Environmental Geotechnics Botanical and geotechnical characteristics of blanket peat at three Irish bogflows --Manuscript Draft-Manuscript Number:
ENVGEO-D-17-00089R1
Full Title:
Botanical and geotechnical characteristics of blanket peat at three Irish bogflows
Article Type:
Themed Issue: Geotechnical aspects of peatland restoration and management
Abstract:
Systematic investigations of instability of blanket peat began in the 1990s and quickly identified the potential importance of botanical controls on the properties and behaviour of the peat involved in the failures. During 2010-12 investigations of the blanket peat at three bogflows in northwest Ireland were done with the aim of establishing relationships between botanical characteristics and standard physical and geotechnical properties, assuming the latter to be meaningful but recognising that this may not be the case. In-situ measurements and investigations at all three sites were followed by laboratory characterisation of small core, block and monolith samples. The botanical composition of the peat could not be fully determined due to the high degree of decomposition. However, analysis of macrofossils allowed distinct depthrelated patterns of several botanical indicators to be determined. In particular the monocotyledon fragments, dominated by Eriophorum vaginatum, showed distinct and potentially useful distributions throughout the peat. Overall results showed that the basal peat at one site was discernibly different from the other two sites having fewer monocotyledons, fewer fibres, higher dry bulk density and higher saturated hydraulic conductivity. This approach therefore offers a potential basis for developing a means of assessing peat mass characteristics from small auger samples.
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Botanical and geotechnical characteristics of blanket peat at three Irish bogflows ................................................................................................................................................
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E S Foteu Madio and A P Dykes .................................................................................................................................................... Alan Dykes ...............................................................................................................................................
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Response to Reviewer and Editor Comments
COMMENTS FROM ASSESSOR On page 8: “The Fm and Rm fibre fractions were estimated in the field according to the von Post system”: Elaborate how this was done. Text added: The Fm and Rm fibre fractions were estimated in the field based on the von Post system as presented by Hobbs (1986, p.79): Fine fibres (Fm) are ‘fibres and stems smaller than 1 mm in diameter or width’ and coarse fibres (Rm) are ‘fibres, stems, and rootlets greater than 1 mm in diameter or width’. To both of these definitions we added ‘or any plant particle’ and took the size boundary as ‘< or > 1 mm in all directions’. The von Post scheme uses a four point scheme from 0 ‘nil’ to 3 ‘high content’ but without a microscope it is difficult to be certain that there are no fragments of fibre present. Consequently we removed ‘0’ and assessed the quantity according to a five point scale: 1 = very low content (VL), 2 = low content (L), 3 = medium content (M), 4 = high content (H) and 5 = very high content (VH). “The bi-linear correction of the deviator stress due to membrane stiffness was applied to the results”: Give suitable reference. This statement was inserted in error has been corrected with added text: The bi-linear correction of the deviator stress due to membrane stiffness was not applied to the results because although the effect may be significant, (i) there is no consensus on appropriate corrections given complex peat-membrane interactions, and (ii) this was primarily a comparative study that was not necessarily expected to determine the exact value of the shear strength of peat. On page 12: “Field shear vane readings from depths between 1.25 and 2.00 m were between 6.6 and 14.0 kPa at all sites …..”: What vane correction factor, if any, was applied in determining these values. Text added: Uncorrected field shear vane readings from depths between 1.25 and 2.00 m were between 6.6 and 14.0 kPa at all sites and there were insufficient results from which to identify any patterns in the data. No corrections were applied because this was intended as a comparative study and the shear vane is known to be inappropriate for the determination of the undrained strength of peat due to the effects of fibres, although it can be used to identify patterns of peat strength variation with depth. On page 15: “constant head method”: the methodology was not presented in manuscript: please include in section 3: Methods The ‘constant head’ method for measuring permeability/saturated hydraulic conductivity is sufficiently routine that a detailed account of the method is surely not warranted? However, text has been added: For the constant head method we used a laboratory permeameter arrangement as described by, for example, Klute and Dirksen (1986) or Head (1994). Undisturbed core samples collected in thin-walled tubes 50 mm long (‘L’) × 50.5 mm diameter were trimmed to size, saturated in tap water and mounted vertically to form a permeameter maintaining a constant head of 0.15 m of water on the top of the sample. Water that passed through the sample was collected underneath and measured. The constant head saturated hydraulic conductivity was calculated according to Darcy’s Law from: k = VL / (tA.ΔH) where k = permeability = saturated hydraulic conductivity (m s–1) V = volume of water collected (m3) t = time (s) of water collection A = cross-sectional area of peat sample (2.00×10–3 m2) L = length of peat sample (0.050 m) ΔH = head difference across peat sample length (0.200 m)
On page 17: “We are not convinced that peat strength would reduce with increasing fibre content as shown in Fig. 11F”: check this statement against the figure, and confirm OK On reflection, although a hint of such a trend can be discerned from Fig. 11F, it is perhaps so vague that it is not sufficiently ‘real’ to be worth commenting on at all. Therefore the sentence has been deleted. On page 19: “Previous studies have found that higher fractions of coarse fibres had no effect on measured strength compared with lower coarse fibre contents (Zhang and O’Kelly 2014; Hendy et al. 2014);…..” Please check these referenced sources: At least for the first mentioned study, the testing undertaken was consolidated drained (CD) triaxial compression, and the purpose of this investigation was to demonstrate, among other things, that CD triaxial testing of (fibrous) peat produces meaningless strength results, since the test specimen in essentially undergoing 1D consolidation and not shearing in the conventional sense. In Section 5 of their paper (bottom of p.46 to p.48 inclusive), Zhang and O’Kelly (2014) present results from their tests that show, surprisingly, no real differences between the three peat preparations. They then comment on the unsuitability of the particular tests given the observed sample responses, but our comment is valid since we refer only to the measured strength and make no inference or assumptions regarding the validity of the results that those measurements represent. Figure 11: Include R2 values for correlations shown in the figures All values added to Figs. 12A-E inclusive.
REVIEWER #1 General comment: The Authors present an interesting study, with appreciable investigation effort and experimental honesty. The conclusions are not very strong but the problematic approach of the paper results in a discussion very useful for researchers. In my opinion, the paper is suitable for publication on the journal, but it should be improved by addressing the following comments. The absence of significant correlations between botanical features and mechanical parameters should be better discussed in order to address specific guidelines for the stability analyses of this kind of geotechnical context, for example by stating, due to the impossibility of using good empirical correlations to deduce the peat strength parameters, the importance of planning specific laboratory geotechnical tests for each site. Text added to the Discussion (last-but-one paragraph): However, given that the measured strengths at this site were no different from the others, we cannot say whether measurement of those characteristics would be useful for peats formed from significantly different plant assemblages. It is not possible to generalise any implications of our results for peatlands in general, and notwithstanding previous comments we cannot assume that any of our correlations between botanical and geotechnical characteristics will apply throughout Ireland. There is thus a clear necessity for carefully planned laboratory testing of peat from the site of any proposed development, probably requiring excavation of trial pits for the extraction of appropriate undisturbed samples. However, general recommendations for the most appropriate tests – and testing procedures suitable for peat – will probably take some time to emerge from ongoing research programmes. In this respect, the section describing the three sites should be renamed and integrated by adding a specific discussion on the most typical landsliding/failure mechanism for these peaty slopes. The needed of deducing undrained strength values should be related to the observed/expected kinetic of the in-situ failure processes: why are you interested in the undrained strength? Did you always detect fast undrained failure mechanism for these landslides? Explain and discuss.
Section 2 has been renamed ‘Blanket Bog Failures in Ireland’ with the existing ‘Study Sites’ text now comprising subsection 2.1. An additional page of text has been inserted at Section 2 to address the several points raised by the reviewer in this comment. In this respect, you must specify if the Mohr’s Circles you show are in terms of effective stresses or not. Since you mention the effect of pore pressures on their size, the reader could only suspect you have represented effective stresses, but you must specify it both in the text and in the caption of the figure. Otherwise, if the circles are in total stresses, make attention to the comment on the gas effect and explain better what you mean. Text added: Given that the assumed effect of pore pressures in undrained shear tests is to reduce the friction towards zero because the water is incompressible, then the presence of compressible gas within some pore spaces could allow some (additional) frictional resistance to arise during testing. Hanrahan (1954) found that the gas content of Irish Sphagnum peat may be considerably in excess of 5% of the volume and that significant volumes of gases such as sulphuretted and phosphoretted hydrogen (phosphine), as well as methane, could be emitted during construction involving the compression of peat. Therefore the possibility of gas affecting both permeability and pore pressures must be allowed for when interpreting results. Provide some additional hypotheses for the causes of the profile of tensile strength: does the reduction with depth depend on the coarse fibres profile only? Could you invoke a diagenetic process of “crusting” giving cohesion to the material in the upper soil? If not, please discuss in terms of chemical and physical environment. Text added: At individual sites it is possible that such a trend of decreasing tensile strength with depth may not always be found, although there are insufficient relevant data to be able to comment further. Helenelund (1967) suggested that the fibre contents, types and orientations – which depend on the morphology and the mode of growth of the original plant assemblage that formed the peat – may have major influences on the tensile strength. The macrofossil analyses of peats from our study sites revealed remains of sedges, the degree of humification of which increase with depth. In such monocotyledon peat, fibres are the remains of vascular bundles formed from the root systems that grow perpendicularly to the ground surface. The resulting tensile strength will therefore be related to the resisting force produced by the fibres, the frequency of which decreases with depth and is inversely proportional to the degree of humification. The tensile strength results obtained by Helenelund (1967) from Sphagnum bog peat, which has very few fibres, are comparable with the lowest of our results, showing that the monocotyledon peats at our sites generally have higher tensile strengths than Sphagnum bog peat. Due to the effect of compression during the accumulation of the peats, some fibres that were originally distributed vertically through the peat become squashed progressively into a horizontal alignment as pressure increases. The degree of inclination of these fibres toward the horizontal plane should therefore also increase with depth. The tensile strength values presented in this study were measured in a horizontal plane, intended to represent the effect of the peat mass pulling apart above a basal (shear?) failure zone. The effect of fibre orientation should be to increase the tensile strength with depth since horizontal breaking up of a failing peat mass is resisted by sometimes significant lengths of fibres adhering to amorphous colloidal matrix material. However, the role of living and minimally decomposed roots within the near-surface acrotelm layer combined with the very high degree of humification below the acrotelm appears to entirely override the fibre orientation effect. Rename the final section as “Conclusions and Future Work” and put in this section the lines 498-510. Done.
Further detailed observations: Avoid abbreviation of “sampling point” with SP: it creates confusion with the abbreviation of the sites. All instances changed to ‘Sampling Point’.
Table 1- Change the column name “Context” into “Geomorphological context”. Done. Rename 4.2: “Physical and mechanical properties of the peat”. Done. Line 292: Make attention to the meaning of “pre-consolidation” in Geotechnics: do you mean simply “consolidation”? Sorry, yes – we meant consolidation prior to strength determination. Amended accordingly. The caption of Figure 12 is not clear: do you mean “Different estimates of thickness…..” ? Effectively, yes, that is what we mean. Amended to your suggested wording. When you mention the stability analysis with Safety Factor equal to 1 for deducing mobilized strength values, use the term “back analysis”. Amended accordingly.
REVIEWER #2 Line 58: It would be useful to expand the introduction to present some key findings of previous studies on ''botanical controls on peat properties and instability''. The whole point is that there aren’t any such previous studies, and the few that do present some relevant data arrived at contradictory findings (O’Kelly 2017), hence our added text: The need for research into botanical controls on peat properties was further emphasised with respect to blanket peat instability by Kirk (2001), Dykes (2008a) and O’Kelly (2017) in response to findings from their investigations of physical and geotechnical properties thus far. Indeed, O’Kelly (2017) highlighted the scarcity of published works on the topic and the contradictory findings from the few such studies. The present research (Foteu Madio 2012) arose directly from this dearth of previous studies. Line 151: In the literature, there has been much debate on the accuracy of water content values determined using oven drying for organic soils such as peat and the appropriate temperature in this method. Could you comment on why you have chosen oven-drying for 24 h at 105°C for water content determination? Text added: There has been some debate in recent years regarding the appropriate drying temperature for water content determination, including evidence of the possibility of charring of the peat at temperatures higher than 8090°C (O’Kelly 2014). Further, O’Kelly (2014) found experimentally that the possible additional loss of mass due to charring is negligible compared with the mass of any retained water due to incomplete drying, particularly intracellular water within peat fibres that may constitute a significant proportions of the peat mass (Foteu Madio 2013). O’Kelly (2014) therefore recommended following the standard specification for mineral soils of 105°C, as used by many previous workers including Skempton and Petley (1970) and Hobbs (1986). We adopted the latter approach for the demonstrated reasons of standardisation and comparability of results.
Line 233: Water content is a key parameter to understand the geotechnical properties of earth structures. Seasonal changes of soil water content can cause significant seasonal changes in pore pressures, which affect soil strength. Have you considered (or would you recommend) pore pressure as a key controlling parameters for triggering landslides in peat covered slops? This is a difficult issue to address without substantial additional text. Therefore we have used two short paragraphs at different points in the manuscript to try to provide an adequate response. Text inserted into Section 2: It is likely that the peaty-debris slides are triggered by pore pressure effects, in part due to subsurface storm runoff being confined beneath a saturated and effectively impermeable peat cover. Peat slides (interface failures) probably occur for the same reason. Failure within the peat is a more complex issue because of the dual influences of effectively impermeable and normally saturated but weak catotelm peat material and the internal structure of the peat mass (sensu ‘rock mass’ considerations) that may experience high turbulent flows and even artesian conditions within networks of natural peat pipes and (relict) desiccation cracks (Dykes and Warburton 2007a, 2008a; Gilman and Newson 1980; Holden and Burt 2003). Text inserted at the end of the Discussion: Finally, the very low shear strength indicated above demands some consideration with respect to water conditions within the peat. Blanket bogs in the British Isles may experience water table variations of up to 0.5–1.0 m, but these are occasional reductions below the surface during warm periods of summer weather (Evans et al. 1999; Holden and Burt 2003). The usual condition for these deposits is to be fully saturated to the surface, i.e. with normal effective stress ≈ 0 and maximum pore water pressure most of the time. Periods of summer drying may increase the normal effective stress by a few kPa due to the reduced pore water pressure, i.e. temporarily increasing the effective shear strength. Failure within the peat cannot, therefore, be the result of raised pore water pressures throughout the peat matrix due to heavy rainfall (although it could due to external loading). The hydraulic effects of water-filled pipes, cracks and other voids (e.g. Dykes, this volume – in review) may play significant roles in the initiation of failure, i.e. peat mass effects, are thought to be more important than simply the peat matrix (shear) strength, but much more research is needed to test this hypothesis. Line 258: Some slides showing the samples used for laboratory testing could be useful for describing the testing procedures and the results. We assumed from the reference to ‘Line 258’ that the comment was concerned with illustrating the tensile strength methodology. Therefore a new Figure has been added that incorporates the only photos we have of this. Added text: Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c). Line 287: "The basic physical properties of the peat at the three landslides are summarised in Table 4. These are consistent with previous results obtained from Straduff Townland (the 1997 bogflow adjacent to ST) and SA by Yang and Dykes (2006)''. It would be good to add values of physical properties from the mentioned studies for comparison. Inserted into Table 4.
REVIEWER #3 The paper aims to present an original study of instability of blanket peat at three bogflows in northwest Ireland. In addition, were performed investigations between botanical characteristics and standard physical and geotechnical properties. The manuscript is balanced and clearly well-written in scientific and technical soundness. The topic is very interesting, emerging and challenging. I suggest only some minor corrections on the manuscript submitted: i) page 2, line 47 (PDF) enter a space - "… until the late 1990sthe occasional" to "until the late 1990s the occasional…" Done. ii) figure 1: missed geographical coordinates and a scale bar in Ireland map; Done. as well as a brief explanation about the map (grey colour is ? strips are?) … is a morphological map? Please improve. Explanatory details added to the caption. My congratulations to the authors for the outstanding manuscript presented. Thank you!
Original file showing changes
1
v. 03 November 2017
2 3
Botanical and geotechnical characteristics of blanket peat at three Irish
4
bogflows
5 6
Eliane S. Foteu Madio †
7
BSc(Hons), MSc, PhD, MCIWM, Director at Envigma Ltd., Clacton-on-Sea, UK
8
School of Geography and Geology, Kingston University, Kingston upon Thames, UK. †
9 10
Alan P. Dykes*
11
BSc(Hons), PhD, FRGS, FHEA, FGS, CGeol, Associate Professor at Kingston University, Kingston upon Thames, UK
12
Department of Civil Engineering, Kingston University, Kingston-upon-Thames, UK.
13
ORCID: 0000-0003-0327-0498
14 15
*Corresponding author:
16
Centre for Engineering, Environment and Society Research, SchoolDepartment of Civil Engineering, Kingston
17
University, Penrhyn Road, Kingston- upon- Thames, KT1 2EE, UK, Tel.: +44 (0)208 417 701, Email:
18
[email protected]
19 20
† Present
21
10 Crossfield Road, Clacton-on-Sea, CO15 3QT, UK, Tel.: +44 (0)1255 428787, Email:
[email protected]
22
Address at the time of this research:
23
School of Geography and Geology, Kingston University, Kingston upon Thames, UK
address: Senior Engineer,
Formatted: Font: Not Italic
24 25
5419 words (excluding Figure captions and Tables), 132 Figures, 4 Tables
26 27
Abstract
28
1
Formatted: Font: Italic
29
Systematic investigations of instability and failure of peat covered hillslopes began in the late 1990s and quickly
30
identified the potential importance of botanical controls on the properties and behaviour of the blanket peat involved in
31
the failures. However, attempts to unravel some of these controls did not begin for several years. During 2010-12
32
investigations of the blanket peat at three relatively recent bogflows in northwest Ireland were done with the aim of
33
establishing some form of relationship between botanical or paleoecological characteristics and standard physical and
34
geotechnical properties, assuming the latter to be meaningful but recognising that this may not be the case. In-situ
35
measurements and investigations at all three sites were followed by extensive laboratory characterisation of small core,
36
block and monolith samples.
37 38
The botanical composition of the peat could not be fully determined due to the very high degree of decomposition.
39
However, analysis of macrofossils allowed distinct depth-related patterns of several key botanical indicators to be
40
determined. In particular the monocotyledon fragments, dominated by Eriophorum vaginatum, showed distinct and
41
potentially useful distributions throughout the peat profiles. Overall results showed that the basal peat at one of the sites
42
was discernibly different from the other two sites having fewer monocotyledons, fewer fibres, higher dry bulk density
43
and higher saturated hydraulic conductivity. This approach therefore offers a potential basis for developing a means of
44
assessing peat mass characteristics from small auger samples.
45 46
Key words
Fabric/structure of soils, Landslides, Strength & testing of materials
47 48
1. Introduction
49 50
Records of failures of peat bogs go back around 500 years to the collapse of Chat Moss near Manchester,
51
northwest England, in 1526 (Crofton 1902). However, until the late 1990s the occasional studies of isolated
52
examples of peatland failures were largely descriptive with estimates of geometric characteristics and
53
occasionally reports of the living plant assemblages present at the time of failure. Systematic investigations
54
began into the stability of blanket peat-covered slopes following significant peat landslides in Northern
55
Ireland (Dykes and Kirk 2001; Kirk 2001) and northern England (Mills 2002; Warburton et al. 2003, 2004).
56
The potential importance of the botanical composition as a controlling factor for the properties and
57
geotechnical behaviour of peat was highlighted earlier by Hobbs (1986), not least because of the widespread
58
adoption by engineers of the von Post scheme for classifying peat deposits (e.g. Landva and Pheeney 1980;
59
Carlsten 1993) which requires the estimation of relative frequencies of fibres and wood/shrub fragments as 2
Formatted: Font: 11 pt
60
well as the degree of decomposition of the plant matter (i.e. the humification). The need for research into
61
botanical controls on peat properties was further emphasised with respect to blanket peat instability by Kirk
62
(2001), Dykes (2008a) and O’Kelly (2017). in response to findings from their investigations of physical and
63
geotechnical properties thus far. Indeed, O’Kelly (2017) highlighted the scarcity of published works on the
64
topic and the contradictory findings from the few such studies. The present research (Foteu Madio et al.
65
2012; Foteu Madio 2013) arose directly from this dearth of previous studies.
66 67
The aim of this paper is to examine whether physical and geotechnical properties of Irish blanket peat can be
68
causally associated with measurable botanical characteristics. It does so by presenting and analysing data
69
representing the properties and characteristics of the peat at the sites of three significant bogflows in
70
northwest Ireland, obtained from a combination of field and laboratory investigations. The importance of this
71
study is to provide the basis for more efficient and reliable methods for assessing the stability of peat with
72
respect to planned interventions such as construction of access roads for windfarms or other purposes.
