae, incl.
Ranunculus acris
t.;
Alchemilla
;
Filipendula
;
Scabiosa
;
Sanquisorba ofcinalis;
and
Valeriana
.
Carduus
, Brassicaceae, Chenopodiaceae,
Artemisia
, Silenaceae,
Urtica
can be ranked among the
synanthropic taxa.
Polygonum persicaria
and
Butomus
may
grow in the wetter places.
Butomus
can be used as a food
source because of its starch content. Cereals (Cerealia indet.
Secale
) were determined among the cultural crops. The
spores of the group Polypodiaceae, as well as
Botrychium
lunaria,
occurred. The sample contained non-pollen objects,
such as undetermined algae, fungi, Cyanobacteria and some
fbre (probably fax).
Figure 14.
Prague Zličín; selected
pollen grains. A –
Quercus
, B –
Pinus
,
C – Chenopidiaceae, D –
Carpinus
, E –
Alnus
,
F –
Trifolium
, G –
Polygonum aviculare,
H – Brassicacee, I –
Lathyrus
t., J –
Mentha
t.,
K –
Anthoceous punctatus
, L – Cerealia indet.
0 40 μm
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
105
4.3.3 Grave 123, sample 507 (negative 821, the bottom of
cofn/middle part)
The second sample from this grave was similar to the
previous sample. The foodplain woody species (
Alnus,
Ulmus
and
Populus
) prevailed among the woody plants,
the woody species of the oak-lime-hornbeam forest group
were present to a lesser extent (
Quercus, Tilia, Carpinus,
and
Acer
).
Pinus sylvestris
,
Corylus
and
Betula
were present in
larger amounts.
The herbs prevailed over woody species. The meadow
species – Asteraceae; Tubuliforae and Liguliforae,
incl.
Centaurea jacea
; Daucaceae, Fabaceae, incl.
Lotus
; Lamiaceae,
Plantago lanceolata
; Poaceae;
Ranunculaceae; Alchemilla predominated among the
herbs. Other synanthropic plants:
Artemisia
; Brassicaceae;
Chenopodiaceae; Silenaceae; and the weed corn-cockle
(
Agrostemma githago
) were confrmed. The sample
contained the pollen of cereals; individual types were
determined as wheat (
Triticum
t.) and rye (
Secale
), as well
as further undetermined cereals (Cerealia indet.). The pollen
grains were corroded. Other herbs might have overgrown the
wetter positions,
e.g.
Mentha, Valeriana
,
Ranunculus acris
t. The genera
Typha
might have grown directly in the water.
Rhizomes of common cattail contain starch (Kurzawska
et al.
2014). The spores of the group Polypodiaceae, as well
as Fungi (
Glomus
), occurred.
4.3.4 Grave 154, sample 1092 (context 1573, the fll of
cofn/middle area)
Sample no. 1092 contained more than one hundred grains.
The species
Betula
and
Pinus sylvestris
prevailed among
the woody plants. The species of the oak-lime-hornbeam
forest group were present to a lesser extent (
Quercus, Tilia,
Carpinus, Acer and Fagus
). The foodplain woody species
(
Alnus, Ulmus
and
Populus
) were also present.
The herbal vegetation was varied. The meadow taxa
prevailed among the herbs: Asteraceae; Liguliforae;
Tubuliforae, incl.
Centaurea
sp.,
C. jacea
; Daucaceae
;
Lamiaceae; Poaceae;
Plantago lanceolata
; Ranunculaceae;
Rosaceae, incl.
Alchemilla
and
Filipendula
; and Silenaceae.
The synanthropic plants Chenopodiaceae, Brassicaceae,
A
rtemisia
,
Urtica
,
Convolvulus
were determined. The pollen
type of cereals (Cerealia indet.) was determined, as was the
species
Daucus
t. used as a cultural crop. The occurrence of
heather –
Calluna,
which can be regarded as an indicator
of poor soils frequently degraded by human activity – is
quite interesting. Among the non-pollen objects there was
an interesting occurrence of coprophilic fungi (
Sordaria
)
together with Fungi indet. and
Glomus.
Particles (hairs) most
likely came from insect and animal bodies.
5. Discussion
5.1 Dating of the graves and their infll
All available radiocarbon dates (Figure 3; Table 3) based
on human bones support the archaeological dating of the
burials (Vávra, Kuchařík 2015) to the Migration Period (ca
5
th
century AD and the turn of the 5
th
and 6
th
century AD),
the so-called Vinařice group. However, it is clear that not all
recovered fnds, artefacts, and ecofacts are of this date.
