Hydroecological safety of
N. I. Alekseevskiy, R. S. Chalov
Department of Hydrology,
Faculty of Geography, Moscow State University
Vorobievy Gory, Moscow, Russia, 119992, phone 7 (495)
9391001 n_alex@hydro.geogr.msu.su
Hydroecological safety depends on water sources availability, water quality and
dangerous hydrological processes development. Theirs changes occur under
natural and anthropogenic factors and lead to the risk of social, economic and
ecological damages. Channel deformations are the reason of risk occurrence [Berkovitch etc., 2000]. Their dangerous expressions develop
under changes of hydrological regime, streams hydraulic characteristics, water
and sediment runoff because instability of channel deposits, channel forms and
channels themselves is caused by natural or anthropological shifts of stream
velocities, water and sediment discharges.
The relationship between sediment yield and channel deformations is explained by the equation of sediment mass balance for the channel reach
W2 – W1 = ±DW, (1)
where W2 and W1 are the sediment loads on the downstream and upstream reach borders, DW is the balance resultant. If the lack of sediment supply by tributaries and from slides exists, DW depends on the volume of river (floodplain and channel) deposits changes DW0:
.
(2)
The eq. (2) shows that the resultant of sediment mass balance and river deposits are equals with contrary sign [Alekseevskiy, 1998]. Under the longitudinal sediment load increase the value of DW > 0. This process is determined by erosion of river sediments (channel banks and/or beds) and accompanied by theirs volume decrease DW0. Sediment volume decrease is expresses by vertical deformations and bottom level drop or horizontal deformations and bank erosion [Chalov, 1979]. Opposite processes occur under the longitudinal sediment load decrease (DW < 0). The increase of river sediments exists (DW0 > 0). In this case the vertical deformations correspond to bottom level increase, horizontal – to the deposition on floodplain banks. When the sediment particles are transported along the channel reach (at the equality of deposited and entrained sediments, when DW = 0) the volume of river sediments is constant (DW0 = 0) and stable channels exist [Karaushev, 1977]:
Wsl = W, (3)
where Wsl is
transporting capacity. It equals to the rate of sediment yield, possible to
transport in each time interval i of
the representative period T under certain
annual water regime and stream hydraulic characteristics. Thus, Wsl depends on flow rate and is characterized by suspended sediment concentration ssl corresponded to the maximum sediment load under
certain hydrological and hydraulic characteristics.
In stable channels bed and bank deformations have lack
of directed development (fig. 1a) and are expressed only in geological time
scale. For the unstable channels the eq. (3) is
disturbed because of natural and anthropogenic transformations of sediment
yield W and transporting capacity Wsl. In each
case there are 2 possible variants of deformations development. If the increase of Wsl and
decrease of W induce the existing of Wsl >W, the
could be removed by the sediment yield increase
and transporting capacity decrease. It occurs by the
channel deformations process. Because of bed
and bank erosion the balance resulting DW>0 and decrease of channel deposits volume appears. The maximal
intensity of channel deposits diminution occurs near the upper reach border. As
the result the channel slope decreases, what is the factor of transporting
capacity reduction. The equality (3) is achieved.
The opposite processes develop at the reaches with Wsl <W. This inequality reflects the sediment load yield increase or transporting capacity reduction. Accumulation processes occur and Wsl grows and W decreases. The maximal sediment accumulation is observed near the upper reach border where the volume of sediment deposits increases (DW0>0). Bed level grows with higher intensity. Sediment load discharge reduces, channel slope and transporting capacity decrease and finally the new state of the “channel-water stream” system leads to the eq. (3).

Figure 1. The response stable stream-channel system to sediment load yield increase: reduction (b) or growth (c) of transporting capacity
Channel processes influence on the social and economic
safety and nature management is controlled by sediment yield and transporting
capacity factors shift. River sediment yield includes suspended load yield (WR) and bed load yield (WG).
Sediment yield components depend on river size and geographical conditions of
river basin determining erosive processes intensity [Sediment yield, 1979; Dedkov, Mozherin, 1984]. When
other factors are similar the stream order increase is accompanied by suspended
and bed load yield growth.
Channel deformations intensity controls risk of
engineering objects damage, water intake shoaling, the riparian lands losses
and depends on WG/WG+R ratio.
It varies in wide ranges in according to changes of sediment yield components [Chalov, Lui Shuguang,
2005]. On the North Russian rivers the relatively small sediment yield is
combined with WG/WG+R = 40–50% and more. It is the consequence of
forest cover and poor erosive processes. Only incised channels with limited
channel deformations are stable and channel deformations are safe for most
human activities. Channels with wide floodplains are unstable. On small rivers the annual erosion
velocities are about 1-
Plateaus composed by loess, abundant soil and gully
erosion are the sources of the southern rivers sediments where WG/WR+G
< 10%. The total sediment yield is 2–3 times more as northern rivers.
