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Răzvan Voicu 
METODE ECOTEHNICE 
DE RESTAURARE ALE 
CURSURILOR DE APĂ 
ECOTECHNIC METHODS 
OF RESTORATIONING 
THE WATERCOURSES 
Bucuresti 
2008
Răzvan Voicu 
METODE ECOTEHNICE DE 
RESTAURARE ALE 
CURSURILOR DE APĂ 
ECOTECHNIC METHODS OF 
RESTORATIONING THE 
WATERCOURSES 
Dr.ing.Răzvan Voicu 
“Prin izvoarele lor munŃii îsi oglidesc istoria. ” 
“Through their sources the mountains reflect their history”
rzvnvoicu@yahoo.com 
ISBN: 978-973-0-05814-7 
Introducere 
Cartea de faŃă este realizată din respectul 
nemărginit pentru Natură, care are amabilitatea de a ne 
lăsa o planetă locuibilă prin care noi, oamenii, să putem 
explora Universul. 
DistanŃarea omului tot mai pronunŃată faŃă de 
Natură, din cauza egoismului si fugii lui după bani, a 
început să aducă o degradare continuă a ecosistemelor. 
Biosfera, a început să-si piardă din valenŃele ei ecologice 
tocmai datorită faptului că nu se Ńine cont de sistemele ei 
funcŃionale, reflectate în sistemele funcŃionale ale 
ecobiomurilor. Natura a realizat în timp diverse si 
performante reŃele ecologice, geologice, energetice, 
biologice , chimice, geografice etc, extrem de sensibile 
prin însăsi structura lor, sedimentate cu grijă de pilonul 
central al Universului: TIMPUL. 
Omul, încearcă prin diferite procedee, să extragă 
câte o componentă, deseori minusculă, din aceste 
structuri, neînŃelegând că prin fiecare componentă pierdută 
structurile biosferei dispar, conducând Terra către forma 
iniŃială unde viaŃa, asa cum este astăzi, nu putea exista. 
Cartea de faŃă, pledează prin metodele ei ecotehnice 
pentru o conlucrare rapidă pe plan global a diferitelor 
stiinŃe aparent intangibile. De fapt, aproape toate stiinŃele 
încearcă să descopere si să înŃeleagă principiile 
Universului. După cum veŃi vedea în această carte, 
conlucrarea benefică dintre ingineria costrucŃiilor 
hidrotehnice si ecologie, a dus la finalizarea teoretică a 
mai multor metode de restaurare ecologică aplicabile pe 
diverse sectoare ale cursurilor de pe întreaga suprafaŃă a 
Terrei.
Ecotehnia, reprezintă o stiinŃă nou apărută, care 
determină o colaborare eficientă interdisciplinară între 
diverse domenii stiinŃifice, în scopul dezvoltării societăŃii 
umane pe principii ecologice, cu ajutor tehnologic 
divers.Viitorul omenirii va depinde de performanŃele 
ecotehniei. 
Metodele ecotehnice prezentate pot fi puse în 
practică dacă se respectă parametrii principali de 
proiectare, dacă există voinŃă politică, înŃelegere civică din 
partea riveranilor si nu numai si o conlucrare perfectă cu 
voinŃă de reusită din partea ambelor tabere stiinŃifice 
(ingineresti si ecologice). Această carte, scoate în evidenŃă 
importanta ecotehniei, un domeniu fără de care omenirea 
nu va avea sorŃi de izbândă. 
Introduction 
This book is written in respect in the immense 
honor of Nature, which has the kindness to leave us a 
habitable planet surface by the means of which, we, the 
people, can explore the Universe. 
The increased distance between human being and 
Nature, because of the selfishness and graspingness, has 
become a continuous degradation for the ecosystems. 
Biosphere began to lose its environmental valences just 
because the human does not take into account its 
operational systems, as reflected in the functional systems 
of ecobiomes. 
4 
In the course of time, nature has created various 
and performed ecological, geological, energetic, 
biological, chemical, geographical networks, and so on, 
having a very sensitive structure, carefully deposited by 
the central pillar of the Universe: TIME. 
The human being is trying, by the means of 
different processes, to extract one component, often 
minuscule, of these structures, not having been conscious 
that with each lost component the biosphere structures 
disappear, leading Earth to its original form where life as 
today, could not exist. This book is pleading by its 
ecotechnic methods for a globally quick collaboration of 
various sciences seemingly intangible. Actually, almost all 
science seeks to discover and understand the principles of 
the Universe. As you will see in this book, the 
advantageous co-working between the hydrotechnical 
building engineering of and ecology, has led to the 
theoretical completion of several methods for 
environmental restoration on various sectors of the courses 
on the entire surface of the Planet. 
Ecotechniques is a new science which determines 
an interdisciplinary and efficient cooperation between 
different scientific domains in order to develop the human 
society regarding the ecological principles, by various 
means of technology. The humans’ future depends on the 
ecotechniques performances. 
The presented ecotechnical methods can be 
practiced if the main parameters of design are followed, if 
there is any political will, civic comprehension of riverain 
people and not in the least a perfect co-operation between 
both scientific camps (engineering and ecologies). 
5
This book accentuates the importance of 
ecotechniques as a all- important domain without which 
the world would have no success. 
1. The ecotechnical method for directioning the 
watercourse on the center of layer and of creating a 
rectangular wetland in the middle of the minor layer. 
The presented ecotechnical method can be applied 
on an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
It can be symmetrically positioned regarding the 
center of rectangular layer of the selected river sector, two 
identical structures made of oxidation-resisting metal (Fig. 