73 74
2. Blanket Bog Failures in IrelandStudy Sites
75 76
The topic of peat mass movements (as distinct from geotechnical engineering of peat) emerged from an
77
esoteric scientific by-way to become a mainstream theme in engineering geology and geomorphology
78
following several major events in late 2003. On 19 September 2003, two entirely independent extreme
79
rainfall events in Co. Mayo, Ireland, and South Shetland, Scotland, triggered multiple failures of peat-
80
covered hillslopes (Dykes and Warburton 2007a, 2008a,b). More significantly for civil engineering, four
81
weeks later the 450,000 m3 Derrybrien Windfarm landslide occurred (Lindsay and Bragg 2005). By that time
82
it had already become clear that the Irish blanket bogs were failing in several slightly different ways, giving
83
rise to morphologically distinctive types of failures (Dykes and Warburton 2007b). Most involve shearing of
84
mineral soil beneath the peat (‘peaty-debris slides’), shearing at the peat-mineral interface (‘peat slides’), or
85
shearing entirely within the basal peat (‘bog slides’). ‘Peat flows’, a term reserved for failures resulting
86
primarily from head-loading, appear to be effectively bearing capacity failures with small areas of shear
87
surface within the basal peat having been observed in the Derrybrien and Ballincollig Hill landslides (Long
88
20054; Dykes and Jennings 2011). 3
Formatted: Superscript
89 90
All of the available evidence relating to ‘bog bursts’ and ‘bogflows’ indicate that these failures involved
91
some sort of in-situ liquefaction of the lower or basal peat, with this (semi-)liquid peat slurry then breaking
92
out from beneath a stronger confining acrotelm layer (or from cut faces through the margins of raised bogs)
93
(Dykes and Warburton 2007b). The precise mechanisms of strength loss are unknown. One hypothesis, for
94
example, is that the basal peat fails like ‘quick clay’ with an initial small shear failure creating a disturbance
95
that propagates rapidly. As such a bogflow may simply be a bog slide involving weaker and wetter peat – but
96
there is a clear distinction because these two types of failure have different peat depth vs. gradient
97
characteristics (A P Dykes, unpublished data). A parallel hypothesis is that in some of these failures the
98
lower layer of the peat deposit was always a fluid body, for example if peat grew over a large pond so as to
99
eventually entirely bury it.
100 101
In almost all cases of failures of (blanket) peat-covered slopes in Ireland, landslide morphologies and runout
102
characteristics display clear evidence of relatively rapid development of failure associated with very high
103
volumes of rainwater, with eyewitness accounts of some recent events (e.g. the Derrybrien peat flow in 2003,
104
the Croaghan peat slide in 2014) corroborating these interpretations. Warburton et al. (2004) discussed the
105
various hydrological processes giving rise to, or controlling, such failures. It is likely that the peaty-debris
106
slides are triggered by pore pressure effects, in part due to subsurface storm runoff being confined beneath a
107
saturated and effectively impermeable peat cover. Peat slides (interface failures) probably occur for the same
108
reason. Failure within the peat is a more complex issue because of the dual influences of effectively
109
impermeable and normally saturated but weak catotelm peat material and the internal structure of the peat
110
mass (sensu ‘rock mass’ considerations) that may experience high turbulent flows and even artesian
111
conditions within networks of natural peat pipes and (relict) desiccation cracks (Dykes and Warburton
112
2007a, 2008a; Gilman and Newson 1980; Holden and Burt 2003). The critical factor here is that rates of
113
deformation and then movement are likely to greatly exceed the saturated hydraulic conductivity of the intact
114
peat mass through which any shear surface may develop. Consequently, the focus of our research is on the
115
undrained strength characteristics of basal peat.
116 117
Formatted: Font: Bold, Italic
2.1 Study sites 4
118
We identified three locally significant bogflows (sensu Dykes and Warburton 2007b) for this study, located
119
within the same region of northwest Ireland: Straduff Townland (hereafter referred to as ‘ST’), Slieve
120
Anierin (‘SA’) and Slieve Rushen (‘SR’) (Fig. 1). Site and landslide characteristics are summarised in Table
121
1 and illustrated in Fig. 2. All were relatively recent, thus limiting the degree of post-failure degradation, and
122
two sites (though not the same landslide at one of these sites) had been investigated previously which
123
provided a cross-check for the peat characterisation results from this study. Furthermore, although the peat at
124
all three sites was generally very similar, one site (Slieve Anierin, below) was noted by Yang and Dykes
125
(2006) to be slightly but nevertheless distinctly different from others including a bogflow at Straduff
126
Townland adjacent to the one used for this study. We anticipated that the results of this new research would
127
also show this.
128 129
Table 1. Summary of site details and characteristics of the study bogflows. Bogflow County Latitude Longitude
Elevation Geology Geomorphological Length Slope Deptha Volume (m) (Carboniferous) Context (m) (°) (m) (m)
Formatted: Line spacing: single Formatted: Line spacing: single
ST
Sligo 54°7.2’N 8°12.9’W
405
Lackagh Sandstone
SR
Cavan 54°8.9’N 7°38.5’W
390
Glenade Sandstone
SA
Leitrim 54°6.3’N 7°58.7’W
440
Lackagh Sandstone
Escarpment failure
200
Basin slope failure 175 Escarpment failure
190
5.5 (top) 3 (mid) 6 (lower)
2.5
35,000
Formatted: Line spacing: single
5.5
2.0
20,000
Formatted: Line spacing: single
4
2.2
22,000
Formatted: Line spacing: single
130 131 132
Notes:
Formatted: Underline
a
Formatted: Line spacing: 1.5 lines
133
< FIGURE 1 >
134
Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (after Hammond 1979).
135
The outlined rectangle is enlarged to show the locations of the three bogflows: (left to right) ST = Straduff Townland,
136
SA = Slieve Anierin, SR = Slieve Rushen. Modified from Yang and Dykes (2006).
Indicative average depth of in-situ peat immediately adjacent to the landslide source area
137 138
< FIGURE 2 >
139
Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the
140
head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat basin
141
into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD). 5
142 143
ST, the Straduff Townland landslide, occurred overnight or early morning on 14 August 2008 during very
144
heavy rain. The dominant morphology is that of a bogflow. However, a basal shear surface around 20 mm
145
above the base of the peat was visible in two small parts of the source area (Dykes 2009; Dykes and Jennings
146
2011). Although the latter observation corresponds with a ‘bogslide’ (Dykes and Warburton 2007b), we will
147
refer to this failure as a bogflow. It involved an area of intact blanket peat between the source areas of
148
bogflows dating from 1945 and 1991, leaving narrow strips of minimally displaced peat separating the
149
failures. The physical characteristics of the peat at the 1991 bogflow, just a few metres from the margin of
150
the later failure, were determined by Yang and Dykes (2006). SA (the Slieve Anierin bogflow) is thought to
151
have occurred during 1998, based on its visible condition when first seen from a light aircraft in November
152
1998 and a conversation with a local resident in 2011. It was described, and the physical characteristics of
153
the peat reported, by Yang and Dykes (2006). The date of SR (the Slieve Rushen bogflow) is uncertain, but
154
the condition of the failure when first inspected in September 2004 was consistent with an age of only a few
155
years, i.e. it most likely occurred during the 1990s (Dykes 2008b).
156 157
3. Methods
158 159
The three bogflows were investigated using the same general methodology as previous studies of peat
160
landslides (e.g. Yang and Dykes 2006). All had previously been surveyed in detail by Dykes (2008b, 2009).
161
The focus for this study was to obtain samples for laboratory testing from a carefully prepared and fully
162
described vertical profile through the full depth of undisturbed in situ peat. Most peat failures leave irregular
163
sub-vertical peat profiles with varying amounts of peat debris covering the lower layers, around several parts
164
of the source area margins. A single study profile (hereafter referred to as the ‘study profile’ or ‘sSampling
165
pPoint’, SP) was selected at each landslide according to the feasibility of creating a clean vertical profile
166
through the full thickness of the peat, i.e. involving the minimum manual excavation of loose peat debris, but
167
ensuring the in-situ peat was undisturbed and not within a few metres of any tension cracks. Safety was
168
ensured by having wide open access to the prepared profile from within the evacuated source area of each
169
landslide, with one person maintaining active watch over the cut face while the other person worked there.
170 6
171
3.1 Field investigations
172
Around each bogflow source area, stratigraphic and topographic surveys were carried out in order to estimate
173
the morphology of the peat deposit and the variability of the peat within it prior to failure. The stratigraphy
174
and maximum depth of the in situ peat was determined on a coarse but regular grid using a 20 mm diameter
175
gouge auger. Maximum peat depths were measured at additional locations by probing with a metal rod. Peat
176
surface elevations were then surveyed at all the stratigraphy and peat depth measurement points by levelling,
177
with the mineral surface elevations being measured within the landslide source areas and calculated for the
178
peat-covered areas around the source areas from the measured peat depths.
179 180
Prior to sampling, a detailed description of the full thickness of the peat at each SPSampling Point was
181
recorded according to the von Post (von Post, 1922, as presented by Landva and Pheeney 1980, and Hobbs
182
1986) and Troels-Smith (Troels-Smith 1955) peat classification schemes. Several sets of samples were
183
obtained from each landslide. Most of the physical/geotechnical samples were obtained from the basal peat
184
at each Sampling Point. Samples were also obtained from the surface and middle peat at the Sampling Point
185
at bogflow ST to provide some indication of depth variations, assuming it to be representative of all three
186
sites. In addition, a Geonor H-60 field shear vane was used to measure the ‘field vane strength’ (FVS) of the
187
in-situ basal peat ~1 m behind each Sampling Point. For palaeoecological (or simply ‘botanical’) analyses,
188
monolith samples were extracted that included most of the thickness of the peat profile at each Sampling
189
Point (missing the uppermost part at SR and SA). In addition, 10 mm cubes of peat were carefully cut from
190
the auger samples from SR at approximately 200 mm depth intervals (Fig. 5 in Section 4 shows results from
191
this component of the work). Table 2 summarises the samples collected.
192 193
Table 2. Samples extracted from the study landslidesbogflows. Landslide / Physical properties – Tensile strength – position in small cores 50 mm blocks 120×120×70 peat profile dia. × 51 mm length mm
Triaxial – Shear strength (direct 38 mm dia. shear) – blocks cores 120×120×70 mm
Monoliths for botanical data 730×100×100 mm
Formatted: Line spacing: single
Formatted: Line spacing: single
ST see right ST basea SA 300-1030
6 at ~650 mm depth 3 at 10-80 mm depth 6 at ~1150 mm depth 3 at 890-960 mm depth
--
3 at 10-80 mm depth 1 at 400-1130 mm 3 at 890-960 mm depth depth
9
6
6
12
2
--
--
--
--
1
7
Formatted: Line spacing: single
Formatted: Line spacing: single
Formatted: Line spacing: single
mm depth SA base a SR 100-830 mm depth SR base b
9
6
6
12
2
--
--
--
--
1
9
6
6
12
2
Formatted: Line spacing: single
Formatted: Line spacing: single
Formatted: Line spacing: single
194 195 196 197
Notes:
Formatted: Underline
a
1600-1700 mm depth below the surface of the peat, 970-1700 mm depth for the lower monoliths
Formatted: Line spacing: 1.5 lines
b
1900-2000 mm depth, 1270-2000 mm depth for the lower monoliths
198
3.2 Laboratory testing
199
Some physical properties of peat can give a rough indication of the state or condition of the peat (Hobbs,
200
1986). Therefore, standard methods were used to determine the water content and bulk density (oven-drying
201
for 24 h at 105°C: O’Kelly 2017), loss on ignition (550°C for 3h: Skempton and Petley 1970; Andrejko et al.
202
1983; Jarrett 1983; Hobbs 1986) and saturated hydraulic conductivity (‘constant head’ method e.g. or Head
203
1994) to provide reference details for correlation with the results of the botanical and geotechnical analyses.
204
There has been some debate in recent years regarding the appropriate drying temperature for water content
205
determination, including evidence of the possibility of charring of the peat at temperatures higher than 80-
206
90°C (O’Kelly 2014). Further, O’Kelly (2014) found experimentally that the possible additional loss of mass
207
due to charring is negligible compared with the mass of any retained water due to incomplete drying,
208
particularly intracellular water within peat fibres that may constitute a significant proportions of the peat
209
mass (Foteu Madio 2013). O’Kelly (2014) therefore, and so recommended following the standard
210
specification for mineral soils of 105°C, as used by many previous workers including Skempton and Petley
211
(1970) and Hobbs (1986). We adopted the latter approach for the demonstrated reasons of standardisation
212
and comparability of results.
213 214
For the constant head method we used a laboratory permeameter arrangement as described by, for example,
215
Klute and Dirksen (1986) or Head (1994). Undisturbed core samples collected in thin-walled tubes 50 mm
216
long (‘L’) × 50.5 mm diameter were trimmed to size, saturated in tap water and mounted vertically to form a
217
permeameter maintaining a constant head of 0.15 m of water on the top of the sample. Water that passed
8
Formatted: Line spacing: Double
218
through the sample was collected underneath and measured. The constant head saturated hydraulic
219
conductivity was calculated according to Darcy’s Law from: k = VL / (tA.ΔH)
220 221
where k = permeability = saturated hydraulic conductivity (m s–1)
222
V = volume of water collected (m3)
223
t = time (s) of water collection
224
A = cross-sectional area of peat sample (2.00×10–3 m2)
225
L = length of peat sample (0.050 m)
226
ΔH = head difference across peat sample length (0.200 m)
227 228
The proportion of intracellular and interparticle water depends upon the structure and morphology of the
229
various plants present and on the degree of humification of peat (Hobbs 1986). Microfossils, including pollen
230
grains, may not represent the original in situ vegetation because they are small enough to be transported by
231
the wind, possibly over long distances. Therefore we investigated the fibres, macrofossil content and the
232
degree of humification of the peat. The latter influences the water holding capacity, pore sizes and fibre
233
quantities and properties, all of which could influence the peat strength. The fibres and macrofossils are
234
likely to directly affect the strength and other geotechnical properties.
235 236
3.2.1 Humification
237
Humification was quantitatively determined in the laboratory followed a modified version of the Bahnson
238
colorimetric method (Aaby and Tauber 1974; Blackford and Chambers 1993; Chambers et al. 1997).
239
Subsamples taken contiguously at every 10 mm from the monoliths were tested. The measurements were
240
obtained using a Hatch 2500 spectrometer set up at 540 nm. Results are expressed as ‘raw’ percentages of
241
light transmission through the diluted peat solution. The more light passes through the peat solution, the less
242
humified the sample.
243 244
3.2.2 Fibres
245
The fibre content (F) is an important characteristic that influences peat stability (Long and Jennings, 2006) as
246
it affects the peat structure and its strength properties. To explore this effect, we firstly re-defined the 9
247
different fractions as follows: (i) a ‘fine fibre’ (Fm) is a fragment or piece of plant tissue between 0.15 and
248
1.00 mm in any dimension including length; and (ii) a ‘coarse fibre’ (Rm) is a fragment or piece of plant
249
tissue > 1 mm in any dimension. In line with the ASTM’s (2008) standard for determining the fibre content
250
of peat, the ‘total fibre fraction’ (Ft) is been defined as all fibres ≥ 0.15 mm in any dimension. The humus
251
fraction (Fh) is defined as all particles < 0.15 mm in any dimension. We recognise that it is difficult to
252
determine a specific shape of some fibres and that, depending on the orientation of the fibre, any dimension
253
of a fibre or particle of a particular shape (e.g. elongated fibres) can prevent it passing through a hole in the
254
sieve, so further refinements to this methodology are likely to be needed in the future.
255 256
The Fm and Rm fibre fractions were estimated in the field according tobased on the von Post system as
257
presented by Hobbs (1986, p.79): Fine fibres (Fm) are ‘fibres and stems smaller than 1 mm in diameter or
258
width’ and coarse fibres (Rm) are ‘fibres, stems, and rootlets greater than 1 mm in diameter or width’. To
259
both of these definitions we added ‘or any plant particle’ and took the size boundary as ‘< or > 1 mm in all
260
directions’. The von Post scheme uses a four point scheme from 0 ‘nil’ to 3 ‘high content’ but without a
261
microscope it is difficult to be certain that there are no fragments of fibre present. Consequently we removed
262
‘0’ and assessed the quantity according to a five point scale: 1 = very low content (VL), 2 = low content (L),
263
3 = medium content (M), 4 = high content (H) and 5 = very high content (VH). All of the other fractions
264
defined above were determined in the laboratory and recorded using a similar 5-point scheme:
265
1 = fibre content ≤ 40%
266
2 = fibre content > 40 and ≤ 60%
267
3 = fibre content > 60 and ≤ 80%
268
4 = fibre content > 80 and ≤ 95%
269
5 = fibre content > 95%
270
Differentiating peat in this way enabled field estimates to be corrected with measurements obtained from
271
laboratory tests, and this simple 5-point scale allowed cluster analyses of the results to be carried out in a
272
consistent way.
273 274
For the laboratory determinations, duplicate subsamples of known masses were taken every 70 mm from
275
along the lowest monolith sample from each site. These were analysed differently in order to separate the 10
276
peat into different fractions, the initial part of the procedure following ASTM (2008) but with a much
277
smaller initial sample mass. Thus the fibre contents of the lowest 0.7 m of the peat profile at each landslide’s
278
Sampling Point were fully quantified. The first subsample was soaked in a dispersing agent (5% sodium
279
hexametaphosphate) for approximately 15 hours and then the peat was gently washed through a 0.15 mm
280
mesh size sieve using tap water. The fibrous material retained on the sieve was washed through a further 1
281
mm sieve and the fine fraction that passed through was collected. The fibres retained on the 1 mm sieve
282
comprised the coarse fraction. Both fractions were oven-dried at 105°C until constant masses were achieved.
283
The masses of fine and coarse fibres were combined to obtain the total mass of fibres. The mass of humus
284
was obtained from the difference between the mass of total fibres and the initial dry mass of peat determined
285
from the second subsample. The second subsample was dried at 105ºC for 24 h and the mass ratio of dry to
286
wet peat determined. The duplicate peat samples had slightly different masses and assuming that their
287
respective mass ratios of dry to ‘field wet’ peat were equal, the corresponding initial mass of the sample used
288
for fibre content testing was established. The fibre (Ff)/humus (Fh) fractions (without any mineral matter)
289
were then expressed as percentages of the initial dry mass (Ms) as follows:
Formatted: Font: 11 pt Formatted: Font: 11 pt
290
F f / h = (M f / h / M s) × 100
291
where Ff/h is the fibre/humus fraction (%), Mf/h is the mass (g) of the fibre/humus fraction after drying at
292
105°C to constant mass then subtracting the mass of ash, and Ms is the mass (g) of the initial peat sample
293
after drying at 105°C to constant mass less the mass of ash.
294 295
3.2.3 Macrofossils
296
The heterogeneity of peat is due to the variability of factors and environmental gradients that influence its
297
initiation and development (Moore, 1984; Charman, 2002). The original plant composition of peat
298
influences its structure and is assumed to affect its geotechnical properties. We used macrofossil analysis to
299
assess these botanical factors. 10 mm cubes of peat were obtained from the along the length of each monolith
300
sample, with 40–80 mm separation except within the basal peat where the cubic subsamples were
301
contiguous. Analysis was undertaken using the ‘Quadrat and Leaf Count Macrofossil Analysis technique’
302
(QLCMA) developed at the Southampton Palaeoecology Laboratory (Barber et al. 1994). The method
303
estimates the percentage coverage of all macrofossil types with the aid of a 10 × 10 grid graticule in the
304
eyepiece of a stereomicroscope. Monocotyledon epidermis tissues and Sphagnum branch leaves were 11
305
examined further at a magnification of ×400 under transmitted light. Daniels and Eddy (1990) (for
306
Sphagnum), Smith (2004) (for other bryophytes), Grosse-Brauckmann (1972) and Katz et al. (1977) (for
307
vascular plants) were used to identify the remains.
308 309
The additional small cubic samples obtained from SR were further investigated using the method developed
310
by Walker and Walker (1961), in which on a scale of 0 to 5, 0 indicates absence and 5 indicates that the
311
sample consisted largely of a particular macrofossil. This was done to check that peat at the Sampling Point
312
was representative of the entire blanket bog.
Formatted: Font: 11 pt Formatted: Font: 11 pt
313 314
3.2.4 Shear strength
315
The mechanism of failure of in-situ peat in natural landslides is uncertain and indeed there may be different
316
mechanisms operating in different contexts. Examples of these are outlined in Section 2. Our tests focused
317
on undrained shear strength because of the documented rapid development of failures compared with the
318
measured very low permeability of Irish catotelm peat (e.g. 10–6 to 10–9 m s–1: see Section 4.2.1). We used a
319
direct shear apparatus with a 100 mm × 100 mm shearbox to try to obtain reproducible values of shear
320
strength using normal stresses representing in-situ conditions, i.e. typically less than 5 kPa (after Dykes
321
2008a). Samples were sheared at normal stresses of 0.7, 1.2, 1.7, 2.2, 3.2, 4.2 and 5.6 kPa using the method
322
outlined by Dykes (2008a), i.e. no pre-consolidation, but with a slightly higher shear rate of 1 mm min–1
323
(2×10–5 m s–1) to represent moderate failure (IUGS, 1995) with the associated likelihood of some undrained
324
shearing effects..