Bed load materials are the only channel forming sediments in the North. In the
South the main part of the suspended load materials is also channel forming
sediments. It determines the instability of southern rivers, intensity of
horizontal deformations (10–100 m/year), bed level shifts because of large riffles
movement up to 100–1000 m/year and as a result the high risk of water resources
use (Terek, Kuban and Ob
rivers in Russia). Sediment yield and transporting capacity are transformed because
of evolution of river systems and changes of basin natural conditions and also
under nature management in river basins and channels. Deforestation, marshes
drainage, mining, riverbed excavation are the main human activities affecting
the suspended sediment load variations. Transporting capacity shifts mainly due
to water runoff (flow) regulation, riverbed excavation and changes of channel
width, depth and length (tab. 1). The impact of hydraulic project and quarries
digging differs between upstream and downstream reaches of works facilities.
Inside-basin and inter-basin water redistribution are also an important
factors. In the rivers – receiving waters transporting capacity increases, in
the rivers – water sources transporting capacity decreases. Wsl and/or W changes are
accompanied by the channel deformation, thus natural management is usually the
reason of damage expressions.
The spatial-temporal scales of
the equation (3) transgression are much different. Global environmental
changes, large hydraulic projects, inter-basin water redistribution,
deforestation are spread over vast territories and river basins in historical
and geological duration. The risk level of main directed channel deformations
is determined by velocity and rate of these changes. Also during natural
evolution of channel forms the eq. (3) may be broken.
As a result the deepening or shoaling of braided rivers branches, the channel
banks erosion or accumulation occur. The same processes exist under human
impact on channels, water runoff and sediment yield. Under the installation of
water reservoirs and mass quarries digging the disturbance of the equality Wsl =W involve
large stream reaches including theirs tributaries; the influence of the single
quarry is exerted over a short reach and leads to the local deformations. In
one case the disturbance of hydroecological safety is
characterized by general or regional and permanent scale, in another – it is
local and brief.
Table 1. Anthropogenic impact on river
sediment movement (Alekseevkiy, 1998)
|
Anthropogenic
impact |
Sediment
yield change factors |
Suspended load
DR and bed load DG yield change |
|||
|
Water discharge
change DQ |
Suspended
sediment concentration change Ds |
s
sòð |
âî âðåìåíè Dt |
ïî äëèíå (Dx) ó÷àñòêà ðåêè |
|
|
Hydraulic projects: upstream
dams downstream dams |
D Q DQ ¹ 0 |
Ds < 0 Ds < 0 |
s > sòð s< sòð |
DR/Dt<0 DG/Dt <0 DR/Dt<0 DG/Dt<0 |
DR/Dx<0
DG/Dx<0 DR/Dx>0
DG/Dx>0 |
|
Channel quarries: upstream downstream |
DQ |
Ds ≥ 0 Ds < 0 |
s £ sòð s < sòð |
DR/Dt DR/Dt<0
DG/Dt<0 |
DR/Dx DR/Dx>0
DG/Dx>0 |
|
Channel cut-off |
DQ |
Ds > 0 |
s < sòð |
DR/Dt>0 DG/Dt>0 |
DR/Dx>0 DG/Dx > 0 |
|
Water redistribution: downstream
water intake Inter-basin redistribution |
DQ<0 DQ>0 |
Ds≥0 Ds>0 |
s>sòð s<sòð |
DR/Dt DR/Dt>0
DG/Dt>0 |
DR/Dx<0 DG/Dx<0 DR/Dx>0
DG/Dx>0 |
The level of channel processes risk depends on the intensity of channel deformations, their directed or recurrent development, frequency of occurrence on each river – on the channel stability as a whole. That’s why the estimation of channel deformations risk is produced according to the channel stability characteristics (tab. 2) – Lohtin number and Makkaveev stability coefficient:
,
,
(4)
where d is size of channel deposits (mm), I – slope (‰), b – channel width, m.
The impact of channel processes risk on social and
industrial units is assesses by the risk scale from 0 till 5 points. The upper
border (point 5) is absent for the rivers of
The level of channel processes risk depends on channel pattern type. Meandering, braided or relatively straight channels are characterized by the special rules of location of accumulation and erosion areas, during different phases of channel forms development. Because of their evolution the intensity of deformations increases or decreases. Conditions of channel deformations development (geological and geomorphologic) are also an important factor. Incised channels or channels with wide floodplain occur.
In natural conditions the directed vertical
deformations are distinguished by small intensity (mm/year), their results are
expressed during thousands of years. Thus they may be disregarded at hydroeconomic projects. Vertical deformations lead to bed
level shifts according to development of channel forms. Conditions of intensive
vertical deformations are infrequent. In
Table 2. Types of channel processes risk [Berkovitch etc., 2000]
|
Risk of
channel processes (channel
stability) |
Points |
Stability
characteristics |
Channel
deformations characteristics |
||||||
|
L |
ks |
Cã |
Uñð |
Umax |
| ||||