Plant Use and Cereal Cultivation Inferred from Integrated Archaeobotanical Analysis of an Ottoman Age Moat Sequence (Szigetvár, Hungary)
Abstract
Suleiman the Magnificent died during the siege of Szigetvár in 1566, close to the battlefield in Turbék Vineyard Hill site, Hungary. On the place of his death, a memorial place was established with a tomb, a mosque, a monastery, and a deep moat system north of the building complex. After its destruction, the memorial place was covered with demolished material and soil. This significant site was re-identified and excavated during the archaeological, historical, and geoarchaeological research work that started in 2015. As a result of the correlative evaluation of previously published sedimentological and chronological data, the filling of the moat accumulated during the seventeenth century. Our goal was the natural and anthropogenic vegetation reconstruction of the adjacent region of the memorial place and the plant utilization of the community living there. During the analyses, more than 30,000 plant remains were identified belonging to 77 taxa. The results gave indications for ploughed lands, vegetable and fruit cultivation, vineyards, pasture lands, forest patches, and trampled areas related to active human activity. The lithostratigraphic and geochronological results of the moat sequence coincide well with our carpological and anthracological data.
1 Introduction
Suleiman the Magnificent (1494–1566) was one of the greatest sultans that ever ruled the Ottoman Empire who led 13 campaigns and died during the siege of Szigetvár in 1566, close to the battlefield in Szigetvár – Turbék Vineyard Hill site, Hungary. At the location of his death, a memorial place was established with a tomb, a mosque, a monastery, and a deep moat system north of the building complex (Figure 1). According to written resources (Fodor, 2020) a new pilgrim town, which Ottoman name was Türbe Kasabasi, was established at the decision of the next Sultan (Selim II) of the Ottoman Empire (Pap et al., 2015).

Location of the Szigetvár – Turbék Vineyard Hill site, Hungary (Gulyás et al., 2022).
How the former leader of the Ottoman Empire ended up in present-day Hungary is worth briefly summarizing. In the north-western part of Anatolia, the Ottoman Sultan, who founded the first Ottoman Dynasty at the end of the thirteenth century and the beginning of the fourteenth century, founded a relatively small country of a few thousand square kilometres. Then, through a steady and gradual expansion, they conquered Asia Minor, the Balkan Peninsula, and the city of Constantinople (modern Istanbul). By the fifteenth century, the Balkan countries, with the help of the Kingdom of Hungary, were fighting to the death against the Ottoman armies, which were expanding and conquering the Crimea, the western and northern Black Sea, the Azov Sea, and the Polish Kingdom of the late Middle Ages. Despite a preventive Christian war (with Bulgarian, Romanian, Albanian, Serbian, and Hungarian participants) throughout the Balkans, the key fortress of the Kingdom of Hungary, Nándorfehérvár (today’s Belgrade), was occupied after a second great siege in 1521, opening the way to Ottoman conquest of the interior of the Carpathian Basin. The Christian armies (Hungarian, Polish, Czech, and Croatian) defending the Kingdom of Hungary were annihilated by the Ottoman army which was led by Sultan Suleiman I at Mohács in 1526. In this battle, the Hungarian (and Czech) king (Louis II of Anjou, of Polish and French descent) was killed. After the war at Mohács, the Ottoman Empire gradually conquered a large part of the territory of the Kingdom of Hungary. At the same time, Egypt, Syria, Arab territories, almost the whole of the Middle East, Libya, and the coast of Algeria were conquered. Since they considered the Hungarian nobility to be related to the Turks, they established a vassal state dependent on the Ottoman Empire in the eastern part of the Carpathian Basin in the Transylvanian Basin (the Principality of Transylvania) and sought to conquer the Danube River valley. Their ultimate goal was to conquer the city of Vienna (which they called the Golden Apple), the centre of the Habsburg Empire.
The southern and central parts of the Kingdom of Hungary were conquered and integrated into the administrative system of the Ottoman Empire. While the northern and western parts of the Kingdom of Hungary became an integral part of the Habsburg Empire, which gave a legitimate ruler after the war at Mohács. During the conquest wars, the siege and capture of Szigetvár happened in 1566, defended by the Christian troops of the Croatian general Miklós Zrínyi (Nikola Šubić Zrinski). Sultan Suleiman, the leader of the Ottoman troops, was 72 years old by this time and died before the end of the siege, but the Sultan’s council concealed his death, and it was only after the siege and the release of the troops that his death was announced in Constantinople. The date of construction of the memorial place was put between 1577 and 1578 (Fodor, 2020; Hancz, 2014; Kitanics, 2014, Pap et al., 2015; Pap, 2019). Unfortunately, only sporadic historical data (tax documents, certificates) can be found about the location, environment, and land use of the memorial complex and the pilgrim town (Table 1).
Historical sources of Szigetvár–Turbék Vineyard Hill site (Pap et al., 2015)
Source of information | Places mentioned and their geographical nature | Land use | Installation of the site | Vegetation, plants and crops mentioned | |
---|---|---|---|---|---|
1. | Cserenkó Ferenc (1566) | Szemlőhegy hill, “up on the hill” | No data | No data | No data |
2. | Budina Sámuel (1566) | Szemlőhegy | near the vineyards | No data | Grape |
3. | Ottoman source (1573) | No data | Orchard | Not yet built-in | Fruits (no species are mentioned) |
4. | Ottoman registry (1574) | No data | No data | Tekke (dervish monastery), a mosque where Suleiman’s body was buried temporarily | No data |
5. | Ottoman registry (1579) of Szigetvár and its neighbourhood | Suleiman Khan’s monastery (kasaba) | 1 Vineyard, 5 arable lands | A settlement of two mahallas: Mehmed’s (son of Bajezid) with 23 households and Veli’s (son of Ali) with 28 households | Grape, cereals |
6. | Evlia Çelebi (1664) | On the top of a high mountain | Garden-hill location | Elongated building | Garden, grape |
7. | Wagner, Ch. (1689) | Hill (Türbe Daghi) | Vineyards and orchards | No data | Cherry, grape |
8. | Urbarium (1692) | Village of Turbék on a hill | Orchard, vineyard and arable land | Masonry church with high tower | Fruit, grape, cereals |
9. | Urbarium (1692) | Turbék vineyard hill | Vineyards and orchards | Abandoned Ottoman mosque | Grape, fruit |
10. | Hoffinanz Ungarn (1693) | Turbék | No data | marble chapels, lead roof, tower where Suleiman’s tomb once stood | No data |
11. | Urbarium (1720) | Vinayard hill | Vineyard | A mosque in the shape of a tomb | Grape |
12. | Prothocollum (1717–1734) | Ottoman fortification | Arable land (corn) and uncultivated land where the fort once stood | Ottoman walls, a fortress, and well | Corn, grape |
13. | Prothocollum (1738) | Ottoman fortification | Arable land (corn) | Tekke (dervis monastery) | Corn |
14. | Urbarium (1747) | Ottoman fortification | Arable land | No data | Cereals |
15. | Contractus (1789) | Ottoman fortification | Arable land | No data | Cereals |
Sources: 1: Ruzsás & Angyal, 1971; 2: Molnár, 1978; 3: Vatin, 2005; 4: Sinan Bey oğlu eski Sadrazam Şehit Mehmet Paşa Vakfı 1574; 5: Vass, 1993; 6: Çelebi et al., 2003; 7: Wagner, 1700; 8: [Archival document], (1604–1891); 9: [Archival document], 1692; 10: [Archival document], 1692; 11. [Archival document], 1693; 12. [Archival document], (1717–1734); 13: [Archival document], 1720; 14: [Archival document], 1738; 15: [Archival document], 1747.