1.2) that, in their run, are symmetrically positioned 
towards the center of selected river sector. These 
structures are dimensioned regarding the water flow Q, 
layer’s depth H, rectangular layer’s width L and the 
selected sector’s length l. 
Inside metallic systems or structures of 1-3 cm 
thickness, excavation on mobile bridges positioned on the 
selected layer sector is performed in order to plant 
hydrophilic plants (reed, bulrush, sallow, cat tail, alder, 
aquatic plants etc.) in order to create performing wetlands. 
Plants are selected according to the local clime and, also, 
according to the necessities of new created ecosystem. 
The metallic structures are facilitating the physical 
building of an ecosystem, directly, and after the species of 
hydrophilic plants are planted, the metallic structures help 
them to grow fast. 
6 
After planting and growth, inside a new created 
wetland, of 50% of herby aquatic flora biomass and 20% 
of ligneous biomass which just set the radicular mass 
giving signs of development, the water shall be set free 
percentually through the dams created by the junction area 
of the metal structures frameworks with the selected 
watercourse for environmental restoration (Fig. 1.2). After 
removal of metallic structures with specialized equipment, 
the new created wetlands on the watercourse become 
higher with 5 to 15 cm (x) compared to the multiannual 
average level of water (d) before the environmental 
restoration (fig.1.1). 
The metallic systems dimensioning is performed in 
proportion to the slope ≈ 1 ‰, structure of layer along the 
banks, granulometric structure of a layer, therefore 
biotope, the amount of biomass necessary to the proper 
functioning of the ecosystem, etc. 
7
8 
Why do we want to create the wetlands on the 
selected river sectors that are extremely polluted primarily 
with organic matter and secondly metals? We know that 
wetlands: are an important habitat for fish and mollusks, 
water birds and a large number of animals, and for many 
plants, insects and other inhabitants contribute to 
maintaining the quality of water, filter the pollutants, 
retain the sedimentary material, oxygenate the water by a 
rich vegetation, absorb the nutrients (nitrogen, 
phosphorus, etc.), recycle them or, regulate the 
microclimate, contribute to preventing floods, erosion, 
aquifer reloading, water supplies, the production of timber, 
reeds and other exploitable plants, energy production 
(peat), offering areas for grazing, fishing, hunting, 
recreation, educational activities, scientific research and 
last but not least the wetlands have an aesthetic value to be 
appreciated. We know that a wetland slows the passage of 
water and increases the nutrients and sediments carried by 
flowing water, lodging sediments downstream may be 
blocking the water, reduce the force of rain and impede 
the floods down the river, by storing water in the soil or 
retain it at the surface, such as wetlands replaced 
advantageous hydrotechnical structures and not only, built 
at large expenses. After the development of wetlands 
within the new ecosystem, we can also create riparian 
areas by leveling the banks and planting some species of 
plants which are can adapt to those areas. 
9
The riparian areas are important ecologically for a 
variety of reasons: provide an erosion control through the 
regularization of transport and distribution of sediments, 
improve water quality, produce organic matter for aquatic 
habitats and ensure the wild habitat regarding the flora and 
fauna, remove the excess of nutritive substances and other 
contaminated substances, shape the fluctuations of water 
temperature , maintain the reloading flux and the baseline 
flux of groundwater towards running water, stabilize the 
banks and have effective control upon floods. 
10 
Due to newly created wetlands in the river sector 
where ecotechnical methods have been applied, the initial 
flow Q will be approximately the same as Q ', the flow of 
the particular sector (fig.1.4). If the water level passes over 
newly created wetlands, the rate of flow in the selected 
layer sector is less than the rate of flow before the layer 
11
sector chosen for reconditioning because layers surfacing 
in order to build riparian areas (fig.1.3) and due to the 
impact of water with newly created wetlands. If the water 
level does not pass over newly created wetlands, the rate 
of flow in the selected layer is higher than the previous 
rate of flow when the layer sector was chosen for 
reconditioning. The newly created wetlands both 
functional and riparian can resist the drought on a 
relatively large period of time providing habitat for the 
lotic fauna. 
Where is possible, the wetlands should be 
correlated with riparian areas because together with, by 
their multiple features, they considerably improve the 
ecological valence of the newly created ecosystem, as well 
as the layer sector adjacent areas chosen for the 
application of the presented method. 
1.1 The ecotechnical method of directioning the 
water laterally within the layer and of creating the 
area on the side of minor rectangular-shaped layer. 
The presented ecotechnical method can be applied 
on an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
A structure made of oxidation-resisting metal and 
very resistant plastic (Fig. 1.1.1) can be symmetrically 
positioned regarding the center of rectangular layer of the 
selected river sector, providing space in the middle of the 
layer for ecological restoration. 
12 
This structure is dimensioned regarding the water 
flow Q, layer’s depth H, rectangular layer’s width L and 
the selected sector’s length l. 
After fixing the metal structure for redirecting the 
water towards the centre of the selected layer, some 
arrangements within the metal or very resistant plastic 
systems of 1 and 3cm thicknesses, can be performed by 
hydraulic or normal excavation on mobile bridges 
positioned on the selected layer sector is performed in 
order to plant hydrophilic plants (reed, bulrush, sallow, cat 
tail, alder, aquatic plants etc.) in order to create performing 
wetlands. Plants are selected according to the local clime 
and, also, according to the necessities of new created 
ecosystem. The metallic structure is facilitating the 
physical building of an ecosystem, directly, and helps the 
plants to grow fast. After planting and growth, inside a 
new created wetland, of 50% of herby aquatic flora 
biomass and 20% of ligneous biomass which just set the 
radicular mass giving signs of development, the water 
shall be set free percentually through the dams created by 
the junction area of the metal structures frameworks with 
the selected watercourse for environmental restoration. 
