Huddart, D. & Glasser, N.F. 2007. Quaternary of Northern England. Geological Conservation Review Series No. 25, JNCC, Peterborough, ISBN 1 86107 490 5. The original source material for these web pages has been made available by the JNCC under the Open Government Licence 3.0. Full details in the JNCC Open Data Policy
Upper Teesdale
D. Huddart
Introduction
Red Sike Moss is situated on the Upper Teesdale National Nature Reserve and SSSI on Widdybank Fell, Durham. This fell is a raised limestone plateau at 523 m OD. To the west is the Cow Green reservoir and the Cautley Snout waterfall; the ground to the south and south-east falls to the River Tees at Falcon Clints. The area is underlain by the Melmerby Scar Limestone (Lower Carboniferous Limestone Series) and the quartz-dolerite Whin Sill, which was intruded into the limestone at the end of the Carboniferous Period. This intrusion partially metamorphosed the limestone to form the Sugar Limestone, which is important for the development and preservation of the Teesdale flora. Red Sike Moss is located between Red Sike and Tinkler's Sike and it has an actively growing surface of Sphagnum species, including Calluna vulgaris, Eriophorum vaginatum and E. angustifolium, Erica tetralix, Narthecium ossifragum, Drosera rotundifolia and many Carex species. The western end of the moss shows erosion by drainage channels
The site is important for reconstructing Flandrian vegetation history in Upper Teesdale, which is an area of international botanical importance, containing a number of species such as Gentiana verna and Kobresia simpliciuscula, which are found in only a few other locations in Britain and Minuartia stricta, which is found nowhere else (Turner et al., 1973; Bradshaw and Clark, 1976; Ratcliffe, 1978). These Teesdale rarities represent a wide range of geographical elements in Europe and represent a convergence of phytogeographical elements (Piggott, 1956; Bradshaw and Clark, 1965, Bradshaw, 1970). The rarities occur in communities occupying habitats of diverse character. Many are found in various grassland communities (Shimwell, 1968), existing as windows in the acidophilous moorland cover. Other communities that include rarities have a more limited distribution, and are associated with certain mining spoil heaps with high lead and zinc concentrations, where base-rich drainage water flows over the surface, and those on quartz-dolerite and limestone screes. They have aroused considerable discussion as to their origin and potential survival ever since the early and mid-nineteenth centuries (Backhouse, 1844) and subsequently (Blackburn, 1931; Godwin, 1949; Piggott and Walters, 1954; Piggott, 1956; Hutchinson, 1966; Bellamy et al., 1969a, b; Squires, 1970, 1971; Bradshaw et al., 1976; Clapham, 1978; Turner, 1978). The list in Winch et al. (1805) shows that most of the famous Teesdale plants had been found there by 1805. The decision taken by the Tees and Cleveland Water Board in 1966 to build a reservoir and drown the stretch of the Tees above Cauldron Snout emphasized the conservation importance of the area (Turner et al., 1973; Squires, 1978) and it has provided opportunities to study the origin of plant assemblages and the factors that have enabled the rarities to persist in such assemblages (Bellamy et al., 1969a, b; Squires, 1970; Turner et al., 1973).
Description
The stratigraphy can be seen along the edge of Tinkler's Sike and was examined along three transects
Zone G a grass–plantain–heather assemblage
Zone A an oak–alder assemblage
Zone 0 an oak–elm–hazel assemblage
Zone H a hazel–pine assemblage
Zone HJ a hazel–juniper–willow assemblage
Zone J a juniper–willow–herb assemblage
The pollen diagram from RSII is given in
The relationships between these local pollen assemblage zones and those of Godwin (1940) and the chronozones of West (1970) are given in
Interpretation
Late-glacial c. 10 000 years BP
The Late-glacial Zone III deposit indicates a period of herbaceous vegetation with abundant grasses and sedges and a wide variety of other species. These include such common Late-glacial species as Artemisia, Filipendula, Helianthemum, Rumex and Thalictrum. Betula nana, juniper and willow species pollen occur in sufficient quantity to indicate that locally these shrubs were flourishing
At TSI the basal few centimetres are thought to have formed in the Late-glacial pollen assemblage zone J, corresponding to very late in Godwin's Zone III. The evidence comes from the very low tree pollen percentages and over 20% juniper pollen, together with a 14C date of 9900 years BP for the 135 cm level. The peat above this level has a different pollen assemblage, with a high percentage of hazel and both oak and elm recording up to 10%. This assemblage, together with a date of 8250 years BP for the 120 cm level at the end of pollen assemblage zone H, indicates that it is part of Godwin's Zone VI. This means that there is a depositional break during Zones IV and V.
