Sediment and Wood Dynamics in Forests Managed for Timber Production in New South Wales, Australia
Abstract
Over the next several decades there may be substantial pressure
to extract timber from within harvest exclusion zones, or buffer
strips along headwater streams to meet the projected increase in
the global demand for forest products. Forest management
activities have the potential to significantly modify woody
debris loads in buffer strips, and thus the availability of
material for recruitment into headwater streams. Therefore, it
is important that forest management practices in these headwater
systems take account of the role wood supplied from buffer strips
play in the development of channel structure and sediment
retention capacity.
Most of the research on the effects of timber harvesting in
buffer strips on sediment dynamics and wood accumulation in small
headwater streams has been carried out in the Northern
Hemisphere, in particular the Pacific Northwest of North America.
Australia, in contrast to these regions, is tectonically
inactive, with rivers that are characterised by highly variable
flow regimes, and low sediment loads. Consequently it is likely
that the drivers of erosion and sedimentation and woody debris
recruitment are different. Where studies have been conducted in
Australia, they have mostly been on larger systems in catchments
not typical of the small headwater basins and ephemeral channels
where the majority of timber harvesting in the coastal forest of
New South Wales occurs.
The main aim of this study is therefore to advance our
understanding of the physical interactions between buffer strips
and small zero order ephemeral headwater channels, and the
potential impact of timber harvesting on these interactions. To
address this main aim, five related research aims were proposed
and focussed on: 1) assessing the characteristics of large wood
pieces and their geomorphic significance in the channels; 2)
identification of how, and from what distance the LW pieces were
recruited to the channels; 3) measuring the impact of harvesting
in the zero order basins and buffer strips along the channels;
and 4) modelling the effect on channel erosion and sediment
transport of in-channel obstructions created by large wood.
To achieve this, five zero order channels in a native forest on
the south coast of New South Wales, Australia, were instrumented
with rain gauges and weirs to monitor rainfall, streamflow,
turbidity, and suspended sediment concentration over a seven and
a half year period. After a five year calibration period, four
of the catchments were harvested, while one remained as a
control. In the harvested catchments there were two replicated
treatments; harvesting in the 10 m buffers, and no harvesting in
the 10 m buffers.
Two major methods were applied to identify interactions in the
zero order channels between buffer strips and in-channel large
wood obstructions, and the potential impact of timber harvesting
on these interactions. The first was analysis of the effect of
timber harvesting using a range of statistical techniques
including generalised linear models and maximum likelihood
estimation. The second method invoked a cellular landscape and
river reach process model to simulate the role of channel
obstructions created by large wood on channel erosion and
sediment transport. The process model was parameterised and
calibrated against an observed discharge and suspended sediment
record. Following calibration, 12 discharge and large wood
obstruction scenarios were carried out to model erosion and
suspended sediment transport over a timber harvesting cycle.
Results of the statistical analysis showed that harvesting had a
significant impact on runoff and suspended sediment yield
relative to the control, but did not have a significant impact on
turbidity or suspended sediment concentration. There was no
significant difference in post-harvest runoff, turbidity,
suspended sediment concentration, or suspended sediment yield
between the treatments. In the treatment where there was no
harvesting in buffers, the significant increase in suspended
sediment yield dissipated after 18 months and was accompanied by
a hydrological recovery in peak flows toward pre-harvest values.
In the treatment where there was harvesting in the buffers, there
was no hydrological recovery in peak flows, nor was there a
decrease in suspended sediment yields 18 months after harvesting.
Erosion rates in the harvested catchments over the 32 month
post-harvest period were three times greater than the control
erosion rate, but were still less than the sustainable erosion
rate recommended for Australia, and were largely in balance with
regional estimates of soil production.
The majority of large wood interacting with the channels, and
forming obstructions behind which sediment was stored had
diameters ≤ 30 cm. Most of this wood was being delivered from
the channel margins within the buffer strips. Most of the
sediment within the zero order channels was stored on the channel
bed, and was an order of magnitude greater than the amount of
sediment stored behind obstructions. Of the sediment stored
behind obstructions, large wood provided the majority of storage
sites.
The use of the process model to increase and extend the observed
discharge record provided some useful insights into the temporal
and spatial pattern of erosion, sediment storage and transport,
and complimented the statistical analysis of harvesting impacts
by extending these processes over a harvesting cycle. The
benefit of retaining buffers alongside the zero order channels
was demonstrated by a substantial reduction in channel erosion
and suspended sediment yield obtained through the inclusion of
in-channel large wood obstructions in the cellular landscape and
river reach model. Therefore it is important that harvesting
practices maintain sufficient volume of standing wood in these
buffer strips alongside zero order channels to ensure ongoing
recruitment of large wood to the channel network. The management
implications of this study are not just relevant for coastal New
South Wales, but also for other catchments where their
hydroclimatologies may produce similar results.
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