The metallic systems dimensioning is performed in 
proportion to the slope ≈ 1 ‰, structure of layer along the 
banks, granulometric structure of a layer, therefore 
biotope, the amount of biomass necessary to the proper 
functioning of the ecosystem, etc. Due to newly created 
wetlands (fig. 1.1.2) in the river sector where ecotechnical 
methods have been applied, the initial flow Q will be 
approximately the same as Q ', the flow of the particular 
sector. 
13
If the water level passes over newly created 
wetlands, the rate of flow in the selected layer sector is 
less than the rate of flow before the layer sector chosen for 
reconditioning because layers surfacing in order to build 
riparian areas. If the water level does not pass over newly 
created wetlands, the rate of flow in the selected layer is 
higher than the previous rate of flow when the layer sector 
was chosen for reconditioning. The newly created 
wetlands both functional and riparian can resist the 
drought on a relatively large period of time. 
14 
15
16 
2. Method of layer drilling and terraces performance 
for riparian areas. 
In case of mountain rivers, which generally have a 
good ecological condition because of the lack of the 
anthropogenic item, the banks erosion and powerful floods 
destroy the habitat of many aquatic inhabitants and create 
great damages to the people. That is why I proposed to 
apply this method (fig.2.1) on water courses in Romania 
and beyond. 
17
18 
The method consists in carrying out circular 
drilling in the river layer in order to reduce the rate of flow 
into the layer of the river, to take the surplus of water from 
the wave of flood and create refuge platforms for many 
aquatic inhabitants. The circular drilling performed into 
the layer is done according to river flow: for a rate of flow 
of 4 m³/s the radius of drilling is about 1m, the thickness 
between 0.10 m and 0.20 m, for a rate of flow of 3 m³/s 
the resulting radius of drilling is about 0.80 m, the 
thickness between 0.10 meters and 0.20 meters, for a rate 
of flow of 2 m³/s the radius of drilling is approximately 
0.50 m, the thickness is between 0.10 meters and 0.05 m. I 
gave some examples to better understand how these 
operations of drilling into the layer should be 
dimensioned. Given that the layers of watercourses in the 
mountain regions are so different morphologically, the 
size of these drillings will be finally set only depending on 
the local conditions. 
19
On the bank where the drillings into the layer have 
not been made, terraces will be built in order to create 
riparian areas. (Fig. 2.2). These terraces are effective in 
many cases: control the erosion by the means of sediments 
transport and distribution regularization, increase water 
quality, produce organic matter for aquatic habitats and 
ensure the wild habitat for flora and fauna, eliminate the 
excess of nutritional substances and other contaminated 
substances, shape the fluctuations of water temperature, 
maintain the flux of recharging and the base flux of 
groundwater towards water flowing, stabilize the banks 
and have control over the floods. 
So those three important issues the mountain rivers 
are facing with caused by strong floods and accidental 
pollution (damaged properties, devastation of habitats, 
water contamination) can largely be solved if we put into 
effect the following method: Method of layer drilling 
and terraces performance for riparian areas. 
The riparian people must understand that the 
method no 2 implies lower costs than the classic methods 
of diking that it has a greater efficacy against floods than 
the classic methods, it provides to the layer a natural 
touristic aspect, create and maintain a functional 
ecosystem, a real antipollution firewall for everyone. 
20 
3. Derivation method of the water flow through 
parallel channels and building the bridge over the 
selected sector, as support for increasing the 
hydrophilic vegetation 
The presented ecotechnical method can be applied on 
an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
21
Before building the biotope bridge, which will 
support the land for the growth of hydrophilic massive 
vegetation, quantity of water must be directed through two 
rectangular channels which encompasses half-and-half 
around 10% of the river flow in the sector that will be 
restored (Fig. 3.1). The two channels with q1 and q2 rate 
flow are made for several reasons: 
- if there is no q1 and q 2 , the biotope 
bridge will restrict the flow Q, and in case 
of strong flood, it will be destroyed with 
all the ecosystem created. 
- being less than Q, the flow Q’ may be 
much cleaned of hydrophilic vegetation. 
- due to the lateral drilling inside of those 
two parallel channels, wetlands and 
riparian areas benefic for the watercourse 
are achieved, as it is known. 
After banks consolidation and leveling by the 
means of excavators and other equipment, and after fixing 
the bridge biotope which is a steel inoxidable structure of 
grating welded longitudinally and transversally forming 
rectangles of about 0.05 x0, 08m between them, on a 
metallic foundation, and after fixing the land on the bridge 
by the means of longitudinal profiles made of inoxidable 
metal welded on the metallic structure of the bridge, 
hydrophilic vegetation adaptable for that area shall be 
plant (fig.3.2). 
22 
The sustaining support of the biotope bridge is 
clamped to the layer by the means of a dowels system and 
it is made of inoxidable metallic material as the bridge, 
built of perpendicular welded grating that form rectangles 
of about 0.05 x0, 08m, particularly made so as not to 
inhibit the growth of radicular mass of the planted 
hydrophilic vegetation. The biotope bridge will be 
provided with rectangular metallic windows. Throughout 
the length of the bridge support pillars must be established 
in order not to collapse because of the weight of soil and 
vegetation. This bridge is dimensioned regarding the water 
flow Q, layer’s depth H, rectangular layer’s width L and 
the selected sector’s length l, the supporting soil mass and 
environment conditions. The average slope of the 
watercourse must be of ≈ 1 ‰. The structural 
dimensioning of the biotope bridge is done by a static 
calculation, depending on the mass of soil that presses 
uniformly on the metal structure. 
