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XI/1/2020
INTERDISCIPLINARIA ARCHAEOLOGICA
NATURAL SCIENCES IN ARCHAEOLOGY
homepage: http://www.iansa.eu
Landscape Transformed: Archaeological, Historical and Environmental
Dating of the Early Modern Field System in Valštejn, Czech Republic
Ivana Šitnerová
a,b*
, Jaromír Beneš
a,b
, Ivana Trpáková
c
, Jiří Bumerl
a,b
, Veronika Komárková
a
,
Tereza Majerovičová
a,b
, Lenka Hrabáková
b
, Kristina Janečková
c
a
Laboratory of Archaeobotany and Palaeoecology, Faculty of Science, University of South Bohemia, Na Zlaté stoce 3,
370 05 České Budějovice, Czech Republic
b
Institute of Archaeology, Faculty of Arts, University of South Bohemia, Branišovská 31a, 370 05 České Budějovice, Czech Republic
c
Department of Land Use and Improvement, Faculty of Environmental Sciences, Czech University of Life Sciences, Kamýcká 129,
135 00 Prague-Suchdol, Czech Republic
1. Introduction
There are several main types of arable feld systems across
the world. The most common are terraced felds, then feld
systems with visible boundaries between parcels, followed
by open felds (Agnoletti
et al.
, 2015). Field systems called
open felds mostly dominate in Great Britain. These unhedged
felds have a wide variety of forms. They can be made up as a
system of long strip parcels grouped into blocks, they could
be in the form of dispersed strips, or they could comprise
compact blocks (Pollard
et al.
, 1974;
Rackham, 1986;
Williamson, 2018). Terraced felds, especially typical for
Asia (called “paddy felds”) (Iiyama
et al.
, 2005; Fukamachi,
2017), are also found in South America (Goodman-Elgar,
2008), and in the African mountainous regions of Ethiopia,
Uganda and Rwanda (Tarolli
et al.
, 2014). In a European
context, terraced felds are most common in southern Europe
and in Alpine regions (Varotto
et al.
, 2019; Tarolli
et al.
,
2019). In western and central Europe, the most common
types of feld systems are defned by visible boundaries,
usually without signifcant terracing. These are referred to
as “bocage” and “hedgerow landscapes” in western Europe
(France and Great Britain) (Baundry
et al.
, 2000). A similar
type of this landscape is also found in the Czech Republic,
where this agrarian hinterland of villages is called “plužina”.
It is defned as an economically usable part of the landscape
belonging to a single village settlement, and it is the sum
of all the felds, meadows and pastures interconnected by
Volume XI ● Issue 1/2020 ● Pages 89–101
*Corresponding author. E-mail: ivana.pravcova@gmail.com
ARTICLE INFO
Article history:
Received: 19
th
March 2020
Accepted: 15
th
July 2020
DOI: http://dx.doi.org/10.24916/iansa.2020.1.7
Key words:
feld system
radiocarbon AMS
modern soil dating
210
Pb and
137
Cs
archaeobotany
anthracology
old wood efect
landscape transformation
ABSTRACT
The historical feld system of Valštejn represents one of the most extensive historical landscape
complexes in the Czech Republic. Archaeological excavation of a former agricultural terrace (now
a meadow) revealed the elaborate construction of a wall and stone foundation under the former
arable feld. This construction probably served for drainage and for soil protection. Archaeobotanical
sampling facilitated the use of the charred plant material for radiocarbon dating of the soil profle,
supported by the measurement of radionuclides
210
Pb and
137
Cs activity in order to estimate the age and
stratigraphic integrity of the soil. An interesting record was obtained by archaeobotanical analyses of
the lowermost layer, where wood charcoal and needles of fr (
Abies alba
) were identifed and dated
by AMS
14
C. A discrepancy between the younger needle and much older charcoal could indicate an
example of the old wood efect in archaeological chronology. The study has brought comprehensive
results using environmental archaeology methods and sheds light on one of the stages of historical
landscape transformation of the Early Modern Ages in central Europe.
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Landscape Transformed: Archaeological, Historical and Environmental Dating of the Early Modern Field System in Valštejn, Czech Republic
90
a network of paths (Gojda, 2000). The visible parts of this
hinterland can be typical feld strips and agrarian terraces.
The agrarian hinterland of a village came to be defned
in central Europe by the traditional concept of German
historical geography (in German “die Flur”: Krüger, 1967;
Born, 1979; Denecke, 1979; Sperling, 1982). This school
defnes “die Flur” as the historically-developed structure of
a village’s landholding, whose current layout is the result
of many changes in dynamics, local economy and property
ownership. The term “die Flur” was a big topic in German
historical literature of the 19
th
century, frequently enriched
with a certain ethnic signifcance. Attention has been paid in
the last decades to the origins of diferent types of agrarian
hinterland associated with various historical villages.