In February 1664, Count Pál Esterházy, the prince of the Habsburg Empire and Palatine of the Kingdom of Hungary, during the winter campaign that was led by Miklós Zrínyi, made a feather drawing of the occupied tomb (Figure 2), in which it is visible that a moat surrounded the tomb fortress from the north. During this campaign, the complex was partially destroyed and then rebuilt. The life of the tomb and the pilgrim town ended in 1689 after the successful siege of the Szigetvár fortress and the occupation of the tomb by the Habsburg army. The buildings of the memorial site were demolished in 1692, the pilgrim town was abandoned, and the whole area was depopulated (Pap et al., 2015). The land was divided into an agricultural zone, where orchards, arable lands, gardens, and vineyards were established. The memorial place was covered with demolished material and soil. This significant site was re-identified and excavated only during the archaeological, historical, and geoarchaeological research work by Pál Fodor and Norbert Pap, which started in 2015. Following the complex identification of the site of the tomb (Pap et al., 2015), the location of the filled-up moat was identified by geoarchaeological drillings and then excavated under the supervision of archaeologists. During the fieldwork, several datable artefacts (an Ottoman medini, a denarius of Mathias II, and a Turkish knife) have come to light indicating the seventeenth-century origin of the moat sequence. Based on the chronological data (Figure 3), the moat must have been in use between 1651 ± 36 cal AD years and 1692 AD (Gulyás et al., 2022). Two major changes, erosion-accumulation events are notable in the sediment sequence of the profile based on lithological, sedimentological (Sümegi, 2020), geochemical, magnetic susceptibility, and chronological analyses (Gulyás et al., 2022). Based on chronological data, the older event must be placed to around 1670 ± 12 and 1674 ± 14 cal AD years (Gulyás et al., 2022), which is in line with historical dates marking the destruction of the site during the winter campaign of the Hungarian troops in 1664 (Fodor, 2020; Hancz, 2014; Kitanics, 2014; Pap et al., 2015; Pap, 2019). The second event corresponds to another destruction of the site (1684 ± 36 cal AD years), probably the re-occupation of the site in 1688/1689 (Fodor, 2020; Gulyás et al., 2022; Hancz, 2014; Kitanics, 2014; Pap et al., 2015; Pap, 2019).

Pál Eszterházy’s drawing about the memorial place from 1664. 1 = The tomb of Suleiman I. (türbe), 2 = interior of the Ottoman mosque, 3 = exterior of the Ottoman mosque, 4 = building of the halveti dervish (Ottoman monastery: závija) 5 = moat of the ottoman memorial place, 6 = the building of the Ottoman soldiers protecting the memorial place; red circle denotes sampling location.
This publication presents the results of anthracological and carpological analyses of the filling of the moat protecting the Dervish monastery, one of the most important elements of this excavation. We aimed to specify the archaeobotanical character of the memorial tomb and the eating habits of the population of the monastery and the pilgrim town. As there are only sporadic written sources and information about the memorial place and the pilgrim town, as well as about the environment of the site and its former inhabitants, our data provide new information on the natural flora, cultivated plants, and diet of people who lived there in the seventeenth century.
2 Materials and Methods
2.1 Location, Climate, and Natural Vegetation
Szigetvár is located in SW Hungary (Figure 1), in Baranya county, 33 km from Pécs and 40 from Kaposvár. The coordinates of the study site are 46°07′92″N and 17°84′58″E, 113 m a.s.l. The climate of the site is moderately warm and moderately dry (Figure 4). Continental and sub-Mediterranean climates characterize the site with warmer winters. According to the data of the nearest climate station (Pécs), its annual average temperature is 15.4°C, and its precipitation is 624 mm. The most important potential forest communities of the Somogyi flora are alder-ash (Alneto–Fraxinetum pannonicae) groves, oak–ash–elm gallery forest (Querco–Ulmetum), silver lime–turkey oak (Tilio argenteae–Quercetum cerris), hornbeam-sessile oak (Querco petraeae–Carpinetum praeillyricum), and beech forest (Vicio oroboidi-Fagetum; Marosi & Somogyi, 1990).
2.2 Sampling, Carpological, and Anthracological Analyses
Samples were taken at every 15 cm in a column for the archaeobotanical analysis. A total of 14 samples of ca. 30 L (per sample) were taken and wet-sieved to retrieve organic remains suitable for paleoecological studies. The archaeobotanical material was isolated in standard flotation equipment (Weiss & Kislev, 2004) in a laboratory, to avoid recent contamination. A sieve with 0.4 mm mesh was used to catch light fractions such as smaller seeds (e.g. poppy seed; Figueiral, Bouby, Buffat, Petitot, & Terral, 2010). Charcoals larger than 4 mm in size were counted (Asouti, 2003; Asouti & Austin, 2005; Chabal, Fabre, Terral, & Théry-Parisot, 1999; Keepax, 1988). We used identification atlases, professional publications (Cappers, 2006; Jacomet & Kreuz 1999; Jacomet, 2006; Nixon, Murray, & Fuller, 2011), and our recent comparative material for the identification of thousands of carpological remains (seeds/fruits). The charred wood remains were analysed by an optical microscope at 100, 200, and 500 × magnifications. Wood anatomical identification publication (Schweingruber, 1990) was used, as well as our own subfossil and fossil reference collection (Náfrádi, 2015) for the identification.
3 Results
3.1 Anthracology
During the flotation to recover the macrobotanical material, a high number (5,445 pcs) of charred wood fragments were found in the moat of the tomb. Some of the remains were poorly preserved due to overburning, and thus could not be identified to genus level. The results of the anthracological analysis are detailed in Table 2. Oak (Quercus sp.), maple (Acer sp.), alder (Alnus sp.), and poplar/willow (Populus/Salix sp.) genera were identified. In the charred charcoal material, coniferous fragments were identified, and a more precise identification was not possible due to overburning.
The number and taxon of charred wood remains of Szigetvár – Turbék Vineyard Hill site, Hungary
Depth (cm) | Preservation (+: well; –: poor) | Total number of fragments | Taxon |
---|---|---|---|
40–55 | + | 143 | Quercus |
55–60 | ‒ | 120 | Quercus |
18 | Overburnt Alnus | ||
60–85 | + | 42 | Acer |
66 | Alnus | ||
209 | Quercus | ||
85–100 | + | 352 | Quercus |
100–115 | + | 25 | Alnus |
310 | Quercus | ||
115–130 | ‒ | 109 | Quercus |
12 | Populus/Salix | ||
19 | overburnt | ||
130–145 | ‒ | 75 | Acer |
89 | Alnus | ||
182 | Quercus | ||
42 | Overburnt | ||
145–160 | + | 24 | Acer |
32 | Alnus | ||
342 | Quercus | ||
160–175 | ‒ | 112 | Alnus |
288 | Quercus | ||
302 | Overburnt | ||
175–190 | + | 376 | Acer |
440 | Alnus | ||
190–205 | + | 42 | Acer |
119 | Alnus | ||
526 | Quercus | ||
205–220 | ‒ | 350 | Overburnt coniferous |
220–235 | + | 354 | Alnus |
235–250 | + | 181 | Alnus |
96 | Populus/Salix | ||
48 | Overburnt |
3.2 Carpology
As a result of the carpological analysis, 77 taxa of 14 samples were found that cover 32,557 remains of fragments (Tables 3–5). In the individual samples and the complex carpological assemblage, the diaspora of European black elderberry (Sambucus nigra [23,678 remains]), European dwarf elder (Sambucus ebulus [4,610 remains]), and greater celandine (Chelidonium majus [2,949 remains]) dominated; the number of these species (31,237) accounted for the ratio of 95.94% of the findings. Therefore, during quantitative evaluation, the number of these species was not considered, and we took the ratio of these three species to zero when assessing the dominance of each group/taxa, for better perspicuity. So the indicator elements with a lower ratio and their quantitative change became more evident in the examined profile.