For example, for 100m metallic bridge, with 4m 
opening and 1m height, some windows of about 0.05 x0, 
5m shall be placed in the centre, symmetrically, regarding 
the bridge centre, any three meters at 1/3 of the sustaining 
support of the metallic structure. The windows will be 
designed related to the bridge size as well as the outside 
brightness. The hydrophilic vegetation, which is adaptable 
to the area in question, is taken from wetlands and riparian 
areas. This has ecosystemical functionality and is planted 
on the bridge of steel structure in order to create an aquatic 
miniecosystem like "the mangrove forest." 
23
In addition to protecting wildlife, soil 
sedimentation, protection against erosion, conservation of 
biological diversity, the mangrove forest, also, constitutes 
a natural filter, through its “aerial” roots, against pollution 
caused by organic substances, heavy metals, chemical 
fertilizers and particulate matter. In the newly formed 
ecosystem, the roots of hydrophilic trees, which are to be 
planted over 20% of their natural size, with time (several 
years), will enter through the grids of the metallic bridge 
into the selected sector of the river layer and into the 
banks of the layer sector. Inside this small forest, various 
species of obsolescent birds and animals may live and rest. 
Under the bridge, inside the water, a similar natural 
habitat like the one into the watercourses, benefic for 
the ihtiofauna shall be created, where species protected 
by law and properly developed hydrophilic vegetation 
can be found. 
Besides the fact that this method leads to the 
creation of an ecosystem as a natural filter against 
pollution of any kind, dissipater against floods, banks 
stabilizer, it also represents a way of biomass creation and 
protection which will belong to the river sector selected 
for the research but to all limitrophe areas of this river 
sector. The robustness of this work as well as the low costs 
in comparison with classical methods of environmental 
protection, in my opinion, makes this ecotechnical method 
became an effective support for the aquatic and riparian 
ecosystems. 
24 
25
4. The method of creating parallel channels with 
wetlands areas. 
The presented ecotechnical method can be applied 
on an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
26 
The river flow must be directed through two 
rectangular channels, each of them having a capacity of 
10% of the layer sector flow, which is going to be restored 
(fig.4.1). The two channels with flows q1 and q2 are built 
for several reasons: 
- water filtration within the three areas 
- creating a performing riparian area 
Within the channels, two pools which are shared 
by three or more biomass ecological lanes (wetlands) 
composed of hydrophilic plants (name of the plants) used 
as filter for water, are built. 
The method of creating parallel channels with 
wetlands lanes is a modern ecological method that, besides 
acting like an efficient filter regarding the contaminated 
water, it is also acting like a floods dissipater. The 
compact lanes consisted of vegetation facilitate the growth 
of aquatic flora and fauna because of the water quality: for 
example: the last basin is habitat for ihtiofauna which 
disappeared from the watercourse or is about disappearing. 
The method is effective, generally, for the 3rd quality of 
water. Many aquatic birds may live into these basins. 
A new functional ecosystem consisting of water, 
wetlands and riparian areas, extremely useful for the areas 
with less biomass, is to be created. 
27
5. Creating wetlands into the minor layer by successive 
meandering. 
The presented ecotechnical method can be applied 
on an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
28 
In the selected sector, two parallel side channels 
that will take over almost all rate of flow from the studied 
sector shall be created in order to perform the ecological 
restoration. After the lateral channels will have been 
developed and will have been in service, the old layer of 
the river sector where the water flows not longer, will be 
filled with earth having the same physical-chemical 
qualities in order to create a rectangular compact belt 
where mixed areas of riparian forests and wetlands shall 
be created (fig 5.1). 
Wetlands are an important habitat for fish and 
mollusks, water birds and a large number of animals, and 
for many plants, insects and other inhabitants contribute to 
maintaining the quality of water, filter the pollutants, 
retain the sedimentary material, oxygenate the water by a 
rich vegetation, absorb the nutrients (nitrogen, 
phosphorus, etc.), recycle them or, regulate the 
microclimate, contribute to preventing floods, erosion, 
aquifer reloading, water supplies. The riparian areas shape 
the fluctuations of water temperature, maintain the flux of 
recharging and the base flux of groundwater towards water 
flows, stabilize the banks and have control over the floods. 
Taking into account the functions of wetlands and riparian 
areas listed above I proposed this method which facilitates 
a direct collaboration between riparian areas and wetlands 
by creating a performing and auto-functional ecosystem. 
The main and secondary water supply channels which 
capture 20% of the maximum flow Q of a river sector, 
maintain the functionality of riparian-wetlands areas. (fig 
5.1). 
29
The components of this method of ecological 
restoration are dimensioned regarding the water flow Q, 
layer’s depth H, rectangular layer’s width L and the 
selected sector’s length l. The hydrophilic vegetation 
(alders, sallow, bushes and semi-aquatic grass, etc.), that 
are to be used for creating riparian areas and wetlands, 
must be perfectly adaptable to the area. This newly created 
ecosystem will be a rest area for birds of passage; some of 
them are protected by law. Thus the wetlands and the 
riparian areas successfully replace the artificial structures 
built with high and non-functional expenses. 
After the recent big floods in Romania and not 
only, the big floods cannot be totally counter-balanced by 
the lake accumulation, dams, watercourses recalibration, 
check dams, watercourses concreting etc. The only 
solution can be an engineering project about 
environmental principles in order to strive towards an 
ecological arrangement of watercourses. Without having 
the necessary information about ecological principles, 
nobody will be able to perform a sustainable and efficient 
construction. The Nature’s reaction regarding the 
destructive offensive of people will find the necessary 
means to protect its ecosystems or to create new ones, 
affecting the ample hydrotechnical construction, so their 
existence and humans’ also. Those consequences are valid 
for all anthropogenic construction. 