Recent studies omit the ethnical meaning underpinning the
historical circumstances of settlement activities (Žemlička,
2014). The German schools of agrarian history and historical
geography were followed by ethnographic and historical
research in Czechoslovakia and in the Czech Republic (Pohl,
1934–1935; Dohnal, 2003; Klír, 2003). Transformation of
the landscape is observed primarily through the prism of
medieval colonization (Klápště, 2005; 2012; Žemlička,
1997; 2014). Field systems and their patterns are, of course,
an integral part of medieval and Early Modern villages to
which they belong.
The archaeology of medieval and Early Modern villages
has primarily focused on their residential area, particularly on
abandoned medieval settlement zones with buildings. Such
interest in agrarian hinterland dates from the second half of
the last century. New methods of remote sensing (Gojda,
John eds., 2013; Holata
et al.
, 2018) and environmental
archaeology (Houfková
et al.
, 2015; 2019; Hejcman
et al.
,
2013a; 2013b) have contributed much to the research of the
agrarian hinterland of villages. Thanks to this new research,
it is now possible to resolve questions of dating, function and
the characters of agrarian background efectively.
One of the frst archaeological studies focusing on the
identifcation of the village agrarian hinterland in Bohemia
was taken in the Kostelec nad Černými lesy region by
Z. Smetánka and J. Klápště (Klápště, 1978;
Klápště,
Smetánka, 1979; Smetánka, Klápště, 1981), and in Moravia
by V. Nekuda in the abandoned village Pfafenschlag
Figure 1.
1a: The map section with the Czech Republic within central Europe and the location of Valštejn (red dot) and others feld systems under research
(green dots: feld systems around Oblík hill near Louny; Malonín near Míčovice; feld systems around Rokštejn castle near Panská Lhota; and Debrné
near Trutnov). 1b: Valštejn village illustrated on the frst military mapping which took place from the 1760s to 1780s. The village had the German name
of Wallstein. The scale of the map is 1:28000. Sources: Laboratory of Geoinformatics FE UJEP, Ministry of the Environment of the Czech Republic and
Austrian State Archive/Military Archive in Vienna. 1c and 1d: Current landscape around Valštejn. Photo by T. Jůnek.
1a
1b
1c1d
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91
(Nekuda, 1975). The feld systems were more systematically
identifed thanks to the aerial survey and aerial laser
scanning of the landscape (Gojda, 2000; Gojda
et al.
, 2011).
The frst direct archaeological research of feld systems was
carried out in the Šumava Mountains near Vlachovo Březí
(Beneš
et al.
, 1999). The direct excavation of feld strips
and hedgerows is still an exceptional activity in Czech
archaeology. One example is the former arable hinterland
around the abandoned village of Sloupek in West Bohemia
(14
th
–15
th
century AD), where hedgerows were constructed
by an accumulation of stones without any systematic
building trait or design (Vařeka, 2018). From an historical-
geographical point of view, Ervín Černý was the frst to
collect knowledge concerning abandoned villages and their
agrarian hinterland and who divided it into several types and
shapes (Černý, 1973; 1979).
Historical feld systems have also been the focus of natural
science disciplines, such as pedology (Hejcman
et al.
,
2013a), hydrology (Bayer, Beneš, 2004) and geochemistry
(Horák
et al.
, 2018; Horák, Klír, 2017; Janovský, Horák,
2018). The frst detailed multi-proxy analysis of abandoned
terraced felds in the Czech Republic was undertaken
in Malonín in South Bohemia. The aim of this research
was to date the hedgerow of the past feld system. The
radiocarbon data obtained demonstrated the chronology of
the hedgerows, which substantially preceded the frst written
sources regarding the village (Houfková
et al.
, 2015).
From the standpoint of landscape ecology, feld systems
and agrarian terraces enhance some important landscape
functions, providing landscape connectivity and serving as
important animal and plant habitats, especially in landscapes
with otherwise low ecological stability (Forman, Godron,
1986; Wilson, Forman, 1995). The hedgerows and agrarian
terraces also signifcantly afect the microclimate of felds,
and control soil erosion (Burel, Baudry, 1995), prevent
uneven stream fow through the year (Mérot, 1999), reduce
pesticide drift and fertilizer misplacement (Ucar, Hall, 2001;
Marshall, Moonen, 2002), and serve as a bufer against
nitrates (and much else) for water protection (Caubel-Forget
et al.
, 2001).
This project focuses on the identifcation and description
of all remnants of historical feld systems in the open
landscape and on providing detailed data on selected types
and cases. These systems represent various kinds in diferent
Czech landscape types (lowlands, highlands and mountain
areas). The main task of this detailed feld research is the
dating of these remnants and the collection of other data
for their detailed description and landscape reconstruction
(Figure 1a).
