It is my experience that the accepted so-called 'knowledge' of
dryland river behaviour, the character of related environments,
and the sediments they leave behind, is riddled with misunderstanding
and presumption. Whilst the whole of this website is dedicated to
correcting this situation, and advancing true understanding, this
particular section is intended to highlight some of the worst problems
I frequently encounter. After summarizing the myth, I attempt to
show how it is false.
The first category of problem is the presumption that dryland rivers
are fundamentally no different to rivers elsewhere. Related to this
is misunderstanding about the nature of drylands themselves.
That dryland rivers are distinctive should no longer be in doubt.
I have summarized on a separate web page the main
points of difference. See also the excellent review by Knighton
& Nanson (1997).
The second category of problem is the tendency for unsubstantiated
guesswork about what dryland rivers are like, based on what people
think they know. This includes extrapolation from other settings,
and the creation of purely hypothetical models unanchored in observations
of modern systems. It also ends up oversimplifying the nature of
dryland environments.
Many of the myths in this second category relate to topics I believe
are, or should be, at the leading edge of dryland rivers research.
In these cases, you will find further discussion of the subject
through the Hot topics menu option at the top-left of this page.
The mistakes resulting from these myths are particularly important
for those involved with interpretation of the rock record, especially
from the subsurface. Perhaps the biggest impact is on palaeoclimate
interpretation and depositional setting.
Do you have your own favourite dryland myth? Please .
Not built by Hollywood ...
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"Drylands are dry, aren't they? The dominant
physical processes are those driven by the wind. Water action is
trivial to non-existent."
This is a common misconception that comes about because precipitation
in drylands is infrequent. Because vegetation is limited or absent
in drylands, the wind takes on a geomorphological role to a much
larger degree than in other environments. But this does not mean
water action is absent. Indeed, it is one of the startling paradoxes
of drylands that although they are regions of little rain, the details
of their surfaces are mostly the products of the action of rivers
(Graf, 1988, p.3).
Surface runoff is of considerable importance, though usually occurring
episodically. Even in the driest areas, high-magnitude sheet floods
can have significant geomorphic effects, though they have rarely
been observed or recorded (because they are generally unpredictable,
but see McGee 1897 and Rahn 1967 for exceptions). Rather special
to drylands is that low-intensity rainfall will produce significant
runoff, because infiltration rates are low (partly as a result of
the lack of vegetation).
Aeolian sand-seas (the general impression the lay-person has of
deserts, thanks to films such as Lawrence of Arabia) generally form
less than 30% of the dryland landscape, rising to just 38% for Australia
(see Thomas 1997, p.9, table 1.5).
An example of how water action dominates over wind action comes
from the north end of the Namib Sand Sea, in Namibia, Africa (Fig.
1). This example is just one of many that could be selected
to make this point. The general direction of sand movement due to
wind action is roughly to the north (Lancaster 1989). Although the
dunes encroach into the course of the ephemeral River Kuiseb between
floods, the irregular floods are still capable of preventing the
dunes from advancing further north. The Kuiseb catchment is large
enough to supply adequate water to achieve this, but not all Namibian
rivers are so lucky. See Fig.
1 for more details.
This myth is common amongst European-trained geologists attempting
subsurface sedimentological interpretation. Their experience of
the world is mostly (exclusively?) of temperate humid conditions,
and their knowledge of drylands comes solely from the news and entertainment
media, or from brief vacations to drylands (when of course they
see no rainfall).
"All stream flow is in the form of flash
floods each lasting just a few hours."
If a person manages not to succumb to the "It never rains"
myth, then usually their next statement is to perpetuate the myth
that all dryland floods are flash floods. I suspect this arises
because most of the (few) detailed surveys of flood behaviour in
drylands have been done in small, high-gradient drainage catchments
where flows are dominated by convective storms and flash floods
truly are the norm.
In reality, there is a great temporal and spatial variability in
precipitation, and consequently a wide range in flood magnitude
and duration. Loosely, flood duration correlates directly with catchment
area. The literature is biased towards rivers with small catchments.
This is clear from the examples shown in Fig.
2.
"Dryland rivers are all ephemeral, flowing
for just a few hours at a time, then drying up completely."
This myth arises partly out of the previous one "All floods
are flash floods", partly from a lack of precision with the
term 'ephemeral', and partly because of a lack of thought about
dryland geography.
Etymologically, the word "ephemeral" derives from the
Greek meaning "lasting only a day". It is used colloquially
to mean "lasting a very short time". But it should not
be used synonymously with 'dryland river', which commonly is what
happens. As shown above (Fig.