For example, pottery fragments of pre- or protohistoric
date, ranging from the Neolithic to La Tène period, were
recorded as intrusions in the infll of the graves, due to
processes connected with contamination and residuality in
the past.
The strong surface erosion of artefacts, high fragmentation
level, and overall bad preservation did not allow closer
chronological determination in some cases, and indicated
exposure to long-term and/or vigorous pre-depositional
transformations. The existence of earlier – late Iron Age
to Early Roman period – human activities in the area has
been indicated by the radiocarbon dating of an animal
bone retrieved from the fll of grave 142 (feature 1555,
Poz-64646, 1970±30 BP; after calibration 45 BC–85 AD,
95.4%). Possibility that some parts of the plant remains are
also of this age cannot be ruled out.
In addition, radiocarbon dating of selected plant remains
indicates that part of the plant remains had been contaminated
from the much younger “sub-recent to modern” age. For
example, the cofee bean (
Cofea arabica
) dated to modern
times (UGAMS 20578) was recovered from the cofn
in grave no. 31 (layer 387), the carbonized caryopsis of
Hordeum vulgare
dated to 75BP± 30 (after calibration 1690–
1925 AD, 95,4%; Poz-64640) came from grave no. 175
(sample 1333), and the non-carbonized seed of
Ficus carica
dated to 210 BP±25 (after calibration 1646 AD – recent, 93%;
UGAMS 20579) from grave no. 164. It is highly unlikely
that all these dates are the result of dating contaminated
material. They were pre-treated in HCl prior to the dating
in CAIS. It is more plausible to suggest that: a) the infll of
graves consists of a mixture of fnds from diferent periods,
attesting to previous and later occupation or use on this site;
and, b) despite many preventive arrangements during the
excavations-undertaken in unfavourable weather conditions-
and during the fotation of the samples, it was not possible to
avoid the retrieval of contaminating material (fnds dated as
recent). The danger of not recognizing the “irrelevant” fnds
in multi-cultural sites is considerable, especially if many
plant taxa were used or occurred on the sites over several
millennia. This can lead to unreal values/counts of the taxa
within studied contexts, periods, or sites. However, the
preservation of some earlier fragile plant macroremains (
e.g.
Asteraceae, Apiaceae) from the culture layers and features
which became, due to the postdepositional processes, part
of the secondary looting shaft infll, is not presupposed to
a high degree. Moreover, the spectrum of crops from grave
samples did not correspond with the crop spectrum of the
Neolithic or Late Bronze Age in central Bohemia (Kočár,
Dreslerová 2010; Dreslerová, Kočár 2013). It is impossible
to wholly exclude contamination by Late Bronze Age crops,
but it is possible to suppose the dominance of
Triticum
dicoccum
for the Late Bronze Age with regard to the site’s
localization in an “old settlement area” in loess bedrock
image/svg+xml
IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
106
and cambisol. The structures of crops (the proportion of the
species) in the samples from the Migration Period graves in
Zličín are diferent from the Late Bronze Age crop structures
of settlements unearthed in the western outskirts of
contemporary Prague (
e.g.
Kněževes, Kněžívka, Hostivice;
see Dreslerová
et al.
2013). Therefore, we suppose that part
of the collection of carbonized macroremains is possible to
date to the Migration Period. Diferences between Zličín and
Březno (Tempír 2007) could be the result of real diferences
between both the communities in their settlement strategies
and agricultural management, or by the way their burial rites
and rituals are connected with their crops.
Conversely, contamination by later/recent plant
macroremains was confrmed, for example by non-
carbonized remains of
Amaranthus
sp. that were in samples
from graves, nonfuneral features and roads. Most of the
species of
Amaranthus
are neophytes (Kubát
et al.
2002)
and their presence before the 16
th
century AD is improbable.
Seeds of
Amaranthus
sp. are very small and could easily
penetrate the soil profle.
Helianthus
sp. and also
Pistacia
vera
are
probably connected with recent contamination by
workers during the excavation or fotation. Diasporas of
Cofea
cf.
arabica
,
Ficus carica
and
Prunus persica
were
degraded in their surfaces and did not look recent (Figure 9).
However, the peach stone was considered a Migration Period
grave provision because of the large size of the fnd and the
reality that the stones were found during the excavation, not
in fotation (
cf.