The frst chosen feld system belongs to the village of
Valštejn in Zlaté Hory Highlands, in the region of Silesia,
where extensive long feld strips ofer one of the best-
preserved historical agrarian systems in the Czech Republic
(Figures 1c and 1d). The Valštejn feld system was selected
for this study because of its outstanding historical integrity.
Previous research (Molnárová
et al.
, 2008) indicates that both
the pattern of feld ownership and the hedgerows delineating
this ownership have been preserved to a remarkable level.
The size and geomorphological setting of the Valštejn feld
system ofer a wide range of habitats with variable ecological
conditions, thus providing an opportunity for studying its
efect on biodiversity.
The main goal of the research in the village Valštejn and
its hinterland is to gain new archaeological information about
these particular former long feld strips and their hedgerows
enabling an informed view of their construction, stratigraphy
and dating. There is a general gap in our archaeological
knowledge concerning these types of landscape features
in central Europe. To date, only the felds system around
the village of Malonín have been dated by scientifc
methods (Houfková
et al.
, 2015). Therefore, we decided
to systematically sample diferent types of these features
across the Czech Republic. One specifc task was to test the
accuracy of dating in comparison with the general “time-lag”
model postulated in a recent study by Fanta
et al.
(2020).
They describe a systematic bias between the frst mention of
villages in historical sources and their archaeological dating.
Our study could ofer a comparison with the feld system
of the medieval village of Malonín and a specifc time-
lag (if indeed it exists) for an Early Modern village and its
hinterland in a diferent type of central European landscape.
2. Materials and methods
2.1 History of the study site
The village of Valštejn was founded according to written
records (Kořínek, 2018) in 1618 AD by Jan Kryštof of
Wallenstein (Valdštejn in Czech). The settlement was a
medium-sized village, consisting of Greater and Smaller
Valštejn (Wallstein in German). The frst representation of
the village on a map is found on the Müller Map of Moravia
from 1716 AD, and subsequently Valštejn appears in the
First Military Mapping, where it is described as Alt and Neu
Wallstein (Figure 1b). Greater Valštejn was a parish village
with a church built in between 1793 and 1795 AD. The
church was destroyed in 1984 AD, but the parish house is
preserved to this day and its oldest part dates approximately
to 1610 AD. There is also evidence that Valštejn did not exist
before 1602 AD (Kořínek, 2018). Thanks to this information
it is obvious that Valštejn was built in between the years
1602 AD and 1610 AD and that it is older than the frst
written sources (Kořínek, 2018; Historický lexikon obcí ČR,
2006; Hosák, 2004; Bartoš
et al.
, 1994).
Valštejn is an agrarian mountainous village in Silesia
situated at an altitude of 517–550 m asl. The soil is loamy-
sand of an inferior quality, shallow in depth on its original
base of phyllite (slate) or on its basalt geological substrate.
The main crop planted here was rye, oats and barley, and
people produced hay for cattle and used wood from the
forest, according to the protocols of Joseph’s cadastre from
1787 (Josefský katastr 1785–1792, č. 1518). The total area
of the arable felds in the 18
th
century was 269 ha, meadows
accounting for only 23.5 ha, forests for 27.5 ha, pastures
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Landscape Transformed: Archaeological, Historical and Environmental Dating of the Early Modern Field System in Valštejn, Czech Republic
92
for 78.5 ha, and orchards approximately for 30 ha. The
settlement zone indicates wooden houses with orchards. The
long narrow strip felds above the valley were separated by
pathways, belts of barren soil or pastures (Bartoš
et al.
, 1994;
Josefský katastr 1785–1792, č. 1518; Figure 2).
2.2 Valštejn village and its feld system as an object
of study
The choice of the Valštejn agrarian hinterland for detailed
archaeological and environmental study is based on a
representation of landscape types across the Czech Republic.
The feld systems were selected according to their variability
and geographical setting. They comprise a lowland type
(systems around Oblík hill in Northwest Bohemia), sub-
mountainous region (colline zone) type (Rokštejn by Panská
Lhota in the Bohemian-Moravian Highlands), Debrné in the
Krkonoše (Giant Mountains) Foothills, and two mountainous
villages (Valštejn and Malonín) (Figure 1a). Fully forested
landscapes were not included, being out of the scope of the
project.
The feld system of Valštejn lies in the Zlaté Hory Highlands
ranging in altitude from 500 to 700 m asl. (Figure 3). It falls
into the 5
th
vegetation zone dominated by fr-beech woodland
according to Zlatník (Zlatník, 1956; 1976). This vegetation
type was confrmed by pollen analyses from several sites in
the Jeseníky Mountains (Abraham
et al.