2), floods vary greatly in duration.
Two aspects of dryland rivers often get overlooked. The first is
groundwater contribution to flow. The second is sourcing of flow
outside the dryland region.
A common classification of streams is into:
Ephemeral: ( = transitory, short-lived), flowing briefly
and rarely, and returning to dry condition in between; usually
sourced entirely from precipitation;
Intermittent: flow occasionally, irregularly; usually
has a flow contribution from groundwater as well as from rainfall;
Perennial, typically when flow is sourced outside the
region.
These terms are in common use but lack rigid definition. Also,
there is a continuous progression from perennial streams through
intermittent streams to ephemeral streams. Whereas the middle and
lower reaches of streams in humid regions rarely or never cease
flowing and can properly be called perennial, almost every year
many of their upstream feeders run dry where they are not fed by
springs. In basins cut in impermeable bedrock, prolonged droughts
can halt flow in most channel reaches. Karst (limestone country)
that has some surface drainage often includes streams that are spatially
intermittent; frequently it also contains temporally intermittent
streams that flow only when heavy rain raises the groundwater table
and reactivates outlets above the usual level. Temporally intermittent
streams also occur in dry areas where, at low stage, only some channel
reaches contain flowing water.
Groundwater contribution
There is a general presumption that groundwater contribution is
negligible in drylands. The reasoning usually goes like this: because
precipitation is low and infrequent, and evaporation rates are high,
water-table height will be depressed, and usually will be considerably
below the base of channels. Though this is certainly true in many
places, it cannot be taken as an all-pervading rule, not in time
nor in space.
For example, a common phenomenon in dryland rivers is the occurrence
of rapid and deep incision, producing what in the western USA are
referred to as arroyos. This can occur without any change in base-level,
the dominant control probably being climatic (Waters & Haynes,
2001).
Such incision can easily take the channel base down to or below
the prevailing water-table, allowing significant groundwater contribution
to the river, prolonging flood flow and resulting in semi-permanent
surface water. It is unclear exactly what impact this might have
on sediment transport and internal structures.
In the example documented from the Santa Cruz River, Arizona, USA
(Waters 1988), the groundwater flow led to the creation of permanently
wet marshes and the accumulation of organic-rich clays within
the channel. If such a sedimentary record was intersected in a borehole,
it is likely it would be interpreted as the product of a lake rather
than an in-channel deposit of restricted extent.
Similar examples exist on other dryland rivers, such as the middle
reaches of the Huab River in northwest Namibia (Figs
3 & 4),
but I know of none that have been documented in any detail.
Externally-sourced rivers
Rivers which depend on catchments outside dryland regions may display
very complex behaviour. For example, the Nile River is sourced from
three principle headwaters: the White Nile drains large lakes in
the southern headwaters of Uganda, and is clearly sourced from a
tropical humid region; the Blue Nile and the Atbara, its other two
sources, drain northern and central parts of Ethiopia, a dryland
region. The Blue Nile and Atbara supply the bulk of the sediment
to the lower Nile and Nile Delta, an interesting observation in
the context of which climatic regions produce the greatest amount
of sediment (see the Distinctiveness page Sediment
Production item). But the lower Nile is dependent for water
volume on the White Nile. The net result is the Quaternary sedimentological
history of the Nile is highly complex (see overview in Williams
et al., 1998, p.153-155).
"It is too dry to support vegetation except
in trivial amounts."
Certainly vegetation is much more limited than in other regions,
and this has a profound impact on infiltration, surface runoff and
sediment availability. But it is definitely not true that vegetation
is totally absent. What does happen is that vegetation tends to
concentrate along, and often in, the channel, and is more restricted
on the floodplain. See for example Fig.
4 above, the Huab River in Nambia, where the modern course of
the river is picked out by vegetation.
"Because it is so dry, sediments deposited
in drylands are not disturbed by bioturbation - it is too dry for
bugs. If you see bioturbation (in any significant amount), then
it these must be lake sediments."
Occasionally this myth is modified by the concession there may
be small amounts of rooting, though of course plant material is
not preserved because the environment is too strongly oxidising.
This myth reflects again a profound misunderstanding of the amount
of biological activity in drylands. Drylands are host to an extremely
wide range of insects (especially flies and beetles), arachnids
(spiders and scorpions), reptiles (lizards and snakes), and mammals
(gerbils, moles, rats), that dwell in, feed in, or deposit their
larvae in, dryland alluvium and aeolian sediment. Granted, the particular
species are typically highly evolved to deal with the conditions
(e.g. the tenebrionid beetles in the Namib that get water by standing
upside down at the crest of dunes when it is foggy). Bioturbation
intensity reflects sedimentation rate and moisture availability.