Formatted: Superscript Formatted: Superscript
325 326
The triaxial tests were intended to give an indication of the undrained shear strength and associated stress-
327
strain behaviour of the peat by means of rapid unconsolidated-undrained tests on standard 38 mm diameter ×
328
76 mm high samples (carried out according to Head (1994)) at a range of cell pressures at the lowest end of
329
what was possible with the available equipment, i.e. 50, 100 and 200 kPa. To minimise membrane effects we
330
used thinner membranes, samples were allowed to saturate before the axial load was applied at 1 mm min–1
331
as for the direct shear tests. After each test, the sample was visually inspected to assess the failure
332
mechanism or any other deformation. The bi-linear correction of the deviator stress due to membrane
333
stiffness was not applied to the results because although the effect may be significant, (i) there is no 12
334
consensus on appropriate corrections given complex peat-membrane interactions, and (ii) this was primarily
335
a comparative study that was not necessarily expected to determine the exact value of the shear strength of
336
peat.
337 338
3.2.5 Tensile strength
339
The tensile strength of block samples of undisturbed peat was measured using the equipment (Fig. 3C) and
340
procedure described by Dykes (2008c). This involved applying a tensile load, in 100 g increments, to half of
341
the cross-sectional area of each 100 × 100 mm test sample by means of five 10 mm wide steel fingers (Fig.
342
3A), the tensile resistance being provided by the four 12.5 mm wide strips of peat between the fingers (Fig.
343
3B). Tensile stress and strain were recorded 30 s after the application of each load increment until the sample
344
failed. Although results obtained using this method have been found to be reproducible and consistent, two
345
key limitations are recognised: (i) the apparatus does not allow a vertical load to be placed on the sample to
346
replicate the condition of the basal peat in-situ; and (ii) significant sample disturbance may occur during
347
installation due to large fibres or woody fragments (Dykes 2008c).
348 349
< FIGURE 3 >
350
Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the
351
centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample
352
following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’
353
assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the
354
weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this
355
apparatus are provided in Dykes (2008c).
356 357 358
4. Results
359 360
4.1 Field descriptions of the peat
361
The peat at the three landslides showed remarkably little variability in terms of structure and macrofossil
362
content. Four major stratigraphic units were identified at each site. The first unit (starting at the top),
13
Formatted: Font: Not Bold
363
including the living roots near the surface, comprised slightly humified peat, with each unit below being
364
progressively more humified and the fourth unit at the base having highly humified and/or greasy peat,
365
sometimes with bitumen or sludge like patches (Table 3; e.g. Fig. 34). The identifiable plant material in the
366
peat was predominantly monocotyledon (‘monocot’) remains (‘Turfa herbacea’ in the Troels-Smith scheme)
367
including undifferentiated roots, stems and leaves (Fig. 45). This general lack of variation between (Table 3)
368
and within (Fig. 45) sites allowed us to consider one Sampling Point as being broadly representative of each
369
landslide site.
370 371
< FIGURE 34 >
372
Figure 34. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was
373
located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013).
374 375
< FIGURE 45 >
376
Figure 45. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5,
377
etc. refer to sampling positions: A1 to A9 are shown in Fig. 45; E1/E3 and E4/E7 are located either side of the
378
downslope extent of the source area. The materials found at each position are from, and in the same order as, this list:
379
Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot
380
leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013).
381 382
4.2 Physical and mechanical properties of the peat
383 384
4.2.1 Geotechnical characteristics
385
The basic physical properties of the peat at the three landslides are summarised in Table 4. These are broadly
386
consistent with previous results obtained from Straduff Townland (the 1997 bogflow adjacent to ST) and SA
387
by Yang and Dykes (2006). FUncorrected field shear vane readings from depths between 1.25 and 2.00 m
388
were between 6.6 and 14.0 kPa at all sites and there were insufficient results from which to identify any
389
patterns in the data. No corrections were applied because this was intended as a comparative study and the
390
shear vane is known to be inappropriate for the determination of the undrained strength of peat due to the
391
effects of fibres, although it can be used to identify patterns of peat strength variation with depth.
14
392 393
Results from the experimental low-stress direct shear tests (without pre-consolidation prior to shearing) are
394
shown in Fig. 56. These are consistent with results obtained from basal peat at another landslide in
395
northwestern Ireland (identified as ‘E6’ by Kirk (2001): Dykes 2008a). The surface peat at ST clearly
396
demonstrates a higher strength due to the greater density, and probably strength, of less humified fibres.
397
Samples inevitably consolidate under even these small loads as shearing takes place. Straight line
398
approximations in the normal stress range 2-5 kPa would all give cohesion intercepts of 1-4 kPa (Fig. 56). If
399
the peat was overconsolidated by up to 10-15 kPa as seems to be the general case (O’Kelly 2017), such low
400
shear stress values within this range of applied normal loads should not be expected.
Formatted: Font: 11 pt
401 402
Results from the unconsolidated-undrained triaxial tests similarly demonstrate the inherently low shear
403
strength of the basal peat with all three sites in the range 1.5-2.5 kPa (Fig. 67). Slight variations in the
404
diameters of the Mohr’s circles arise from the heterogeneity of the peat mass, as also observed in raised bog
405
peat by Hanrahan (1954), but may also result from gas in the peat causing variations in pore water pressures
406
within the samples. Given that the assumed effect of pore pressures in undrained shear tests is to reduce the
407
friction towards zero because the water is incompressible, then the presence of compressible gas within some
408
pore spaces could allow some (additional) frictional resistance to arise during testing. Hanrahan (1954) found
409
that the gas content of Irish Sphagnum peat may be considerably in excess of 5% of the volume and that
410
significant volumes of gases such as sulphuretted and phosphorated hydrogen (phosphine), as well as
411
methane, could be emitted during construction involving the compression of peat. Therefore the possibility
412
of gas affecting both permeability and pore pressures must be allowed for when interpreting results.
413 414
Fig. 78 shows the tensile strengths obtained from this and previous studies using the same methodology
415
(Dykes 2008c). The tensile strengths of the basal peat at the three landslides in this study are all less than 3
416
kPa except where locally reinforced by matted woody fragments.
417
With the exception of two outliers, which arose from the respective samples containing significant fragments
418
of decomposing roots or woody stems, there is an apparent trend of reducing tensile strength with depth.
419
Although this trend arises from combined results from several locations in Ireland, the similarities of all
420
other measured peat properties between all of these sites (Dykes 2008c; Dykes and Warburton 2008a; Dykes 15
Formatted: Font: Italic
421
and Jennings 2011) means that this general trend is probably real. The tensile strengths of the basal peat at
422
the three landslides in this study are all less than 3 kPa except where locally reinforced by matted woody
423
fragments.At individual sites it is possible that such a trend of decreasing tensile strength with depth may not
424
always be found, although there are insufficient relevant data to be able to comment further.
425 426
Helenelund (1967) suggested that the fibre contents, types and orientations – which depend on the
427
morphology and the mode of growth of the original plant assemblage that formed the peat – may have major
428
influences on the tensile strength. The macrofossil analyses of peats from our study sites revealed remains of
429
sedges, the degree of humification of which increase with depth. In such monocotyledon peat, fibres are the
430
remains of vascular bundles formed from the root systems that grow perpendicularly to the ground surface.
431
The resulting tensile strength will therefore be related to the resisting force produced by the fibres, the
432
frequency of which decreases with depth and is inversely proportional to the degree of humification. The
433
tensile strength results obtained by Helenelund (1967) from Sphagnum bog peat, which has very few fibres,
434
are comparable with the lowest of our results, showing that the monocotyledon peats at our sites generally
435
have higher tensile strengths than Sphagnum bog peat. Due to the effect of compression during the
436
accumulation of the peats, some fibres that were originally distributed vertically through the peat become
437
squashed progressively into a horizontal alignment as pressure increases. The degree of inclination of these
438
fibres toward the horizontal plane should therefore also increase with depth. The tensile strength values
439
presented in this study were measured in a horizontal plane, intended to represent the effect of the peat mass
440
pulling apart above a basal (shear?) failure zone. The effect of fibre orientation should be to increase the
441
tensile strength with depth since horizontal breaking up of a failing peat mass is resisted by sometimes
442
significant lengths of fibres adhering to amorphous colloidal matrix material. However, the role of living and
443
minimally decomposed roots within the near-surface acrotelm layer combined with the very high degree of
444
humification below the acrotelm appears to entirely override the fibre orientation effect.
445 446
< FIGURE 56 >
447
Figure 56. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from
448
around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan,
449
obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a).
16
Formatted: English (United States)
450 451
< FIGURE 67 >
452
Figure 67. Mohr’s Circles (total stresses) obtained from unconsolidated-undrained triaxial tests on peat samples from
453
the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu
454
Madio (2013).
455 456
< FIGURE 78 >
457
Figure 78. Tensile strength results obtained from the three landslides in this study and from previous studies using the
458
same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW-
459
08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred
460
on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’.
461
Modified from Foteu Madio (2013).
462 463
4.2.2 Humification and fibres
464
The results of the quantitative determination of humification, recorded as the ‘raw’ percentage of light
465
transmission through the peat, showed no significant differences between the mean values for the three sites.
466
However, only the results from ST showed a clear reduction in light transmission (i.e. increase in degree of
467
humification) with depth (Fig. 89).
468 469
Table 3. Summary description of the peat at each landslide Sampling Point (Foteu Madio 2013). The four major
470
stratigraphic units are separated by the solid lines of the Table.
Depth (m) 0.00-0.40 0.40-0.78 0.78-1.22 1.22-1.60 1.60-1.80 >1.80
Peat profile description at ST Light brown fibrous peat, slightly humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength. Black and moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength. Light brown with dark patches, very weak and moderately humified peat. Monocotyledon fine fibre limited. Low horizontal tensile strength. Brown, moderately to strongly humified peat. Monocotyledon fine fibre present. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Rare and very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart.
Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single
Depth (m)
Peat profile description at SR1
Formatted: Line spacing: single
0.00-0.15
Brown fibrous peat with moderately humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength.
Formatted: Line spacing: single
17
0.15-0.36
Brown, less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength.
Formatted: Line spacing: single
0.36-0.58
Dark brown humified peat with monocotyledon fragments. Low horizontal tensile strength.
Formatted: Line spacing: single
0.58-0.88
Dark brown decomposing peat with monocotyledon fragments. Low horizontal tensile strength.
Formatted: Line spacing: single
>1.64
Dark grey, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1 on the Munsell soil colour chart.
Depth (m)
Peat profile description at SA
0.88-1.58 1.58-1.64
0.00-0.76 0.76-1.56 1.56-1.76 1.76-1.78 >1.78
471 472
Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single
Dark fibrous peat, slightly humified, mainly monocotyledon fine fibres, low amorphous material and moderate horizontal tensile strength. Light brown less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat, moderate amorphous material and moderate horizontal tensile strength. Black humified peat with monocotyledon fragments. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart.
Note 1
Formatted: Line spacing: single
Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Line spacing: 1.5 lines
Recorded in July 2010 prior to the moorland fire.
473 474
Table 4. Summary of physical properties of peat at the three landslides., including previous data from Yang and Dykes
475
(2006)*. Water content a,b (% mass fraction)
Loss on Ignition c (%)
Saturated bulk density e (Mg m–3)
Dry bulk density e Saturated (Mg m–3) hydraulic conductivity h,i (m s–1)
700-900 *620-860 600-700 600-700 *600-740
94.5-95.6 *97.8-98.8 94.6-97.2 d 95.0 *97.7-98.5
1.00 f *1.06 1.00 1.00 *1.05
0.10-0.20 *0.13 0.10-0.20 0.20 g *0.15
Formatted: Line spacing: single
Formatted: Line spacing: single
ST SR SA
476 477 478 479 480 481 482 483 484 485 486
10–9 to 10–8 * < 10–11 10–9 to 10–6 10–8 to 10–6 * < 10–11
Notes
Formatted: Line spacing: single Formatted: Superscript Formatted: Line spacing: single Formatted: Line spacing: single Formatted: Superscript
a
There was negligible difference between field-wet and saturated water contents at all sites
b
Indicative ranges of mean values from 256-319 samples per site
c
Indicative ranges of mean values from 123-196 samples per site
d
The basal peat at Slieve Rushen was noticeably higher in organic matter than any other sampled peat
e
Mean values from 20-26 samples per site
f
The basal peat at Straduff Townland was noticeably higher (~1.10 Mg m–3) than any other sampled peat
g
The peat at Slieve Anierin had higher dry bulk densities throughout its depth
h
Indicative ranges of mean values from 19-26 samples per site, obtained using a ‘constant head’ method
i
Results obtained using a ‘falling head’ method were consistently 102-103 m s–1 higher than the respective ‘constant
head’ values
487
18
Formatted: Line spacing: 1.5 lines
488
The mean ‘total fibre fraction’ (Ft) of the lowest 0.7 m of the peat profile at each landslide Sampling Point,
489
based on 70 depth-consecutive measurements per site, was 68% at ST, 71% at SR and 56% at SA. As Fig.
490
910 shows, the latter appears to indicate a small but consistent difference from the other two, having slightly
491
fewer coarse fibres throughout the sampled depth range. At all three sites there is a general trend of reducing
492
coarse fibre content with depth but the fine fibre content seems to increase slightly towards the base of SR.
493 494
< FIGURE 89 >
495
Figure 89. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST).
496 497
< FIGURE 910 >
498
Figure 910. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A)
499
Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013).
500 501 502
4.3 Peat stratigraphy according to macrofossil results
503
The blanket bog at the Sampling Point at each landslide mostly comprised the remains of monocotyledon
504
plants, particularly E. vaginatum (Fig. 1011). Monocotyledon contents were lowest within the basal peat
505
zones (as defined by cluster analysis) and, at ST, immediately above the basal zone.
506 507
< FIGURE 1011 >
508
Figure 1011. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter
509
values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram
510
produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters
511
corresponding to zones in the diagram. Source: Foteu Madio (2013).
512 513
4.4 Comparing botanical and geotechnical characteristics
514
The results were examined in order to identify any statistical associations (using Pearson’s ‘r’ correlation
515
coefficient) between physical/geotechnical parameters, and then between geotechnical characteristics and
516
botanical results, that may have physical explanations potentially exploitable for predictive purposes. In this
19
517
study, only significant (p < 0.05) correlations with |r| > 0.7 at all three landslides were interpreted as possibly
518
indicating a causal relationship because the study was based on a single monolith per study site.
519
Furthermore, the full depth of the peat at each site was not analysed for most of the parameters investigated.
520
The only significant associations with |r| > 0.7 that were found between physical/geotechnical parameters at
521
all three sites were between: (i) the humus fraction, Fh, and the total fibre content, Ft (Fig. 1112A); (ii) the
522
total fibre content, Ft, and the coarse fibre fraction, Rm (Fig. 1112B); (iii) the humus fraction, Fh, and the
523
coarse fibre fraction, Rm; and (iv) the coarse fibre fraction, Rm – and therefore also the total fibre content
524
and the humus fraction – and the field water content (Fig. 1112C).
525 526
Figs. 1112D and 1112E show the only consistently high correlations (p < 0.05) between macrofossil data and
527
physical/geotechnical properties of peat, i.e. between: (i) the total fibre content and the proportion of
528
monocot fragments; and (ii) the von Post degree of humification and the percentage of unidentified organic
529
matter. This may arise from the QLCMA method used for macrofossil analyses probably being more
530
appropriate for Sphagnum peat with small leaves that can be easily counted, compared with monocotyledon
531
peat with larger original plant fragments. The general lack of strong or consistent associations correlations
532
between the physical/geotechnical and botanical parameters at the three landslides suggests that these
533
physical properties cannot be used as indicators of peat mass structure and, thus, of potential peat instability.
534
However, the method used to quantify the fibre contents (Section 3.2.2, above) may be useful for
535
investigating relationships between the structural properties of failed Irish blanket peats in order to classify
536
peat for stability assessments.
537 538
The macrofossil analyses at the three landslides showed that the original plant assemblage was
539
predominantly monocotyledons, especially Eriophorum vaginatum. Therefore, the undrained strengths
540
obtained at the three landslides were plotted against the other properties (e.g. coarse fibre content in Fig.
541
12F) in order to investigate any possible relationship that may exist. The statistical analyses revealed no
542
significant correlation coefficients (p < 0.05). We are not convinced that peat strength would reduce with
543
increasing fibre content as shown in Fig. 11F and we suspect that this may be an artefact of the limited data.
544
20
545
Fig. 1213 shows the thickness of a weak basal layer at each site identified by cluster analyses of the results
546
(e.g. Fig. 1011). If all three landslides failed in a similar manner (i.e. by initial basal shearing), then it
547
appears that field observations of shear surfaces within a few tens of mm above the peat-mineral interface
548
can be explained in terms of formation of a failure zone (a) within the weakest layer of the peat profile, and
549
(b) at the lowest elevation within that weakest layer giving a continuous plane above the level of any large
550
stones or woody remnants that would resist shearing within the basal peat. The mean thickness of this layer
551
based on cluster analyses of the data (e.g. Fig. 1011) is around 170 mm, but this is clearly overestimated
552
because of the lack of a clear depth-related trend in the quantitative humification results (‘raw’ % light
553
transmission) from Straduff Townland and is probably less than 140 mm in reality.
554 555
< FIGURE 1112 >
556
Figure 1112. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat.
557
(A) Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs.
558
field water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post
559
humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid
560
line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013).
561 562
< FIGURE 1213 >
563
Figure 1213. Variation of mean thickness of basal peat depths according to specific physical properties at all three
564
landslides.
565 566
5. Discussion
567 568
The three sites investigated for this study were remarkably similar in terms of the characteristics of their
569
blanket peat. Slieve Anierin had a lower fraction of identifiable monocot fragments and a correspondingly
570
higher fraction of unidentified organic matter, but this may simply reflect greater decomposition of the same
571
plants rather than being evidence of different constituents. The smaller proportion of coarse fibres throughout
572
the peat at this site, and particularly towards the base, supports the interpretation of more advanced
573
decomposition. However, the higher dry bulk density and slightly higher saturated hydraulic conductivities 21
574
(Table 4) perhaps indicate a very slightly different composition. One tensile strength measurement at this site
575
was significantly out of line with the others (Fig. 78) due to a high density of woody remains within one test
576
sample, but the other measures of shear strength were entirely consistent with the other two sites. Therefore
577
we suggest that this site has essentially the same palaeoenvironmental history of peat accumulation as the
578
others. Furthermore, the similarity between these results and some obtained from other landslide sites
579
throughout northwestern and western Ireland and Northern Ireland (e.g. Kirk 2001; Yang and Dykes 2006;
580
Dykes 2008c; Dykes and Warburton 2008a; Dykes and Jennings 2011; Dykes, this issue) and indeed eastern
581
Ireland (e.g. Boylan and Long 2010) strongly suggests that the general geotechnical characteristics of upland
582
blanket peat throughout the island of Ireland are very similar everywhere.
583 584
Much of the present vegetation of Ireland’s blanket bogs is dominated by sedges (e.g. E. vaginatum),
585
heathers (Ericacae, including Calluna vulgaris) and some Sphagnum and other mosses. These are all
586
represented in the analyses, with the sedges dominating the identifiable macrofossils (Fig. 910). In many
587
places there are the remains of trees at the base of the peat, which act like fragments of weathered bedrock to
588
resist movement of the peat over the in situ ground. However, at these three sites, separated by up to 20 km,
589
there is a weak basal layer around 150 mm thick that can be clearly distinguished from the peat above on the
590
basis of the properties measured for this study. Intriguingly, a higher proportion of the macrofossils can be
591
identified as monocot fragments in this layer, which somewhat contradicts the idea of greater decomposition.
592
On the other hand, fibre contents reduce sharply towards this basal layer (Fig. 910). O’Kelly (2017)
593
suggested that the properties of fibrous peat depend on the fibre content, but we suggest that these Irish
594
blanket peats cannot be considered to be ‘fibrous’ in the same sense, since even the acrotelm layer may
595
contain relatively few identifiable fibres. The issue is in any case unclear. Previous studies have found that
596
higher fractions of coarse fibres had no effect on measured strength compared with lower coarse fibre
597
contents (Zhang and O’Kelly 2014; Hendy et al. 2014); Price et al. (2005) found that fibre content was not
598
related to compressibility, and Lee et al. (2015) concluded that the effect of fibre orientation on frictional
599
shearing resistance was not clear. However, Boylan and Long (2010) undertook a quantitative analysis of
600
fibre contents adjacent to peat slides in Co. Wicklow and found lower fibre contents with depth. We
601
therefore conclude that the occurrence of failure in upland Irish blanket bogs must be at least in part due to
602
the lower fibre content, as well as higher overall degree of decomposition, towards the base of the peat. 22
603 604
We found some relationships between measured properties of the peat we analysed. The very strong
605
association ( |r| > 0.95) between the humus fraction, coarse fibre fraction and total fibre content at the three
606
landslides mean that only one of these parameters may be needed to investigate other properties of peat. This
607
association can be explained by the fact that with increasing plant decomposition, the size and amount of
608
organic particles decrease, resulting in low fibre contents (Fig. 1112A). When the fibre content decreases, the
609
water content also decreases (Fig. 1112C) because the voids within the fibres, which contain the largest
610
amount of water (MacFarlane and Radforth 1968), also decrease. The coarse fibres influence peat structure
611
and possibly strength (see above) and may be used for stability assessments given that at all three sites they
612
were similarly abundant and showed high ( |r| > 0.9) correlations with other properties. However, the
613
apparent uniformity of the peat across these sites precludes any suggestion that this may form the basis of a
614
generalised approach, in the absence of further studies from different peatlands (e.g. Northern England or
615
Scotland). Figs. 1112D and 1112E merely highlights the effect of humification in that if there are more fibres
616
remaining then there should also be more macrofossils that have not yet decomposed too far to be identified.