30 
6. The method of layer’s ecologizing by the means of a 
metallic structure similar to the biotope bridge’s 
structure from extent no 3. 
The presented ecotechnical method may be applied 
on an anthropogenic or natural channel, concreted and 
unconcreted, with a varied form of layer, not necessarily 
rectangular or trapezoidal, which is located on a hill or 
plain from various parts of the Earth. 
This method is effective, also, for the concreted or 
paved water courses in North-West Europe which transit 
different cities. 
31
A metallic inoxidable structure of grating welded 
longitudinally and transversally forming rectangles of 
about 0.05 x0, 08m between them, is created. In case of 
unconcreted river sectors having a layer with an 
unadequate geometrical shape, then the shape of layer will 
be changed by the means of excavators of other 
mechanisms for drilling in order to create metallic 
structures easier (fig6.1). On this steel structure, a layer of 
aquatic soil shall be fixed by the means of an inoxidable 
wire system; the layer thickness will be set according to 
the layer’s opening and rate of flow, and various aquatic 
plants resistant to depollution but also to redress the 
zoobentos in the, shall be fixed, also will lead to creation 
of some fish species. These aquatic plants will act as a 
filter. The metallic structure having 1 to 3 cm thickness, 
will be introduced and fixed into the layer after the 
hydrophilic vegetation will have reached 50% of maturity. 
The 50% growth of the vegetation is valid only for 
nonligneous plants (aquatic grass, reeds, etc.). For 
hydrophilic ligneous plants (alders, sallow etc.) 20% of 
maturity is available, where the most important aspect is 
related to fixing and development of the radicular mass. 
Besides the inoxidable wire net, the radicular systems, 
also, includes the soil mass. The hydrophilic ligneous 
vegetation (alder, sallow etc.) will be planted by the end of 
the lower base of the cross-sectional wet perimeter and 
into the minor layer, too (fig 6.3). The ecological 
preparation of the layer sector which is to be renaturated 
(that means hydrophilic ligneous vegetation shall be plant 
into the soil surface), will be performed in a place fairly 
close to that sector. 
32 
Soil will be fixed on the inoxidable metal structure 
by an inoxidable net wire (fig 6.2). That upstream side of 
the net that encompasses soil will be protected against the 
water flow by an inoxidable metallic support welded 
together with the metal structure. 
After work completion, the water layer must be 
0.01 to 0.02 m over ground level inside the metallic 
framework. The land dimensioning will be made 
depending on the average level of the water, slope, flow 
and rate of flow in the sector. This method is applied for 
the layer sectors with housing construction and patrimony, 
which are very close to the river banks and that can not be 
moved in case the water courses can not be changed. 
33
7. Performing passage areas between different flow 
sectors of watercourse and the old channels of the 
river. 
The presented ecotechnical method can be applied 
on an anthropogenic or natural channel, without concrete, 
situated on a hill or plane surface of different areas on the 
Planet. 
There are a variety of stagnant water channels and, 
also, of water flowing channels along water courses. 
Water quality of rivers can be improved through such 
channels by connecting them to water courses. This 
method shows a way to make the connection between the 
watercourse and the stagnant/running water channels, with 
the completion of operation of the new ecosystem created. 
The lentic channel has no direct connection with the new 
sector. This is supplied with water through underground 
springs and rain water (Fig 7.1). It is necessary to create a 
lotic system for water circulation in the lentic channel. 
This is achieved through a breach located downstream, 
where the bank separates the watercourse from the 
stagnant water channel. The connection between 
watercourse and lentic channel must be performed by 
means of durable plastic pipes which are to be fixed into 
the soil between river layer that needs restoration and the 
lentic channel.Before fixing the plastic pipes ot tubes into 
the ground which separates the the lentic channel with 
stagnant water, the ground is pulled so that the pipes are 
covered with 0.20 m and 0.50 m of soil. 
34 
The soil thickness should be taken into account the 
soil morphology and the possibility of maintaining water 
so as to create riparian areas and wetlands. The water will 
enter through channels’ batteries simultaneously with the 
penetration of water into the breach created on the bank. 
Riparian areas and the wetlands, that are to be 
formed after water flow goes over the top inside the sector 
layer selected for restoration, will function as real filters 
and stabilize the banks, both for the layer of the old 
channel and for the layer of the river chosen for study. The 
plastic pipes inside the connection channels, are designed 
according to the necessary quantity of water inside a 
stagnant water channel. Batteries of plastic pipes, 
according to the size and structure of the transited soil, are 
fitted with holes to create performing wetland, even a 
riparian area above them, consisted in grass and shrubs, 
water trees (examples for the temperate zone). 
Through plastic pipe holes the water will be 
extended across the entire mass of ground by leaking, 
infiltration and capillarity. One side of the pipes is put 
inside the layer, at the minimum level of river water and 
the other side is placed inside the stagnant water channel, 
throwing out the water captured from the river layer.(fig 
7.2). The pipes’ holes are linearly disposed on eight 
directions in order to occupy a large of groundwater 
irrigation. A wetland for protection against communal and 
municipal discharges is created on the right side of 
stagnant water channel by leveling the banks. Through 
conducts or connecting pipes will flow almost the same 
rate of flow as through the breach. 
35
The water flow average should be of 1 ‰. Qb ≈ 
nq, where n is the number of connecting pipes between the 
sector selected for restoration and the stagnant water 
channel. 
The ecotechnical systems are dimensioned 
regarding the water flow Q, rate of flow V, layer’s depth 
H, rectangular layer’s width L and the selected sector’s 
length l, the size of stagnant water channel and the 
environmental conditions. 
