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Keil, P. (2019): Industrial nature and species diversity in the Landscape Park Duisburg-Nord. – Electronic Publications of the Biological Station of Western Ruhrgebiet 39 (2019): 1‒6.

Authors:
  • Biologische Station Westliches Ruhrgebiet
Elektronische Aufsätze der Biologischen Station Westliches Ruhrgebiet 39 (2019): 1–6
Electronic Publications of the Biological Station of Western Ruhrgebiet 39 (2019): 1‒6
© Biologische Station Westliches Ruhrgebiet e. V., Ripshorster Str. 306, D-46117 Oberhausen http://www.bswr.de
Industrial nature and species diversity in the
Landscape Park Duisburg-Nord*
*modified and updated version of Keil (2016)
PETER KEIL
Biologische Station Westliches Ruhrgebiet e.V., Ripshorster Str. 306, D-46117 Oberhausen;
E-Mail: peter.keil@bswr.de
Introduction
Industrial brownfield sites (syn. industrial wastelands) form the backbone of urban biodiversi-
ty in the central Ruhr Region and are places for experiencing nature and for environmental
education. In terms of its size, structural variety and biodiversity, the Duisburg-Nord Land-
scape Park occupies a prominent position. Its vegetation presents an almost complete spec-
trum of different development stages (succession stages) on diverse sites. These range from
pioneer communities, tall herbaceous perennials and scrub formations to pioneer forests (in-
dustrial forest) and together produce an astonishing diversity of species.
The Landscape Park is quite rightly considered a local hotspot for biodiversity in the western
Ruhr Region. Furthermore, its industrial nature is of high ecological value because it contrib-
utes not only to the preservation of many rare and endangered species but also to the con-
servation of urbanised nature in the Ruhr Region’s conurbations. The Landscape Park con-
tains this enormous species diversity because of its great variety of habitats. Besides the in-
dustrial technogenic soils around the former blast furnace site, the sinter plant, the mine and
the cokery, it also includes agricultural soils at Ingenhammshof and Emstermannshof. The
physiochemical properties of the soils are significantly different and so influence the species
composition and plant ecology (Scholz et al. 2018).
The Biological Station has been involved in the collection of scientific data on plant and ani-
mal life since 2005, in cooperation with the park administration, are also involved with the
formulation of maintenance and development plans (Keil 2016).
Flora in the park
Scientific assessments, which had been conducted by the Biological Station over the past
fourteen years, identified over 700 plant tribes. Despite the fact that some were unstable and
2 Peter Keil
disappeared after a time and others comprised planted or sown plants that had run to seed,
this is an enormous number, rarely found on sites of a comparable size in Germany. We
begin to appreciate this scale when comparing it to the approximately 2,000 plant species
native to North Rhine Westphalia. Also impressive is the number of plants included on the
Red List; almost 50 such species were identified in past years. It is remarkable that the ma-
jority thrive either on dry, warm, raw soils typical of industrial sites, large areas of which are
found around the shaft mines or on the nutrient-poor, uncompacted banks along the Old Em-
scher. The park’s many special habitats are important for the establishment of threatened
Red List species, particularly the walls of buildings and bunkers as well as temporary water
bodies, the Old Emscher and many water-filled basins.
Fig. 1 und 2: Industrial nature in the Landscape Park Duisburg-Nord. Remains of the former ironworks with spo-
nan vegetation. (Fotos P. Keil).
Typical indigenous indicator species on dry, warm, nutrient-poor substrates are e.g. silvery
cinquefoil (Potentilla argentea), small cudweed (Filago minima) or common centaury and
Industrial nature and species diversity in the Landscape Park Duisburg-Nord 3
lesser centaury (Centaurium erythraea, C. pulchella). Rare non-indigenous plant species re-
cently introduced to industrial sites (neophytes) are stinkwort (Dittrichia graveolens) or sticky
goosefoot (Chenopodium botrys), to name but a few.
Fig. 3 and 4: High phytodiversity in different places in the park. Former railway tracks (l.); former site of a
coalmine, shaft Thyssen 4/8 (r.) (Fotos P. Keil).
The bunkers and walls in the Landscape Park support a wide variety of special ferns which in
North Rhine Westphalia mainly grow in upland regions and whose distribution is of phytoge-
ographical interest. Particularly noteworthy are the two relatively common species hart’s
tongue fern (Asplenium scolopendrium) and maidenhair spleenwort (Asplenium trichomanes)
but also other species not as commonly found in the region, e.g. black spleenwort (Aspleni-
um adiantum-nigrum), limestone fern (Gymnocarpium robertianum) or different tribes of pol-
ypody (Polypodium spp). Aquatic plants and young reed grow in open, sunny stretches of the
Old Emscher. Important floating leaf plants and reed beds include various pondweed species
(Potamogeton spp), phragmites and different sedges. Freely growing stands of woody plants,
4 Peter Keil
which were neither planted nor silviculturally managed, also provide high scientific interest.