Cultivated plant remains of Szigetvár – Turbék Vineyard Hill site, Hungary
Species | Charred/Preservation (+/+: charred and well preserved; −/+: non-charred and well preserved; +/−: charred and poorly preserved; −/−: non-charred and poorly preserved) | Depth (cm) | ||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
40–55 | 55–70 | 70–85 | 85–100 | 100–115 | 115–130 | 130–145 | 145–160 | 160–175 | 175–190 | 190–205 | 205–220 | 220–235 | 235–250 | Total number | ||
+/+; −/+; +/−; −/− | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | |
Hordeum vulgare | +/+ | 1 | 1 | 1 | 3 | |||||||||||
Hordeum vulgare L. var. polystichon Haller | +/+ | 6 | 3 | 3 | 73 | 5 | 90 | |||||||||
Cerealia fragm. | +/+ | 35 | 36 | 40 | 33 | 32 | 2 | 51 | 12 | 241 | ||||||
Panicum miliaceum | +/+ | 2 | 2 | 1 | 1 | 3 | 1 | 1 | 1 | 12 | ||||||
Secale cereale | +/+ | 5 | 4 | 3 | 2 | 7 | 1 | 1 | 6 | 2 | 9 | 19 | 1 | 1 | 61 | |
Triticum aestivum/nudum/turgidum | +/+ | 2 | 3 | 1 | 1 | 2 | 1 | 1 | 3 | 2 | 16 | |||||
Triticum sp. | +/+ | 1 | 1 | 2 | ||||||||||||
Number of cereals | 42 | 49 | 46 | 5 | 44 | 4 | 3 | 46 | 5 | 84 | 74 | 19 | 2 | 2 | 425 | |
Taxon richness | 3 | 5 | 4 | 2 | 4 | 4 | 3 | 5 | 3 | 4 | 4 | 3 | 2 | 2 | 7 | |
Brassica nigra | +/+ | 5 | 9 | 6 | 4 | 1 | 1 | 1 | 27 | |||||||
Lens culinaris | +/+ | 1 | 1 | 2 | ||||||||||||
Linum usitatissimum | +/+ | 1 | 1 | |||||||||||||
Pisum sativum | +/+ | 1 | 2 | 1 | 4 | |||||||||||
Papaver somniferum | +/+ | 1 | 1 | |||||||||||||
Pastinaca sativa | −/− | 1 | 1 | |||||||||||||
Number of leguminous, oil and fibre plants | 1 | 5 | 9 | 7 | 5 | 1 | 2 | 4 | 1 | 1 | 36 | |||||
Taxon richness | 1 | 1 | 1 | 2 | 2 | 1 | 2 | 3 | 1 | 1 | 6 | |||||
Corylus avellana | +/+ | 1 | 1 | 1 | 3 | |||||||||||
Juglans regia | +/+ | 1 | 1 | |||||||||||||
Prunus avium/cerasus | +/+ | 5 | 3 | 5 | 3 | 10 | 4 | 2 | 32 | |||||||
Prunus cf. domestica | +/+ | 2 | 1 | 3 | ||||||||||||
Vitis vinifera | −/+ | 10 | 2 | 16 | 6 | 1 | 1 | 1c | 37 | |||||||
Number of fruits | 15 | 5 | 23 | 9 | 1 | 1 | 2 | 2 | 10 | 4 | 3 | 1 | 76 | |||
Taxon richness | 2 | 2 | 3 | 2 | 1 | 1 | 2 | 2 | 1 | 1 | 2 | 1 | 5 | |||
Total number of cultivated plants | 58 | 59 | 78 | 21 | 50 | 6 | 7 | 48 | 9 | 94 | 79 | 23 | 2 | 3 | 537 | |
Total taxon richness | 6 | 7 | 8 | 6 | 7 | 6 | 7 | 7 | 6 | 5 | 6 | 6 | 2 | 3 | 18 |
Weed remains of Szigetvár – Turbék Vineyard Hill site, Hungary (*during quantitative evaluation the number of these species were not considered)
Species | Charred/Preservation (+/+: charred and well preserved; −/+: non-charred and well preserved; +/−: charred and poorly preserved; −/−: non-charred and poorly preserved) | Depth (cm) | ||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
40–55 | 55–70 | 70–85 | 85–100 | 100–115 | 115–130 | 130–145 | 145–160 | 160–175 | 175–190 | 190–205 | 205–220 | 220–235 | 235–250 | Total number | ||
+/+; −/+; +/−; −/− | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | |
Agrostemma githago | +/+ | 1 | 1 | |||||||||||||
Bromus arvensis | +/+ | 2 | 1 | 3 | ||||||||||||
Bromus secalinus | +/+ | 1 | 1 | 0 | 2 | |||||||||||
Carduus nutans | −/− | 2 | 3 | 1 | 1 | 7 | ||||||||||
Centaurea cyanus | +/+ | 1 | 1 | 2 | ||||||||||||
Chelidonium majus* | −/− | 10 | 16 | 34 | 78 | 182 | 446 | 752 | 621 | 14 | 436 | 189 | 138 | 25 | 8 | 2,949 |
Chenopodium album | −/− | 37 | 10 | 15 | 52 | 52 | 18 | 7 | 15 | 13 | 2 | 32 | 27 | 16 | 6 | 302 |
Chenopodium hybridum | −/− | 5 | 3 | 3 | 14 | 14 | 4 | 5 | 2 | 1 | 1 | 1 | 12 | 7 | 3 | 75 |
Chenopodium murale | −/− | 1 | 1 | 1 | 1 | 1 | 1 | 1 | 7 | |||||||
Datura staronium | −/− | 30 | 14 | 21 | 18 | 14 | 10 | 2 | 21 | 1 | 16 | 2 | 1 | 150 | ||
Descurainia sophia | +/+ | 5 | 2 | 3 | 1 | 4 | 1 | 1 | 1 | 18 | ||||||
Fallopia convolvulus | +/+ | 1 | 2 | 3 | ||||||||||||
Galium aparine | +/+ | 1 | 1 | |||||||||||||
Galium spurium | +/+ | 1 | 2 | 1 | 4 | |||||||||||
Glaucium corniculatum | −/− | 1 | 1 | |||||||||||||
Hyoscyamus niger | −/− | 1 | 1 | 2 | ||||||||||||
Lolium temulentum | +/+ | 1 | 1 | 2 | 1 | 5 | ||||||||||
Leonurus cardiaca | −/− | 1 | 1 | |||||||||||||
Malva pusilla | −/− | 1 | 1 | |||||||||||||
Picris hieracioides | −/− | 5 | 2 | 2 | 4 | 1 | 1 | 1 | 16 | |||||||
Polygonum aviculare agg. | +/+ | 1 | 1 | 2 | ||||||||||||
Polygonum lapatifolium | +/+ | 1 | 1 | |||||||||||||
Portulaca oleracea | −/− | 39 | 15 | 4 | 10 | 1 | 1 | 1 | 7 | 78 | ||||||
Sambucus ebulus* | −/− | 18 | 119 | 190 | 327 | 365 | 213 | 250 | 875 | 532 | 388 | 102 | 425 | 432 | 332 | 4,610 |
+/+ | 2 | 1 | 5 | 13 | 16 | 1 | 4 | |||||||||
Sambucus nigra* | −/− | 49 | 289 | 293 | 698 | 1,181 | 1,259 | 1,707 | 4,336 | 753 | 3,784 | 5,603 | 1,681 | 974 | 328 | 23,678 |
+/+ | 1 | 3 | 6 | 16 | 71 | 292 | 292 | 57 | 5 | |||||||
Setaria glauca | +/+ | 1 | 1 | 1 | 3 | |||||||||||
Setaria viridis/verticillata | +/+ | 2 | 1 | 3 | ||||||||||||
Sinapis arvensis | +/+ | 1 | 1 | 1 | 5 | 1 | 1 | 10 | ||||||||
Solarum nigrum | +/+ | 1 | 1 | |||||||||||||
Spergula arvensis | −/− | 1 | 1 | 1 | 3 | |||||||||||
Stachys annua | −/− | 1 | 1 | |||||||||||||
Stellaria media | −/+ | 11 (6C) | 3 | 1 | 1 | 1 | 17 | |||||||||
Urtica dioica | −/− | 1 | 1 | 1 | 1 | 1 | 1 | 6 | ||||||||
Number of weeds | 214 | 484 | 570 | 1,214 | 1,832 | 2,036 | 3,032 | 6,189 | 1,319 | 4,694 | 5,942 | 2,290 | 1,469 | 679 | 31,964 | |
Taxon richness | 13 | 14 | 13 | 15 | 10 | 14 | 10 | 12 | 10 | 12 | 13 | 12 | 14 | 7 | 33 |
Near-natural vegetation and ornamental vegetation remains of Szigetvár – Turbék Vineyard Hill site, Hungary
Depth (cm) | Charred/Preservation (+/+: charred and well preserved; −/+: non-charred and well preserved; +/−: charred and poorly preserved; −/−: non-charred and poorly preserved) | 40–55 | 55–70 | 70–85 | 85–100 | 100–115 | 115–130 | 130–145 | 145–160 | 160–175 | 175–190 | 190–205 | 205–220 | 220–2350 | 235–250 | Total number |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Species | +/+; −/+; +/−; −/− | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs | pcs |
Eleocharis palustris | +/+ | 1 | 1 | 2 | ||||||||||||
Carex vulpina | +/+ | 1 | 1 | 1 | 1 | 4 | ||||||||||
Schoenoplectus lacustris | +/+ | 1 | 1 | |||||||||||||
Solanum dulcamara | −/− | 1 | 1 | |||||||||||||
Alisma plantago-aquatica | −/− | 1 | 1 | |||||||||||||
Carex flacca Schreb. | +/+ | 1 | 1 | 2 | ||||||||||||
Carex hirta | −/− | 1 | 1 | |||||||||||||
Barbarea stricta. | −/− | 1 | 1 | |||||||||||||
Myosoton aquaticum | +/+ | 1 | 2 | 1 | 1 | 5 | ||||||||||
Ranunculus repens | +/+ | 1 | 1 | |||||||||||||
Chenopodium polyspermum | −/− | 5 | 4 | 9 | ||||||||||||
Chrysanthemum leucanthemum | +/+ | 1 | 1 | |||||||||||||
Carex distans. | +/+ | 2 | 2 | |||||||||||||
Betula pendula | −/− | 1 | 2 | 2 | 2 | 7 | ||||||||||
Fragaria vesca | +/+ | 1 | 1 | 1 | 3 | |||||||||||
Picea abies | +/− | 1 | 1C | 2 | ||||||||||||
Prunus spinosa | +/+ | 1 | 1 | |||||||||||||
Rubus fruticosus | −/− | 1 | 1 | 2 | ||||||||||||
Veronica hederifolia | +/+ | 1 | 1 | |||||||||||||
Prunella vulgaris | +/+ | 1 | 1 | |||||||||||||
Calamintha acinos | −/− | 1 | 1 | |||||||||||||
Lamium amplexicaule. | −/− | 1 | 1 | 2 | ||||||||||||
Medicago minima. | +/+ | 1 | 1 | |||||||||||||
Plantago lanceolata | +/+ | 1 | 1 | |||||||||||||
Ranunculus bulbosus | −/− | 1 | 1 | |||||||||||||
Rumex crispus | +/+ | 1 | 1 | |||||||||||||
Trifolium repens | −/− | 1 | 1 | |||||||||||||
Number of seeds | 4 | 0 | 3 | 9 | 5 | 6 | 1 | 3 | 9 | 1 | 3 | 6 | 5 | 1 | 56 | |
Taxon richness | 4 | 0 | 3 | 8 | 1 | 4 | 1 | 3 | 8 | 1 | 3 | 3 | 4 | 1 | 27 |
The carpological findings were diverse regarding charring and preservation (Tables 3–5). The wet condition of the moat helped preserving findings, half of the remains were carbonized, but still identifiable. The moat was periodically or permanently filled with water which preserved the seeds. As uncharred remains were also found in very deep layers, we do not consider it to be recent contamination.