Quast, Siegmann 2000). Imports of luxury
food (including pistachio, fgs and peaches) to central
Europe during the Roman Period were well documented, so
the dating of fnds in Prague Zličín were problematic without
the radiocarbon dating of individual remains (Bekels,
Jacomet 2003; Van der Veen 2011). Plant macroremains
from Prague Zličín probably consist of three main groups:
1) residuals of plant material from earlier occupation events;
2) plant remains from the Migration Period; and, 3) later
contaminations – from any time after the burial up to recent
times.
5.2 Formation of the fll of the graves
Archaeologists usually tend to consider a burial as a result of
a single event and, therefore, the grave content is ordinarily
described as “a discrete unit of fnds”. For the jewellery and
other direct burial provisions (grave goods), this is probably
the case. However, the data obtained here show a much
more complicated picture; one which has methodological
potential, at least. The mere presence of looting shafts (
i.e.
secondary interventions) should act as a great warning for
the researcher when considering the mechanisms of grave
fll formation. The structure of the macroremains and pollen
grains refects a long-term “dumping ground”, turning every
single grave into an “environmental trap” exposed for a long
time to numerous external infuences. The botanical remains
can be, in principle, divided into three sub-assemblages
related to diferent times. Residuals represent the
ante quem
fnds predating the burials, therefore we describe this group
as an intrusion transformed and transported from the original
(at the site unrecognized) cultural layers. The second group
is
ad quem
related to the grave itself. The contamination
set of the botanical remains is younger then the burials and
emerged
post quem
. It seems that seeds of plants were not
used as grave oferings during the Migration Period. This
can be postulated because the density of both carbonized and
non-carbonized remains in the bottom parts of the graves is
the same or lower as elsewhere in the graves (Figure 4).
Carbonized macroremains which predate (
ante quem
) the
burials are most probably connected to various settlement
activities of people living in the area in pre- or protohistory.
The recovered taxa and types of remains indicate that they
could be the result of, for example, non/intentional burning
of grasslands or ruderal areas, or household ovens, and/or
specialised kilns necessary for iron production (presupposed
Figure 15.
Prague Zličín; model of
infltration of plant remains into the contexts
of graves (blue – cofns, green – graves
infll, orange – looting shafts, purple –
topsoil, brown – cultural layer.
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Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
107
in the western outskirts of Prague for the Roman/Migration
Periods).
The following hypothetical reconstruction of processes
connected with the development of the site from the time
of funeral activity to the time of archaeological excavation
is based on archaeobotanical data – taxa structure and taxa
density within samples. First, grave pits were dug in areas
where the topsoil (and layers below) represented a cultural
layer with plant macro and micro remains. Unfortunately, the
topsoil with the cultural layer was removed by a construction
company prior to the excavations, so the comparative data
were not available. Second, the cofn with the deceased (and
associated grave goods) was lowered down into the grave-pit.
Third, the pit was re-flled. This accounts for the presence of
“older” charred plant macroremains, and the mixing of earlier
and-with the burial-contemporary plant material (Figure 15A).
After some time, a looting shaft was dug and the grave was
robbed
1
. The looting shaft was not flled immediately, but was
left open and it flled up gradually, such that plant material
from the surface and the nearby cultural layer eroded into the
shaft and penetrated to the bottom of the grave. Gradually, the
looting shaft was flled in (Figure 15 B). The concentration
of both carbonized and non-carbonized plant remains in the
samples which came from the border between cofns and
looting shafts (and looting shaft and grave infll) was higher
than in the cofns, shafts and infll (Figure 4). Many taxa
were characteristic of samples from the boundary between
cofns and looting shafts (Figure 11), so the penetration
of plant material after the robbery was probably massive.
Therefore, it seems that a majority of the plant material is
connected with processes which took place immediately
after the robbery. The time between the burial and robbery
is not known. But, most probably, the graves were marked,
or the robbers knew or could still see the graves, as the
looting shafts led to the heads and thoraxes of the deceased.
Fragments of wood from coniferous taxa could represent the
remains of construction or grave equipment (Doležal, Vávra
2015, 131–149). Wood of
Pinus
,
Picea
and
Abies
was found
in all parts of the graves (Figures 13 and 10).
Carbonized remains of crops indicate that something
happened between the time of burial of the deceased and
the flling of the looting shaft. Firstly, there is a change in
the ratio of cereals to pulses (Figure 6), and secondly, while
Triticum spelta
and
T. dicoccum
are present in samples from
the grave infll,
Panicum miliaceum
occurs only in contexts
connected with the shafts (Figure 8). It seems that part of
the material in the shafts (millet, some pulses) either became
part of a new cultural layer, or these remains represent the
residue of an activity which took place during the reopening
of the graves (feasts, rituals,
etc.