617
Fig. 1112F shows that whichever method of strength determination is used (excluding the field vane), the
618
(shear) strength of the basal peat appears to be around 2 kPa. This is consistent with stability analyses of
619
landslides involving failure within the peat (i.e. bog slides, bogflows and some peat flows sensu Dykes and
620
Warburton 2007b) as reported by Dykes (2008c), Dykes and Jennings (2011) and Farrell (2012) and with test
621
results obtained from other similar studies in Ireland (e.g. Dykes 2008c; Dykes et al. 2008).
622 623
The very low shear strength indicated above demands some consideration with respect to water conditions
624
within the peat. Blanket bogs in the British Isles may experience water table variations of 0.5–1.0 m, but
625
these are occasional reductions below the surface during warm periods of summer weather. The usual
626
condition for these deposits is to be fully saturated to the surface, i.e. with normal effective stress ≈ 0 and
627
maximum pore water pressure most of the time. Periods of summer drying may increase the normal effective
628
stress by a few kPa due to the reduced pore water pressure, i.e. temporarily increasing the effective shear
629
strength. Failure within the peat cannot, therefore, be the result of raised pore water pressures throughout the
630
peat matrix due to heavy rainfall (although it could due to external loading). The hydraulic effects of water-
631
filled pipes, cracks and other voids may play significant roles in the initiation of failure, i.e. peat mass 23
632
effects, are thought to be more important than simply the peat matrix (shear) strength, but much more
633
research is needed to test this hypothesis.
634 635
Two of the characteristics identified as being slightly different at Slieve Anierin, i.e. the monocot content and
636
the coarse fibre content, can be readily determined from small auger samples because they are quantified
637
with respect to the dry mass. A hand auger capable of cutting ‘intact’ core samples, notwithstanding issues of
638
sample deformation due to compression or fibres not being cut cleanly (Long and Boylan 2013; Hendy et al.
639
2014), could in principle provide samples for simple determination of dry bulk density and possibly saturated
640
hydraulic conductivity, i.e. the other two slightly distinctive characteristics. However, given that the
641
measured strengths at this site were no different from the others, we cannot say whether measurement of
642
those characteristics would be useful for peats formed from significantly different plant assemblages. It is not
643
possible to generalise any implications of our results for peatlands in general, and notwithstanding previous
644
comments we cannot assume that any of our correlations between botanical and geotechnical characteristics
645
will apply throughout Ireland. There is thus a clear necessity for comprehensive laboratory testing of peat
646
from the site of any proposed development, probably requiring excavation of trial pits for the extraction of
647
appropriate undisturbed samples. However, general recommendations for the most appropriate tests – and
648
testing procedures suitable for peat – will probably take some time to emerge from ongoing research
649
programmes.
650 651
Finally, the very low shear strength indicated above demands some consideration with respect to water
652
conditions within the peat. Blanket bogs in the British Isles may experience water table variations of up to
653
0.5–1.0 m, but these are occasional reductions below the surface during warm periods of summer weather
654
(Evans et al. 1999; Holden and Burt 2003). The usual condition for these deposits is to be fully saturated to
655
the surface, i.e. with normal effective stress ≈ 0 and maximum pore water pressure most of the time. Periods
656
of summer drying may increase the normal effective stress by a few kPa due to the reduced pore water
657
pressure, i.e. temporarily increasing the effective shear strength. Failure within the peat cannot, therefore, be
658
the result of raised pore water pressures throughout the peat matrix due to heavy rainfall (although it could
659
due to external loading). The hydraulic effects of water-filled pipes, cracks and other voids (e.g. Dykes, this
660
volume – in review) may play significant roles in the initiation of failure, i.e. peat mass effects, are thought 24
661
to be more important than simply the peat matrix (shear) strength, but much more research is needed to test
662
this hypothesis.
663
Dykes (2008a, p.344) wrote: ‘The research priorities are therefore to investigate the botanical controls on the
664
geotechnical properties of peat, to establish a reliable method for determining the shear strength of peat, and
665
to identify or develop a reliable method for analysing the stability of blanket bog covered slopes.’ More
666
recently, O’Kelly (2017, p.21) stated that: ‘More extensive testing of peats with different botanical
667
compositions is recommended to confirm relationships between tensile strength, other strength parameters
668
and humification level’. All of these issues are now starting to be addressed more systematically by a few
669
researchers in several countries. However, more extensive integrative research is needed, perhaps involving
670
palaeoecologists alongside geotechnical engineers, to explore the causes and geotechnical effects of different
671
peat accumulation scenarios. Detailed measurements of all possible characteristics, such as presented in this
672
study, are required for several known sites of peat landslides in each of several different biogeographical
673
zones such as Dartmoor (SW England), North Pennines (N England), Isle of Skye (W Scotland), Shetland
674
Islands (N Scotland), ideally including full depth variations at each study location in order to generate
675
sufficient data for reliable statistical analyses.
676 677
6. Conclusions and Future Work
678 679
The upland blanket bogs of northwestern Ireland appear to be formed from essentially the same assemblages
680
of plant species, dominated by sedges (mostly represented by Eriophorum vaginatum), and therefore having
681
similar physical and botanical characteristics. The data describing those characteristics show a statistically
682
distinct basal layer around 150 mm thick characterised by, in particular, a sharp reduction in the coarse – and
683
total – fibre content. Tensile strength, experimental low stress direct shear and unconsolidated undrained
684
triaxial compression measurements of peat strength converge on a value of around 2 kPa which is consistent
685
with stability back-analyses requiring undrained shear strengths of around 2 kPa for FS = 1.0. Contrary to
686
some published accounts, it appears that the lack of coarse fibres may be a contributory factor in the
687
incidence of peat slope failures. Some relationships between measured properties suggest that there may be
688
usable indicators of peat strength and stability conditions, possibly obtainable by means of samples from
25
689
hand augers, but the apparent uniformity of the peat at these three locations precludes any definitive proposal
690
of useful new methodologies at present.
691 692
Dykes (2008a, p.344) wrote: ‘The research priorities are therefore to investigate the botanical controls on the
693
geotechnical properties of peat, to establish a reliable method for determining the shear strength of peat, and
694
to identify or develop a reliable method for analysing the stability of blanket bog covered slopes.’ It has been
695
recognised for some time that the development of methods for reliably estimating the shear strength of peat
696
is likely to require some detailed investigations of botanical controls on relevant geotechnical properties (e.g.
697
Dykes 2008a). More recently, O’Kelly (2017, p.21) stated that: ‘More extensive testing of peats with
698
different botanical compositions is recommended to confirm relationships between tensile strength, other
699
strength parameters and humification level’. All of these issues are now starting to be addressed more
700
systematically by a few researchers in several countries. However, more extensive integrative research is
701
needed, perhaps involving palaeoecologists alongside geotechnical engineers, to explore the causes and
702
geotechnical effects of different peat accumulation scenarios. Detailed measurements of all possible
703
characteristics, such as presented in this study, are required for several known sites of peat landslides in each
704
of several different biogeographical zones such as Dartmoor (SW England), North Pennines (N England),
705
Isle of Skye (W Scotland), Shetland Islands (N Scotland), ideally including full depth variations at each
706
study location in order to generate sufficient data for reliable statistical analyses.
707 708
Acknowledgements
709 710
This work was funded by Kingston University’s Centre for Earth and Environmental Science Research (CEESR)
711
studentship support fund. EF thanks Prof M Waller (Kingston University), Dr P Hughes (University of Southampton)
712
and Dr M Grant (Kingston University/Wessex Archaeology) for advice and assistance with palaeoecological research
713
techniques. We are grateful to Prof E Bromhead for redrawing Figure 34, and to Mr C Somerfield for assistance with
714
the triaxial testing.
715 716
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717
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718
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Charman DJ (2002) Peatlands and Environmental Change. Wiley, Chichester.
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Dykes AP (2008b) Geomorphological maps of Irish peat landslides created using hand-held GPS. Journal of Maps
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753
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(eds)). ICE Publishing, London, UK, pp.463-479.
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Foteu Madio ES (2013) Botanical and geotechnical influences on peat instability. Unpublished PhD thesis, Kingston University, UK.
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Foteu Madio ES, Dykes AP, Waller MP, Hughes P and Grant MJ (2012) Botanical and geotechnical influences on peat
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Gilman K, Newson MD (1980) Soil Pipes and Pipeflow: a Hydrological Study in Upland Wales, British Geomorphological Research Group Monograph 1. Geobooks: Norwich. Grosse-Brauckmann G (1972) Über pflanzliche Makrofossilien mitteleuropäischer Torfe - I. Gewebereste krautiger Pflanzen und ihre Merkmale. Telma2, 19-55.
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Hammond RF (1979) The Peatlands of Ireland. Survey Bulletin No. 35. An Foras Talúntais, Dublin
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Hanrahan ET (1954) An investigation of some physical properties of peat. Géotechnique 4, 108-123.
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Head KH (1994) Manual of Soil Laboratory Testing, Permeability, Shear Strength and Compressibility Testing.
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Volume 2. Wiley, New York. Helenelund KV (1967) Vane tests and tension tests on fibrous peat. Proceedings of the Geotechnical Conference, Oslo, Vol. 1, 199–203. 28
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Hendy MT, Barbour SL and Martin CD (2014) Evaluating the effect of fiber reinforcement on the anisotropic undrained
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Hobbs NB (1986) Mire morphology and the properties and behaviour of some British and foreign peats. Quarterly Journal of Engineering Geology 19, 7-80. Holden J, Burt TP (2003) Hydrological studies on blanket peat: the significance of the acrotelm–catotelm model. Journal of Ecology 91: 103–113. IUGS – International Union of Geological Sciences Working Group on Landslides (1995) A suggested method for describing the rate of movement of landslides. Bulletin International Association of Engineering Geology 52, 75-78. Jarrett PM (1983) Summary. In Testing of Peats and Organic Soils (Jarrett PM (ed)). ASTM Special Technical Publication, 820. American Society for Testing and Materials, Philadelphia, pp.233-237.
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Katz NJ, Katz SV and Skobeyeva EI (1977) Atlas of plant remains in peat soil. Nedra [In Russian].
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Kirk KJ (2001) Instability of blanket bog slopes on Cuilcagh Mountain, N.W. Ireland. Unpublished PhD thesis.
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University of Huddersfield, UK. Klute A, Dirksen C (1986) Hydraulic conductivity and diffusivity: laboratory methods. Methods of Soil Analysis
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Part 1. Physical and Mineralogical Methods. Agronomy Monograph (2nd edition), Vol. 9. Soil Science Society
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of America, Madison, pp. 687– 734. Landva AO and Pheeney PE (1980) Peat fabric and structure. Canadian Geotechnical Journal 17(3), 416-435.
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Lee J-S, Seo S-Y and Lee C (2015) Geotechnical and geophysical characteristics of muskeg samples from Alberta,
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Canada. Engineering Geology 195, 135-141. Lindsay R, Bragg O (2005) Wind farms and blanket peat: a report on the Derrybrien bog slide (2nd edition). Derrybrien Development Cooperative Ltd., Gort. Long M (2005) Review of peat strength, peat characterisation and constitutive modelling of peat with reference to landslides. Studia Geotechnica et Mechanica XXVII, 67-90. Long M and Boylan N (2013) Predictions of settlement in peat soils. Quarterly Journal of Engineering Geology and Hydrogeology 46, 303-322.
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Long M and Jennings P (2006) Analysis of the peat slide at Pollatomish, County Mayo, Ireland. Landslides 3(1), 51-61.
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MacFarlane IC and Radforth NW (1968) Structure as a basis of peat classification. National Research Council of
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Canada (Ottawa). Reprinted from Proceedings, Third International Peat Congress held in Quebec, Canada, 18-23
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August 1968, pp.91-97.
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Mills AJ (2002) Peat slides: morphology, mechanisms and recovery. Unpubl. PhD thesis. University of Durham, UK.
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Moore PD (1984) The classification of mires: An introduction. In European Mires (Moore PD (ed)). Academic Press, London, pp.1-10. O’Kelly BC (2014) Drying temperature and water content–strength correlations. Environmental Geotechnics 1 (EG2), 81-95. O’Kelly BC (2017) Measurement, interpretation and recommended use of laboratory strength properties of fibrous peat. Geotechnical Research, published on-line at http://dx.doi.org/10.1680/jgere.17.00006. Price JS, Cagampan J and Kellner E (2005) Assessment of peat compressibility: is there an easy way? Hydrological Processes 19, 3469-3475. Skempton AW and Petley DN (1970) Ignition loss and other properties of peats and clays from Avonmouth, Kings Lynn and Cranberry Moss. Geotechnique 20(4), 343-356.
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Smith AJE (2004) The moss flora of Britain and Ireland (2nd edition). Cambridge University Press, Cambridge.
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Troels-Smith J (1955) Karakterisering af lose jordater (Characterisation of unconsolidated sediments). Denmarks
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Geologiske Undersogelse 4(3), 1-73. von Post L (1922) Sveriges geologiska undersoknings torvinventering och nagre av dess hittills vunna resultat, sr. mosskulturfor. Tidskr 1, 1-27. Walker D and Walker PM (1961) Stratigraphic evidence of regeneration in some Irish bogs. Journal of Ecology 49, 169-185. Warburton J, Higgit D and Mills A (2003) Anatomy of a Pennine peat slide, northern England. Earth Surface Processes and Landforms 28(5), 457-473. Warburton J, Holden J and Mills AJ (2004) Hydrological controls of superficial mass movements in peat. Earth-Science Reviews 67(1-2), 139-156. Yang J and Dykes AP (2006) The liquid limit of peat and its application to the understanding of Irish blanket bog failures. Landslides 3(3), 205-216. Zhang L and O’Kelly BC 2014 The principle of effective stress and triaxial compression testing of peat. Geotechnical Engineering 167, 40-50.
List of Figures
Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (after Hammond 1979). The outlined rectangle is enlarged to show the locations of the three bogflows: (left to right) ST = Straduff Townland, SA = Slieve Anierin, SR = Slieve Rushen. Modified from Yang and Dykes (2006). Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat
30
846 847 848 849 850 851 852 853 854 855 856 857 858 859 860 861 862 863 864 865 866 867 868 869 870 871 872 873 874 875 876 877 878 879 880 881 882 883 884 885 886
basin into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD). Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c). Figure 34. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013). Figure 45. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5, etc. refer to sampling positions: A1 to A9 are shown in Fig. 45; E1/E3 and E4/E7 are located either side of the downslope extent of the source area. The materials found at each position are from, and in the same order as, this list: Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013). Figure 56. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan, obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a). Figure 67. Mohr’s Circles obtained from unconsolidated-undrained triaxial tests on peat samples from the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu Madio (2013). Figure 78. Tensile strength results obtained from the three landslides in this study and from previous studies using the same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW-08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’. Modified from Foteu Madio (2013). Figure 89. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST). Figure 910. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A) Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013). Figure 1011. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters corresponding to zones in the diagram. Source: Foteu Madio (2013). Figure 1112. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat. (A) Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs. field water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013). Figure 1213.Variation of mean thickness of basal peat depths according to specific physical properties at all three landslides.
31
887
888 889 890 891 892 893 894 895 896 897 898 899
Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (grey shading, after Hammond 1979). The outlined rectangle is enlarged, right, to show the relative locations of the three bogflows and their upland contexts: (left to right) ST = Straduff Townland, SA = Slieve Anierin, SR = Slieve Rushen. In this study area map, grey shading is land above 300 m elevation, horizontal stripes indicate water bodies and the solid black line is the international border. Modified from Yang and Dykes (2006).
32
900
901
902 903 904 905 906
Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat basin into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD).
33
Formatted: Centered
907 908 909 910 911 912 913
914 915 916
Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c).
Figure 34. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013).
34
917 918 919 920 921 922
Figure 45. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5, etc. refer to sampling positions: A1 to A9 are shown in Fig. 45; E1/E3 and E4/E7 are located either side of the downslope extent of the source area. The materials found at each position are from, and in the same order as, this list: Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013).
8.0 7.0
Shear stress (kPa)
6.0 5.0 4.0 3.0
ST ST near surface SR SA E6 replicate (Dykes 2008a) E6 (Dykes 2008a)
2.0 1.0 0.0 0.0
923 924 925 926 927 928
1.0
2.0
3.0
4.0 5.0 6.0 7.0 8.0 Normal stress (kPa)
9.0
10.0 11.0 12.0
Figure 56. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan, obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a).
35
929
930
931 932 933 934
Figure 67. Mohr’s Circles obtained from unconsolidated-undrained triaxial tests on peat samples from the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu Madio (2013).
0
1
2
3
4
Tensile strength (kPa) 5 6 7 8 9 10 11 12 13 14 15 16 17
0 0.2 0.4
Depth (m)
0.6 0.8 1 1.2 1.4 1.6 1.8
935 936 937 938 939 940
2
ST SR SA MHA-00s (Dykes 2008c) SDF-08 (Dykes and Jennings 2011) BHW-08 (Dykes and Jennings 2011) DCM-03: SE5 (Dykes and Warburton 2008)
Figure 78. Tensile strength results obtained from the three landslides in this study and from previous studies using the same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’. Modified from Foteu Madio (2013).
941 36
942 943 944 945 946 70
y = 53.03 - 19.05x R² = 0.5405
Transmission (%)
60 50 40 30 20 10 0
947 948
0 0.25 0.5 0.75 1 1.25 1.5 1.75 2 Depth below ground surface (m) Figure 89. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST).
949 950 951 952 Percentage (%) of the initial dry mass of peat
A 0
10
20
30
40
50
60
70
80
90
100
0.9 Humus fraction (<0.15 mm) Fine fibres (0.15-1mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
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Depth (m)
1.1 1.2 1.3 1.4 1.5 1.6 1.7 1.8
953
1.9
37
B 0
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20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70 80
90
100
0.9 1.0 1.1
Depth (m)
1.2 1.3 1.4 1.5 1.6 Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.7 1.8 1.9
954 C
0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70 80
90
100
0.9 1.0 1.1
Depth (m)
1.2 1.3 1.4 1.5 1.6
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.7 1.8
955 956 957
1.9
Figure 910. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A) Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013).
958 959 960 961
38
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963
964 965 966 967 968 969
Figure 1011. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters corresponding to zones in the diagram. Source: Foteu Madio (2013).
39
(A)
(B)
100 90 80 70 60 50 40 30 20 10 0
Total fibre content (%)
R2 = 0.98 R2 = 0.93 R2 = 0.86
971 972
100 90 80 70 60 50 40 30 20 10 0
ST SR SA
Total fibre content (%)
970
(C)
(D) Monocotyledon fragments (%)
100 90 80 70 60 50 40 30 20 10 0
Field water content (%)
1000 900 800 700 600 R2 = 0.66
500
R2 = 0.67
400
R2 = 0.41
300
ST SR SA
0 10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
R2 = 0.09
SR
R2 = 0.33
SA
R2 = 0.32
(F) 120
ST
R2 = 0.14
14
100
SR
R2
12
Triaxial test
SA
R2 = 0.50
10
Tensile str.
80
= 0.30
Peat strength (kPa)
Unidentified organic matter (%)
ST
0 10 20 30 40 50 60 70 80 90 100 Total fibre content (%)
(E)
60 40 20
Field vane
Direct shear
8 6 4 2
0
0
4
975 976 977 978 979 980
ST SR SA
0 10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
0 10 20 30 40 50 60 70 80 90 100 Humus fraction (%)
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973 974
R2 = 0.96 R2 = 0.96 R2 = 0.98
5 6 7 8 9 10 Degree of humification (von Post)
0
10 20 30 40 50 60 70 80 90 100
Coarse fibre fraction (%)
Figure 1112. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat. (A) Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs. field water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013).
981 982 40
Thickness of basal layer (mm)
600
ST SR
500
SA
400 300 200 100 0
983 984 985
Field description
'Raw' % light transmission
Fibre content
Macrofossil content
Quantitative fibre content
Site average
Figure 1213. VariationDifferent estimates of mean thickness of basal peat depths according to specific physical properties at all three landslides.