, 2017). This zone is
today typical for its mosaics of forests, meadows, pastures
and felds with scattered built-up areas of villages. Humans
did not signifcantly afect this type of landscape until the
13
th
century. The main colonisation took place during the 16
th
and 17
th
century. It led to the deforestation of the landscape
and the creation of pastures. Now these areas are mostly used
as meadows (Löw, Míchal, 2003; Chytrý, 2017).
2.3 Archaeological excavation
Appropriate place for archaeological excavation and
environmental sampling was selected according to the
methodology of Houfková
et al.
(2015). The second
horizontal terraced belt was chosen for the digging of trench
labelled S1 through the hedgerow and the sampling of soil.
It is situated to the north-east of the Valštejn stream at an
altitude of 540 m asl. The boundary of this feld strip was
made with a stony wall stretching that runs in a northwest-
southeast direction. Due to the specifc nature of its
construction, the trench was divided into two parts – an area
under the wall and an area above the wall. The fnal trench
Figure 2.
The orthophoto map presenting Valštejn village and its agricultural background. The yellow line represents the current built-up area, the green
line represents the area of agrarian hinterland, and the red line limits the cadastre area of Valštejn. The red dot marks the site of the archaeological excavation
of the hedgerow (trench S1).
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93
was 11 m long, 1 m wide and the bedrock was at a maximum
depth of 1 m (Figure 4).
The area under the wall consisted of a shallow stony base;
stones were therefore only cleaned up and photographically
documented. Soil samples were taken from the space
between stones just for comparison. The area above the wall
was systematically uncovered in mechanical layers of 10 cm.
Each mechanical layer was prepared by hand, sampled and
photographed. The trench was excavated to the bedrock. The
whole trench was documented by photogrammetry. Each
step of the excavation was recorded in writing. The trench
was positioned by GPS and photographed by a drone.
2.4 Archaeobotanical and anthracological analyses
Samples were taken from the mechanical layer situated
40 cm below the ground surface (−40 cm) and below,
because of the contamination and too fresh sediment of the
upper layers above. From –40 cm, samples were then taken
at every 10 cm of the mechanical layers of trench S1 up to
1 m depth. There was a concentration of bigger stones at the
level of −90 cm, and due to this, samples were taken both
between and under the stones, the bedrock being reached at
−100 cm.
Samples (10 l each, total amount 100 l) were extracted
by water fotation, using a fotation tank of ANKARA type.
The light fraction was collected on sieves with mesh size
0.25 mm. Uncharred and charred remains were used for this
study (Anderberg, 1994; Berggren, 1981). Anthracological
samples were acquired from the fotated bulk samples. The
charcoals and wood fragments obtained had a total weight of
29.031 g. Charcoal analysis was carried out on completely
burned charcoal with a total weight of 10.49 g. Botanical
0 200 m
Figure 3.
The elevation model of landscape relief shows the altitude of feld systems at Valštejn from 500 to 700 metres asl. Red dot illustrates the site of
excavation at altitude 540 m (trench S1).
Figure 4.
Stratigraphic section across a hedgerow of the agricultural terrace (trench S1) with a description of the archaeological layers.
0 2 m
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macroremains were observed by a standard binocular
microscope Nikon C-LEDS at magnifcation 10× to 50×.
The charcoal fragments were identifed using an optical
microscope Nikon Eclipse 80i and an anatomical atlas of
wood (Schweingruber, 1990). Data obtained regarding
the individual taxa were expressed in number of charcoal
fragments and the charcoal anthracomass (Figure 7a). The
specifc anthracomass, as in this case, is defned by the ratio
between total mass of selected charcoals and the total mass
of soil particles smaller than 5 mm (Thinon, 1992; Carcaillet,
Thinon, 1992).
2.5 Radiocarbon dating
The key method used in the research of the Valštejn feld
system was radiocarbon dating of the botanical macroremains
already efectively used in our older investigation elsewhere
(Houfková
et al.,
2015). Charred seeds with optimal short-
life intervals are suitable for radiocarbon dating and are
usually present in sediments of historical felds at very low
concentrations. Charred wood, contrary to short-lived seeds,
could give an older date for an archaeological context than
the situation really is. The “old wood efect” (Schifer, 1986,
Kim
et al.
, 2019 with more recent literature) results from
the fact that a wood fragment can originate from part of an
older fallen tree. However, dating of such charred wood
fragments can be useful; they can indicate the presence of
older biological materials in the soil. Therefore, both charred
seeds and charred wood fragment were used for radiocarbon
dating. Five macrofossil samples and one charcoal sample
were sent for radiocarbon dating. It was not possible to send
the same species of macroremains and therefore two seeds of
Rumex,
from a depth of 60–70 cm and 80–90 cm, and three
needles of
Abies,
from a depth of 40–50 cm, 70–80 cm and
90–100 cm, were chosen for dating (Figure 8a). The charcoal
sample came from the lowest layer 90–100 cm. These samples
were measured by a spectrometer 1.5 SDH-Pelletron Model
“Compact Carbon AMS” in Poznan Radiocarbon Laboratory
in Poland. The data results were calibrated online using
OxCal 4.2 (Bronk Ramsey, 2009) based on the IntCal 13
atmospheric curve (Reimer
et al.