).
1
The interval between the burial and the looting difers from case to case.
One must realize that the burial ground was used for some 3–4 generations.
Proof of the presence of connective tissue was observed in several cases,
i.e.
there was no decay at the time of reopening (Vávra
et al.
2012, pp. 12–13).
In some other cases, by contrast, only the skeletons or disturbed assemblage
of bones in a variable state of preservation from the original burial were
observed.
The cultural layer overlying the graves was then
transformed again after the looting shafts became flled in.
Some transport of much younger seeds through sediments
from the surface down to the bottom of the graves (Figure 15
C) is attested by the radiocarbon data (Table 9, Figure 3).
Such p
ost quem
contamination,
e.g.
uncharred seeds of
Cofea arabica
and
Ficus carica
, was interpreted as being
dated to historical and modern periods (history of
Cofea
in
postmedieval contexts; see, for example, Beneš
et al.
2014).
Waste from Prague was transported to the felds behind the
city walls and used as manure from the High Middle Ages
onward (Hofmann 1992, 331–332). Seeds and fruits, present
in this waste, could penetrate the soil profle, for example, as
a consequence of bioturbation (Karlík, Poschold 2014).
As mentioned above, prior to excavation the topsoil
had been removed, to approximately 50 cm in depth. The
excavation of each grave took many days, so the possibility
of contamination of sediments by diaspores from the vicinity
(
e.g.
uncharred seeds of
Amaranthus
sp. and
Chenopodium
album
abundant in the grave fll and looting shafts) or by
trampling from the boots of the excavators cannot be ruled
out (Figure 15 D). The high number of fnds we consider
recent contamination (Table 4) is striking, and we cannot
be sure if it is not the result of sampling contaminated
sediments due to the negligence of the support staf, and/or
inconsistencies during the fotation of the samples.
In contrast to plant macroremains, we believe that pollen
from the graves in Prague Zličín, taken from the bottom of
the graves (below cofns) or from inside the cofns, might
better refect the original content (
e.g.
Šálková
et al.
2015). It
is known that the pollen grains of crops attach to the clothing
during agricultural work and the processing of crops.
Prehistoric textiles usually contain large amounts of cereal
pollen (Enevold 2013). Therefore relatively high numbers of
cereal pollen and the pollen of meadow plants in the graves
at Prague-Zličín could indicate that people were buried in
the clothes they used for everyday activity. Spores of fungi
which grow on decaying organic matter (like the coprophilic
Sordaria
) are most probably the direct result of the decay of
the cofn and the body of the deceased. Other spores might
indicate the presence of fowers (
Glomus
the most common
species growing in symbioses with the roots of fowers), or
the lining of the cofn with hay (
e.g.
Chaetomium
).
Various threads of both plant and animal origin were
recovered from the fotation samples. We did not succeed in
precise identifcation, but some of them are probably fbres
from fax (
e.g.
Kvavadze, Narimashvili 2006; Kvavadze,
Gagoshidze 2008) and some of animal hair. Thread from
sample 391 (grave 116) is very similar to human hair.
It could be concluded that both macroremains and pollen
analyses did not distinctly refect the processes connected
with the burial rite. Most of the uncharred wood remains,
preserved due to the higher soil moisture content, originated
from cofns, but some are probably remains from other
artefacts buried in the graves: other constructions, tools for
digging, oferings. Their relatively high numbers and wide
spectra point to their abundance in graves.
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
108
5.3. Problems with the refection of the environment
Pollen spectra obtained from grave infll in the Prague Zličín
burial ground could be considered protohistorical, because
most of the positive pollen samples were taken from cleaned
profles of the bottoms of the graves. These pollen grains
could have several origins: fowers in the cofn; pollen
penetrated into the clothing or funeral textiles; pollen rain at
the time of the burial process; contamination of the infll of
the cofn after the robbing of the grave through the looting
shaft; or, contamination by the processes of bioturbation.
No sample from contexts diferent from the cofn area was
representative. It is possible to suppose that samples from
various contexts could be positive in the case of contamination
of pollen samples. On the other hand, four representative
pollen samples from the bottoms of graves could be, with
caution, interpreted as a refection of the environment of
the Migration Period based on the following consideration.