Recognition of terrestrial trace fossils is a specialised skill.
Distinction of dryland traces from those of other climates is even
more difficult. But this is no excuse for presuming drylands are
devoid of trace fossils.
Steve Hasiotis (University of Kansas) is in the process of finishing
a new book on trace fossils and ichnology that will be of considerable
help in this regard. Look for it in 2002, to be published by AAPG.
"Because it is dry, there will be no plants
or bugs, and thus little organic matter, so soils do not form."
This is an example of trying to guess what happens based on an
incomplete understanding of drylands. It is partly based on a misunderstanding
of the nature of soil processes - few sedimentologists get good
training in soil formation and palaeosol recognition. It also comes
about because dryland soils are often relatively immature, so are
much harder to spot in the rock record. And, as with so many other
aspects of drylands, soils in such settings are much more poorly
understood and documented than those in temperate and humid regions.
Most of the studies claiming success in using soils in interpreting
the architecture of dryland region sediments are premised on the
soils of those regions developing in exactly similar ways to those
in other climate regions. Careful analysis of the literature on
modern soils shows that dryland region soils are distinctly different
to the soils of other regions. Furthermore, they may be developed
to such a minimal degree that they show negligible variation across
the floodplain, even though they may represent similar amounts of
time to well-developed soils in other climates. Application of temperate
region models in these circumstances would lead to the incorrect
interpretation that sedimentation rate was high, and the river systems
combed the floodplain at a rapid rate.
The published sedimentological literature on dryland soils is biased
almost exclusively to two 'types' of soil: Vertisols and Calcretes
(horizons enriched in calcium carbonate, not strictly a soil type).
Anyone taking the time to read relevant literature carefully would
discover that this gives a misleading view of dryland alluvial systems,
as it overlooks that:
Vertisols are not unique to drylands. They will form in all
climate regimes where there is adequate water, but cannot form
in the driest conditions. Reliable evidence to show a particular
Vertisol occurrence is a dryland one is hard to come by, and can
often end up in circular reasoning.
Vertisols are found in less than 5% of modern drylands. From
a dryland perspective, therefore, they are an unusual feature
not a typical one.
Vertic structures in sediment, the diagnostic feature of Vertisols,
are poor indicators of fluvial architecture: they develop extremely
quickly (5-200 years), and are often specific to certain site
conditions rather than climate conditions.
Calcium carbonate enrichment, to form a calcrete, can be incorporated
into the profile of several different types of soil. Whether this
happens or not is often entirely independent of the behaviour
of the fluvial system, being primarily a function of availability
of CaCO3. The absence of calcrete in a succession should not be
interpreted as an artefact of the fluvial system (e.g. high sedimentation
rate) unless there is clear evidence nearby (laterally or stratigraphically)
that shows pedogenic calcrete could have developed.
Calcium carbonate enrichment can occur through soil-forming
processes (pedogenic calcrete) or due to early diagenesis from
non-pedogenic processes (groundwater calcrete), sometimes even
due to both operating more or less simultaneously. Distribution
of groundwater calcrete usually bears little relation to fluvial
architecture, often being controlled by fault and hydrothermal
systems related to basin development. Some workers did not or
could not distinguish between pedogenic and groundwater calcrete,
so invalidating their interpretations of fluvial architecture.
Aside even from the issue of availability of CaCO3, pedogenic
calcrete is not a ubiquitous or diagnostic dryland feature. Royer
(1999) has shown it does not occur where mean annual precipitation
is less than about 100 mm. Although not usually developed where
precipitation exceeds 760 mm (Royer, 1999), calcite nodules have
been documented from Holocene soils on the floodplains of the
(humid region) Mississippi River (in Vertisols!) (Slate et al.,
1996; Aslan & Autin, 1998; Slate, 1998).
"The Bijou Creek lithofacies model gives
the diagnostic appearance of dryland rivers."
When it comes to interpreting the rock record, especially in the
subsurface, we are dependent on having knowledge of the range of
possibilities - we see what we expect to see. Lithofacies models
can be extremely helpful in untangling the complexities of nature.
But this is a case in point where the models can be positively dangerous.
Given all the statements made above, and in the page on the Distinctiveness
of Dryland Rivers, it is in any case unreasonable to expect
one model to represent the wide range of complexity.