, 2013).
2.6 Dating of modern soil by radionuclides
The sampling of soil in the archaeological trench was aimed
at acquiring the stratigraphic order of samples for detection of
soil age (Chen
et al.
, 2020). The analysis of the radionuclide
210
Pb and
137
Cs activity can ofer information as to whether
topsoil sedimentation was gradual or if it was disturbed by
agricultural or other more recent activity. The radionuclide
210
Pb is an isotope in the environment with a half-life of
22.6 years (Gaspar
et al.
, 2013). Dating of a soil profle
can also indicate if the sediment in the profle is older than
ca. 100 years (already not containing this isotope), which
is the limit of this
210
Pb method (Wintle, 2007, p.25). The
isotope
137
Cs is widely used in environmental soil science
(Owens
et al.
, 1997; Evans
et al.
, 2017; Huisman
et al.
,
2019). The radionuclide
137
Cs with a half-life of 30 years
does not occur naturally; it was introduced by atmospheric
nuclear detonations from 1952–1962, and by the Chernobyl
nuclear disaster in 1986, which deposited
137
Cs over a vast
area of Europe. This artifcial radionuclide can be used in
geoarchaeology as a marker for the very recent age of a soil
and as a tracer for (sub-)recent soil erosion (Huisman
et al.
,
2019).
The aim of dating the soil in trench S1 is age estimation.
An absence of radionuclides, or their very low concentration,
can also control for the sedimentary integrity of the soil
profle in the trench. The main task was therefore to verify
the radiocarbon dating of the charred remains and exclude
contamination and local disturbances.
Samples for determination of modern soil deposits from
the agricultural terrace were collected from the profle of a
trench. Samples were collected at 5 cm intervals and taken at
accurate positions down the 1 m deep profle. About 7 grams
of each sample were completely dried by lyophilisation.
Gamma-decay counts of the radionuclide (
210
Pb,
226
Ra,
137
Cs)
concentrations were measured at the CEN Radiochronology
Laboratory, Canada, using a High-Purity Germanium
detector (HPGe).
2.7 Archaeological artefacts
The counting and analysing of archaeological artefacts is a
useful tool for the relative dating of soil layers in agricultural
terraces (Beneš
et al.
, 1999; Houfková
et al.
, 2015). Artefacts
can also be used as a marker of extensive manuring activity
on past arable felds and on former arable soils (Beneš, 1998;
Kuna
et al.
, 2004; Jones, 2004). This soil trait is recognizable
by the counting of small artefacts using residual material
determination after soil sample fotation.
3. Results
3.1 Archaeological excavation and sedimentary
description
The soil profle shows the sediment compositions, which do
not change much in their natural layers. Any diferences are
mainly in the amount and type of clastic admixtures. The
frst natural layer (0–10 cm) contained a brown-grey humus
clay with a small admixture of a fne clastic slate. The second
natural layer (10–50 cm) mainly contained a light brown-
grey clay with an admixture of a fne clastic slate. The third
natural layer (50–90 cm) contained a light brown-grey clay
with an admixture of a coarse clastic slate. The fourth natural
layer (90–100 cm) contained a brown-yellow clay with an
admixture of charcoal (Figure 4).
One of the most signifcant and surprising archaeological
observations was detected at the bottom of the trench. Here,
we found an artifcially composed stone basement at the
level of –90 cm, consisting of stones intentionally placed
immediately next to the internal wall construction of the
hedgerow. This construction bears evidence of elaborated
intentional construction using larger fat stones ftting together
in several layers. Spaces between these stones were flled
by smaller stones resembling gravel. The entire construction
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95
Figure 5.
View of trench S1 (11×1 m) across the hedgerow of the agricultural terrace. The bedrock is situated at a depth of 1 m. The picture shows two areas,
one above the wall and one below the wall. In the area below the wall there is noticeably greater accumulation of stones.
Figure 6.
3D model of trench S1. A sophisticated construction of stones, which served as a protection from landslip and probably as an efective drainage
element, is visible at the model.
probably had a stabilizing and drainage function, serving the
purpose of soil erosion control and prevention of landslides
(Figures 5 and 6).
3.2 Archaeobotanical and anthracological analysis
Botanical macroremains were present in samples at very
small concentrations. The charred macroremains formed a
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smaller part of the assemblage; however, their appearance
is important for both dating and reconstruction of past
vegetation cover. The macroremains from the layers −40
to –80 cm have only an indicative role, while the charred
macroremains in the lowest strata of soil (−80 to –100 cm)
could be related to the building activity during the terrace
construction event. The dominant macroremains type in
the lower strata are charred needles of fr, following by
Cerealia
in a bad state of preservation, charred raspberry
(
Rubus idaeus
), and probably red elderberry (
Sambucus
cf.
racemosa
) (see Supplementary Online Material).