Pollen samples are generally partly compatible with the
macroremains and wood samples from cofns (R). But, in
detail, direct comparison could only be applied in the case of
grave 154 (where the spectrum of the macroremains does not
contains any neophytes), because samples of macroremains
from graves 120 and 124 are unfortunately not available. The
signifcant structure of wood/charcoals with dominant
Pinus
sylvestris
corresponds with the pollen structure in grave 154.
Pollen grains of
Quercus
as well as charcoals are numerous
there. Despite the fact the pollen of
Picea
was not present,
its wood was numerous. It could refect the cofn or grave
construction. Both pollen and macroremains from grave 154
refected dominant ruderal vegetation.
The general picture of the vegetation reconstruction gained
by diferent methods from a number of the graves, however,
does not refect only the Migration Period (part of the plant
macroremains is certainly later-contamination/perhaps-
earlier-residuals). Rather, it widely shows the development
of the cultural landscape of the central Bohemian region at a
time of human activity in protohistory, potentially at the time
of the contamination of the grave infll.
If the fll was actually signifcantly contaminated by earlier
plant material, the contamination would have occurred at a
time when feld or rubble dominated the site. A responsible
reconstruction of the environment of the area in the hinterland
of the burial ground would need to obtain comparative
material from settlement features. But settlement features of
the Migration Period in Prague Zličín have not been found;
in Bohemia they have been found infrequently and have had
a low density of macroremains.
The samples from the sandy sediments contained rather a
small amount of corroded palynomorphs, or they were quite
sterile (the rest of samples). This has probably been caused
by oxidation and mechanical processes during sedimentation,
which causes a loss of pollen from the sedimentary record
(Havinga 1967). This does not concern four samples that, on
the contrary, were abounding in pollen, but also contained
corroded palynomorphs.
The pollen assemblages from the sediment samples very
clearly refected the surrounding local vegetation at the time
of pollen sedimentation. The ratio of woody species and
herbs
in individual samples apparently refects the human presence
and infuence on the surroundings. The landscape was probably
sparsely covered with trees. The woody species of the oak-
lime-hornbeam forest group were documented. The occurrence
of hygrophilous woody species and trees reconstructed the
presence of a wetland or spring area in the vicinity. Also,
species of wetter habitats appeared. Conifers are represented by
Pinus sylvestris
,
Picea
and
Abies
pollen. The pollen of meadow
species prevailed among the herbs. The weed and synanthropic
species, as well as cultural crops, also occurred.
The structure of macroremains was well compatible with
the pollen structure, but it refected the local character of the
area of the burial ground. The carbonized remains refected the
human activities connected with working with crops and fre.
The remains of crops, weeds and ruderal plants were dominant
among the carbonized macroremains, while remains of plants
typical for diferent types of meadows, pastures and forests
were documented less frequently. Non-carbonized remains
probably refected a natural environment which was deforested,
with only occasional occurrences of trees and shrubs (
Betula
pendula, Tilia
sp.,
Sambucus nigra
and
S. racemosa
). The non-
carbonized plant macroremains reconstructed the dominance of
ruderal and weedy vegetation in the vicinity of the archaeological
site. Also, macroremains of plant species characteristic of the
vegetation of trampled habitats were frequent. The species
typical for mesophilous meadows and pastures were commonly
documented. The rare presence of a
Potamogeton
macrofossil
highlights the presence of water habitat. The presence of
Abies
alba, Picea abies, Pinus sylvestris
needles could draw our
attention to the processing of wood.
The result of the anthracological analysis reveals the
common composition of the frewood obtained from the
vicinity of the site during an unknown time period. The size
of many charcoal pieces was very small (2–3 mm); this is
probably connected to some re-deposition of the material.
The species spectrum corresponds with the average charcoal
rain on prehistoric as well as medieval archaeological sites
in the region (Novák
et al.
2012). The composition of the
charcoal species is characteristic of the dominance of oak
and pine. Dating of the charcoal collection was problematic
without the radiocarbon dating of every individual piece of
charcoal. Results of the anthracological analysis indicate the
presence of acidophilous oak forest (as.
Luzulo-Quercetum
).