They develop into industrial woodlands whose peculiar and uncontrolled patterns create a
jungle-like impression.
Fig. 5 and 6: Impressions from the park (l.) clarifiers with presence of jellyfish (Craspedacusta sowerbii); (r.) High
biodiversity in dry greenland (Fotos P. Keil).
Fauna in the Park
Taking a look at the wildlife in the park also reveals some astonishing facts. The Biological
Station has been recording groups of animals in the park for many years with notable results.
Seven species of bats have been identified and 38 bird species are known to nest in the
park; in addition, there are seven possible breeding birds. The Landscape Park provides
habitats for six amphibian species, including the natterjack toad, an indicator species for in-
dustrial nature, and one reptile.
35 different dragonflies have also been identified, more than half of all dragonfly species cur-
rently found in North Rhine Westphalia. Additionally, 17 species of grasshoppers were noted,
Industrial nature and species diversity in the Landscape Park Duisburg-Nord 5
with the blue-winged grasshopper (Oedipoda caerulescens), the slender blue-winged grass-
hopper (Sphingonotus caerulans) and the ant-loving cricket (Myrmecophilus acervorum) as
management indicator species for open industrial brownfields. Sufficiently detailed studies of
butterflies and bees have not been conducted in the park but interesting evidence of signifi-
cant and endangered species has been recorded.
Particularly fascinating is the occurrence of a yet to be scientifically described, non-native
harvestman species (Leiobunum sp), which has been spreading in the park since 2006. Also
remarkable is the nearly annual occurrence of the freshwater jellyfish Craspedacusta sower-
bii in the round basins of the former sewage treatment plant since 2002 (see Fig. 5)
Environmental education in the park
This impressive, and in a national context remarkable industrial nature is the subject of envi-
ronmental education programmes and public information activities by the Biological Station.
In the context of a lack of near-natural open spaces in the densely populated north of Duis-
burg, the park offers a place for the experience of nature and the education of children and
young people. Thoroughly embedded in its work in the Landscape Park is the cooperation
with schools (weekly extracurricular lessons), excursions for citizens and universities, hosting
of species diversity days, professional conferences and multiplier training courses for teach-
ers and environmental educators (Niehuis et al. 2019).
Fig. 7: Environmental education. Training adults as multipliers of industrial nature (Foto P. Keil).
6 Peter Keil
Literature
Keil, P. (2016): Species diversity and industrial nature. - In: Latz, P: Rust red. The Landscape Park
Duisburg-Nord. Essays by Bodmann, E., Danielzik, K.-H. , Dettmar, J., Keil, P., Latz, T., Lipkowsky,
G., Riehl, W., Walter, K. & Winkels, R. and Introductions by Ganser, K. & Treib, M., Hirmer, Mu-
nich. p. 120-121.
Keil, P.; Kowallik, C.; Kricke, R.; Loos, G. H.; Schlüpmann, M. (2007): Species diversity on urban-
industrial brownfields with urban forest sectors compared with semi-natural habitats in western
Ruhrgebiet (Germany) – First results of investigations in flowering plants and various animal
groups. – EFUF 2007, May 16-19, 2007: 33-35.
Niehuis, V.; Schneider, K.; Buch, C.; Keil, P. (2019): Environmental education in urban forest(s) in the
Ruhr area. In: Vreese, R. d. (ed.): Urban Forests: Full of energy, 22nd European Forum on Urban
Forestry (EFUF2019), May 22-24, 2019 Cologne, Germany. – Book of Abstracts: p. 73.
Scholz, T.; Keil, P.; Schmitt, T. (2018): Nutrient and water supply of succession stages on industrial
brownfield - a case study in the Landscape Park Duisburg-Nord, W-Germany [in german] – Deche-
niana (Bonn) 171: 24-37.
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Nature-based solutions (NbS) offer opportunities to incorporate green elements into cultural heritage conservation and management practice in cities and unlock associated co-benefits. However, concern about potential negative impacts of nature on built heritage (i.e., biodeterioration of heritage materials, loss of heritage values, and complicating practical heritage conservation and management) can act as a barrier to the uptake of NbS in some locations. We propose that NbS could be adapted, developed, and applied to address specific heritage conservation challenges as well as contribute to wider social benefits. In turn, urban built heritage can provide a valuable and largely underexplored space for NbS activities. Focussing on ten key benefits of NbS in cities (improving health, sequestering carbon, enhancing biodiversity, providing acoustic comfort, reducing the urban heat island, enhancing sustainable water management, facilitating urban agriculture, improving air quality, contributing to economic vitality through jobs and investment, and enhancing social cohesion), we illustrate how built heritage can both benefit from NbS and contribute to their wider success. We show how built heritage can benefit through reducing or mitigating the deterioration of heritage materials, improving the visitor experience, enhancing values, and stimulating investment. At the same time, built heritage conservation can support the delivery and success of NbS in cities by offering additional locations to implement and connect NbS schemes, providing inspiration for closer relationships between nature and society, and enriching NbS benefits by adding a cultural element. We conclude that flexibility is needed to link built heritage and NbS, yet the opportunities are great. Cultural and natural heritage are vital components of resilient and sustainable urban communities, fostering shared values by connecting people with the past and with nature. Better integrating built heritage into the wider NbS paradigm shows great promise for strengthening and broadening these linkages.