10 000–8800 years BP
In this period the peat stopped growing, but began forming again in pollen assemblage zone H. By the beginning of this zone the total tree pollen appears only marginally higher than at the end of the Late-glacial. Graminae, Cyperaceae and other herbaceous pollen frequencies have decreased correspondingly, but they are still well represented at the end of the period. There is no question of closed woodlands having formed.
8800–8000 years BP
In this period (pollen assemblage zone H), oak and elm pollen appear and the frequency of hazel is high. There is no juniper but willow and herbaceous pollen types are still abundant. The total tree pollen frequencies rise steadily on the TSI diagram and by 8000 years BP the frequency is between 30 and 40%. Birch and pine are increasing but it is unlikely there would be closed woodland.
8000–5770 years BP
At the beginning of this period the pine frequency is high and alder and oak low, or zero. By the end the latter two species have risen to high values and pine has disappeared. It is clear that pine grows best on the limestone and persisted there for longer than it did elsewhere (Turner et al., 1973). This conclusion is supported by the fact that Carex ericetorum (a Teesdale rarity) is now restricted to the Sugar Limestone. Today it grows in the ground flora of pinewoods in European Russia (Keller, 1927), and where it occurs in the grassland of the East Anglian Breckland it is thought by Watt (1971) to indicate the former existence of pinewoods.
5770–5000 years BP
In this period there is evidence for a long break in peat formation from sometime before 5000 years BP until well after 3390 ± 90 years BE At TSI the major oak–elm–hazel pollen assemblage of zone 0 can be subdivided into Oa (no alder), Ob (little alder) and Oc (higher values for oak and alder and lower for pine: see
Depth (cm) | Description |
0–12 | Dark brown crumbly Calluna peat with some Eriophorum remains, Juncus seeds, megaspores of Selaginella selaginoides with Carex seeds |
12–25 | Light brown, Calluna–Eriophorum peat containing remains of sedges and megaspores of Selaginella |
25–40 | Dark brown peat containing burnt Calluna stems |
40–112 | Dry, moderately humified, light brown Phragmites peat with burnt Calluna stems, seeds of Carex sp. and Menyanthes trifoliata and megaspores of Selaginella |
112–135 | Light brown Phragmites peat containing twigs of Betula, leaves and seeds of B. nana, seeds of Menyanthes and Carex sp., a single seed of Lychnis flos-cuculi, Chara oospores and megaspores of Selaginella |
135–143 | Phragmites peat with a few Betula fragments and seeds of Carex sp., Carduus cirsium sp., Viola sp. and Lychnis flos-cuculi and megaspores of Selaginella |
At the time of the forest maximum the tree pollen frequency contributed between 30–50% of the total pollen spectrum on the Teesdale diagrams (Turner et al., 1973), which contrasts, for example, with the Cranberry Bog (County Durham) lowland diagram (Turner, 1970), where the herb frequency averages some 5% as opposed to the 30–40% for Upper Teesdale. Hence the woods were open compared with the lowlands, to allow a varied herbaceous flora to flourish and contribute a large percentage to the total pollen spectrum.
5000 years BP and later
The open woodland covering most of Upper Teesdale by 5000 years BP was replaced where the soil was becoming waterlogged by blanket peat and where it was better drained by grassland. The change from woodland to blanket peat seems to have been an irreversible process. At Tinkler's Sike there are a series of alternating high and low Graminae and Plantago frequencies near the top, and as these changes occur in the 15 cm of peat above the level dated at 2570 ± 80 years BP, it seems likely that they represent varying intensities of human occupation from the Late Bronze Age onwards. This is pollen assemblage Zone G and is correlated with Godwin's Zone VIII.
The pollen record of the Teesdale rarities
Of the 75 species of flowering plants described by Piggott (1956), 16 have pollen that is diagnostic at species level and 11 have been recorded in the Upper Teesdale pollen diagrams (Turner et al., 1973). These are indicated in
Laboratory code | Depth (cm) | Pollen horizon | Age, in radiocarbon years BP (before 1950) |
GaK-2027 | 14 | Rise in Gramineae Callum and Plantago; beginning of zone G | 2570 ± 80 |
GaK-2028 | 44 | Beginning of zone A | 3390 ± 90 |
GaK-2029 | 70 | Beginning of subzone Oc | 6150 ± 160 |
GaK-2030 | 120 | End of zone H | 8250 ± 280 |
GaK-2031 | 135 | End of zone J | 9900 ± 190 |
Red Sike, which indicates that it has increased with the spread of grassland too. Polygonum viviparum is recorded in pollen assemblage zone G at Red Sike Moss and zone J at TSI, and seems to have been most abundant when the limestone grassland spread to its maximum extent. Saxifraga stellaris has been recorded from RSII in zones J and G, and from RSII and Tinkler's Sike in zone 0, so demonstrating its presence in the Late-glacial, at the forest maximum and since the expansion of blanket bog and grassland.