In Tables 3–5, the preservation of certain carpological species and if they are carbonized or not are marked as +/+; +/−;−/+;−/− (+/+: charred and well preserved; −/+: non-charred and well preserved; +/−: charred and poorly preserved; −/−: non-charred and poorly preserved). In most cases, the species were either only carbonized or not carbonized in each sample. In general, the cultivated plants and their weeds were carbonized. Where a species was both carbonized and not carbonized, we indicated this by adding letter C (carbonized) in the sample depth, e.g. common grapevine (Vitis sp.) between 145 and 160 cm had 1 seed that was carbonized (1 C). However, where a given depth (sample) had a mixture of carbonized and not carbonized, we left the number of seeds and indicated next to it how many of these were carbonized (e.g. common chickweed [Stellaria media] 11 (6 C) = 6 out of 11 seeds were carbonized).
3.2.1 Cultivated Plants
About 20% of the analysed plant species are cultivated crops (18 species, 537 pieces remains). More categories could be distinguished in this group (Table 3).
3.2.1.1 Cereals
The majority of cultivated plants (Table 4), in terms of both species (41%) and the number of remains (74%), are cereals, although the majority of the grains were poorly preserved. Totally five cereal species turned up in the samples (Table 4). Barley (Hordeum distichon/vulgare) has the highest number among cereals (93 remains), and the majority is six-row barley (Hordeum polystichum). The number of rye (Secale cereale) is slightly lower, 61 remains. The number of common wheat/bread wheat (Triticum aestivum/nudum/turgidum, 16 remains) and common millet (Panicum miliaceum, 12 remains) is nearly similar in the samples of the moat. More than 200 cereal fragments were found that could not be identified at species level.
3.2.1.2 Leguminous, Oil and Fibre Plants, Herbs
Lentil (Lens culinaris, two pieces) and pea (Pisum sativum, four remains) turned up in two and three samples. Opium poppy (Papaver somniferum, one remain) occurred only in one sample while black mustard (Brassica nigra, 27 remains) in seven samples. Both flax (Linum usitatissimum, one remain) and parsnip (Pastinaca sativa, one remain) turned up in only one sample (Table 3).
3.2.1.3 Cultivated Fruits
Only a small number of fragmented seeds/fruit stones of cultivated fruits were present in the samples of the moat filling. Nevertheless, these have an indicative value (Table 3). All hard-shell fragments were charred. In most samples, sweet cherry/sour cherry (Prunus avium/cerasus) fruit stones occurred (32 remains). Unfortunately, the exact identification of the fragmented seeds was not possible; however, it certainly was a cultivated form (Faust & Surányi, 1999; Necipoğlu, 1997). In addition, the hard-shell fragments of plum (Prunus domestica, three remains) and walnut (Juglans regia, one remain) were identified. Fragments of hazelnut (Corylus avellana, three remains) were found in three samples. Common grape vine (Vitis vinifera, 37 remains) seeds turned up in half of the samples, and most of them were fragmented; however, undamaged seeds occurred as well which may provide an opportunity to determine additional cultural varieties and types (Mravcsik et al., 2015). Most of the grape seeds were waterlogged, ten remains of charred grape seeds turned up only in one sample.
3.2.2 Arable and Ruderal Weeds
The species list and the number of weed remains per sample are detailed in Table 4. As we mentioned earlier, European black elderberry (Sambucus nigra), European dwarf elder (Sambucus ebulus), and greater celandine (Chelidonium majus) occurred with the highest values. White goosefoot (Chenopodium album), thorn apple (Datura stramonium), common purslane (Portulaca oleracea), and maple-leaved goosefoot (Chenopodium hybridum) turned up in much smaller, but still significant quantities. Other species are represented in much smaller numbers; however, weeds indicating the sowing season (Colledge, Conolly, & Shennan, 2004; Grabowski, 2011; Kreuz & Schäfer, 2011; Lempiäinen-Avci, Haggrén, Rosendahl, Knuutinen, & Holappa, 2017; Pelling, Campbell, Carruthers, Hunter, & Marshall, 2015; Pósa, Vinogradov, & Gyulai, 2020) have also been found among them, for example, corn-cockle (Agrostemma githago), field brome (Bromus arvensis), rye brome (Bromus secalinus), flixweed (Descurainia sophia), cornflower (Centaurea cyanus), false cleavers (Galium spurium), wild mustard (Sinapis arvensis), darnel (Lolium temulentum), and corn spurry (Spergula arvensis).
3.2.3 Near-Natural Vegetation
Many-seeded goosefoot (Chenopodium polyspermum), giant chickweed (Myosoton aquaticum), and true fox sedge (Carex vulpine) were the most frequent taxa among the elements of natural vegetation (Table 5). Common spikerush (Eleocharis palustris), blue sedge (Carex flacca), distant sedge (Carex distans), strawberry (Fragaria vesca), European blackberry (Rubus fruticosus), and common henbit (Lamium amplexicaule) turned up in few samples, while other taxa appeared in only one sample.
3.2.4 Ornamental Plants
The remains of European white birch (Betula pendula) and the cone and pine needles of Norway spruce (Picea abies) turned up (Table 5).
4 Discussion and Conclusion
4.1 Results in the Light of Erosion-Accumulation Events
Gulyás et al. (2022) marked two erosion-accumulation events according to grain size, geochemical analysis, and magnetic susceptibility data. These two intervals between 110–130 and 170–180 cm indicate an eroded soil covering the surrounding areas. These two zones are identified as erosion-accumulation events I (between 190 and 160 cm) and II (between 130 and 50 cm; Figure 5). Furthermore, the second event can be subdivided into two more zones, between 130 and 100 cm and between 100 and 50 cm (Gulyás et al., 2022).

Walter–Lieth climate diagram based on the data of Pécs climate station in the same microlimatic position as Szigetvár – Turbék Vineyard Hill site 1. Monthly average temperature 2. Monthly averages (red dots) of the hottest months (multi-year average) 3. Monthly averages (blue dots) of the coldest months (multi-year average) 4. Monthly average precipitation 5. Precipitation maximum at the beginning of summer 6. Secondary autumn precipitation maximum (sub-Mediterranean climatic effect).
Figure 5 clearly shows the changes in the number of cereals, legumes, fruits, near-natural vegetation, weeds, greater celandine (Chelidonium majus), European dwarf elderberry (Sambucus ebulus), European black elderberry (Sambucus nigra), and charred wood remains in the profile from the bottom up. Even though only small amounts of remains were found for some plant groups, the curves show good correspondence. The quantitative variation of cereals is the opposite of that of natural vegetation. The reduction in the proportion of natural vegetation coincided with the first stage of erosion when Hungarian troops destroyed the memorial site during the winter campaign of 1664. Likewise, the peak in the amount of charcoal can be dated to this period. Taking into account geochemical analyses, including potassium variations (Gulyás et al., 2022), the charcoal peaks follow the potassium peaks exactly, confirming the presence of burning horizons (Figure 5). Probably the burning of the buildings during the re-occupation of the area in the second half of the seventeenth century contributed to the poor preservation of the remains, as the Christian troops ransacked the memorial site and partially destroyed it, but did not take the castle of Szigetvár (Gulyás et al., 2022).