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Click here to download Main Text Foteu Madio and Dykes R1 FINAL.docx
v. 17 March 2018
Botanical and geotechnical characteristics of blanket peat at three Irish bogflows
Eliane S. Foteu Madio † BSc(Hons), MSc, PhD, MCIWM, Director at Envigma Ltd., Clacton-on-Sea, UK
Alan P. Dykes* BSc(Hons), PhD, FRGS, FHEA, FGS, CGeol, Associate Professor at Kingston University, Kingston upon Thames, UK ORCID: 0000-0003-0327-0498
*Corresponding author: Centre for Engineering, Environment and Society Research, Department of Civil Engineering, Kingston University, Penrhyn Road, Kingston upon Thames, KT1 2EE, UK, Tel.: +44 (0)208 417 701, Email:
[email protected]
†
Present address:
10 Crossfield Road, Clacton-on-Sea, CO15 3QT, UK, Tel.: +44 (0)1255 428787, Email:
[email protected] Address at the time of this research: School of Geography and Geology, Kingston University, Kingston upon Thames, UK
7422 words (excluding Figure captions and Tables), 13 Figures, 4 Tables
Abstract
Systematic investigations of instability and failure of peat covered hillslopes began in the late 1990s and quickly identified the potential importance of botanical controls on the properties and behaviour of the blanket peat involved in the failures. However, attempts to unravel some of these controls did not begin for several years. During 2010-12 investigations of the blanket peat at three relatively recent bogflows in northwest Ireland were done with the aim of
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establishing some form of relationship between botanical or paleoecological characteristics and standard physical and
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geotechnical properties, assuming the latter to be meaningful but recognising that this may not be the case. In-situ
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measurements and investigations at all three sites were followed by extensive laboratory characterisation of small core, block and monolith samples.
The botanical composition of the peat could not be fully determined due to the very high degree of decomposition. However, analysis of macrofossils allowed distinct depth-related patterns of several key botanical indicators to be determined. In particular the monocotyledon fragments, dominated by Eriophorum vaginatum, showed distinct and potentially useful distributions throughout the peat profiles. Overall results showed that the basal peat at one of the sites was discernibly different from the other two sites having fewer monocotyledons, fewer fibres, higher dry bulk density and higher saturated hydraulic conductivity. This approach therefore offers a potential basis for developing a means of assessing peat mass characteristics from small auger samples.
Key words
Fabric/structure of soils, Landslides, Strength & testing of materials
1. Introduction
Records of failures of peat bogs go back around 500 years to the collapse of Chat Moss near Manchester, northwest England, in 1526 (Crofton 1902). However, until the late 1990s the occasional studies of isolated examples of peatland failures were largely descriptive with estimates of geometric characteristics and occasionally reports of the living plant assemblages present at the time of failure. Systematic investigations began into the stability of blanket peat-covered slopes following significant peat landslides in Northern Ireland (Dykes and Kirk 2001; Kirk 2001) and northern England (Mills 2002; Warburton et al. 2003, 2004). The potential importance of the botanical composition as a controlling factor for the properties and geotechnical behaviour of peat was highlighted earlier by Hobbs (1986), not least because of the widespread adoption by engineers of the von Post scheme for classifying peat deposits (e.g. Landva and Pheeney 1980; Carlsten 1993) which requires the estimation of relative frequencies of fibres and wood/shrub fragments as well as the degree of decomposition of the plant matter (i.e. the humification). The need for research into botanical controls on peat properties was further emphasised with respect to blanket peat instability by Kirk (2001), Dykes (2008a) and O’Kelly (2017) in response to findings from their investigations of physical and
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geotechnical properties thus far. Indeed, O’Kelly (2017) highlighted the scarcity of published works on the topic and the contradictory findings from the few such studies. The present research (Foteu Madio et al. 2012; Foteu Madio 2013) arose directly from this dearth of previous studies.
The aim of this paper is to examine whether physical and geotechnical properties of Irish blanket peat can be causally associated with measurable botanical characteristics. It does so by presenting and analysing data representing the properties and characteristics of the peat at the sites of three significant bogflows in northwest Ireland, obtained from a combination of field and laboratory investigations. The importance of this study is to provide the basis for more efficient and reliable methods for assessing the stability of peat with respect to planned interventions such as construction of access roads for windfarms or other purposes.
2. Blanket Bog Failures in Ireland
The topic of peat mass movements (as distinct from geotechnical engineering of peat) emerged from an esoteric scientific by-way to become a mainstream theme in engineering geology and geomorphology following several major events in late 2003. On 19 September 2003, two entirely independent extreme rainfall events in Co. Mayo, Ireland, and South Shetland, Scotland, triggered multiple failures of peatcovered hillslopes (Dykes and Warburton 2007a, 2008a,b). More significantly for civil engineering, four weeks later the 450,000 m3 Derrybrien Windfarm landslide occurred (Lindsay and Bragg 2005). By that time it had already become clear that the Irish blanket bogs were failing in several slightly different ways, giving rise to morphologically distinctive types of failures (Dykes and Warburton 2007b). Most involve shearing of mineral soil beneath the peat (‘peaty-debris slides’), shearing at the peat-mineral interface (‘peat slides’), or shearing entirely within the basal peat (‘bog slides’). ‘Peat flows’, a term reserved for failures resulting primarily from head-loading, appear to be effectively bearing capacity failures with small areas of shear surface within the basal peat having been observed in the Derrybrien and Ballincollig Hill landslides (Long 2005; Dykes and Jennings 2011).
All of the available evidence relating to ‘bog bursts’ and ‘bogflows’ indicate that these failures involved some sort of in-situ liquefaction of the lower or basal peat, with this (semi-)liquid peat slurry then breaking 3
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out from beneath a stronger confining acrotelm layer (or from cut faces through the margins of raised bogs) (Dykes and Warburton 2007b). The precise mechanisms of strength loss are unknown. One hypothesis, for example, is that the basal peat fails like ‘quick clay’ with an initial small shear failure creating a disturbance that propagates rapidly. As such a bogflow may simply be a bog slide involving weaker and wetter peat – but there is a clear distinction because these two types of failure have different peat depth vs. gradient characteristics (A P Dykes, unpublished data). A parallel hypothesis is that in some of these failures the lower layer of the peat deposit was always a fluid body, for example if peat grew over a large pond so as to eventually entirely bury it.
In almost all cases of failures of (blanket) peat-covered slopes in Ireland, landslide morphologies and runout characteristics display clear evidence of relatively rapid development of failure associated with very high volumes of rainwater, with eyewitness accounts of some recent events (e.g. the Derrybrien peat flow in 2003, the Croaghan peat slide in 2014) corroborating these interpretations. Warburton et al. (2004) discussed the various hydrological processes giving rise to, or controlling, such failures. It is likely that the peaty-debris slides are triggered by pore pressure effects, in part due to subsurface storm runoff being confined beneath a saturated and effectively impermeable peat cover. Peat slides (interface failures) probably occur for the same reason. Failure within the peat is a more complex issue because of the dual influences of effectively impermeable and normally saturated but weak catotelm peat material and the internal structure of the peat mass (sensu ‘rock mass’ considerations) that may experience high turbulent flows and even artesian conditions within networks of natural peat pipes and (relict) desiccation cracks (Dykes and Warburton 2007a, 2008a; Gilman and Newson 1980; Holden and Burt 2003). The critical factor here is that rates of deformation and then movement are likely to greatly exceed the saturated hydraulic conductivity of the intact peat mass through which any shear surface may develop. Consequently, the focus of our research is on the undrained strength characteristics of basal peat.
2.1 Study sites We identified three locally significant bogflows (sensu Dykes and Warburton 2007b) for this study, located within the same region of northwest Ireland: Straduff Townland (hereafter referred to as ‘ST’), Slieve Anierin (‘SA’) and Slieve Rushen (‘SR’) (Fig. 1). Site and landslide characteristics are summarised in Table 4
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1 and illustrated in Fig. 2. All were relatively recent, thus limiting the degree of post-failure degradation, and
119 1
two sites (though not the same landslide at one of these sites) had been investigated previously which
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provided a cross-check for the peat characterisation results from this study. Furthermore, although the peat at all three sites was generally very similar, one site (Slieve Anierin, below) was noted by Yang and Dykes (2006) to be slightly but nevertheless distinctly different from others including a bogflow at Straduff Townland adjacent to the one used for this study. We anticipated that the results of this new research would also show this.
Table 1. Summary of site details and characteristics of the study bogflows. Bogflow County Latitude Longitude
Elevation Geology Geomorphological Length Slope Deptha Volume (m) (Carboniferous) Context (m) (°) (m) (m)
ST
Sligo 54°7.2’N 8°12.9’W
405
Lackagh Sandstone
SR
Cavan 54°8.9’N 7°38.5’W
390
Glenade Sandstone
SA
Leitrim 54°6.3’N 7°58.7’W
440
Lackagh Sandstone
Escarpment failure
200
Basin slope failure 175 Escarpment failure
190
5.5 (top) 3 (mid) 6 (lower)
2.5
35,000
5.5
2.0
20,000
4
2.2
22,000
Note a
Indicative average depth of in-situ peat immediately adjacent to the landslide source area
< FIGURE 1 > Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (after Hammond 1979). The outlined rectangle is enlarged to show the locations of the three bogflows: (left to right) ST = Straduff Townland, SA = Slieve Anierin, SR = Slieve Rushen. Modified from Yang and Dykes (2006).
< FIGURE 2 > Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat basin into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD). 5
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ST, the Straduff Townland landslide, occurred overnight or early morning on 14 August 2008 during very heavy rain. The dominant morphology is that of a bogflow. However, a basal shear surface around 20 mm above the base of the peat was visible in two small parts of the source area (Dykes 2009; Dykes and Jennings 2011). Although the latter observation corresponds with a ‘bogslide’ (Dykes and Warburton 2007b), we will refer to this failure as a bogflow. It involved an area of intact blanket peat between the source areas of bogflows dating from 1945 and 1991, leaving narrow strips of minimally displaced peat separating the failures. The physical characteristics of the peat at the 1991 bogflow, just a few metres from the margin of the later failure, were determined by Yang and Dykes (2006). SA (the Slieve Anierin bogflow) is thought to have occurred during 1998, based on its visible condition when first seen from a light aircraft in November 1998 and a conversation with a local resident in 2011. It was described, and the physical characteristics of the peat reported, by Yang and Dykes (2006). The date of SR (the Slieve Rushen bogflow) is uncertain, but the condition of the failure when first inspected in September 2004 was consistent with an age of only a few years, i.e. it most likely occurred during the 1990s (Dykes 2008b).
3. Methods
The three bogflows were investigated using the same general methodology as previous studies of peat landslides (e.g. Yang and Dykes 2006). All had previously been surveyed in detail by Dykes (2008b, 2009). The focus for this study was to obtain samples for laboratory testing from a carefully prepared and fully described vertical profile through the full depth of undisturbed in situ peat. Most peat failures leave irregular sub-vertical peat profiles with varying amounts of peat debris covering the lower layers, around several parts of the source area margins. A single study profile (hereafter referred to as the ‘study profile’ or ‘Sampling Point’) was selected at each landslide according to the feasibility of creating a clean vertical profile through the full thickness of the peat, i.e. involving the minimum manual excavation of loose peat debris, but ensuring the in-situ peat was undisturbed and not within a few metres of any tension cracks. Safety was ensured by having wide open access to the prepared profile from within the evacuated source area of each landslide, with one person maintaining active watch over the cut face while the other person worked there. 6
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3.1 Field investigations Around each bogflow source area, stratigraphic and topographic surveys were carried out in order to estimate the morphology of the peat deposit and the variability of the peat within it prior to failure. The stratigraphy and maximum depth of the in situ peat was determined on a coarse but regular grid using a 20 mm diameter gouge auger. Maximum peat depths were measured at additional locations by probing with a metal rod. Peat surface elevations were then surveyed at all the stratigraphy and peat depth measurement points by levelling, with the mineral surface elevations being measured within the landslide source areas and calculated for the peat-covered areas around the source areas from the measured peat depths.
Prior to sampling, a detailed description of the full thickness of the peat at each Sampling Point was recorded according to the von Post (von Post, 1922, as presented by Landva and Pheeney 1980, and Hobbs 1986) and Troels-Smith (Troels-Smith 1955) peat classification schemes. Several sets of samples were obtained from each landslide. Most of the physical/geotechnical samples were obtained from the basal peat at each Sampling Point. Samples were also obtained from the surface and middle peat at the Sampling Point at bogflow ST to provide some indication of depth variations, assuming it to be representative of all three sites. In addition, a Geonor H-60 field shear vane was used to measure the ‘field vane strength’ (FVS) of the insitu basal peat ~1 m behind each Sampling Point. For palaeoecological (or simply ‘botanical’) analyses, monolith samples were extracted that included most of the thickness of the peat profile at each Sampling Point (missing the uppermost part at SR and SA). In addition, 10 mm cubes of peat were carefully cut from the auger samples from SR at approximately 200 mm depth intervals (Fig. 5 in Section 4 shows results from this component of the work). Table 2 summarises the samples collected.
7
200 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 201 24 202 25 203 26 27 204 28 29 205 30 31 206 32 33 34 207 35 36 208 37 38 209 39 40 210 41 42 43 211 44 45 212 46 47 213 48 49 214 50 51 215 52 53 54 216 55 56 217 57 58 218 59 60 219 61 62 63 64 65
Table 2. Samples extracted from the study bogflows. Landslide / Physical properties – Tensile strength – position in small cores 50 mm blocks 120×120×70 peat profile dia. × 51 mm length mm ST see right ST basea SA 300-1030 mm depth SA base a SR 100-830 mm depth SR base b
Triaxial – Shear strength (direct 38 mm dia. shear) – blocks cores 120×120×70 mm
6 at ~650 mm depth 3 at 10-80 mm depth 6 at ~1150 mm depth 3 at 890-960 mm depth
--
Monoliths for botanical data 730×100×100 mm
3 at 10-80 mm depth 1 at 400-1130 mm 3 at 890-960 mm depth depth
9
6
6
12
2
--
--
--
--
1
9
6
6
12
2
--
--
--
--
1
9
6
6
12
2
Notes a
1600-1700 mm depth below the surface of the peat, 970-1700 mm depth for the lower monoliths
b
1900-2000 mm depth, 1270-2000 mm depth for the lower monoliths
3.2 Laboratory testing Some physical properties of peat can give a rough indication of the state or condition of the peat (Hobbs, 1986). Therefore, standard methods were used to determine the water content and bulk density (oven-drying for 24 h at 105°C: O’Kelly 2017), loss on ignition (550°C for 3h: Skempton and Petley 1970; Andrejko et al. 1983; Jarrett 1983; Hobbs 1986) and saturated hydraulic conductivity (‘constant head’ method) to provide reference details for correlation with the results of the botanical and geotechnical analyses. There has been some debate in recent years regarding the appropriate drying temperature for water content determination, including evidence of the possibility of charring of the peat at temperatures higher than 80-90°C (O’Kelly 2014). Further, O’Kelly (2014) found experimentally that the possible additional loss of mass due to charring is negligible compared with the mass of any retained water due to incomplete drying, particularly intracellular water within peat fibres that may constitute a significant proportions of the peat mass (Foteu Madio 2013), and so recommended following the standard specification for mineral soils of 105°C as used by many previous workers including Skempton and Petley (1970) and Hobbs (1986). We adopted the latter approach for the demonstrated reasons of standardisation and comparability of results. 8
220 221 1
For the constant head method we used a laboratory permeameter arrangement as described by, for example,
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Klute and Dirksen (1986) or Head (1994). Undisturbed core samples collected in thin-walled tubes 50 mm long (‘L’) × 50.5 mm diameter were trimmed to size, saturated in tap water and mounted vertically to form a permeameter maintaining a constant head of 0.15 m of water on the top of the sample. Water that passed through the sample was collected underneath and measured. The constant head saturated hydraulic conductivity was calculated according to Darcy’s Law from: k = VL / (tA.ΔH) where k = permeability = saturated hydraulic conductivity (m s–1) V = volume of water collected (m3) t = time (s) of water collection A = cross-sectional area of peat sample (2.00×10–3 m2) L = length of peat sample (0.050 m) ΔH = head difference across peat sample length (0.200 m)
The proportion of intracellular and interparticle water depends upon the structure and morphology of the various plants present and on the degree of humification of peat (Hobbs 1986). Microfossils, including pollen grains, may not represent the original in situ vegetation because they are small enough to be transported by the wind, possibly over long distances. Therefore we investigated the fibres, macrofossil content and the degree of humification of the peat. The latter influences the water holding capacity, pore sizes and fibre quantities and properties, all of which could influence the peat strength. The fibres and macrofossils are likely to directly affect the strength and other geotechnical properties.
3.2.1 Humification Humification was quantitatively determined in the laboratory followed a modified version of the Bahnson colorimetric method (Aaby and Tauber 1974; Blackford and Chambers 1993; Chambers et al. 1997). Subsamples taken contiguously at every 10 mm from the monoliths were tested. The measurements were obtained using a Hatch 2500 spectrometer set up at 540 nm. Results are expressed as ‘raw’ percentages of
9
248
light transmission through the diluted peat solution. The more light passes through the peat solution, the less
249 1
humified the sample.
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3.2.2 Fibres The fibre content (F) is an important characteristic that influences peat stability (Long and Jennings, 2006) as it affects the peat structure and its strength properties. To explore this effect, we firstly re-defined the different fractions as follows: (i) a ‘fine fibre’ (Fm) is a fragment or piece of plant tissue between 0.15 and 1.00 mm in any dimension including length; and (ii) a ‘coarse fibre’ (Rm) is a fragment or piece of plant tissue > 1 mm in any dimension. In line with the ASTM’s (2008) standard for determining the fibre content of peat, the ‘total fibre fraction’ (Ft) is been defined as all fibres ≥ 0.15 mm in any dimension. The humus fraction (Fh) is defined as all particles < 0.15 mm in any dimension. We recognise that it is difficult to determine a specific shape of some fibres and that, depending on the orientation of the fibre, any dimension of a fibre or particle of a particular shape (e.g. elongated fibres) can prevent it passing through a hole in the sieve, so further refinements to this methodology are likely to be needed in the future.
The Fm and Rm fibre fractions were estimated in the field based on the von Post system as presented by Hobbs (1986, p.79): Fine fibres (Fm) are ‘fibres and stems smaller than 1 mm in diameter or width’ and coarse fibres (Rm) are ‘fibres, stems, and rootlets greater than 1 mm in diameter or width’. To both of these definitions we added ‘or any plant particle’ and took the size boundary as ‘< or > 1 mm in all directions’. The von Post scheme uses a four point scheme from 0 ‘nil’ to 3 ‘high content’ but without a microscope it is difficult to be certain that there are no fragments of fibre present. Consequently we removed ‘0’ and assessed the quantity according to a five point scale: 1 = very low content (VL), 2 = low content (L), 3 = medium content (M), 4 = high content (H) and 5 = very high content (VH). All of the other fractions defined above were determined in the laboratory and recorded using a similar 5-point scheme: 1 = fibre content ≤ 40% 2 = fibre content > 40 and ≤ 60% 3 = fibre content > 60 and ≤ 80% 4 = fibre content > 80 and ≤ 95% 5 = fibre content > 95% 10
277
Differentiating peat in this way enabled field estimates to be corrected with measurements obtained from
278 1
laboratory tests, and this simple 5-point scale allowed cluster analyses of the results to be carried out in a
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consistent way.
For the laboratory determinations, duplicate subsamples of known masses were taken every 70 mm from along the lowest monolith sample from each site. These were analysed differently in order to separate the peat into different fractions, the initial part of the procedure following ASTM (2008) but with a much smaller initial sample mass. Thus the fibre contents of the lowest 0.7 m of the peat profile at each landslide’s Sampling Point were fully quantified. The first subsample was soaked in a dispersing agent (5% sodium hexametaphosphate) for approximately 15 hours and then the peat was gently washed through a 0.15 mm mesh size sieve using tap water. The fibrous material retained on the sieve was washed through a further 1 mm sieve and the fine fraction that passed through was collected. The fibres retained on the 1 mm sieve comprised the coarse fraction. Both fractions were oven-dried at 105°C until constant masses were achieved. The masses of fine and coarse fibres were combined to obtain the total mass of fibres. The mass of humus was obtained from the difference between the mass of total fibres and the initial dry mass of peat determined from the second subsample. The second subsample was dried at 105ºC for 24 h and the mass ratio of dry to wet peat determined. The duplicate peat samples had slightly different masses and assuming that their respective mass ratios of dry to ‘field wet’ peat were equal, the corresponding initial mass of the sample used for fibre content testing was established. The fibre (Ff)/humus (Fh) fractions (without any mineral matter) were then expressed as percentages of the initial dry mass (Ms) as follows: F f / h = (M f / h / M s) × 100 where Ff/h is the fibre/humus fraction (%), Mf/h is the mass (g) of the fibre/humus fraction after drying at 105°C to constant mass then subtracting the mass of ash, and Ms is the mass (g) of the initial peat sample after drying at 105°C to constant mass less the mass of ash.
3.2.3 Macrofossils The heterogeneity of peat is due to the variability of factors and environmental gradients that influence its initiation and development (Moore, 1984; Charman, 2002). The original plant composition of peat influences its structure and is assumed to affect its geotechnical properties. We used macrofossil analysis to 11
306
assess these botanical factors. 10 mm cubes of peat were obtained from the along the length of each monolith
307 1
sample, with 40–80 mm separation except within the basal peat where the cubic subsamples were
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contiguous. Analysis was undertaken using the ‘Quadrat and Leaf Count Macrofossil Analysis technique’ (QLCMA) developed at the Southampton Palaeoecology Laboratory (Barber et al. 1994). The method estimates the percentage coverage of all macrofossil types with the aid of a 10 × 10 grid graticule in the eyepiece of a stereomicroscope. Monocotyledon epidermis tissues and Sphagnum branch leaves were examined further at a magnification of ×400 under transmitted light. Daniels and Eddy (1990) (for Sphagnum), Smith (2004) (for other bryophytes), Grosse-Brauckmann (1972) and Katz et al. (1977) (for vascular plants) were used to identify the remains.