The records for G. verna, Dryas octopetala
Fossil remains of many of the rarities have been found in many parts of Britain during the Late Devensian and so the Teesdale assemblage is relict. It has been assumed that the present open communities contain those components of the Late Devensian vegetation that persisted in refugia during the Flandrian where positive processes ensured their survival (Piggott and Walker, 1954; Godwin, 1956; Piggott, 1956). However, some of the habitats in which the rarities are found today are the result of ecological change during the Flandrian (Bellamy et al., 1969a, b; Squires, 1970, 1971, 1978; Turner et al., 1973). Minimum competition is a feature of all the communities containing rarities. Their survival during the woodland phase (8000–3000 years BP) depended on the presence of treeless areas, or a low tree density, because many of the rarities are heliophytes and therefore open woodland or woodland with some openings was necessary.
When the blanket peat developed about 5500 years BP there was a critical period for the rarities, all herb values declined because of increasing heather and they were restricted to peat-free areas. After 3000 BP trees were replaced mainly by grassland. At high altitudes in Teesdale, woodland regeneration may have been limited and once trees were eliminated, grassland species were encouraged in the base-rich areas. Tree destruction might have been caused by grazing and browsing of native fauna, such as the aurochs (Johnson and Dunham, 1963), or the red deer (Dimbleby and Simmons, 1974). The grazing intensity may well have increased as the area available decreased with the continued extension of the blanket peat. Increases in the origin and extent of grassland also have been interpreted as a result of prehistoric peoples' activities (Turner et al., 1973). Evidence comes from microliths and the remains of domestic cattle (Johnson and Dunham, 1963; Proctor, 1965, 1976) and implicit evidence is present in the pollen diagrams (Squires, 1970, 1971, 1978; Turner et al., 1973), particularly the grass pollen and ruderal pollen, especially ribwort plantain.
During the blanket peat initiation and extension in the mid-Flandrian many refugia disappeared. By contrast removal of woodland promoted the erosion of substrates and one result was the creation of habitats such as those found on the Sugar Limestone. This allowed the migration of rarities from their diminished refugia and resulted in the creation of new communities. Johnson et al. (1971) argued that the Sugar Limestone is a subsurface phenomenon formed beneath a thin drift cover or soil, its presence at the surface being the result of subaerial erosion of the overlying sediment. The present Sugar Limestone outcrops are the product of either the past 5000 years (Turner et al., 1973), or the past 3000 years (Squires, 1978). So most of the rarities in the Teesdale assemblage are relict, that is individually they have a history of 10 000–12 000 years in the area but the palaeoecological evidence suggests that their present-day distribution is not relict. The rarities are more widespread now than at any other time in their Flandrian history because many of the present-day habitats are recent, or at most 5000 years old. Only those areas such as flushes, springs, quartz-dolerite and limestone screes have been long-standing refugia. These areas must have been crucial in the survival of rare species, particularly during the blanket bog extension. However, at least three species that once belonged to the relict flora have become extinct within comparatively recent times: sainfoin and the purple saxifrage since the spread of grassland and blanket bog, and Jacob's ladder within the past 150 years (Turner et al., 1973). Thus the present widespread distribution of the rarities can be looked at as the latest stage in the following sequence (Squires, 1978).
- c. 10000–8000 years BP: widespread distribution with the predominance of positive processes; i.e. local instability from gelifluction and groundwater fluctuations, minimal competition and base-rich soils and surface water.
- c. 8000–3000 years BP: minimal distribution with the preponderance of negative processes; i.e. soil leaching, tree immigration and blanket peat development restricted rarities to refugia.
- c. 3000 years BP: increased distribution because of increasing positive processes that characterize the modern habitats, which allowed the expansion of refugia; i.e. large-scale and local instability (groundwater fluctuations, erosion especially by wind, trampling and burrowing, minimal competition and human interference).
Conclusions
Red Sike Moss and other sites in Upper Teesdale are very important sites where it is possible to see the changes in the Late-glacial and Flandrian flora and where the complex history of the Teesdale rarities can be established. It is one of the most important locations in Britain for conservation: its rare plant assemblages and its palaeoecological development can be compared with both lowland sites in County Durham, such as Neasham Fen (see site report, this chapter), and higher sites on the Moor House National Nature Reserve, such as Valley Bog (see site report, this chapter).