![Figure 5
Main archaeobotanical groups and their number through the profile (*the number of Sambucus nigra [23,678 pieces], Sambucus ebulus [4,610 pieces], Chelidonium majus [2,949 pieces] remains were not taken into account in the calculation of dominance).](/document/doi/10.1515/opar-2022-0359/asset/graphic/j_opar-2022-0359_fig_005.jpg)
Main archaeobotanical groups and their number through the profile (*the number of Sambucus nigra [23,678 pieces], Sambucus ebulus [4,610 pieces], Chelidonium majus [2,949 pieces] remains were not taken into account in the calculation of dominance).
The highest number of cereals appeared during the first erosion-accumulation event. This probably suggests that the memorial place was cleaned up after the Hungarian troops had ransacked it, meaning that these cereal grains were re-accumulated multiple times before being thrown into the moat surrounding the memorial site. The spread of near-natural vegetation elements and that of greater celandine (Chelidonium majus), European dwarf elderberry (Sambucus ebulus), and European black elderberry (Sambucus nigra) is contrasting. The seeds of grape vine appeared after the first attempt of the Hungarian troops to re-occupy the area; however, only sporadic grape seeds were found, but they are nevertheless indicative. There are written historical records about the presence of vineyards on the site from the second half of the sixteenth century (Table 1, sources 3 and 5) that support grape production and wine consumption. The Ottoman Empire and the spreading Islamic customs, which prohibit the consumption of wine according to the Qur’an, did not restrict (Fodor, 1998) the development of viticulture in the conquered territories and wine consumption for Christian communities was allowed if they paid wine tax (Égető, 1993; Hegyi, 1976; Káldy-Nagy, 1985). This later, together with the wine trade tax, could have been a very significant amount based on written sources of taxation (Fekete, 1993; Pákay, 1984; Szakály, 1981) and, of course, Ottoman communities also paid tax for growing grapes (Káldy-Nagy, 1985). Tax sheets (Fekete, 1993; Pákay, 1984; Szakály, 1981) and written sources (Table 1) indicate that well-developed grape production subsisted despite wars (Andrásfalvy, 1961).
4.2 Evaluation of Chared Wood Remains
One of the prominent issues of our archaeobotanical analyses is how charred wood remains got into the moat of the tomb. On the one hand, the wood material may have derived from the firewood of the tomb’s heating system and come from household waste from the people living in the pilgrim town. On the other hand, the destruction and burning of the tomb in 1664 and in 1689/90 (Gulyás et al., 2022) may also have contributed to the accumulation and overburning of charred material.
The anthracological data indicate that non-native, planted coniferous trees might have existed in the vicinity of the tomb. These identified taxa have completely different properties. Oak and maple trees are hardwoods that possibly were used as structural elements such as columns or beams. Both taxa were used as beams, columns, furniture, monuments, entrances, or doors and as firewood (Hæggström, 1992; Rinaldi, Mazzanti, & Bosi, 2013). Contrarily, alder and poplar/willow trees are softwoods and are mainly used for making wattle fences, partitioning rooms, the construction of the walls of adobe houses and wells (Cywa, 2018; Murray, Murray, & Lindsay, 2009; Mighall et al., 2018).
Oak remains may have derived from the wood material of the bridge over the moat that was marked in the historical map from 1664 (Figure 2) as well. It is well known that Ottoman bridges were predominantly made of oak in the Carpathian basin (Papp & Gryneus, 2011). Additionally, oak utilization as construction wood (Papp & Gryneus, 2011) in Ottoman fortresses, baths, and usually everywhere in architecture was widespread as it can be used in many ways. Maple was only secondary compared to oak and could be used on surfaces as a wainscot wood (Cywa, 2018; Deforce, 2017) during the construction of the tomb, and in baths (Yeşilada et al., 1999). Signs of abrasion indicating filling up and re-accumulation could not be detected on charcoal samples. Coniferous charcoals were overburnt thus we were not able to identify them at a species level. However, the presence of spruce needles in the archaeobotanical assemblage might support their presence as ornamental trees in the monastery garden. Since the local ecological conditions of the study area differ from the natural needs of spruce and birch, these species could have been planted around the tomb or transported from a further site.
4.3 Cereal Cultivation in the Seventeenth Century
Besides charred wood remains a significant number (32,557 remains) of other macrobotanical remains were found, covering 77 taxa, so a detailed carpological analysis was performed.
A change in sustenance cannot be ruled out either, since as a result of the war, food production had to change towards the more mobile, extensive animal husbandry that required less human work, from the second half of the sixteenth century (Bartosiewicz, 1995). The dynamic growth of animal husbandry may also have been amplified by trade, so the population growth and urbanization in Italy, Germany, the Czech Republic, and Austria promoted the increase of living animal trade (Bartosiewicz, 1995).
The exposure of the site, its loess bedrock, the anthroposol soil (Capra, Ganga, Grilli, Vacca, & Buondonno, 2015) that formed from brown forest soil due to human impact (fertilization, agriculture), and the microclimatic conditions of the area (Figure 2) enabled diverse crop production even during the colder and wetter climatic period of the Little Ice Age in the seventeenth century. Barley (Hordeum sp.) is one of the oldest crops; it has been grown since the Neolithic in the Carpathian Basin (Gyulai, 2010). It has been used for making porridge, bread, beer, and as animal forage, nowadays as well (Sullivan, Arendt, & Gallagher, 2013). The significance of rye (Secale cereale) increased during the medieval period in the Carpathian basin (Gyulai, 2010). It was sewn together with wheat (Cossani, Savin, & Slafer, 2007). Rye spikes, rising above wheat, were pinched. In the case of a whole field when rye grew above the wheat, it was cut to make the wheat ripe. Rye is less demanding than wheat in terms of soil and climatic conditions (Nesbitt & Samuel, 1998). The utilization of rye is similar to wheat; it is used as bread flour and thatching roofs (de Moulins, 2007). Written historical records (Table 1) also mention ploughed lands already from the second half of the sixteenth century.
Cereal cultivation was widespread in the Carpathian Basin in the seventeenth century (Figure 6); at the same time, its significance decreased considerably compared to the sixteenth century. On the one hand, the whole basin became a war zone (Sümegi et al., 2016), which resulted in a population decrease, so the production area of cereals may have decreased as well.

Map of archaeobotanical finds of cereals in the Carpathian Basin during the seventeenth century. 1. Szentgotthárdi fort – Ilon, Grynaeus, & Torma, 2007, Gyulai, 2010. 2. Kőszegi fort – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 3. Pápa fort – Torma, 1996b, Gyulai, 2001, 2010. 4. Tata fort – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 5. Esztergomi fort – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 6. Vác town (trade centre) – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001. 7. Szécsény fort – Torma, 1996a. 8. Sárospataki fort – Gyulai, Emődi, Mravcsik, & Pósa, 2013. 9. Debrecen town – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 10. Szolnoki fort – Hartyányi & Patay, 1970, Torma, 1996a, Gyulai, 2001, 2010. 11. Budapest – 1. osman site – Hartyányi & Patay, 1970, Torma, 1996a, Gyulai, 2001, 2010. 12. Budapest – 2. osman (Rácfürdő) – Hartyányi & Patay, 1970, Torma, 1996a, Gyulai, 2001, 2010. 13. Székesfehérvár – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 14. Dunaföldvári vár – Hartyányi & Patay, 1970, Torma, 1996a, Gyulai, 2001, 2010. 15. Szigetvár – Turbék Alsó Szőlőhegy site (in this manuscript). 16. Kaposvár – Hartyányi et al., 1967/1968, Torma, 1996a, Gyulai, 2001, 2010. 17. Pogányszentpéter (Christian monastery – sixteenth century, it was destroyed between 1526 and 1566) – Füzes, 1972, Torma, 1996a, Gyulai, 2001, 2010. 18. Sümeg – Sarvaly village (sixteenth century, it was destroyed between in 1536) – Skoflek, 1985, Torma, 1996a, Gyulai, 2001, 2010. Written data: Lászlófalvi Velics & Kammerer, 1886, 1890, Szilágyi, 1895, Imreh, 1999, Rácz, 2020.
Military stockpiles were very important regarding grain sustenance due to constant wars, for the continuous provision of military supplies in the Carpathian Basin (Hartyányi & Patay, 1970). Ottoman travellers also referred to military and civilian warehouses in the seventeenth century (Fodor, 2020). Historical notes of military warehouses provide information about cereal composition collected in the form of taxation. At the same time, the archaeobotanical analysis of military warehouse finds indicates some differences compared to our archaeobotanical results (Hartyányi & Patay, 1970).