36 
37
8. The method for changing the shape of a river sector 
banks in order to create new ecosystems. 
There are many situations where the banks of 
rivers doe not favor the growth of vegetation, do not 
protect people against floods and where the ihtiofauna can 
not move, laterally or longitudinally, in case of pollution. 
Therefore, by the means of ecotechniques, the banks of 
rivers will be shaped and transformed into environmental 
banks in order to be able to bear ecosystems created by 
wetlands and riparian areas. In this case, a study upon the 
layer sector where the banks are totally inefficient both 
ecologically and engineerically regarding the protection 
against floods is elaborated. 
38 
On the right bank of the river is a small quantity of 
hydrophilic and completely inefficient vegetation for the 
bank establishment in order to act as a filter for the 
polluted water and as habitat for various hydrophilic 
inhabitants. The left bank of the river has no vegetation, is 
gnawed and does not resist in case of major floods. 
In this situation, the right bank must be built in 
terraces of height h 'and length l' as shown in (fig.8.2) in 
order to form a wetland and a riparian area controlling soil 
erosion through the regularization of sediments transport 
and distribution, enhancing the quality of water, producing 
organic matter for aquatic habitats and providing wild 
habitat for flora and fauna, eliminating the excess of 
nutritional substances and other contaminated substances, 
modeling the fluctuations of water temperature, 
maintaining the recharging and basic flux of groundwater 
towards running water, stabilizing the banks and 
controlling the floods. After building the terraces on the 
bank, a plastic support for a strong sustaining of the banks 
and the planted hydrophilic vegetation, is fixed. The left 
bank has not so much place for remodeling, therefore, 
where is possible, we can extend it regarding the average 
level of water and the layer’s width, so we will do it 
vertically. Inside the layer, where the extension has been 
performed, some dissipaters shall be mounted for each 
meter and the newly created bank will be protected by 
wooden fascines. 
39
After remodeling, the initial width L of the layer 
sector becomes width L '. Flow will be the same as Q but 
V will become smaller - V'- according to the flow 
functional parameters. 
40 
The above-mentioned methods are available because: 
- New functional and useful ecosystems are built 
for areas without many biocenotic values. 
- Confers an excellent habitat for various species 
of flora and fauna that have migrated or lived in 
newly created ecological areas. 
- After environmental restoration the groundwater 
quality will be improved and useful for riverain 
people and more. 
- The natural aesthetic aspect that encourages the 
organized tourism will have other values. 
41
- Beside the classical improvement of river water 
(cleaning, treatment), the methods listed above 
imply much lower costs. 
Very important to know: 
- The restored ecological zones must be 
immediately designated as areas SPA 
(avifaunistic protection areas) and SCI (areas of 
communitarian interest). 
- The development local fauna and flora must be 
carefully surveilled. 
- Drastic measures must be taken for those who 
fail to comply with environmental law. 
- In case of proper conditions, the ecological 
restoration of water course must be performed 
in order to recover and make operational the 
local ecobiomes. 
- The ecosystemic energy system should be 
maintained by creating new ecosystems. 
42 
Concluzii 
ConŃinutul acestei cărŃi arată prin exemple 
concrete, că râurile care reprezintă de fapt suportul vieŃii 
pot fi restaurate dând o undă de speranŃă florei si faunei 
acvatice si semiacvatice. DispariŃia niselor ecologice din 
cauza impactului antropic asupra ecosistemelor de orice 
fel, a dus la dispariŃia funcŃionalităŃii trofice deci la 
dispariŃia biocenozelor din cadrul ecosistemelor lăsând 
biotopurile nefuncŃionale. Cu ajutorul metodelor 
prezentate se crează miniecosisteme funcŃionale, 
adevărate generatoare ecologice, care vor duce la crearea 
funcŃionalităŃii locale si apoi globale a reŃelei 
ecobiomurilor din cadrul bazinelor hidrografice.Ceea ce 
am prezentat sunt doar cateva dintre metodele ce pot fi 
aplicate, dar în funcŃie de condiŃiile locale pot realiza si 
alte metode de restaurare ecologică a sectoarelor 
cursurilor de apă. łin să precizez, că în cărŃile mele, am 
încercat să scot in evidenŃă importanŃa gândirii ecologice 
prin crearea metodelor de restaurare ecologică a 
cursurilor de apă. Este necesar, acolo unde sunt condiŃii, 
ca sectorul de albie reconstruit, adică ecosistemul să nu 
fie izolat ci să stabilească legături si cu alte ecosisteme pe 
cursul râului, astfel încât acestea să formeze un ecobiom 
local progresiv funcŃional. 
Ecotehnia, bazându-se pe principii solide 
ecologice direcŃionează alte stiinte către perceperea si 
folosirea principilor naturale cu schimburi energetice 
funcŃionale benefice pentru mediul înconjurător, cu 
consumarea minimă a combustibililor fosili sau a altor 
resurse naturale. 
43
Închei, cu încrederea că, cititorii mei, unii mult 
mai profesionisti decât mine în domeniul ecotehniei, dar 
si alŃii din multe alte domenii stiinŃifice si nu numai, vor 
fi responsabili,vor înŃelege si vor veni cu soluŃii viabile în 
vederea păstrării măcar în condiŃiile actuale ale mediului 
înconjurător pentru generaŃiile viitoare. 
Conclusion 
The content of this book shows, by concrete 
examples, that the rivers which, actually represent the life 
support, can be restored by giving a hope for aquatic and 
semi-aquatic flora and fauna. Disappearance of ecological 
niches because of the anthropogenic impact upon 
ecosystems of any kind, led to the disappearance of 
trophic functionality , therefore, disappearance of 
biocenosis of the ecosystems leaving non-functional 
biotops. By the means of presented methods, it was 
possible to create functional miniecosystems, genuine 
ecological generators, which will lead to the creation of 
local and after global functionality of the ecobiomes 
network within the hydrographical basins. I have just 
presented some of the methods that can be applied, but, 
depending on local conditions, other methods of 
ecological restoration of watercourse sectors can be 
provided. 