The high proportion of
Pinus
and
Quercus,
and the rare
occurrences of other trees,
probably suggest an open and low
woodland canopy. The low species diversity may indicate
the important human impact on the environment in the area
surrounding the archaeological site. As potential natural
vegetation, the acidophilous oak forest (
Luzulo-Quercetum
)
and oak-hornbeam forest (
Melampyro
-
Carpinetum
) has
been hereby assumed (Neuhäuselová 2001). Anthracological
analysis generally supposes that people have probably
obtained frewood from the woody species growing in the
close vicinity of archaeological sites (Shackleton, Prins
1992; Jansen
et al.
2013). The frewood is considered to be
mostly non-selective, but the charcoal spectra from the wood
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IANSA 2016 ● VII/1 ● 87–110
Tereza Šálková, Alena Dohnalová, Jan Novák, Tomáš Hiltscher, Jaroslav Jiřík, Jiří Vávra: Unrecognized Taphonomy as a Problem of Identifcation
and the Scale of Contamination of Archaeobotanical Assemblages – the Example of Prague – Zličín Migration Period Burial Ground
109
for those special purposes, or wood that was imported from
the wider area, generally show reduced species composition
(
e.g.
Novák
et al.
2012). The structure of woods and
charcoals was diferent both in terms of which species was
most dominantly represented, and in their species spectrum.
It is possible that the charcoal and wood remains refected
other processes from diferent times.
It could be concluded that a reconstruction of the natural
environment, based on results from features in a site with
a long development of human activity and a low density
of plant material, is unrealistic without a wide spectrum
of radiocarbon data. We supposed that the pollen samples
from the bottoms of graves were not contaminated. Based on
this pollen we might thus reconstruct the open agricultural
landscape. Plant macroremains and the remains of wood
and charcoal do not hinder this reconstruction, but the
uncertainties are considerable. It could be concluded that
the burial ground was located in the cultural landscape of
the previous and following periods, and that the area was
intensively exploited by the planting of felds, depositing
of waste in rubble sites,
etc.
Based on the results from the
Migration Period graves in Prague Zličín, we can conclude
that this type of material (graves in a multi-cultural settlement
area with a low density of macroremains) are insufcient for
a contemporary reconstruction of the natural landscape at the
time of burial.
6. Conclusion
Diferent sources of botanical materials (macroremains,
wood, charcoal pieces and pollen) from the various contexts
– cofns, looting shafts and infll from the Migration Period
graves in Prague Zličín, excavated in 2005–2008 – indicate
the following:
1. Most of the cofns were probably manufactured from
Quercus
, while other potential equipment used and
constructions found within graves were made from
coniferous taxa (
Picea
,
Pinus
, and
Abies
).
2. Charcoal pieces from grave contexts are dominated by
Quercus
and
Pinus
, while less common is the presence
of
Fagus silvatica.
Charcoal pieces of
Abies
,
Acer
,
Betula
,
Corylus
,
Picea
,
Salix/Populus
, and
Tilia
are
not numerous. Charcoal pieces from the graves most
probably refect the wood taxa used for fuel in the
area of the burial ground and are probably connected
with secondary re-deposition and a species spectrum
corresponding to the average charcoal rain of an
archaeological site in this region.
3. The assortment of crops difers from that which has been
known for the Migration Period in the Czech Republic.
It is more similar to the Roman Period in the Czech
Lands (Kočár, Dreslerová 2010) or in the Middle Danube
Region (Hajnalová 2011); however, see point 4. For
regions that were trading and in contact with Bohemia,
the structure of crops is diferent (
e.g.
Gorbanenko 2014;
Hopf 1979; Rösch, Jacomet, Karg 1992).
4. Plant macroremains recovered from graves seem to be
of other than funerary origin. They do not represent
grave goods (oferings), but instead originate from
farming and household activities performed at the site,
or in its close vicinity before and/or after establishment
of the graveyard.
5. Despite the fact that the graves were well sampled, it
was not possible to reconstruct the burial rite in detail.
Sampling methods, though vigorous, were inadequate,
as they did not eliminate or take into account the danger
of contamination. The density of plant material in the
graves was generally low, yet the efect of residuals
and contamination was substantial.
Acknowledgement
This research was supported by the Czech Science
Foundation; grant number P405/13-8955S. For support
during the completing of this article we wish to thank GAJU
145/2016 H. This article was also supported by inspiring
environments of grant Papaver. Centre for human and plant
studies in Europe and Northern Africa in the postglacial
period, reg. no: cz.1.07/2.3.00/20.0289. We would also like
to thank Petr Kočár for his inspirational ideas, and Mária
Hajnalová and two anonymous reviewers for their helpful
comments. We are also grateful to Michael Hensen for
proofreading the text.
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