Uncharred botanical macroremains were found in the
samples and form part of the seed bank. The most frequent
originated from the mechanical layer −40 to –50 cm
(Figure 10). The majority of fnds belong to ruderals
(
Chenopodium album, Chenopodium
sp.,
Urtica dioica
),
but grassland species are present as well (
Ajuga genevensis,
Fragaria vesca/viridis, Alchemilla
sp.) The quantity of
uncharred macroremains decreased with depth. The ruderals
and weeds remains (
Chenopodium album, Chenopodium
sp.
, Verbascum blattaria, Polygonum aviculare, Veronica
hederifolia). Rubus fruticosus
and
Sambucus
cf.
racemosa
indicate a forest edge in the deepest layer (−90 to –100 cm).
Given the small number of fnds it is difcult to make broader
conclusions.
The lowermost “construction” layer (−90 to –100 cm)
contained a large amount of wood charcoal. A total of
211 fragments were analysed. Altogether only four tree taxa
were identifed. The quite dominant species was fr (
Abies
alba
), which was determined in 188 cases. Other identifed
tree taxa were alder (
Alnus
sp.) and poplar (
Populus
sp.)
– with almost the same number of determinations – and
pine (
Pinus sylvestris
) in one case. The average density
of anthracomass (1.049 g/l) was calculated from the total
weight of the analysed charcoal (10.49 g). The average
anthracomass was not calculated from the total weight
(29.031 g) due to the presence of unburned fragments in the
sample (Figure 7). All the mentioned tree taxa correspond to
the vegetation composition of a beech and fr forest, which
is assumed in the area from the map of natural potential
vegetation (Neuhäuslová
et al.
, 2001) and generally recorded
by palaeoecological data in the Jeseníky mountain area
(Dudová
et al.
, 2018).
Figure 7.
a) Basic quantitative anthracological data from the trench S1
soil deposits. b) Graph of representation of individual taxa (in perc.):
Abies
89.1%,
Populus
5.7%,
Pinus
0.5% and
Alnus
4.7%.
Figure 8.
a) Botanical macroremains, samples for
14
C. b) Radiocarbon dates diagram. Intervals of calendar age are given, where the true ages of the samples
are encompassed with a probability of ca. 68% and ca. 95%. Samples were dated in the Poznan Radiocarbon Laboratory. The dates were calibrated in the
OxCal software.
a)
b)
a)
b)
Samples for
14
C analysis from locality Valstejn
(Czech Republic)
Number of sampleType of materialSpeciesDepth
4050needlesAbies
40–50 cm
6070seedRumex
60–70 cm
7080needlesAbies
70–80 cm
8090seedRumex
80–90 cm
90100needlesAbies
90–100 cm
90100AcharacoalAbies
90–100 cm
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97
3.3 Radiocarbon dating
The radiocarbon dates obtained are summarized in Figure 8b.
Charred seeds and needles from the upper layers of the soil
profle (–40 cm to –90 cm) are dated to the 17–19
th
century.
A charred needle of
Abies alba
from the bottom layer
(–90 to –100 cm), which is immediately next to the stone
construction (Valstejn 90100), are dated to the interval 1479–
1644 AD (probability 95.4 %); a charred wood fragment
(Valstejn 90100A) from the same bottom layer is dated to
the interval 1299–1415 AD (95.4 % probability). Whereas
the dating of seeds falls into the historical period of village of
Valštejn’s foundation (“shortly before 1618”), the dating of
the charred wood fragment is ca. two centuries older.
3.4 Dating of modern soil deposits by radionuclides
The highest activity of the isotope
210
Pb is in the frst sample
–5 cm (top of soil profle in trench S1) with a value of
isotopic activity 0.106 Bq/g, (Figure 9). Soil samples from
lower positions express a much lower activity of isotope
210
Pb (–10 cm, –15 cm: 0.044 and 0.047 Bq/g). Isotopic
210
Pb
activity in the lower soil profle positions shows very low
values. The top of the soil profle represents arable soil with an
age indication no older than (arbitrary) 100 years. The lower
part of the soil profle can be assigned as older than 100 years.
Except for a very slightly elevated signal at a depth of –30 cm
(0.042 Bq/g), every layer above and below that layer indicated
activity around 0.030 Bq.
Figure 9.
Diagram depicting the activity of
the isotopes
210
Pb,
137
Cs and
226
Ra in the soil
profle of the trench S1.
Figure 10.
Schematic diagram depicting a comparison of radiocarbon age, lithology of the soil profle, botanical macroremains, artefacts and isotopes
210
Pb
and
137
Cs.