Of 16 fluvial facies models recently summarised by Miall (1996,
fig. 8.8, p.203-205), three in particular are considered to be relevant
to drylands: he calls them "ephemeral sandy meandering",
"sheetflood distal braided", and "flashy, ephemeral
sheetflood". The first two of these bear considerable similarity
to each other, and to others of the fluvial profiles. There is of
course the problem about what ephemeral should be taken to mean
(see above), so maybe some of the other
models may be relevant, but that has yet to be shown in the literature.
The "ephemeral sandy meandering" model seems to be needed
because of a single description in the literature (Shepherd, 1987)
of a single occurrence of lateral accretion surfaces at a bend in
the Rio Puerco River in Mexico. Whilst it is perfectly conceivable
that dryland rivers can meander, and leave behind point bars, this
instance has now been brought into doubt in the course of new detailed
studies by Schlumberger Research to build an outcrops database:
the Shepherd example is believed now to be downstream accretion
at a section cut at an unusual angle (Ian D. Bryant, personal communication
1999).
The last model is also based on a single instance in the literature,
this time on the description of Bijou Creek by McKee et al. (1967),
and is dominated by upper flow-regime plane-bed lithofacies, a dominance
which Miall admits to be misguided (Miall, 1996 p. 54 paragraph
3), though he hasn't modified the model or the descriptions! Such
plane-bed lithofacies occur in just one of the logged Bijou Creek
sections and form only about 5% of the deposits observed by Williams
(1966, 1970, 1971) from the large floods in the Lake Eyre basin
of central Australia.
My own studies have led me to the general conclusion that the so-called
Bijou Creek facies model may be relevant solely for high-gradient
rivers in small catchments. We have no reliable models for other
dryland rivers.
Please don't get me wrong here, I am not accusing Andrew Miall
of creating this myth. Indeed, we should all be grateful to him
for the exhaustive compilations he has produced, which I am sure
we all turn to at some time or other. He might have perpetuated
the myth a bit, but it is the general users of the literature who
must take ultimate responsibility for their own conclusions.
The main problem is that our overall understanding of dryland river
systems is poor. Sedimentological interpretations continue to be
rooted in the 1970s and early 1980s, and have not kept pace with
new geomorphological knowledge. The important advances made in geomorphology
in the last decade have had little impact on sedimentological thinking,
and have not been matched with complementary sedimentology research.
The little new work there is, such as on the Plio-Pleistocene of
the Rio Grande (e.g. Mack et al., 1997; Mack & Leeder, 1998;
Mack & Leeder, 1999; Pérez-Arlucea et al., 2000), the
role of river capture (Mather, 2000), and the way climate can induce
phases of incision or construction without requiring a base level
change (Mack et al., 1998; Harvey et al., 1999), have yet to influence
mainstream writing.
The existing sedimentological literature is premised on a tiny
number of original field studies of modern dryland systems. To make
matters worse, derivative papers that use these primary results,
to interpret the rock record, get cited as support for subsequent
interpretations as though they themselves are primary sources. Concepts
and models have been built, and spread through the literature, that
are based on extremely weak science and a very limited appreciation
of dryland systems. This limited view is not necessarily a fault
of the authors, just a reflection of the lack of data on modern
drylands.
One of the most common examples of this phenomenon is the way the
work of Ian Tunbridge on interpretation of the Devonian-age Trentishoe
formation in North Devon (an extension of the Old Red Sandstone
of S. Wales) is quoted as justifying interpretation of other units
as dryland "ephemeral" rivers (citing in support either
Tunbridge, 1981; or Tunbridge, 1984). Tunbridge did a good job interpreting
his outcrops in the light of the then-current knowledge.
But this work was solely on rock record examples, not modern rivers,
and it in turn draws on just a tiny number of primary studies of
ephemeral rivers.
I see this phenomenon several times a year in papers I am asked
to review and in graduate student dissertations.
ASLAN, A. & AUTIN, W.J. 1998. Holocene flood-plain
soil formation in the southern lower Mississippi Valley: Implications
for interpreting alluvial paleosols. Geological Society of America
Bulletin, 110, 433-449.
GRAF, W.L. 1988. Fluvial processes in dryland rivers.
Springer-Verlag, Berlin.
HARVEY, A.M., SILVA, P.G., MATHER, A.E., GOY, J.L.,
STOKES, M. & ZAZO, C. 1999. The impact of Quaternary sea-level
and climatic change on coastal alluvial fans in the Cabo de Gata
ranges, southeast Spain. Geomorphology, 28, 1-22.
KNIGHTON, A.D. & NANSON, G.C. 1997. Distinctiveness,
diversity and uniqueness in arid zone river systems. In: THOMAS,
D.S.G. (ed.) Arid zone geomorphology: process, form and change in
drylands. 2nd edition. Wiley, Chichester, 185-203.