Figure 6 shows that even the smaller settlements in the sixteenth century had more substantial grain reserves and, on this basis, probably had a larger population. The smaller castles occupied by Christians and Ottomans (Szentgothárd, Kőszeg, Pápa, Tata, Esztergom, and Szécsény) had approximately the same, subordinate quantities of cereals, indicating that these castles may have had approximately insignificant population and military. The excavated türbe also falls into this category. However, the türbe was a religious centre (Fodor, 2020). At the same time, we have to note that the fossilization of the archaeobotanical material also influenced the preservation of the charred remains. The coincidental, subordinate cereal quantity of the six smaller-sized castles cannot be a coincidence – especially when compared to the quantity of excavated cereals from larger Ottoman castles (Kaposvár, Székesfehérvár, and Szolnok) or a principality centre (Sárospatak), or a larger commercial centre (Vác). This is particularly striking when compared with the fortress of Dunaföldvár which was occupied by Ottoman troops. It was built along the Danube River earlier which is the main staging area for the Ottoman armies. In the Dunaföldvár fortress, a large quantity of cereals was stored in military warehouses, far in excess of the number of soldiers stationed in the fortress, precisely for the marching armies (Gyulai, 2001, 2010; Hartyányi, Nováki, & Patay, 1967/1968).
As described earlier, the comparison of the archaeobotanical material shows that the quantity of cereals of the türbe was just as subordinate as that of the smaller castles (Szentgothárd, Kőszeg, Pápa, Tata, Esztergom, and Szécsény; Figure 6). This allows us to reconstruct a minimal garrison and population. However, the grain reserves of the major settlements and fortresses (Székesfehérvár and Szolnok) suggest a larger population in the seventeenth century. Based on this we might infer that the population of the smaller settlements – the peripheral ones – declined in the seventeenth century. At the same time, the population of the larger settlements increased which might be indicated in the larger number of cereals in the archaeobotanical material. This suggests that the population may have been resettled.
Hartyányi and Patay (1970) published the Ottoman archaeobotanical material of a presumably baking house with and oven, as well as grinding stones from Dunaföldvár. An iron mortar and a charred, wooden mortar were also discovered in the ruins of the baking house. Grain remains were found on the surface of the mortar. The recovered material was dominated by cereals, mainly wheat and rye. In smaller quantities, multi-row barley (Hordeum vulgare [three grains]), and double-row barley (Hordeum distichon [five grains]) were also recovered from the archaeobotanical assemblage. Based on the identical number of common wheat (Triticum aestivum/nudum/turgidum) and rye (Secale cereale), the double sowing of wheat and rye emerged. The reason for the difference in the composition of the cereals is the special importance of the türbe. As it was a religious centre, important personalities, including the leaders of the imperial armies, visited it (Fodor, 2020), while mainly conscript soldiers lived in the Dunaföldvár fortress. The finds from the türbe and Dunaföldvár suggest that the Ottoman military aristocracy consumed a different composition of food, including bread, then the common soldiers.
There could be several reasons for the dominance of barley (Hordeum sp.) in the archaeobotanical assemblage of the türbe. On the one hand, there was the already mentioned imperial – religious reason (Fodor, 2020); on the other hand, locally grown crops might be used, and it cannot be excluded that artificial selection among the cereals was already established at sowing time, compensating for the effect of the climatic change (regionally cooler and wetter climate in the seventeenth century, Rácz, 2020). Thus, rye (Secale sp.) and barley (Hordeum sp.) dominated. At the same time, barley (Hordeum sp.) also dominated in the grains recovered from Esztergom castle (Gyulai, 2001, 2010; Hartyányi et al., 1967/1968; Torma, 1996a), alongside the absolute dominance of millet, which is essential for feeding the common soldiers and less sensitive to growing conditions. A total of 12 remains of common millet (Panicum miliaceum) were found in the excavated section of the moat in Szigetvár. This is probably related to the prominent position of the türbe, as official, prominent Ottoman personalities have not been served millet dishes up, which were probably consumed by the permanent military guards of the türbe and/or the staff serving in the türbe.
4.4 Plant Use in the Vicinity of the Türbe
The high species and the individual number of certain plant species deriving from crops, weeds, and the near-natural vegetation may provide significant information about the former agricultural activities, and habitats surrounding the settlement. Based on the ecological needs of weeds, we can separate different floral categories (Behre, 1988), which provide information on habitat types (Table 6).
Identified species, their habitat, and utilization
Taxon | Category | Habitat | Utilization | Total number |
---|---|---|---|---|
Hordeum vulgare | Cereal | Arable land | Bread, porridge | 3 |
Hordeum vulgare L. var. polystichon Haller | Cereal | Arable land | Bread, porridge | 90 |
Cerealia fragm. | Cereal | Arable land | Bread, porridge | 241 |
Panicum miliaceum | Cereal | Arable land | Bread, porridge | 12 |
Secale cereale | Cereal | Arable land | Bread, porridge | 61 |
Triticum aestivum/nudum/turgidum | Cereal | Arable land | Bread | 16 |
Triticum sp. | Cereal | Arable land | Bread, porridge | 2 |
Brassica nigra | Leguminous, oil, fibre plants and herbs | Vegetable garden | Spice, tradicional medicince plant | 27 |
Lens culinaris | Leguminous, oil, fibre plants and herbs | Vegetable garden | Food, cooking | 2 |
Linum usitatissimum | Leguminous, oil, fibre plants and herbs | Vegetable garden | Oil, textile plant, traditional medicine plant | 1 |
Pisum sativum | Leguminous, oil, fibre plants, and herbs | Vegetable garden | Food, cooking | 4 |
Papaver somniferum | Leguminous, oil, fibre plants and herbs | Vegetable garden | Traditional medicince plant | 1 |
Pastinaca sativa | Leguminous, oil, fibre plants, and herbs | Vegetable garden | Food, traditional medicine plant | 1 |
Prunus avium/cerasus | Fruit | Orchard | Fruit, refreshing, brandy | 32 |
Prunus cf. domestica | Fruit | Orchard | fruit, brandy | 3 |
Corylus avellana | Fruit | Orchard | Fruit | 3 |
Juglans regia | Fruit | Orchard | Fruit, oil | 1 |
Vitis vinifera | Fruit | Viticulture | Fruit, refreshing, wine, and spirit of wine | 37 |
Agrostemma githago | Weed | Arable land | Toxic weed | 2 |
Bromus arvensis | Weed | Arable land | Weed | 3 |
Bromus secalinus | Weed | Arable land | Weed | 2 |
Carduus nutans | Weed | Ruderal | Weed, traditional medicinal plant | 7 |
Centaurea cyanus | Weed | Ruderal | Weed, traditional medicinal plant | 2 |
Chelidonium majus | Weed | Ruderal | Weed, traditional medicinal plant | 2,949 |
Chenopodium album | Weed | Ruderal | Weed, hunger bred, traditional medicinal plant | 302 |
Chenopodium hybridum | Weed | Ruderal | Weed | 75 |
Chenopodium murale | Weed | Ruderal | Weed | 7 |
Datura staronium | Weed | Ruderal | Toxic weed, traditional medicinal plant from the New World(!) | 150 |
Descurainia sophia | Weed | ruderal | Toxic weed, traditional medicinal plant from the New World(!) | 18 |
Fallopia convolvulus | Weed | Ruderal | Toxic weed | 3 |
Galium aparine | Weed | Ruderal | Weed, traditional medicinal plant | 1 |
Galium spurium | Weed | Ruderal, arable land | Weed | 4 |
Glaucium corniculatum | Weed | Ruderal | Weed | 1 |
Hyoscyamus niger | Weed | Ruderal | Weed, traditional and medicinal plant | 2 |
Lolium temulentum | Weed | Arable land | Weed | 5 |
Leonurus cardiaca | Weed | Ruderal, arable land | Weed, traditional medicinal plant | 1 |
Malva pusilla | Weed | Ruderal | Weed, traditional medicinal plant | 1 |
Picris hieracioides | Weed | Ruderal | Weed, traditional medicinal plant | 16 |