The additional small cubic samples obtained from SR were further investigated using the method developed by Walker and Walker (1961), in which on a scale of 0 to 5, 0 indicates absence and 5 indicates that the sample consisted largely of a particular macrofossil. This was done to check that peat at the Sampling Point was representative of the entire blanket bog.
3.2.4 Shear strength The mechanism of failure of in-situ peat in natural landslides is uncertain and indeed there may be different mechanisms operating in different contexts. Examples of these are outlined in Section 2. Our tests focused on undrained shear strength because of the documented rapid development of failures compared with the measured very low permeability of Irish catotelm peat (e.g. 10–6 to 10–9 m s–1: see Section 4.2.1). We used a direct shear apparatus with a 100 mm × 100 mm shearbox to try to obtain reproducible values of shear strength using normal stresses representing in-situ conditions, i.e. typically less than 5 kPa (after Dykes 2008a). Samples were sheared at normal stresses of 0.7, 1.2, 1.7, 2.2, 3.2, 4.2 and 5.6 kPa using the method outlined by Dykes (2008a), i.e. no pre-consolidation, but with a slightly higher shear rate of 1 mm min–1 (2×10–5 m s–1) to represent moderate failure (IUGS, 1995) with the associated likelihood of undrained shearing effects.
The triaxial tests were intended to give an indication of the undrained shear strength and associated stressstrain behaviour of the peat by means of rapid unconsolidated-undrained tests on standard 38 mm diameter × 12
335
76 mm high samples (carried out according to Head (1994)) at a range of cell pressures at the lowest end of
336 1
what was possible with the available equipment, i.e. 50, 100 and 200 kPa. To minimise membrane effects we
2 3 337
used thinner membranes, samples were allowed to saturate before the axial load was applied at 1 mm min–1
4 5 338
6 7 339 8 9 340 10 11 341 12 13 14 342 15 16 343 17 18 344 19 20 345 21 22 23 346 24 25 347 26 27 348 28 29 349 30 31 32 350 33 34 351 35 36 352 37 38 353 39 40 354 41 42 43 355 44 45 356 46 47 48 357 49 50 358 51 52 359 53 54 360 55 56 361 57 58 362 59 60 363 61 62 63 64 65
as for the direct shear tests. After each test, the sample was visually inspected to assess the failure mechanism or any other deformation. The bi-linear correction of the deviator stress due to membrane stiffness was not applied to the results because although the effect may be significant, (i) there is no consensus on appropriate corrections given complex peat-membrane interactions, and (ii) this was primarily a comparative study that was not necessarily expected to determine the exact value of the shear strength of peat.
3.2.5 Tensile strength The tensile strength of block samples of undisturbed peat was measured using the equipment (Fig. 3C) and procedure described by Dykes (2008c). This involved applying a tensile load, in 100 g increments, to half of the cross-sectional area of each 100 × 100 mm test sample by means of five 10 mm wide steel fingers (Fig. 3A), the tensile resistance being provided by the four 12.5 mm wide strips of peat between the fingers (Fig. 3B). Tensile stress and strain were recorded 30 s after the application of each load increment until the sample failed. Although results obtained using this method have been found to be reproducible and consistent, two key limitations are recognised: (i) the apparatus does not allow a vertical load to be placed on the sample to replicate the condition of the basal peat in-situ; and (ii) significant sample disturbance may occur during installation due to large fibres or woody fragments (Dykes 2008c).
< FIGURE 3 > Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c).
13
364 365 1 2 3 366 4 5 367 6 7 368 8 9 369 10 11 370 12 13 14 371 15 16 372 17 18 373 19 20 374 21 22 23 375 24 25 376 26 27 377 28 29 378 30 31 32 379 33 34 380 35 36 381 37 38 382 39 40 383 41 42 384 43 44 45 385 46 47 386 48 49 387 50 51 388 52 53 389 54 55 390 56 57 391 58 59 392 60 61 62 63 64 65
4. Results
4.1 Field descriptions of the peat The peat at the three landslides showed remarkably little variability in terms of structure and macrofossil content. Four major stratigraphic units were identified at each site. The first unit (starting at the top), including the living roots near the surface, comprised slightly humified peat, with each unit below being progressively more humified and the fourth unit at the base having highly humified and/or greasy peat, sometimes with bitumen or sludge like patches (Table 3; e.g. Fig. 4). The identifiable plant material in the peat was predominantly monocotyledon (‘monocot’) remains (‘Turfa herbacea’ in the Troels-Smith scheme) including undifferentiated roots, stems and leaves (Fig. 5). This general lack of variation between (Table 3) and within (Fig. 5) sites allowed us to consider one Sampling Point as being broadly representative of each landslide site.
< FIGURE 4 > Figure 4. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013).
< FIGURE 5 > Figure 5. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5, etc. refer to sampling positions: A1 to A9 are shown in Fig. 5; E1/E3 and E4/E7 are located either side of the downslope extent of the source area. The materials found at each position are from, and in the same order as, this list: Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013).
14
393
4.2 Physical and mechanical properties of the peat
394 1 2 3 395 4 5 396 6 7 397 8 9 398 10 11 399 12 13 14 400 15 16 401 17 18 402 19 20 403 21 22 23 404 24 25 405 26 27 406 28 29 407 30 31 32 408 33 34 409 35 36 410 37 38 411 39 40 412 41 42 43 413 44 45 414 46 47 415 48 49 416 50 51 52 417 53 54 418 55 56 419 57 58 420 59 60 61 421 62 63 64 65
4.2.1 Geotechnical characteristics The basic physical properties of the peat at the three landslides are summarised in Table 4. These are broadly consistent with previous results obtained from Straduff Townland (the 1997 bogflow adjacent to ST) and SA by Yang and Dykes (2006). Uncorrected field shear vane readings from depths between 1.25 and 2.00 m were between 6.6 and 14.0 kPa at all sites and there were insufficient results from which to identify any patterns in the data. No corrections were applied because this was intended as a comparative study and the shear vane is known to be inappropriate for the determination of the undrained strength of peat due to the effects of fibres, although it can be used to identify patterns of peat strength variation with depth.
Results from the experimental low-stress direct shear tests (without consolidation prior to shearing) are shown in Fig. 6. These are consistent with results obtained from basal peat at another landslide in northwestern Ireland (identified as ‘E6’ by Kirk (2001): Dykes 2008a). The surface peat at ST clearly demonstrates a higher strength due to the greater density, and probably strength, of less humified fibres. Samples inevitably consolidate under even these small loads as shearing takes place. Straight line approximations in the normal stress range 2-5 kPa would all give cohesion intercepts of 1-4 kPa (Fig. 6). If the peat was overconsolidated by up to 10-15 kPa as seems to be the general case (O’Kelly 2017), such low shear stress values within this range of applied normal loads should not be expected.
Results from the unconsolidated-undrained triaxial tests similarly demonstrate the inherently low shear strength of the basal peat with all three sites in the range 1.5-2.5 kPa (Fig. 7). Slight variations in the diameters of the Mohr’s circles arise from the heterogeneity of the peat mass, as also observed in raised bog peat by Hanrahan (1954), but may also result from gas in the peat causing variations in pore water pressures within the samples. Given that the assumed effect of pore pressures in undrained shear tests is to reduce the friction towards zero because the water is incompressible, then the presence of compressible gas within some pore spaces could allow some (additional) frictional resistance to arise during testing. Hanrahan (1954) found that the gas content of Irish Sphagnum peat may be considerably in excess of 5% of the volume and that significant volumes of gases such as sulphuretted and phosphorated hydrogen (phosphine), as well as 15
422
methane, could be emitted during construction involving the compression of peat. Therefore the possibility
423 1
of gas affecting both permeability and pore pressures must be allowed for when interpreting results.
2 3 424 4 5 425
6 7 426 8 9 427 10 11 428 12 13 14 429 15 16 430 17 18 431 19 20 432 21 22 23 433 24 25 434 26 27 435 28 29 436 30 31 32 437 33 34 438 35 36 439 37 38 440 39 40 441 41 42 43 442 44 45 443 46 47 444 48 49 445 50 51 52 446 53 54 447 55 56 448 57 58 449 59 60 61 450 62 63 64 65
Fig. 8 shows the tensile strengths obtained from this and previous studies using the same methodology (Dykes 2008c). The tensile strengths of the basal peat at the three landslides in this study are all less than 3 kPa except where locally reinforced by matted woody fragments. With the exception of two outliers, which arose from the respective samples containing significant fragments of decomposing roots or woody stems, there is an apparent trend of reducing tensile strength with depth. Although this trend arises from combined results from several locations in Ireland, the similarities of all other measured peat properties between all of these sites (Dykes 2008c; Dykes and Warburton 2008a; Dykes and Jennings 2011) means that this general trend is probably real. At individual sites it is possible that such a trend of decreasing tensile strength with depth may not always be found, although there are insufficient relevant data to be able to comment further.
Helenelund (1967) suggested that the fibre contents, types and orientations – which depend on the morphology and the mode of growth of the original plant assemblage that formed the peat – may have major influences on the tensile strength. The macrofossil analyses of peats from our study sites revealed remains of sedges, the degree of humification of which increase with depth. In such monocotyledon peat, fibres are the remains of vascular bundles formed from the root systems that grow perpendicularly to the ground surface. The resulting tensile strength will therefore be related to the resisting force produced by the fibres, the frequency of which decreases with depth and is inversely proportional to the degree of humification. The tensile strength results obtained by Helenelund (1967) from Sphagnum bog peat, which has very few fibres, are comparable with the lowest of our results, showing that the monocotyledon peats at our sites generally have higher tensile strengths than Sphagnum bog peat. Due to the effect of compression during the accumulation of the peats, some fibres that were originally distributed vertically through the peat become squashed progressively into a horizontal alignment as pressure increases. The degree of inclination of these fibres toward the horizontal plane should therefore also increase with depth. The tensile strength values presented in this study were measured in a horizontal plane, intended to represent the effect of the peat mass pulling apart above a basal (shear?) failure zone. The effect of fibre orientation should be to increase the tensile strength with depth since horizontal breaking up of a failing peat mass is resisted by sometimes 16
451
significant lengths of fibres adhering to amorphous colloidal matrix material. However, the role of living and
452 1
minimally decomposed roots within the near-surface acrotelm layer combined with the very high degree of
2 3 453 4 5 454 6 7 455 8 9 456 10 11 457 12 13 458 14 15 459 16 17 18 460 19 20 461 21 22 462 23 24 463 25 26 464 27 28 465 29 30 466 31 32 33 467 34 35 468 36 37 469 38 39 470 40 41 471 42 43 472 44 45 473 46 47 474 48 49 475 50 51 52 476 53 54 477 55 56 478 57 58 479 59 60 61 480 62 63 64 65
humification below the acrotelm appears to entirely override the fibre orientation effect.
< FIGURE 6 > Figure 6. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan, obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a).
< FIGURE 7 > Figure 7. Mohr’s Circles (total stresses) obtained from unconsolidated-undrained triaxial tests on peat samples from the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu Madio (2013).
< FIGURE 8 > Figure 8. Tensile strength results obtained from the three landslides in this study and from previous studies using the same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’. Modified from Foteu Madio (2013).
4.2.2 Humification and fibres The results of the quantitative determination of humification, recorded as the ‘raw’ percentage of light transmission through the peat, showed no significant differences between the mean values for the three sites. However, only the results from ST showed a clear reduction in light transmission (i.e. increase in degree of humification) with depth (Fig. 9). 17
481 482 1 2
483 3 4 484 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 485 48 486 49 50 487 51 52 488 53 54 489 55 56 57 490 58 59 491 60 61 62 63 64 65
Table 3. Summary description of the peat at each landslide Sampling Point (Foteu Madio 2013). The four major stratigraphic units are separated by the solid lines of the Table.
Depth (m) 0.00-0.40 0.40-0.78 0.78-1.22 1.22-1.60 1.60-1.80 >1.80
Peat profile description at ST Light brown fibrous peat, slightly humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength. Black and moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength. Light brown with dark patches, very weak and moderately humified peat. Monocotyledon fine fibre limited. Low horizontal tensile strength. Brown, moderately to strongly humified peat. Monocotyledon fine fibre present. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Rare and very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart. Peat profile description at SR1
Depth (m) 0.00-0.15 0.15-0.36
Brown fibrous peat with moderately humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength. Brown, less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength.
0.36-0.58
Dark brown humified peat with monocotyledon fragments. Low horizontal tensile strength.
0.58-0.88
Dark brown decomposing peat with monocotyledon fragments. Low horizontal tensile strength.
>1.64
Dark grey, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1 on the Munsell soil colour chart.
Depth (m)
Peat profile description at SA
0.88-1.58 1.58-1.64
0.00-0.76 0.76-1.56 1.56-1.76 1.76-1.78 >1.78
Dark fibrous peat, slightly humified, mainly monocotyledon fine fibres, low amorphous material and moderate horizontal tensile strength. Light brown less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat, moderate amorphous material and moderate horizontal tensile strength. Black humified peat with monocotyledon fragments. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart.
Note 1
Recorded in July 2010 prior to the moorland fire.
18
492
Table 4. Summary of physical properties of peat at the three landslides, including previous data from Yang and Dykes
493 1
(2006)*.
2 3 4 5 6 7 8 9 10 11 12 494 13 14 495 15 496 16 17 497 18 19 498 20 499 21 22 500 23 501 24 25 502 26 503 27 28 504 29 505 30 31 32 506 33 34 507 35 36 508 37 38 509 39 40 510 41 42 43 511 44 45 512 46 47 513 48 49 514 50 51 52 515 53 54 516 55 56 517 57 58 518 59 60 519 61 62 63 64 65
ST SR SA
Water content a,b (% mass fraction)
Loss on Ignition c (%)
Saturated bulk density e (Mg m–3)
Dry bulk density e Saturated (Mg m–3) hydraulic conductivity h,i (m s–1)
700-900 *620-860 600-700 600-700 *600-740
94.5-95.6 *97.8-98.8 94.6-97.2 d 95.0 *97.7-98.5
1.00 f *1.06 1.00 1.00 *1.05
0.10-0.20 *0.13 0.10-0.20 0.20 g *0.15
10–9 to 10–8 * < 10–11 10–9 to 10–6 10–8 to 10–6 * < 10–11
Notes a
There was negligible difference between field-wet and saturated water contents at all sites
b
Indicative ranges of mean values from 256-319 samples per site
c
Indicative ranges of mean values from 123-196 samples per site
d
The basal peat at Slieve Rushen was noticeably higher in organic matter than any other sampled peat
e
Mean values from 20-26 samples per site
f
The basal peat at Straduff Townland was noticeably higher (~1.10 Mg m–3) than any other sampled peat
g
The peat at Slieve Anierin had higher dry bulk densities throughout its depth
h
Indicative ranges of mean values from 19-26 samples per site, obtained using a ‘constant head’ method
i
Results obtained using a ‘falling head’ method were consistently 10 2-103 m s–1 higher than the respective ‘constant
head’ values
The mean ‘total fibre fraction’ (Ft) of the lowest 0.7 m of the peat profile at each landslide Sampling Point, based on 70 depth-consecutive measurements per site, was 68% at ST, 71% at SR and 56% at SA. As Fig. 10 shows, the latter appears to indicate a small but consistent difference from the other two, having slightly fewer coarse fibres throughout the sampled depth range. At all three sites there is a general trend of reducing coarse fibre content with depth but the fine fibre content seems to increase slightly towards the base of SR.
< FIGURE 9 > Figure 9. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST).
< FIGURE 10 > Figure 10. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A) Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013).
19
520 521 1 2 3 522 4 5 523 6 7 524 8 9 525 10 11 526 12 13 14 527 15 16 528 17 18 529 19 20 530 21 22 531 23 24 532 25 26 533 27 28 29 534 30 31 535 32 33 536 34 35 537 36 37 538 38 39 40 539 41 42 540 43 44 541 45 46 542 47 48 49 543 50 51 544 52 53 545 54 55 546 56 57 58 547 59 60 61 62 63 64 65
4.3 Peat stratigraphy according to macrofossil results The blanket bog at the Sampling Point at each landslide mostly comprised the remains of monocotyledon plants, particularly E. vaginatum (Fig. 11). Monocotyledon contents were lowest within the basal peat zones (as defined by cluster analysis) and, at ST, immediately above the basal zone.
< FIGURE 11 > Figure 11. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters corresponding to zones in the diagram. Source: Foteu Madio (2013).
4.4 Comparing botanical and geotechnical characteristics The results were examined in order to identify any statistical associations (using Pearson’s ‘r’ correlation coefficient) between physical/geotechnical parameters, and then between geotechnical characteristics and botanical results, that may have physical explanations potentially exploitable for predictive purposes. In this study, only significant (p < 0.05) correlations with |r| > 0.7 at all three landslides were interpreted as possibly indicating a causal relationship because the study was based on a single monolith per study site. Furthermore, the full depth of the peat at each site was not analysed for most of the parameters investigated. The only significant associations with |r| > 0.7 that were found between physical/geotechnical parameters at all three sites were between: (i) the humus fraction, Fh, and the total fibre content, Ft (Fig. 12A); (ii) the total fibre content, Ft, and the coarse fibre fraction, Rm (Fig. 12B); (iii) the humus fraction, Fh, and the coarse fibre fraction, Rm; and (iv) the coarse fibre fraction, Rm – and therefore also the total fibre content and the humus fraction – and the field water content (Fig. 12C).
20
548
Figs. 12D and 12E show the only consistently high correlations (p < 0.05) between macrofossil data and
549 1
physical/geotechnical properties of peat, i.e. between: (i) the total fibre content and the proportion of
2 3 550 4 5 551 6 7 552 8 9 553 10 11 554 12 13 14 555 15 16 556 17 18 557 19 20 558 21 22 23 559 24 25 560 26 27 561 28 29 562 30 31 32 563 33 34 564 35 36 565 37 38 566 39 40 567 41 42 43 568 44 45 569 46 47 570 48 49 571 50 51 52 572 53 54 573 55 56 574 57 58 575 59 60 61 576 62 63 64 65
monocot fragments; and (ii) the von Post degree of humification and the percentage of unidentified organic matter. This may arise from the QLCMA method used for macrofossil analyses probably being more appropriate for Sphagnum peat with small leaves that can be easily counted, compared with monocotyledon peat with larger original plant fragments. The general lack of strong or consistent associations correlations between the physical/geotechnical and botanical parameters at the three landslides suggests that these physical properties cannot be used as indicators of peat mass structure and, thus, of potential peat instability. However, the method used to quantify the fibre contents (Section 3.2.2, above) may be useful for investigating relationships between the structural properties of failed Irish blanket peats in order to classify peat for stability assessments.
The macrofossil analyses at the three landslides showed that the original plant assemblage was predominantly monocotyledons, especially Eriophorum vaginatum. Therefore, the undrained strengths obtained at the three landslides were plotted against the other properties (e.g. coarse fibre content in Fig. 12F) in order to investigate any possible relationship that may exist. The statistical analyses revealed no significant correlation coefficients (p < 0.05).
Fig. 13 shows the thickness of a weak basal layer at each site identified by cluster analyses of the results (e.g. Fig. 11). If all three landslides failed in a similar manner (i.e. by initial basal shearing), then it appears that field observations of shear surfaces within a few tens of mm above the peat-mineral interface can be explained in terms of formation of a failure zone (a) within the weakest layer of the peat profile, and (b) at the lowest elevation within that weakest layer giving a continuous plane above the level of any large stones or woody remnants that would resist shearing within the basal peat. The mean thickness of this layer based on cluster analyses of the data (e.g. Fig. 11) is around 170 mm, but this is clearly overestimated because of the lack of a clear depth-related trend in the quantitative humification results (‘raw’ % light transmission) from Straduff Townland and is probably less than 140 mm in reality.
21
577
< FIGURE 12 >
578 1
Figure 12. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat. (A)
2
579 3
Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs. field
4
580 5 6 581 7 8 582 9 10 583 11 12 13 584 14 15 585 16 17 586 18 19 587 20 21 22 588 23 24 589 25 26 27 590 28 29 591 30 31 592 32 33 593 34 35 594 36 37 38 595 39 40 596 41 42 597 43 44 598 45 46 47 599 48 49 600 50 51 601 52 53 602 54 55 56 603 57 58 604 59 60 61 62 63 64 65
water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013).
< FIGURE 13 > Figure 13. Variation of mean thickness of basal peat depths according to specific physical properties at all three landslides.