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98
A similar pattern was shown by the activity of isotope
137
Cs.
The entire top of the soil deposit expressed a high activity of
137
Cs (0.199 Bq/g), whereas at the levels –5 cm and –10 cm
activity still remained relatively high (0.066 and 0.084 Bq/g).
Lower soil samples below –20 cm showed values at almost
a zero level. This structure fully corresponds with the values
of isotope
210
Pb. The results of the
137
Cs measurement indicate
that the soil below 20 cm in the profle has no signal of nuclear
events after 1952 and could have been sedimented before this
date. The values of both isotopes demonstrate that, except for
the topsoil, which was contaminated in the 20
th
century, all the
soil deposit is older and undisturbed.
3.5 Archaeological artefacts
The soil samples contained a small amount of very small
ceramic sherds (5–10 mm) and iron nails (Figure 10).
Ceramic fragment fnds in the fotation residuum from trench
S1 do not exceed ten units per sample (see Supplementary
Online Material). The entire assemblage is comprised of hard,
well-fred, orange, ceramic fragments, then very hard sherds
with yellow glazing. These types of artefacts are present
in the upper layers and can be generally dated according
their technological characteristics to the 18–19
th
century
AD. The same ceramic fragment types are also present in
the lower strata of trench S1, where grey-white sherds are
also present. These grey-white sherds can be dated a little bit
earlier within the early modern period. The fnds of iron nails
and glass fragments are not chronologically signifcant. The
lowermost layer adjacent to the stone construction of terrace
did not contain any sherds.
4. Discussion
The village of Valštejn was founded shortly before 1618 AD
by Jan Kryštof of Wallenstein according to the written
sources. There is evidence that the village did not exist
in 1602 AD, so with high probability the evidence of its
existence suggests the second decade of the 17
th
century
AD (Kořínek, 2018; Historický lexikon obcí ČR, 2006;
Hosák, 2004; Bartoš
et al.
, 1994). The settlement moved
to a higher mountain area in this century and new villages
and their agrarian backgrounds have been established (Kuča,
2014). Radiocarbon data obtained from one of the hedgerows
of the agrarian background of the former Valštejn village
could confrm this date of foundation. There is a very short
time lag in the 17
th
century AD, as far as the establishment
of the village is concerned, between the historical and
archaeological/environmental dating (Fanta
et al.
, 2020).
The similar study for the former village Malonín provides a
comparison. This village in the Šumava Mountains was frst
mentioned in 1349 AD. The radiocarbon data obtained from
the bottom of a trench through a hedgerow showed a date of
1154–1271 AD. These radiocarbon dates preceded the frst
written mention by about ca. 150 years (Houfková
et al.
,
2015). It has been shown that the older village Malonín
demonstrates a longer time lag between the historical and
archaeological dating than was postulated in the general
“time lag” model (Fanta
et al.
, 2020). Despite these facts
we must be very critical with these results: only one trench
was dug in one part of the very large feld system of Valštejn
so far and these results may not apply for other parts of the
feld system. On the other hand, the results of excavation
in Valštejn trench S1 and associated analyses are fully in
agreement with the written sources and with the above-
mentioned general “time lag” model.
The key observation in the archaeobotanical analyses is
the determination of the macroremains of fr (
Abies alba
).
This taxon was determined as charred needles, and also as
charred wood fragments, directly from the layer immediately
covering the basement stone construction at the depth of
–90 to –100 cm. This evidence could indicate a forested
area before the establishment of the village and its agrarian
hinterland, and the action of tree fres during the landscape
transformation and construction of the feld system. The
composition of the past forest in the Jeseníky Mountains
and its surrrounding developed after 3500 BP towards a
dominance of
Fagus
,
Abies
and
Carpinus
, partially initiated
by human activity in later agricultural prehistory (Dudová
et al.
, 2018). Burning activities called
slash-and-burn
were
common practice to obtain land for agriculture from the
Neolithic period onwards (
e.g.
Emanuelsson, Segerström,
2003; Rösch, 2013) and it is probable it happened during the
landscape transformation around Valštejn at the beginning of
the 17
th
century. A similar situation was found in the case of
the four-hundred-year earlier Malonín village feld system
(Houfková
et al.
, 2015).
Abies alba
is a typical mountain
and submountain conifer growing usually at altitudes of
400 to 800 m asl. (Culek
et al.
, 2005). The main expansion
of
Abies
alba
was between the 13
th
and 16
th
century and it
grew mainly in forests near villages, on pastures and on
abandoned agrarian land. The wood of fr was favoured for
construction timber and it was one of the reasons for the
start of the decline in its population. Another reason was its
intolerance of intensive and long-lasting human pressure. The
population of
Abies alba
started to decline very signifcantly
from the 18
th
century and it was replaced by
Pinus
and
Picea
(Kozáková
et al.
, 2011).