Polygonum aviculare agg. | weed | Ruderal | Weed, traditional medicinal plant | 2 |
Polygonum lapatifolium | weed | Ruderal | Weed, traditional medicinal plant | 1 |
Portulaca oleracea | weed | Ruderal | Weed, traditional medicinal plant | 78 |
Sambucus ebulus | Weed | Ruderal | Toxic weed | 4,610 |
Sambucus nigra | Weed | Ruderal | Fruit, medicinal plant | 23,578 |
Setaria glauca | Weed | Ruderal | Poultry food | 3 |
Setaria viridis/verticillata | Weed | Ruderal | Poultry food | 3 |
Sinapis arvensis | Weed | Ruderal | Oil and soap plant, traditional medicinal plant | 10 |
Solanum nigrum | Weed | Ruderal | Toxic weed | 1 |
Spergula arvensis | Weed | Ruderal | Poultry food | 3 |
Stachys annua | Weed | Ruderal | Traditional medicinal plant | 1 |
Stellaria media | Weed | Ruderal | Poultry food, traditional medicinal plant | 17 |
Urtica dioica | Weed | Ruderal | Poultry food, traditional medicinal plant | 6 |
Eleocharis palustris | Weed | Wet ruderal | Weed | 2 |
Carex vulpina | Weed | Wet ruderal | Textile plant | 4 |
Schoenoplectus lacustris | Weed | Wet ruderal | Weed | 1 |
Solanum dulcamara | Weed | Ruderal | Toxic weed | 1 |
Alisma plantago-aquatica | Weed | Wet ruderal | Weed | 1 |
Carex flacca | Weed | Wet ruderal | Textile plant | 2 |
Carex hirta | Weed | Wet ruderal | Textile plant | 1 |
Barbarea stricta | Weed | Ruderal | Traditional medicinal plant | 1 |
Myosoton aquaticum | Weed | Wet ruderal | Toxic weed | 5 |
Ranunculus repens | Weed | Wet ruderal | Traditional medicinal plant | 1 |
Chenopodium polyspermum | Weed | Wet ruderal | Weed | 9 |
Chrysanthemum leucanthemum | Weed | Wet ruderal | Traditional medicinal plant | 1 |
Carex distans | Weed | Wet ruderal | Textile plant, traditional medicinal plant | 2 |
Betula pendula | Natural and ornamental vegetation | Forest, river bank | Natural – ornamental and traditional medicinal tree | 7 |
Fragaria vesca | Natural vegetation | Open woodland, forest edge | Gathered natural and traditional medicinal plant | 3 |
Picea abies | Natural and ornamental vegetation | Dry and wet forest | Natural – ornamental and traditional medicinal tree | 2 |
Prunus spinosa | Natural vegetation | Open woodland, forest edge | Traditional medicinal tree and brandy | 1 |
Rubus fruticosus | Natural vegetation | Open woodland, forest edge, ruderal | Gathered natural and traditional medicinal plant | 2 |
Veronica hederifolia | Weed | Ruderal | Traditional medicince plant | 1 |
Prunella vulgaris | Weed | Ruderal | Traditional medicinal plant | 1 |
Calamintha acinos | Weed | Wet ruderal | Traditional medicinal plant | 1 |
Lamium amplexicaule | Weed | Ruderal | Traditional medicinal plant | 2 |
Medicago minima | Natural vegetation | Meadow and ruderal | Traditional medicinal plant | 1 |
Plantago lanceolata | Weed | Ruderal | Traditional medicinal plant | 1 |
Ranunculus bulbosus | Weed | Ruderal | Traditional medicinal plant | 1 |
Rumex crispus | Weed | Ruderal | Traditional medicinal plant | 1 |
Trifolium repens | Natural vegetation | Meadow and ruderal | Traditional medicinal plant | 1 |
Besides the remains of cereals, the seeds of opium poppy (Papaver somniferum), lentil (Lens culinaris), pea (Pisum sativum), black mustard (Brassica nigra), flax (Linum usitatissimum), and parsnip (Pastinaca sativa) appeared as well, indicating horticulture (Behre, 1988; Jacomet & Kreuz, 1999; Jacomet, 2006). Legumes have been cultivated since the Neolithic in the Carpathian Basin (Gyulai, 2010), and their presence supposes an advanced farming activity and indicates the existence of a well-developed horticulture (Galluzzi, Eyzaguirre, & Negri, 2010). Parsnips could be consumed as roots and herbs (Asif, 2015; Leach, 1982).
Among fruits sweet cherry/sour cherry (Prunus avium/cerasus), plum (Prunus domestica), and walnut (Juglans regia) remain turned up in the moat of the tomb. Although walnut (Juglans regia) and hazelnut (Corylus avellana) grow in many forests of the Carpathian Basin and south-eastern Europe (Bottema, 2000; Pollegioni et al., 2017), they were already maintained and colonized in gardens in the late Medieval period and early modern ages (Islam, 2018).
Based on the historical records (Table 1) the production of cherry was likely in the vicinity of the tomb. Strawberry (Fragaria vesca), European blackberry (Rubus fruticosus), blackthorn (Prunus spinosa), and hazelnut (Corylus avellana) grow in open woodlands, and forest edges (Table 6) and were present in different parts of Europe and the Carpathian basin in the seventeenth century (Gyulai, 2010; Torma, 2003; Sánchez-Pardo, Marron, & Țiplic, 2020).
In addition to crops, a significant number of weed plant remains occurred as well. Based on weeds indicating the cultivation of winter cereals, ploughed lands were created and cereals were cultivated in the vicinity of the tomb and the pilgrim town. Weeds indicating ruderal areas appeared as well, such as field brome (Bromus arvensis), rye brome (Bromus secalinus), nodding thistle (Carduus nutans), hairy crabgrass (Digitaria sanguinalis), cleavers (Galium aparine) and red horned poppy (Glaucium corniculatum; Ujvári, 1957). All of the cereal weeds excavated in the moat of the tomb are considered obligatory weeds (Scholz, 1996). Among cereal weeds, the presence of corn-cockle is of great importance (Humphry, Mortimer, & Marrs, 2001; Spahillari, Hammer, Gladis, & Diederichsen, 1999; Rösch et al., 2014), which fully adapted to cereals (Radosevich, Holt, & Ghersa, 1997). Its saponin content (Holzner, 1982) can cause severe poisoning (Hanley & Whiting, 2005) if it gets into the flour, so it had to be separated from cereal grains.
In addition to cereal weeds, weed seeds of spring-sowing plants (Colledge et al., 2004; Hyvönen, Ketoja, & Salonen, 2003; Ujvári, 1957) appeared as well, such as darnel (Lolium temulentum) and corn spurry (Spergula arvensis; Behre, 2008; Pelling et al., 2015). At the same time, darnel (Lolium temulentum) appeared in rye, wheat, and flax fields in the Carpathian Basin, before mechanization and the use of chemical pesticides. The same characterizes corn spurry (Spergula arvensis); it appears together with spring cereals (Chamanabad, Ghorbani, Asghari, Tulikov, & Zargarzadeh, 2009; New, 1961).
Most summer weeds appear in ruderal and trampled areas as well, such as thorn apple (Datura stramonium), black henbane (Hyoscyamus niger), and nettle-leaved goosefoot (Chenopodium murale; Kreuz, Colledge, & Conolly, 2007; Rösch, Fischer, & Märkle, 2005; Spengler, 2019; Ujvári, 1957). Moreover, some weeds exist in ploughed lands, such as maple-leaved goosefoot (Chenopodium hybridum), hooked bristlegrass (Setaria viridis/verticillata), yellow foxtail (Setaria glauca), and white goosefoot (Chenopodium album) The two latter grow in ruderal areas as well (Behre, 2008; Wallace & Charles, 2013). So, ploughed lands and ruderal areas cannot be distinguished based on weeds, as they occur in both areas of human impact (Lundkvist, 2009; Möhler, 2004). One of the decisive factors in the development of these weeds is their light demand (Möhler, 2004). They exist in habitats characterized by open vegetation and in areas of human impact to different degrees as well.
Datura stramonium is commonly known as thorn apple which originated in Latin America (Singh & Singh, 2013). It was probably introduced to the Carpathian Basin by the Ottoman people based on the data available up to the seventeenth century (Kubinyi, 1842). At the same time, the archaeobotanical analysis of the plant was first carried out in the Carpathian Basin by Ferenc Gyulai and Árpád Kenéz, who analysed more than 55,000 remains from seven sites (Gyulai & Kenéz, 2018). Sporadic remains from the Early Bronze Age (Bell Beaker Culture), late Iron Age (Celtic culture), and Migration period (Sarmatian culture) suggest that the plant grew in the Carpathian Basin long before the first American introductions. A great amount, about 55,000 seeds of thorn apple (Datura stramonium), was found in a sixteenth- to seventeenth-century room in the castle of Hollókő, among the ruins. This not only raises but also confirms its conscious use (Gyulai & Kenéz, 2018).