5. Discussion
The three sites investigated for this study were remarkably similar in terms of the characteristics of their blanket peat. Slieve Anierin had a lower fraction of identifiable monocot fragments and a correspondingly higher fraction of unidentified organic matter, but this may simply reflect greater decomposition of the same plants rather than being evidence of different constituents. The smaller proportion of coarse fibres throughout the peat at this site, and particularly towards the base, supports the interpretation of more advanced decomposition. However, the higher dry bulk density and slightly higher saturated hydraulic conductivities (Table 4) perhaps indicate a very slightly different composition. One tensile strength measurement at this site was significantly out of line with the others (Fig. 8) due to a high density of woody remains within one test sample, but the other measures of shear strength were entirely consistent with the other two sites. Therefore we suggest that this site has essentially the same palaeoenvironmental history of peat accumulation as the others. Furthermore, the similarity between these results and some obtained from other landslide sites throughout northwestern and western Ireland and Northern Ireland (e.g. Kirk 2001; Yang and Dykes 2006; Dykes 2008c; Dykes and Warburton 2008a; Dykes and Jennings 2011) and indeed eastern Ireland (e.g.
22
605
Boylan and Long 2010) strongly suggests that the general geotechnical characteristics of upland blanket peat
606 1
throughout the island of Ireland are very similar everywhere.
2 3 607 4 5 608
6 7 609 8 9 610 10 11 611 12 13 14 612 15 16 613 17 18 614 19 20 615 21 22 23 616 24 25 617 26 27 618 28 29 619 30 31 32 620 33 34 621 35 36 622 37 38 623 39 40 624 41 42 43 625 44 45 626 46 47 627 48 49 628 50 51 52 629 53 54 630 55 56 631 57 58 632 59 60 61 633 62 63 64 65
Much of the present vegetation of Ireland’s blanket bogs is dominated by sedges (e.g. E. vaginatum), heathers (Ericacae, including Calluna vulgaris) and some Sphagnum and other mosses. These are all represented in the analyses, with the sedges dominating the identifiable macrofossils (Fig. 10). In many places there are the remains of trees at the base of the peat, which act like fragments of weathered bedrock to resist movement of the peat over the in situ ground. However, at these three sites, separated by up to 20 km, there is a weak basal layer around 150 mm thick that can be clearly distinguished from the peat above on the basis of the properties measured for this study. Intriguingly, a higher proportion of the macrofossils can be identified as monocot fragments in this layer, which somewhat contradicts the idea of greater decomposition. On the other hand, fibre contents reduce sharply towards this basal layer (Fig. 10). O’Kelly (2017) suggested that the properties of fibrous peat depend on the fibre content, but we suggest that these Irish blanket peats cannot be considered to be ‘fibrous’ in the same sense, since even the acrotelm layer may contain relatively few identifiable fibres. The issue is in any case unclear. Previous studies have found that higher fractions of coarse fibres had no effect on measured strength compared with lower coarse fibre contents (Zhang and O’Kelly 2014; Hendy et al. 2014); Price et al. (2005) found that fibre content was not related to compressibility, and Lee et al. (2015) concluded that the effect of fibre orientation on frictional shearing resistance was not clear. However, Boylan and Long (2010) undertook a quantitative analysis of fibre contents adjacent to peat slides in Co. Wicklow and found lower fibre contents with depth. We therefore conclude that the occurrence of failure in upland Irish blanket bogs must be at least in part due to the lower fibre content, as well as higher overall degree of decomposition, towards the base of the peat.
We found some relationships between measured properties of the peat we analysed. The very strong association ( |r| > 0.95) between the humus fraction, coarse fibre fraction and total fibre content at the three landslides mean that only one of these parameters may be needed to investigate other properties of peat. This association can be explained by the fact that with increasing plant decomposition, the size and amount of organic particles decrease, resulting in low fibre contents (Fig. 12A). When the fibre content decreases, the water content also decreases (Fig. 12C) because the voids within the fibres, which contain the largest amount 23
634
of water (MacFarlane and Radforth 1968), also decrease. The coarse fibres influence peat structure and
635 1
possibly strength (see above) and may be used for stability assessments given that at all three sites they were
2 3 636 4 5 637 6 7 638 8 9 639 10 11 640 12 13 14 641 15 16 642 17 18 643 19 20 644 21 22 23 645 24 25 646 26 27 647 28 29 648 30 31 32 649 33 34 650 35 36 651 37 38 652 39 40 653 41 42 43 654 44 45 655 46 47 656 48 49 657 50 51 52 658 53 54 659 55 56 660 57 58 661 59 60 61 662 62 63 64 65
similarly abundant and showed high ( |r| > 0.9) correlations with other properties. However, the apparent uniformity of the peat across these sites precludes any suggestion that this may form the basis of a generalised approach, in the absence of further studies from different peatlands (e.g. Northern England or Scotland). Figs. 12D and 12E merely highlights the effect of humification in that if there are more fibres remaining then there should also be more macrofossils that have not yet decomposed too far to be identified. Fig. 12F shows that whichever method of strength determination is used (excluding the field vane), the (shear) strength of the basal peat appears to be around 2 kPa. This is consistent with stability analyses of landslides involving failure within the peat (i.e. bog slides, bogflows and some peat flows sensu Dykes and Warburton 2007b) as reported by Dykes (2008c), Dykes and Jennings (2011) and Farrell (2012) and with test results obtained from other similar studies in Ireland (e.g. Dykes 2008c; Dykes et al. 2008).
Two of the characteristics identified as being slightly different at Slieve Anierin, i.e. the monocot content and the coarse fibre content, can be readily determined from small auger samples because they are quantified with respect to the dry mass. A hand auger capable of cutting ‘intact’ core samples, notwithstanding issues of sample deformation due to compression or fibres not being cut cleanly (Long and Boylan 2013; Hendy et al. 2014), could in principle provide samples for simple determination of dry bulk density and possibly saturated hydraulic conductivity, i.e. the other two slightly distinctive characteristics. However, given that the measured strengths at this site were no different from the others, we cannot say whether measurement of those characteristics would be useful for peats formed from significantly different plant assemblages. It is not possible to generalise any implications of our results for peatlands in general, and notwithstanding previous comments we cannot assume that any of our correlations between botanical and geotechnical characteristics will apply throughout Ireland. There is thus a clear necessity for comprehensive laboratory testing of peat from the site of any proposed development, probably requiring excavation of trial pits for the extraction of appropriate undisturbed samples. However, general recommendations for the most appropriate tests – and testing procedures suitable for peat – will probably take some time to emerge from ongoing research programmes.
24
663
Finally, the very low shear strength indicated above demands some consideration with respect to water
664 1
conditions within the peat. Blanket bogs in the British Isles may experience water table variations of up to
2 3 665 4 5 666 6 7 667 8 9 668 10 11 669 12 13 14 670 15 16 671 17 18 672 19 20 673 21 22 23 674 24 25 675 26 27 676 28 29 677 30 31 32 678 33 34 679 35 36 680 37 38 681 39 40 682 41 42 43 683 44 45 684 46 47 685 48 49 686 50 51 52 687 53 54 688 55 56 689 57 58 690 59 60 61 62 63 64 65
0.5–1.0 m, but these are occasional reductions below the surface during warm periods of summer weather (Evans et al. 1999; Holden and Burt 2003). The usual condition for these deposits is to be fully saturated to the surface, i.e. with normal effective stress ≈ 0 and maximum pore water pressure most of the time. Periods of summer drying may increase the normal effective stress by a few kPa due to the reduced pore water pressure, i.e. temporarily increasing the effective shear strength. Failure within the peat cannot, therefore, be the result of raised pore water pressures throughout the peat matrix due to heavy rainfall (although it could due to external loading). The hydraulic effects of water-filled pipes, cracks and other voids (e.g. Dykes, this volume – in review) may play significant roles in the initiation of failure, i.e. peat mass effects, are thought to be more important than simply the peat matrix (shear) strength, but much more research is needed to test this hypothesis.
6. Conclusions and Future Work
The upland blanket bogs of northwestern Ireland appear to be formed from essentially the same assemblages of plant species, dominated by sedges (mostly represented by Eriophorum vaginatum), and therefore having similar physical and botanical characteristics. The data describing those characteristics show a statistically distinct basal layer around 150 mm thick characterised by, in particular, a sharp reduction in the coarse – and total – fibre content. Tensile strength, experimental low stress direct shear and unconsolidated undrained triaxial compression measurements of peat strength converge on a value of around 2 kPa which is consistent with stability back-analyses requiring undrained shear strengths of around 2 kPa for FS = 1.0. Contrary to some published accounts, it appears that the lack of coarse fibres may be a contributory factor in the incidence of peat slope failures. Some relationships between measured properties suggest that there may be usable indicators of peat strength and stability conditions, possibly obtainable by means of samples from hand augers, but the apparent uniformity of the peat at these three locations precludes any definitive proposal of useful new methodologies at present.
25
691
It has been recognised for some time that the development of methods for reliably estimating the shear
692 1
strength of peat is likely to require some detailed investigations of botanical controls on relevant
2 3 693 4 5 694 6 7 695 8 9 696 10 11 697 12 13 14 698 15 16 699 17 18 700 19 20 701 21 22 23 702 24 25 703 26 27 704 28 29 705 30 31 706 32 33 707 34 35 708 36 37 709 38 39 710 40 41 711 42 43 712 44 45 713 46 47 714 48 49 715 50 51 716 52 53 717 54 55 718 56 57 719 58 59 60 61 62 63 64 65
geotechnical properties (e.g. Dykes 2008a). More recently, O’Kelly (2017, p.21) stated that: ‘More extensive testing of peats with different botanical compositions is recommended to confirm relationships between tensile strength, other strength parameters and humification level’. All of these issues are now starting to be addressed more systematically by a few researchers in several countries. However, more extensive integrative research is needed, perhaps involving palaeoecologists alongside geotechnical engineers, to explore the causes and geotechnical effects of different peat accumulation scenarios. Detailed measurements of all possible characteristics, such as presented in this study, are required for several known sites of peat landslides in each of several different biogeographical zones such as Dartmoor (SW England), North Pennines (N England), Isle of Skye (W Scotland), Shetland Islands (N Scotland), ideally including full depth variations at each study location in order to generate sufficient data for reliable statistical analyses.
Acknowledgements
This work was funded by Kingston University’s Centre for Earth and Environmental Science Research (CEESR) studentship support fund. EF thanks Prof M Waller (Kingston University), Dr P Hughes (University of Southampton) and Dr M Grant (Kingston University/Wessex Archaeology) for advice and assistance with palaeoecological research techniques. We are grateful to Prof E Bromhead for redrawing Figure 4, and to Mr C Somerfield for assistance with the triaxial testing.
References Aaby B and Tauber H (1974) Rates of peat formation in relation to degree of humification and local environment as shown by studies of a raised bog in Denmark. Boreas (Oslo) 4(1), 1-18. Andrejko MJ, Fiene F and Cohen AD (1983) Comparison of ashing techniques for determination of the inorganic content of peats. In Testing of Peats and Organic Soils (Jarrett PM (ed)). ASTM Special Technical Publication, 820. American Society for Testing and Materials, Philadelphia, pp.5-20. ASTM (2008) D1997-91: Standard test method for laboratory determination of the fiber content of peat samples by dry mass. American Society for Testing and Materials, Philadelphia.
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723 5 6
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Barber KE, Chambers FM, Maddy D, Stoneman R and Brew JS (1994) A sensitive high resolution record of late Holocene climatic change from a raised bog in northern England. The Holocene 4, 198-205. Blackford JJ and Chambers FM (1993) Determining the degree of peat decomposition for peat based palaeoclimatic studies. International Peat Journal 5, 7-24. Boylan N and Long M (2010) An investigation of two peat slope failures in the Wicklow mountains. Biology and Environment: Proceedings of the Royal Irish Academy 110B (3), 173-184. Carlsten P (1993) Peat - Geotechnical Properties and Up-to-Date Methods of Design and Construction. State-of-the-ArtReport. Linköping: Swedish Geotechnical Institute. Chambers FM, Barber KE, Maddy D and Brew JS (1997) A 5500-year proxy-climate and vegetation record from blanket mire at Talla Moss, borders, Scotland. The Holocene 7, 391-399. Charman DJ (2002) Peatlands and Environmental Change. Wiley, Chichester. Crofton HT (1902) How Chat Moss broke out in 1526. Transactions of the Lancashire and Cheshire Antiquarian Society XX, 139-144. Daniels RE and Eddy A (1990) Handbook of European Sphagna. Institute of Terrestrial Ecology, Natural Environment Research Council. HMSO, London. Dykes AP (2008a) Properties of peat relating to instability of blanket bogs. In Landslides and Engineered Slopes, Volume 1 (Chen ZY, Zhang J, Li Z, Wu A and Ho K (eds)). Taylor and Francis, London, UK, pp.339-345. Dykes AP (2008b) Geomorphological maps of Irish peat landslides created using hand-held GPS. Journal of Maps v2008, 258-276. Dykes AP (2008c) Tensile strength of peat: laboratory measurement and role in Irish blanket bog failures. Landslides 5(4), 417-429. Dykes AP (2009) Geomorphological maps of Irish peat landslides created using hand-held GPS - Second Edition. Journal of Maps v2009, 179-185. Dykes AP (this issue? – still in review) New insights from a recent peat slide at Croaghan, Co. Antrim, Northern Ireland. Dykes AP and Jennings P (2011) Peat slope failures and other mass movements in western Ireland, August 2008. Quarterly Journal of Engineering Geology and Hydrogeology 44(1), 5-16. Dykes AP and Kirk KJ (2001) Initiation of a multiple peat slide on Cuilcagh Mountain, Northern Ireland. Earth Surface Processes and Landforms 26, 395-408. Dykes AP and Warburton J (2007a) Significance of geomorphological and subsurface drainage controls on failures of peat-covered hillslopes triggered by extreme rainfall. Earth Surface Processes and Landforms 32, 1841-1862.
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751 752 1 2 753 3 4
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755 7 8
756 9 10 757 11 12 758 13 14 759 15 16 760 17 18 761 19 20 762 21 22 763 23 24 764 25 26 765 27 28 766 29 30 767 31 32 768 33 34 35 769 36 37 770 38 39 771 40 41 772 42 43 773 44 45 774 46 47 775 48 49 776 50 51 777 52 53 778 54 55 779 56 57 780 58 59 781 60 61 782 62 63 64 65
Dykes AP and Warburton J (2007b) Mass movements in peat: A formal classification scheme. Geomorphology 86(1-2), 73-93. Dykes AP and Warburton J (2008a) Failure of peat-covered hillslopes at Dooncarton Mountain, Co. mayo, Ireland: Analysis of topographic and geotechnical factors. Catena 72, 129-145. Dykes AP and Warburton J (2008b) Characteristics of the Shetland Islands (UK) peat slides of 19 September 2003. Landslides 5, 213-226. Dykes AP, Gunn J and Convery (Née Kirk) KJ (2008) Landslides in blanket peat on Cuilcagh Mountain, northwest Ireland. Geomorphology 102, 325-340. Evans MG, Burt TP, Holden J, Adamson JK (1999) Runoff generation and water table fluctuations in blanket peat: evidence from UK data spanning the dry summer of 1995. Journal of Hydrology 221, 141-160. Farrell ER (2012) Organics/peat soils. In ICE Manual of Geotechnical Engineering: Volume 1, Geotechnical Engineering Principles, Problematic Soils and Site Investigation (Burland J, Chapman T, Skinner H and Brown M (eds)). ICE Publishing, London, UK, pp.463-479. Foteu Madio ES (2013) Botanical and geotechnical influences on peat instability. Unpublished PhD thesis, Kingston University, UK. Foteu Madio ES, Dykes AP, Waller MP, Hughes P and Grant MJ (2012) Botanical and geotechnical influences on peat instability. In Landslides and Engineered Slopes: Protecting Society through Improved Understanding (Vol. 2) (Eberhardt E, Froese C, Turner AK and Leroueil S (eds)). Proceedings of the 11th International and 2nd North American Symposium on Landslides and Engineered Slopes. CRC Press, London, pp.421-427. Gilman K, Newson MD (1980) Soil Pipes and Pipeflow: a Hydrological Study in Upland Wales, British Geomorphological Research Group Monograph 1. Geobooks: Norwich. Grosse-Brauckmann G (1972) Über pflanzliche Makrofossilien mitteleuropäischer Torfe - I. Gewebereste krautiger Pflanzen und ihre Merkmale. Telma2, 19-55. Hammond RF (1979) The Peatlands of Ireland. Survey Bulletin No. 35. An Foras Talúntais, Dublin Hanrahan ET (1954) An investigation of some physical properties of peat. Géotechnique 4, 108-123. Head KH (1994) Manual of Soil Laboratory Testing, Permeability, Shear Strength and Compressibility Testing. Volume 2. Wiley, New York. Helenelund KV (1967) Vane tests and tension tests on fibrous peat. Proceedings of the Geotechnical Conference, Oslo, Vol. 1, 199–203. Hendy MT, Barbour SL and Martin CD (2014) Evaluating the effect of fiber reinforcement on the anisotropic undrained stiffness and strength of peat. Journal of Geotechnical and Geoenvironmental Engineering, published on-line at doi:10.1061/(ASCE)GT.1943-5606.0001154. 28
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Hobbs NB (1986) Mire morphology and the properties and behaviour of some British and foreign peats. Quarterly Journal of Engineering Geology 19, 7-80. Holden J, Burt TP (2003) Hydrological studies on blanket peat: the significance of the acrotelm–catotelm model. Journal of Ecology 91: 103–113. IUGS – International Union of Geological Sciences Working Group on Landslides (1995) A suggested method for describing the rate of movement of landslides. Bulletin International Association of Engineering Geology 52, 75-78. Jarrett PM (1983) Summary. In Testing of Peats and Organic Soils (Jarrett PM (ed)). ASTM Special Technical Publication, 820. American Society for Testing and Materials, Philadelphia, pp.233-237. Katz NJ, Katz SV and Skobeyeva EI (1977) Atlas of plant remains in peat soil. Nedra [In Russian]. Kirk KJ (2001) Instability of blanket bog slopes on Cuilcagh Mountain, N.W. Ireland. Unpublished PhD thesis. University of Huddersfield, UK. Klute A, Dirksen C (1986) Hydraulic conductivity and diffusivity: laboratory methods. Methods of Soil Analysis Part 1. Physical and Mineralogical Methods. Agronomy Monograph (2nd edition), Vol. 9. Soil Science Society of America, Madison, pp. 687– 734. Landva AO and Pheeney PE (1980) Peat fabric and structure. Canadian Geotechnical Journal 17(3), 416-435. Lee J-S, Seo S-Y and Lee C (2015) Geotechnical and geophysical characteristics of muskeg samples from Alberta, Canada. Engineering Geology 195, 135-141. Lindsay R, Bragg O (2005) Wind farms and blanket peat: a report on the Derrybrien bog slide (2nd edition). Derrybrien Development Cooperative Ltd., Gort. Long M (2005) Review of peat strength, peat characterisation and constitutive modelling of peat with reference to landslides. Studia Geotechnica et Mechanica XXVII, 67-90. Long M and Boylan N (2013) Predictions of settlement in peat soils. Quarterly Journal of Engineering Geology and Hydrogeology 46, 303-322. Long M and Jennings P (2006) Analysis of the peat slide at Pollatomish, County Mayo, Ireland. Landslides 3(1), 51-61. MacFarlane IC and Radforth NW (1968) Structure as a basis of peat classification. National Research Council of Canada (Ottawa). Reprinted from Proceedings, Third International Peat Congress held in Quebec, Canada, 18-23 August 1968, pp.91-97. Mills AJ (2002) Peat slides: morphology, mechanisms and recovery. Unpubl. PhD thesis. University of Durham, UK. Moore PD (1984) The classification of mires: An introduction. In European Mires (Moore PD (ed)). Academic Press, London, pp.1-10. O’Kelly BC (2014) Drying temperature and water content–strength correlations. Environmental Geotechnics 1 (EG2), 81-95. 29
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820 9 10 821 11 12 822 13 14 823 15 16 824 17 18 825 19 20 826 21 22 827 23 24 828 25 26 829 27 28 830 29 30 831 31 32 832 33 34 35 833 36 37 834 38 39 835 40 41 836 42 43 837 44 45 838 46 47 839 48 49 50 840 51 841 52 53 842 54 843 55 56 844 57 845 58 59 846 60 847 61 62 63 64 65
O’Kelly BC (2017) Measurement, interpretation and recommended use of laboratory strength properties of fibrous peat. Geotechnical Research, published on-line at http://dx.doi.org/10.1680/jgere.17.00006. Price JS, Cagampan J and Kellner E (2005) Assessment of peat compressibility: is there an easy way? Hydrological Processes 19, 3469-3475. Skempton AW and Petley DN (1970) Ignition loss and other properties of peats and clays from Avonmouth, Kings Lynn and Cranberry Moss. Geotechnique 20(4), 343-356. Smith AJE (2004) The moss flora of Britain and Ireland (2nd edition). Cambridge University Press, Cambridge. Troels-Smith J (1955) Karakterisering af lose jordater (Characterisation of unconsolidated sediments). Denmarks Geologiske Undersogelse 4(3), 1-73. von Post L (1922) Sveriges geologiska undersoknings torvinventering och nagre av dess hittills vunna resultat, sr. mosskulturfor. Tidskr 1, 1-27. Walker D and Walker PM (1961) Stratigraphic evidence of regeneration in some Irish bogs. Journal of Ecology 49, 169-185. Warburton J, Higgit D and Mills A (2003) Anatomy of a Pennine peat slide, northern England. Earth Surface Processes and Landforms 28(5), 457-473. Warburton J, Holden J and Mills AJ (2004) Hydrological controls of superficial mass movements in peat. Earth-Science Reviews 67(1-2), 139-156. Yang J and Dykes AP (2006) The liquid limit of peat and its application to the understanding of Irish blanket bog failures. Landslides 3(3), 205-216. Zhang L and O’Kelly BC 2014 The principle of effective stress and triaxial compression testing of peat. Geotechnical Engineering 167, 40-50.