44 
I would have to mention that, in my books, I tried 
to emphasis the importance of ecological thinking by 
creating ecological methods of watercourses restoration. It 
is necessary, where conditions are available, to rebuild the 
layer’s sector in order not to isolate the ecosystem but to 
maintain connections with other ecosystems along the 
river so that they form a local progressive functional 
ecobiome. 
Based on solid ecological principles, the 
ecotechniques is directing other sciences towards 
perception and use of natural principles along functional 
energetic exchanges beneficial to the environment, by a 
minimal consumption of fossil fuels and other natural 
resources. 
I conclude, having the confidence that my readers, 
some more professional in ecotechniques than me, but also 
others from many other scientific fields and not only, will 
be responsible, will understand and will come up with 
viable solutions in order to preserve at least the actual 
conditions of the environment for the future generations. 
Tipărit la: 
S.C. Nedea Print S.R.L., Bucuresti, 
Tel: 021-685.0514; Fax: 021-771.27.30 
Mobil: 0744.384.598 
E-mail: nedeaprint@hotmail.com 
All rights reserved 
45
ISBN: 978-973-0-05814-7

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Hydraulic structures and bioengineering for rivers!1

  • 1. Răzvan Voicu METODE ECOTEHNICE DE RESTAURARE ALE CURSURILOR DE APĂ ECOTECHNIC METHODS OF RESTORATIONING THE WATERCOURSES Bucuresti 2008
  • 2. Răzvan Voicu METODE ECOTEHNICE DE RESTAURARE ALE CURSURILOR DE APĂ ECOTECHNIC METHODS OF RESTORATIONING THE WATERCOURSES Dr.ing.Răzvan Voicu “Prin izvoarele lor munŃii îsi oglidesc istoria. ” “Through their sources the mountains reflect their history”
  • 3. rzvnvoicu@yahoo.com ISBN: 978-973-0-05814-7 Introducere Cartea de faŃă este realizată din respectul nemărginit pentru Natură, care are amabilitatea de a ne lăsa o planetă locuibilă prin care noi, oamenii, să putem explora Universul. DistanŃarea omului tot mai pronunŃată faŃă de Natură, din cauza egoismului si fugii lui după bani, a început să aducă o degradare continuă a ecosistemelor. Biosfera, a început să-si piardă din valenŃele ei ecologice tocmai datorită faptului că nu se Ńine cont de sistemele ei funcŃionale, reflectate în sistemele funcŃionale ale ecobiomurilor. Natura a realizat în timp diverse si performante reŃele ecologice, geologice, energetice, biologice , chimice, geografice etc, extrem de sensibile prin însăsi structura lor, sedimentate cu grijă de pilonul central al Universului: TIMPUL. Omul, încearcă prin diferite procedee, să extragă câte o componentă, deseori minusculă, din aceste structuri, neînŃelegând că prin fiecare componentă pierdută structurile biosferei dispar, conducând Terra către forma iniŃială unde viaŃa, asa cum este astăzi, nu putea exista. Cartea de faŃă, pledează prin metodele ei ecotehnice pentru o conlucrare rapidă pe plan global a diferitelor stiinŃe aparent intangibile. De fapt, aproape toate stiinŃele încearcă să descopere si să înŃeleagă principiile Universului. După cum veŃi vedea în această carte, conlucrarea benefică dintre ingineria costrucŃiilor hidrotehnice si ecologie, a dus la finalizarea teoretică a mai multor metode de restaurare ecologică aplicabile pe diverse sectoare ale cursurilor de pe întreaga suprafaŃă a Terrei.
  • 4. Ecotehnia, reprezintă o stiinŃă nou apărută, care determină o colaborare eficientă interdisciplinară între diverse domenii stiinŃifice, în scopul dezvoltării societăŃii umane pe principii ecologice, cu ajutor tehnologic divers.Viitorul omenirii va depinde de performanŃele ecotehniei. Metodele ecotehnice prezentate pot fi puse în practică dacă se respectă parametrii principali de proiectare, dacă există voinŃă politică, înŃelegere civică din partea riveranilor si nu numai si o conlucrare perfectă cu voinŃă de reusită din partea ambelor tabere stiinŃifice (ingineresti si ecologice). Această carte, scoate în evidenŃă importanta ecotehniei, un domeniu fără de care omenirea nu va avea sorŃi de izbândă. Introduction This book is written in respect in the immense honor of Nature, which has the kindness to leave us a habitable planet surface by the means of which, we, the people, can explore the Universe. The increased distance between human being and Nature, because of the selfishness and graspingness, has become a continuous degradation for the ecosystems. Biosphere began to lose its environmental valences just because the human does not take into account its operational systems, as reflected in the functional systems of ecobiomes. 4 In the course of time, nature has created various and performed ecological, geological, energetic, biological, chemical, geographical networks, and so on, having a very sensitive structure, carefully deposited by the central pillar of the Universe: TIME. The human being is trying, by the means of different processes, to extract one component, often minuscule, of these structures, not having been conscious that with each lost component the biosphere structures disappear, leading Earth to its original form where life as today, could not exist. This book is pleading by its ecotechnic methods for a globally quick collaboration of various sciences seemingly intangible. Actually, almost all science seeks to discover and understand the principles of the Universe. As you will see in this book, the advantageous co-working between the hydrotechnical building engineering of and ecology, has led to the theoretical completion of several methods for environmental restoration on various sectors of the courses on the entire surface of the Planet. Ecotechniques is a new science which determines an interdisciplinary and efficient cooperation between different scientific domains in order to develop the human society regarding the ecological principles, by various means of technology. The humans’ future depends on the ecotechniques performances. The presented ecotechnical methods can be practiced if the main parameters of design are followed, if there is any political will, civic comprehension of riverain people and not in the least a perfect co-operation between both scientific camps (engineering and ecologies). 5