One fragment of charred fr wood from the bottom layer
(–90 to –100 cm) was dated by the AMS radiocarbon method
(Valštejn 90100A 95.4%, probability 66.1%: 1299 AD–
1370 AD and 29.3% probability: 1380 AD –1415 AD) to the
High Medieval Period. The date is two hundred years older
than the expected construction of the agricultural terrace.
It seems to be an example of a typical “old wood” efect
as reported already for the frst time by M. Schifer (1986)
in the case of a southwestern USA pueblo chronological
discrepancy and reported later by other scholars (Zilhão,
2001; Kim
et al.
, 2019). The fragment of charcoal at the
bottom of trench S1 at Valštejn could have originated from
an old large tree from the near surroundings, felled and burnt
on site during the construction of the agricultural terrace. It
is one possibility of how to explain the discrepancy between
the charcoal and charred needle of the same species. It is not
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Landscape Transformed: Archaeological, Historical and Environmental Dating of the Early Modern Field System in Valštejn, Czech Republic
99
quite excluded that the needle, as an annual living part of
the fr, and the charcoal from the same species, could have
originated from the same individual, or perhaps the same fr
tree cohort.
The soil around Valštejn contained a high proportion
of stones. This fact must have been a problem during
ploughing. The stones had to be collected and piled up in
agrarian mounds, something very common in this region.
Stones were also used as material for construction purposes.
The main features were stony walls as the boundaries of
felds, which also protected the fushing of the topsoil
(the Czech expression for this feature is “kamenice”). The
historical feld system of Valštejn belongs to one of the best-
preserved in the Czech Republic. The stony walls are still
visible and they still fulfl their ecological function. The
length of one stone belt reaches approximately 1.4 km – and
they are already mentioned in describing the boundaries
of the village in the Joseph’s cadastre (Kořínek, 2016).
Hedgerows themselves were also made by the intentional
activity of peasants. As recorded on several other sites, they
built a stony construction on the bedrock with soil on it, and
continued building it regularly everywhere during the high
medieval and early modern landscape transformation. The
same, or a very similar system of hedgerow construction, can
also be found on other feld systems in the Czech Republic
– for example around the Oblík hill near Louny (northwest
Bohemia), and in Debrné (Krkonoše Mountains foothill;
unpublished site report of our research team). The above-
described system of landscape transformation generally
shows very thoughtful and extraordinarily exacting work
during the building activity, which probably took quite a lot
of energy and time of village people.
5. Conclusion
The Valštejn feld system, founded at the beginning of
the 17
th
century AD, belongs to one of the best-preserved
historical landscape units in the Czech Republic. The feld
system itself is quite remarkable, because the multifaceted
feld belts cover around 90% of the cadastre. The
archaeological and environmental research of Valštejn is part
of a broader feld investigation and of the testing of chosen
systems over the entire Czech Republic. The key points of
this study are the following:
The village of Valštejn was founded shortly before 1618 AD
according to historical written sources. The archaeological
excavation has been targeted to obtain material for its exact
dating and environmental reconstruction. Radiocarbon data
obtained from botanical annual macroremains (charred fr
needle) in the bottom layer of trench S1 coincide with the
time of the foundation of village. This radiocarbon date is in
concordance with a small “time-lag” probability (Fanta
et al.
,
2020). This time-lag between the written sources and the
archaeological record could already be only several decades
for the Early Modern Period in comparison to the Medieval
Period, where a time-lag can reach several centuries.
The bottom layer also contained a certain amount of
charcoal, probably originating from old wood burned
during the initial building activity and refecting the tree
canopy elements from before the hedgerow’s construction.
Radiocarbon data from the charcoal of the fr from the
bottom of trench S1 indicates a typical “old wood” efect.
Thanks to the younger (more realistic)
14
C interval obtained
from the fr needle, both data suggest the burning of an
old element of forest felled due to the long-strip feld and
hedgerow construction.
The conclusions of this study provide new insights into
the design and function of agrarian terraces, illustrating their
possible role in soil and water protection. The chosen excavated
hedgerow embodies its demanding construction – requiring
a large investment of labour and human efort. The most
important item of knowledge made by these archaeological
observations is the evidence concerning the elaborated
building stone elements. Such construction probably served
for the purposes of drainage and soil protection.
The study has also made a further contribution to the
method for dating historical feld patterns. As these valuable
landscapes are not yet protected by any legal measures in
the Czech Republic, this information creates a much-needed
basis for policies and protection guidelines aimed at their
conservation and sustainable management.
Acknowledgments
The article was created with the support of the Grant Agency
of the University of South Bohemia (project nr. 130/2019/H
– Theoretical and methodological aspects of development of
PhD programs in historical sciences) and with the support
of the grant: Identifcation and preservation of historic feld
patterns NAKI II – DG18P02OVV060.
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