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In der Schriftenreihe berichten wir über unsere laufenden Arbeiten in den Schutzgebieten, im Bereich der urbanen Biodiversität (hier insbesondere im Themenfeld Industrienatur) und in der Umweltbildung und Öffentlichkeitsarbeit. Zudem werden Neufunde von Pflanzen und Tiere in unserem Zuständigkeitsbereich aufgeführt. Alle Berichte sind online auf unsere webpage http://www.bswr.de/service/jahresberichte/index.php verfügbar. We report on our ongoing work in the protected areas, in the field of urban biodiversity (in particular in the field of industrial nature) and in environmental education and public relations. In addition, new finds of plants and animals are listed in our area of responsibility. All reports are available online on our webpage http://www.bswr.de/service/jahresberichte/index.php.
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The high species diversity of urban-industrial brownfields is well-known from numerous studies (summarized e.g. in Sukopp & Wittig 1998 and Rebele & Dettmar 1996). In the Ruhrgebiet (Northrhine-Westphalia, Germany), lots of data are available for fallow areas in former coal mines and steel works which were embedded in urban settlements (see Seipel & al. 2006). Their high species-diversity is explained by the large variety of ecotopes and numerous microhabitats, e.g. urban forests. In the Western Ruhrgebiet (cities of Duisburg, Mülheim an der Ruhr and Oberhausen) urban-industrial fallow areas have been studied extensively in the past three years. In addition to flowering plants, various animal groups like birds, bats, amphibians, grasshoppers and dragonflies were studied. The results of the studies can be compared with those of natural or semi-natural habitats, to emphasize the importance of these deserted industrial areas for species diversity. Besides, a direct comparison of the number of species, an assessment of occurrence of threatened and endangered species is important as well (Red Data Book of Northrhine-Westphalia, LÖBF 1999). Among these taxa, the number of forest-dwelling species is interesting and highlights the conservation value of urban forests (even considering that flora and fauna of industrial forests differ from that of natural and semi-natural forests). This aspect is apparent in the high number of neophytic trees and shrubs in urban forests. Urban-industrial open brownfields and forests are inhabited by numerous endangered species (according to Red Data Book of Northrhine-Westphalia, LÖBF 1999), e.g.: Flowering plants: Asplenium adiantum-nigrum, Carex praecox, Centaurium pulchellum, Dianthus armeria, Genista tinctoria, Hyoscyamus niger, Kickxia elatine, Malva sylvestris, Nepeta cataria, Salvia pratensis, Sherardia arvensis, Viola tricolor; birds: Meadow Pipit (Anthus pratensis), Little Ringed Plover (Charadrius dubius), Peregrine (Falco peregrinus), Northern Wheatear (Oenanthe oenanthe), Redstart (Phoenicurus phoenicurus), Green Woodpecker (Picus viridis), Little Grebe (Tachybaptus ruficollis), Lapwing (Vanellus vanellus); amphibians: Bufo calamita, Rana lessonae; dragonflies: Lestes virens, Sympecma fusca, Sympetrum fonscolombei; grasshoppers: Oedipoda caerulescens. Species diversity as well as the number of endangered species of open industrial brownfields is higher than in urban forest areas. Compared with most semi-natural habitats within the conurbation of the Western Ruhrgebiet it terms out that the number of endangered species on fallow land in general is fairly similar. And finally, total species diversity can be even higher on fallow land than in most semi-natural areas.
Environmental education in urban forest(s) in the Ruhr area
  • V Niehuis
  • K Schneider
  • C Buch
  • P Keil
Niehuis, V.; Schneider, K.; Buch, C.; Keil, P. (2019): Environmental education in urban forest(s) in the Ruhr area. In: Vreese, R. d. (ed.): Urban Forests: Full of energy, 22nd European Forum on Urban Forestry (EFUF2019), May 22-24, 2019 Cologne, Germany. -Book of Abstracts: p. 73.
Nutrient and water supply of succession stages on industrial brownfield -a case study in the Landscape Park Duisburg-Nord
  • T Scholz
  • P Keil
  • T Schmitt
Scholz, T.; Keil, P.; Schmitt, T. (2018): Nutrient and water supply of succession stages on industrial brownfield -a case study in the Landscape Park Duisburg-Nord, W-Germany [in german] -Decheniana (Bonn) 171: 24-37.