Black henbane (Hyoscyamus niger) is a poisonous weed, all parts of the plant are toxic, especially its root and seed, but organic cultures and folk medicine used it in very small quantities, as a tranquilizer and painkiller, and in the case of rheumatism, spasm, and neural problems (Carter, 1996; Fatur, 2019, 2020; Fenwick & Omura, 2015; Gyulai & Kenéz, 2018; Long, Milburn, Bunting, & Tipping, 1999; Van den Berg, 2008; Van der Veen & Morales, 2015). Chenopodiaceae and Setaria taxa are also considered to be weeds nowadays but have been used by organic agriculture for feeding and grazing animals and as green manure. Thus, their appearance raises several land use possibilities in the study site, from horticulture to ploughed lands and trampled, ruderal areas (Bakels, 1999; Behre, 2008; Charles, Bogaard, Jones, Hodgson, & Halstead, 2002; Latalowa, Badura, & Jarosińska, 2003; Wallace & Charles, 2013). Regarding the number of weed seeds, the mass of seeds belongs to ruderal species indicating trampled areas, roads, and settlements (Lapteva & Korona, 2012; McPartland & Hegman, 2018), for example, motherwort (Leorunus cardiac), common knotgrass (Polygonum aviculare), and hawkweed oxtongue (Picris hieracioides).
The dominant species in the profile, greater celandine (Chelidonium majus), European dwarf elderberry (Sambucus ebulus), and European black elderberry (Sambucus nigra), of which thousands of remains were identified, prefer nutrient-rich, fresh habitats, such as the banks of the moat of the tomb. European black elderberry (Sambucus nigra) and greater celandine (Chelidonium majus) were gathered as well. In addition, greater celandine (Chelidonium majus) was a known herbal drug (Sárközi, Janicsak, Kursinszki, & Kery, 2006), while the fruit and flower of European black elderberry (Sambucus nigra) were consumed as herbal tea (Akbulut, Ercisli, & Tosun, 2009; Porter & Bode, 2017).
Several weed species refer to the presence of vineyards and orchards, such as the remains of hairy crabgrass (Digitaria sanguinalis), common purslane (Portulaca oleracea), common chickweed (Stellaria media), and dwarf mallow (Malva pusilla; Beneš et al., 2002; Poldini, Oriolo, & Mazzolini, 1998; Weiss & Kislev, 2004).
Among the archaeobotanical remains of near-natural vegetation elements, we can find plants that dominate in waterfront areas, floodplains, and wet ditches, such as common spikerush (Eleocharis palustris), true fox sedge (Carex vulpina), common club-rush (Schoenoplectus lacustris), European water-plantain (Alisma plantago aquatica), and blue sedge (Carex flacca). Several of these species exist in ruderal areas as well, for example, giant chickweed (Myosoton aquaticus) or small-flowered winter cress (Barbarea stricta; Hosch & Jacomet, 2001; Šoštarić & Küster, 2001).
The number of meadow species is low. This includes Carex distans (Distant sedge), which is a tolerant species to habitat and can be found in both floodplain vegetation and as a ruderal weed (Cappers, 1993; Nieuwhof, 2006; Święta-Musznicka & Latałowa, 2016). In addition, oxeye daisy (Chrysanthemum leucanthemum) and creeping buttercup (Ranunculus repens) exist in floodplain, ruderal, and inhabited areas as well (Gyulai, Hertelendi, & Szabó, 1992; Henriksen & Robinson, 1996; Latalowa et al., 2003; Sillasoo, 2006). These plants were able to survive in shallow and periodically drying waters, including swamps, and puddles, and as a result, it can be assumed that the moat was wet for at least a part of the year during the seventeenth century.
The remains of birch (Betula sp.) and spruce (Picea abies) may indicate the presence of planted and artificially maintained forest patches or groves, possibly rows of trees or scattered trees near the moat (Beck, Caudullo, de Rigo, & Tinner, 2016; Kovačić & Nikolić, 2005; Šímová et al., 2019; Wistuba, Malik, Gärtner, Kojs, & Owczarek, 2013). The presence of both species is not typical on south-facing slopes at low elevation, which is warmer during summer and is in contradiction to their ecological needs. Moreover, spruce favours altitudes of 800 m above sea level and exists on the northern hillsides in the Carpathian Basin (Beck et al., 2016; Latałowa & van der Knaap, 2006; Šímová et al., 2019). As a result, both plants were probably planted in the Szigetvár – Turbék Vineyard Hill site in the seventeenth century, and it cannot be ruled out that their presence may have been related to the function of the memorial place and the pilgrim town (Alavijeh, 2012). It is possible that coniferous charcoals that could not be identified to the genus level belong to the Picea genus as well.
5 Summary
Based on written resources and our archaeobotanical and anthracological data, we could reconstruct the vegetation in the vicinity of the Ottoman memorial place for the seventeenth century. The agricultural utilization of the larger area was subordinated to food security. The composition of weed vegetation, cereals, and fruit remains implies active human presence, inhabited settlements, gardens, orchards, ploughed lands, and pasturelands. At the same time, it should be noted that according to the agricultural perception of nowadays, a significant proportion of plants classified as weeds today have been widely used by medieval cultures, for food, animal feeding, traditional (folk) therapies, including Islamic medical therapies. The results of archaeobotanical and charcoal data coincide with the reconstructed erosion-accumulation events (Gulyás et al., 2022). The ransack of the site during the winter campaign of 1664, the re-occupation of the site in 1689/90, and the final destruction of the türbe in 1692 appeared in both the archaeobotanical and anthracological, and the detailed sedimentological–geochemical analyses (Gulyás et al., 2022), supporting the written historical records.
Acknowledgements
Geoarchaeological investigations have been implemented by members of the University of Szeged, Interdisciplinary Excellence Centre, Institute of Geography and Earth Sciences, Long Environmental Changes Research Team. Support of Grants 20391-3/2018/FEKUSTRAT, GINOP-2.3.2-15-2016-00009 ‘ICER’ (and NKFIH 129265) are acknowledged by the European Union and the State of Hungary, Ministry of Human Capacities, co-financed by the European Regional Development Fund.
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Funding information: This research was funded by Grants 20391-3/2018/FEKUSTRAT and GINOP-2.3.2-15-2016-00009 “ICER” (and NKFIH 129265) by the European Union and the State of Hungary, Ministry of Human Capacities, co-financed by the European Regional Development Fund.
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Author contributions: All authors have accepted responsibility for the entire content of this manuscript and consented to its submission to the journal, reviewed all the results and approved the final version of the manuscript. A.T. – data Analysis. K.N. – data analysis; writing, review, and editing; visualization. S.G. – review and editing. P.S. – supervisor.
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Conflict of interest: The authors state no conflict of interest.
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Data availability statement: The data sets generated during and/or analyzed during the current study are available from the corresponding author on reasonable request.
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- Social Organization, Intersections, and Interactions in Bronze Age Sardinia. Reading Settlement Patterns in the Area of Sarrala with the Contribution of Applied Sciences
- Creating World Views: Work-Expenditure Calculations for Funnel Beaker Megalithic Graves and Flint Axe Head Depositions in Northern Germany
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- Pottery from Motion – A Refined Approach to the Large-Scale Documentation of Pottery Using Structure from Motion
- On the Value of Informal Communication in Archaeological Data Work
- The Early Upper Palaeolithic in Cueva del Arco (Murcia, Spain) and Its Contextualisation in the Iberian Mediterranean
- The Capability Approach and Archaeological Interpretation of Transformations: On the Role of Philosophy for Archaeology
- Advanced Ancient Steelmaking Across the Arctic European Landscape
- Military and Ethnic Identity Through Pottery: A Study of Batavian Units in Dacia and Pannonia
- Stations of the Publicum Portorium Illyrici are a Strong Predictor of the Mithraic Presence in the Danubian Provinces: Geographical Analysis of the Distribution of the Roman Cult of Mithras
- Rapid Communications
- Recording, Sharing and Linking Micromorphological Data: A Two-Pillar Database System
- The BIAD Standards: Recommendations for Archaeological Data Publication and Insights From the Big Interdisciplinary Archaeological Database
- Corrigendum
- Corrigendum to “Plant Use and Cereal Cultivation Inferred from Integrated Archaeobotanical Analysis of an Ottoman Age Moat Sequence (Szigetvár, Hungary)”
- Special Issue on Microhistory and Archaeology, edited by Juan Antonio Quirós Castillo
- Editorial: Microhistory and Archaeology
- Contribution of the Microhistorical Approach to Landscape and Settlement Archaeology: Some French Examples
- Female Microhistorical Archaeology
- Microhistory, Conjectural Reasoning, and Prehistory: The Treasure of Aliseda (Spain)
- On Traces, Clues, and Fiction: Carlo Ginzburg and the Practice of Archaeology
- Urbanity, Decline, and Regeneration in Later Medieval England: Towards a Posthuman Household Microhistory
- Unveiling Local Power Through Microhistory: A Multidisciplinary Analysis of Early Modern Husbandry Practices in Casaio and Lardeira (Ourense, Spain)
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