List of Figures
Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (after Hammond 1979). The outlined rectangle is enlarged to show the locations of the three bogflows: (left to right) ST = Straduff Townland, SA = Slieve Anierin, SR = Slieve Rushen. Modified from Yang and Dykes (2006). Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat basin into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD).
30
848 849 1 850 2 3 851 4 852 5 6 853 7 854 8 9 855 10 856 11 12 857 13 858 14 15 859 16 860 17 18 861 19 862 20 21 863 22 864 23 24 865 25 866 26 27 867 28 868 29 30 869 31 870 32 33 871 34 35 872 36 873 37 38 874 39 875 40 41 876 42 877 43 44 878 45 879 46 47 880 48 881 49 50 882 51 883 52 53 884 54 885 55 56 886 57 58 59 60 61 62 63 64 65
Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c). Figure 4. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013). Figure 5. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5, etc. refer to sampling positions: A1 to A9 are shown in Fig. 5; E1/E3 and E4/E7 are located either side of the downslope extent of the source area. The materials found at each position are from, and in the same order as, this list: Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013). Figure 6. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan, obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a). Figure 7. Mohr’s Circles obtained from unconsolidated-undrained triaxial tests on peat samples from the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu Madio (2013). Figure 8. Tensile strength results obtained from the three landslides in this study and from previous studies using the same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW-08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’. Modified from Foteu Madio (2013). Figure 9. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST). Figure 10. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A) Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013). Figure 11. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters corresponding to zones in the diagram. Source: Foteu Madio (2013). Figure 12. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat. (A) Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs. field water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013). Figure 13.Variation of mean thickness of basal peat depths according to specific physical properties at all three landslides.
31
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 887 25 888 26 889 27 28 890 29 30 891 31 892 32 33 893 34 894 35 36 37 38 39 40 41 42 43 44 45 46 47 48 895 49 50 51 52 53 54 55 56 57 58 59 60 61 896 62 63 64 65
Figure 1. Location of the study area in northwest Ireland, showing the distribution of peatlands (grey shading, after Hammond 1979). The outlined rectangle is enlarged, right, to show the relative locations of the three bogflows and their upland contexts: (left to right) ST = Straduff Townland, SA = Slieve Anierin, SR = Slieve Rushen. In this study area map, grey shading is land above 300 m elevation, horizontal stripes indicate water bodies and the solid black line is the international border. Modified from Yang and Dykes (2006).
32
1 2 3 4 5 6 7 8 9 10 897 11 12 898 13 899 14 15 900 16 901 17 18 902 19 903 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 904 47 48 905 49 906 50 51 907 52 908 53 54 909 55 910 56 57 911 58 59 60 61 62 63 64 65
Figure 2. General views of the three study areas. (A) Straduff Townland bogflow, looking downslope from above the head (July 2010). (B) Slieve Rushen bogflow, looking across at the failed slope from the other side of the peat basin into which its displaced peat flowed (July 2010). (C) Slieve Anierin bogflow from the air (Nov. 1998, photo by APD).
Figure 3. Measuring the tensile strength of the peat: (A) the two sets of steel ‘fingers’ that are pushed through the centre of a cut block of undisturbed peat 100 mm high × 100 mm wide and 40-60 mm thick; (B) one half of a sample following tensile failure, still adhering to one set of ‘fingers’; (C) the testing apparatus, showing: centre – the ‘fingers’ assembly installed (without a sample); right – the force proving ring; lower far left – the hanger for applying the weights that apply the load just visible beside the end of the cupboards. Details of the design and development of this apparatus are provided in Dykes (2008c).
33
1 2 3 4 5 6 7 8 9 10 912 11 913 12 13 914 14 915 15 16 916 17 917 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 918 41 42 919 43 920 44 921 45 46 922 47 923 48 49 924 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65
Figure 4. Peat stratigraphy across the slope above the head of the Slieve Rushen bogflow. This linear transect was located 7.5 m upslope of the source area head at the closest point. Modified from Foteu Madio (2013).
Figure 5. Results of macrofossil analyses of samples obtained from across the Slieve Rushen bogflow. Labels A1, A5, etc. refer to sampling positions: A1 to A9 are shown in Fig. 5; E1/E3 and E4/E7 are located either side of the downslope extent of the source area. The materials found at each position are from, and in the same order as, this list: Charcoal (0.5-1 mm); Charcoal (less than 0.5 mm); Ericales; Eriophorum vaginatum; Monocot fragments (Monocot leaves at E4), Roots; Sphagnum; Unidentified organic matter. Source: Foteu Madio (2013).
34
8.0 7.0 6.0
Shear stress (kPa)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 925 20 926 21 22 927 23 928 24 25 929 26 930 27 28 29 30 31 32 33 34 35 931 36 37 38 39 40 41 42 43 44 45 932 46 47 48 49 50 51 52 53 54 55 933 56 934 57 58 935 59 936 60 61 62 63 64 65
5.0 4.0 3.0
ST ST near surface SR SA E6 replicate (Dykes 2008a) E6 (Dykes 2008a)
2.0 1.0 0.0 0.0
1.0
2.0
3.0
4.0 5.0 6.0 7.0 8.0 Normal stress (kPa)
9.0
10.0 11.0 12.0
Figure 6. Results from experimental low-stress direct shear tests of basal peat from all three landslides and from around 10-60 mm depth at Straduff Townland. Previous results from bog slide ‘E6’ at Cuilcagh Mountain, Co. Cavan, obtained using the same methodology, are also shown. Modified from Foteu Madio et al. (2012), after Dykes (2008a).
Figure 7. Mohr’s Circles obtained from unconsolidated-undrained triaxial tests on peat samples from the three landslides: (A) ST– Straduff Townland; (B) SR – Slieve Rushen; (C) SA – Slieve Anierin. Source: Foteu Madio (2013).
35
0
2
3
4
Tensile strength (kPa) 5 6 7 8 9 10 11 12 13 14 15 16 17
0 0.2 0.4 0.6
Depth (m)
0.8 1 ST SR SA MHA-00s (Dykes 2008c) SDF-08 (Dykes and Jennings 2011) BHW-08 (Dykes and Jennings 2011) DCM-03: SE5 (Dykes and Warburton 2008)
1.2 1.4 1.6 1.8 2
Figure 8. Tensile strength results obtained from the three landslides in this study and from previous studies using the same methodology. MHA-00s refers to the Maghera bogflow, Co. Galway; SDF-08 is bogflow ST in this study; BHW08 is the Ballincollig Hill peat flow, Co. Kerry; DCM-03 is the collective reference for the 40 landslides that occurred on Dooncarton Mountain, Co. Mayo on 19 September 2003, the results here being obtained from peat slide ‘SE5’. Modified from Foteu Madio (2013).
70
y = 53.03 - 19.05x R² = 0.5405
60
Transmission (%)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 937 20 938 21 22 939 23 940 24 25 941 26 942 27 28 943 29 30 944 31 945 32 33 946 34 35 947 36 948 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 949 54 950 55 56 951 57 952 58 59 953 60 61 954 62 63 64 65
1
50 40 30 20 10 0 0
0.25 0.5 0.75 1 1.25 1.5 1.75 2 Depth below ground surface (m)
Figure 9. ‘Raw’ percentage of light transmission at the Straduff Townland bogflow (ST).
36
Percentage (%) of the initial dry mass of peat
A 0
10
20
30
40
50
60
70
80
90
100
0.9 Humus fraction (<0.15 mm) Fine fibres (0.15-1mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.0
Depth (m)
1.1 1.2 1.3 1.4 1.5 1.6 1.7 1.8 1.9
B 0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70 80
90
100
0.9 1.0 1.1
Depth (m)
1.2 1.3 1.4 1.5 1.6 Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.7 1.8 1.9
C 0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70 80
90
100
0.9 1.0 1.1 1.2
Depth (m)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 955 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 956 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 957 52 958 53 54 959 55 960 56 57 961 58 59 962 60 963 61 62 63 64 65
1.3 1.4 1.5 1.6
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.7 1.8 1.9
Figure 10. Depth variations of fibre contents throughout the lower half of the peat profile at each landslide: (A) Straduff Townland, (B) Slieve Rushen, (C) Slieve Anierin. Source: Foteu Madio (2013).
37
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 964 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 965 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 966 54 967 55 968 56 57 969 58 970 59 60 971 61 62 63 64 65
Figure 11. Macrofossil content of the peat monolith from the three landslides: (a) ST, (b) SR, (c) SA. Parameter values are raw counts for charcoal and E. vaginatum spindles, otherwise percentages. The figure shows the dendrogram produced from unconstrained incremental sum square cluster analysis of strata analysed. Dashed lines separate clusters corresponding to zones in the diagram. Source: Foteu Madio (2013).
38
(B)
Total fibre content (%)
R2 = 0.98 R2 = 0.93 R2 = 0.86
100 90 80 70 60 50 40 30 20 10 0
ST SR SA
Total fibre content (%)
100 90 80 70 60 50 40 30 20 10 0
R2 = 0.96 R2 R2
= 0.96 = 0.98
ST SR SA
0 10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
0 10 20 30 40 50 60 70 80 90 100 Humus fraction (%)
(C)
(D)
1100
Monocotyledon fragments (%)
100 90 80 70 60 50 40 30 20 10 0
1000
Field water content (%)
900 800 700 600 500 400 300
R2 = 0.66
ST
R2
= 0.67
SR
R2 = 0.41
SA
0 10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
ST
R2 = 0.09
SR
R2 = 0.33
SA
R2 = 0.32
0 10 20 30 40 50 60 70 80 90 100 Total fibre content (%)
(E)
(F) 120
ST
R2 = 0.14
14
100
SR
R2 = 0.30
12
Triaxial test
SA
R2
10
Tensile str.
80
Peat strength (kPa)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 973 15 16 974 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 975 33 34 976 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 977 51 52 978 53 979 54 55 980 56 981 57 58 982 59 983 60 61 984 62 63 64 65
(A)
Unidentified organic matter (%)
972
= 0.50
60 40 20
Field vane
Direct shear
8 6 4 2
0
0
4
5 6 7 8 9 10 Degree of humification (von Post)
0
10 20 30 40 50 60 70 80 90 100
Coarse fibre fraction (%)
Figure 12. Correlations between physical/geotechnical parameters and between botanical characteristics of the peat. (A) Total fibre content vs. humus fraction. (B) Total fibre content vs. coarse fibre fraction. (C) Coarse fibre fraction vs. field water content. (D) Monocot fragments vs. total fibre content. (E) Unidentified organic matter vs. von Post humification. (F) Undrained shear strength (including ‘field vane strength’) vs. total fibre content. In (A) to (E), solid line = ST, long dashed line = SR and the thin broken line = SA. After Foteu Madio (2013).
39
1 2 3 4 5 6 7 8 9 10 11 12 13 985 14 15 986 16 17 987 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65
Thickness of basal layer (mm)
600
ST SR
500
SA
400 300 200 100 0 Field description
'Raw' % light transmission
Fibre content
Macrofossil content
Quantitative fibre content
Site average
Figure 13. Different estimates of mean thickness of basal peat depths according to specific physical properties at all three landslides.
40
Figure 1A
Click here to download Figure Foteu Madio and Dykes Fig 1a.tif
Figure 1B
Click here to download Figure Foteu Madio and Dykes Fig 1b.tif
Figure 2A
Click here to download Figure Foteu Madio and Dykes Fig 2a.tif
Figure 2B
Click here to download Figure Foteu Madio and Dykes Fig 2b.tif
Figure 2C
Click here to download Figure Foteu Madio and Dykes Fig 2c.tif
Figure 3
Click here to download Figure Foteu Madio and Dykes Fig 3.tif
Figure 4
Click here to download Figure Foteu Madio and Dykes Fig 4.tif
Figure 5
Click here to download Figure Foteu Madio and Dykes Fig 5.tif
Figure 6
8 7
Shear stress (kPa)
6 5 4 3 ST ST near surface SR SA E6 replicate (Dykes 2008a) E6 (Dykes 2008a)
2 1 0 0
1
2
3
4 5 6 7 Normal stress (kPa)
8
9
10
11
12
Figure 7A
Click here to download Figure Foteu Madio and Dykes Fig 7a.tif
Figure 7B
Click here to download Figure Foteu Madio and Dykes Fig 7b.tif
Figure 7C
Click here to download Figure Foteu Madio and Dykes Fig 7c.tif
Figure 8
Tensile strength (kPa) 0
1
2
3
4
5
6
7
8
9
10 11 12 13 14 15 16 17
0 0.2 0.4
Depth (m)
0.6 0.8 1 1.2
ST SR
1.4
SA
1.6
MHA-00s (Dykes 2008c)
1.8
BHW-08 (Dykes and Jennings 2011)
2
SDF-08 (Dykes and Jennings 2011) DCM-03: SE5 (Dykes and Warburton 2008)
Figure 9
70
y = -18.819x + 52.83 R² = 0.5322
Transmission (%)
60 50 40 30 20 10 0 0
0.25
0.5
0.75
1
1.25
1.5
Depth below ground surface (m)
1.75
2
Figure 10
A 0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70
0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70
80
80
0.9 1.0
Depth (m)
1.1 1.2 1.3 1.4 1.5 1.6 1.7 1.8 1.9
B 0.9 1 1.1
Depth (m)
1.2 1.3 1.4 1.5 1.6
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
1.7 1.8 1.9
C 0
10
20
Percentage (%) of the initial dry mass of peat 30 40 50 60 70
80
0.9 1 1.1
Depth (m)
1.2 1.3 1.4 1.5 1.6 1.7 1.8 1.9
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
80
90
100
Humus fraction (<0.15 mm) Fine fibres (0.15-1mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
80
90
100
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
80
90
Humus fraction (<0.15 mm) Fine fibres (0.15-1 mm) Coarse fibres (>1 mm) Total fibre content (>0.15 mm)
100
Figure 11A
Click here to download Figure Foteu Madio and Dykes Fig 11a.tif
Figure 11B
Click here to download Figure Foteu Madio and Dykes Fig 11b.tif
Figure 11C
Click here to download Figure Foteu Madio and Dykes Fig 11c.tif
Figure 12
R2 = 0.98 R2 = 0.93
0
1000
Monocotyledon fragments (%)
Field water content (%)
0
D
900 800 700 600 R2 = 0.66
500 400 300 0
Unidentified organic matter (%)
100
R2
= 0.67
R2
= 0.41
ST SR SA
40 20 0
-20
5
6
0
F
R2 = 0.14 R2 = 0.30 R2 = 0.50
60
4
100 90 80 70 60 50 40 30 20 10 0
10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
ST SR SA
80
100 90 80 70 60 50 40 30 20 10 0
10 20 30 40 50 60 70 80 90 100 Humus fraction (%)
1100
C
E
B
ST SR SA
Total fibre content (%)
100 90 80 70 60 50 40 30 20 10 0
7
8
9
10
10
14
Peat strength (kPa)
Total fibre content (%)
A
12 10 8 6 4 2 0
-40
0
Degree of humification (von Post)
10
R2 = 0.96 R2
= 0.96 R2 = 0.98 0
0
ST SR SA
10 20 30 40 50 60 70 80 90 100 Coarse fibre fraction (%)
ST
R2 = 0.09
SR
R2 = 0.33
SA
R2 = 0.32
10 20 30 40 50 60 70 80 90 100 Total fibre content (%)
Field vane Triaxial test Tensile str. Direct shear
10
20
30
40
50
60
70
Coarse fibre fraction (%)
80
90 100
Figure 13
Thickness of basal layer (mm)
600
ST
500
SR
400
SA
300 200 100 0 Field description 'Raw' % light transmission
Fibre content
Macrofossil content
Quantitative fibre content
Site average
Table 1
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Table 1. Summary of site details and characteristics of the study bogflows. Bogflow County Latitude Longitude
Elevation Geology Geomorphological Length Slope Deptha Volume (m) (Carboniferous) Context (m) (°) (m) (m)
ST
Sligo 54°7.2’N 8°12.9’W
405
Lackagh Sandstone
SR
Cavan 54°8.9’N 7°38.5’W
390
Glenade Sandstone
SA
Leitrim 54°6.3’N 7°58.7’W
440
Lackagh Sandstone
Escarpment failure
Basin slope failure 175 Escarpment failure
Note a
200
Indicative average depth of in-situ peat immediately adjacent to the landslide source area
190
5.5 (top) 3 (mid) 6 (lower)
2.5
35,000
5.5
2.0
20,000
4
2.2
22,000
Table 2
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Table 2. Samples extracted from the study bogflows. Landslide / Physical properties – Tensile strength – position in small cores 50 mm blocks 120×120×70 peat profile dia. × 51 mm length mm ST see right ST basea SA 300-1030 mm depth SA base a SR 100-830 mm depth SR base b
Triaxial – Shear strength (direct 38 mm dia. shear) – blocks cores 120×120×70 mm
6 at ~650 mm depth 3 at 10-80 mm depth 6 at ~1150 mm depth 3 at 890-960 mm depth
--
Monoliths for botanical data 730×100×100 mm
3 at 10-80 mm depth 1 at 400-1130 mm 3 at 890-960 mm depth depth
9
6
6
12
2
--
--
--
--
1
9
6
6
12
2
--
--
--
--
1
9
6
6
12
2
Notes a
1600-1700 mm depth below the surface of the peat, 970-1700 mm depth for the lower monoliths
b
1900-2000 mm depth, 1270-2000 mm depth for the lower monoliths
Table 3
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Table 3. Summary description of the peat at each landslide Sampling Point (Foteu Madio 2013). The four major stratigraphic units are separated by the solid lines of the Table.
Depth (m) 0.00-0.40 0.40-0.78 0.78-1.22 1.22-1.60 1.60-1.80 >1.80
Peat profile description at ST Light brown fibrous peat, slightly humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength. Black and moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength. Light brown with dark patches, very weak and moderately humified peat. Monocotyledon fine fibre limited. Low horizontal tensile strength. Brown, moderately to strongly humified peat. Monocotyledon fine fibre present. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Rare and very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart. Peat profile description at SR1
Depth (m) 0.00-0.15 0.15-0.36
Brown fibrous peat with moderately humified, mainly monocotyledon fine fibres and low amorphous material, moderate horizontal tensile strength. Brown, less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat and moderate amorphous material, moderate horizontal tensile strength.
0.36-0.58
Dark brown humified peat with monocotyledon fragments. Low horizontal tensile strength.
0.58-0.88
Dark brown decomposing peat with monocotyledon fragments. Low horizontal tensile strength.
>1.64
Dark grey, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1 on the Munsell soil colour chart.
Depth (m)
Peat profile description at SA
0.88-1.58 1.58-1.64
0.00-0.76 0.76-1.56 1.56-1.76 1.76-1.78 >1.78
Dark fibrous peat, slightly humified, mainly monocotyledon fine fibres, low amorphous material and moderate horizontal tensile strength. Light brown less fibrous peat with moderately humified, mainly monocotyledon fine fibre peat, moderate amorphous material and moderate horizontal tensile strength. Black humified peat with monocotyledon fragments. Low horizontal tensile strength. Dark grey, greasy, highly humified and amorphous peat. Very fine monocotyledon fragments. Low to zero horizontal tensile strength. Sandstone in clay matrix, 5YR 3/1on the Munsell soil colour chart.
Note 1
Recorded in July 2010 prior to the moorland fire.
Table 4
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Table 4. Summary of physical properties of peat at the three landslides, including previous data from Yang and Dykes (2006)*.
ST SR SA
Water content a,b (% mass fraction)
Loss on Ignition c (%)
Saturated bulk density e (Mg m–3)
Dry bulk density e Saturated (Mg m–3) hydraulic conductivity h,i (m s–1)
700-900 *620-860 600-700 600-700 *600-740
94.5-95.6 *97.8-98.8 94.6-97.2 d 95.0 *97.7-98.5
1.00 f *1.06 1.00 1.00 *1.05
0.10-0.20 *0.13 0.10-0.20 0.20 g *0.15
10–9 to 10–8 * < 10–11 10–9 to 10–6 10–8 to 10–6 * < 10–11
Notes a
There was negligible difference between field-wet and saturated water contents at all sites
b
Indicative ranges of mean values from 256-319 samples per site
c
Indicative ranges of mean values from 123-196 samples per site
d
The basal peat at Slieve Rushen was noticeably higher in organic matter than any other sampled peat
e
Mean values from 20-26 samples per site
f
The basal peat at Straduff Townland was noticeably higher (~1.10 Mg m–3) than any other sampled peat
g
The peat at Slieve Anierin had higher dry bulk densities throughout its depth
h
Indicative ranges of mean values from 19-26 samples per site, obtained using a ‘constant head’ method
i
Results obtained using a ‘falling head’ method were consistently 10 2-103 m s–1 higher than the respective ‘constant
head’ values
Author photographs - Foteu Madio
Author photographs - Dykes