LANCASTER, N. 1989. The Namib Sand Sea: dune forms,
processes and sediments. A.A. Balkema, Rotterdam.
MACK, G.H., LOVE, D.W. & SEAGER, W.R. 1997. Spillover
models for axial rivers in regions of continental extension: the
Rio Mimbres and Rio Grande in the southern Rio Grande rift, USA.
Sedimentology, 44, 637-652.
MACK, G.H. & LEEDER, M.R. 1998. Channel shifting
of the Rio Grande, southern Rio Grande rift: implications for alluvial
stratigraphic models. Sedimentary Geology, 117, 207-219.
MACK, G.H. & LEEDER, M.R. 1999. Climatic and tectonic
controls on alluvial-fan and axial-fluvial sedimentation in the
Plio-Pleistocene Palomas half graben, southern Rio Grande rift.
Journal of Sedimentary Research, 69, 635-652.
MATHER, A.E. 2000. Impact of headwater river capture
on alluvial system development: an example from the Plio-Pleistocene
of the Sorbas Basin, SE Spain. Journal of the Geological Society
of London, 157, 957-966.
MCGEE, W.J. 1897. Sheetflood erosion. Geological Society
of America Bulletin, 8, 87-112.
MCKEE, E.D., CROSBY, E.J. & BERRYHILL, H.L. 1967.
Flood deposits, Bijou Creek, Colorado, June 1965. Journal of Sedimentary
Petrology, 37, 829-851.
MIALL, A.D. 1996. The geology of fluvial deposits:
sedimentary facies, basin analysis, and petroleum geology. Springer-Verlag,
New York.
PÉREZ-ARLUCEA, M., MACK, G.H. & LEEDER,
M.R. 2000. Reconstructing the ancestral (Plio-Pleistocene) Rio Grande
in its active tectonic setting, southern Rio Grande rift, New Mexico,
USA. Sedimentology, 47, 701-720.
RAHN, P.H. 1967. Sheetfloods, streamfloods and the
formation of pediments. Annals of the American Association of Geographers,
57, 593-604.
ROYER, D.L. 1999. Depth to pedogenic carbonate horizon
as a paleoprecipitation indicator. Geology, 27, 1123-1126.
SHEPHERD, R.G. 1987. Lateral accretion surfaces in
ephemeral stream point bars. In: ETHRIDGE, F.G., FLORES, R.M. &
HARVEY, M.D. (eds) Recent developments in fluvial sedimentology.
SEPM special publication 39, Tulsa, 93-98.
SLATE, J.L., SMITH, G.A., WANG, Y. & CERLING,
T.E. 1996. Carbonate-paleosol genesis in the Plio-Pleistocene St.
David Formation, southeastern Arizona. Journal of Sedimentary Research,
66, 85-94.
SLATE, J.L. 1998. Hydromorphic-soil origin of carbonate
glaebules in pliocene paleosols of southeastern Arizona. Quaternary
International, 51-2, 60-61.
THOMAS, D.S.G. 1997. Arid environments: their nature
and extent. In: THOMAS, D.S.G. (ed.) Arid zone geomorphology: process,
form and change in drylands. 2nd edition. Wiley, Chichester, 3-22.
TUNBRIDGE, I.P. 1981. Sandy high energy flood sedimentation
- some criteria for recognition, with an example from the Devonian
of SW England. Sedimentary Geology, 28, 79-95.
TUNBRIDGE, I.P. 1984. Facies model for a sandy ephemeral
stream and clay playa complex; the Middle Devonian Trentishoe Formation
of North Devon, UK. Sedimentology, 31, 697-715.
WATERS, M.R. 1988. Holocene alluvial geology and geoarchaeology
of the San Xavier reach of the Santa Cruz River, Arizona. Geological
Society of America Bulletin, 100, 479-491.
WATERS, M.R. & HAYNES, C.V. 2001. Late Quaternary
arroyo formation and climate change in the American Southwest. Geology,
29, 399-402.
WILLIAMS, G.E. 1966. Planar cross-stratification formed by the lateral
migration of shallow streams. Journal of Sedimentary Petrology,
36, 742-746.
WILLIAMS, G.E. 1970. The central Australian stream
floods of February-March 1967. Journal of Hydrology, 11, 185-200.
WILLIAMS, G.E. 1971. Flood deposits of the sand-bed
ephemeral streams of central Australia. Sedimentology, 17, 1-40.
WILLIAMS, M.A.J., DUNKERLEY, D.L., DE DECKKER, P.,
KERSHAW, A.P. & CHAPPELL, J. 1998. Quaternary environments.
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