  • 5. This book accentuates the importance of ecotechniques as a all- important domain without which the world would have no success. 1. The ecotechnical method for directioning the watercourse on the center of layer and of creating a rectangular wetland in the middle of the minor layer. The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. It can be symmetrically positioned regarding the center of rectangular layer of the selected river sector, two identical structures made of oxidation-resisting metal (Fig. 1.2) that, in their run, are symmetrically positioned towards the center of selected river sector. These structures are dimensioned regarding the water flow Q, layer’s depth H, rectangular layer’s width L and the selected sector’s length l. Inside metallic systems or structures of 1-3 cm thickness, excavation on mobile bridges positioned on the selected layer sector is performed in order to plant hydrophilic plants (reed, bulrush, sallow, cat tail, alder, aquatic plants etc.) in order to create performing wetlands. Plants are selected according to the local clime and, also, according to the necessities of new created ecosystem. The metallic structures are facilitating the physical building of an ecosystem, directly, and after the species of hydrophilic plants are planted, the metallic structures help them to grow fast. 6 After planting and growth, inside a new created wetland, of 50% of herby aquatic flora biomass and 20% of ligneous biomass which just set the radicular mass giving signs of development, the water shall be set free percentually through the dams created by the junction area of the metal structures frameworks with the selected watercourse for environmental restoration (Fig. 1.2). After removal of metallic structures with specialized equipment, the new created wetlands on the watercourse become higher with 5 to 15 cm (x) compared to the multiannual average level of water (d) before the environmental restoration (fig.1.1). The metallic systems dimensioning is performed in proportion to the slope ≈ 1 ‰, structure of layer along the banks, granulometric structure of a layer, therefore biotope, the amount of biomass necessary to the proper functioning of the ecosystem, etc. 7
  • 6. 8 Why do we want to create the wetlands on the selected river sectors that are extremely polluted primarily with organic matter and secondly metals? We know that wetlands: are an important habitat for fish and mollusks, water birds and a large number of animals, and for many plants, insects and other inhabitants contribute to maintaining the quality of water, filter the pollutants, retain the sedimentary material, oxygenate the water by a rich vegetation, absorb the nutrients (nitrogen, phosphorus, etc.), recycle them or, regulate the microclimate, contribute to preventing floods, erosion, aquifer reloading, water supplies, the production of timber, reeds and other exploitable plants, energy production (peat), offering areas for grazing, fishing, hunting, recreation, educational activities, scientific research and last but not least the wetlands have an aesthetic value to be appreciated. We know that a wetland slows the passage of water and increases the nutrients and sediments carried by flowing water, lodging sediments downstream may be blocking the water, reduce the force of rain and impede the floods down the river, by storing water in the soil or retain it at the surface, such as wetlands replaced advantageous hydrotechnical structures and not only, built at large expenses. After the development of wetlands within the new ecosystem, we can also create riparian areas by leveling the banks and planting some species of plants which are can adapt to those areas. 9
  • 7. The riparian areas are important ecologically for a variety of reasons: provide an erosion control through the regularization of transport and distribution of sediments, improve water quality, produce organic matter for aquatic habitats and ensure the wild habitat regarding the flora and fauna, remove the excess of nutritive substances and other contaminated substances, shape the fluctuations of water temperature , maintain the reloading flux and the baseline flux of groundwater towards running water, stabilize the banks and have effective control upon floods. 10 Due to newly created wetlands in the river sector where ecotechnical methods have been applied, the initial flow Q will be approximately the same as Q ', the flow of the particular sector (fig.1.4). If the water level passes over newly created wetlands, the rate of flow in the selected layer sector is less than the rate of flow before the layer 11
  • 8. sector chosen for reconditioning because layers surfacing in order to build riparian areas (fig.1.3) and due to the impact of water with newly created wetlands. If the water level does not pass over newly created wetlands, the rate of flow in the selected layer is higher than the previous rate of flow when the layer sector was chosen for reconditioning. The newly created wetlands both functional and riparian can resist the drought on a relatively large period of time providing habitat for the lotic fauna. Where is possible, the wetlands should be correlated with riparian areas because together with, by their multiple features, they considerably improve the ecological valence of the newly created ecosystem, as well as the layer sector adjacent areas chosen for the application of the presented method. 1.1 The ecotechnical method of directioning the water laterally within the layer and of creating the area on the side of minor rectangular-shaped layer. The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. A structure made of oxidation-resisting metal and very resistant plastic (Fig. 1.1.1) can be symmetrically positioned regarding the center of rectangular layer of the selected river sector, providing space in the middle of the layer for ecological restoration. 12 This structure is dimensioned regarding the water flow Q, layer’s depth H, rectangular layer’s width L and the selected sector’s length l. After fixing the metal structure for redirecting the water towards the centre of the selected layer, some arrangements within the metal or very resistant plastic systems of 1 and 3cm thicknesses, can be performed by hydraulic or normal excavation on mobile bridges positioned on the selected layer sector is performed in order to plant hydrophilic plants (reed, bulrush, sallow, cat tail, alder, aquatic plants etc.) in order to create performing wetlands. Plants are selected according to the local clime and, also, according to the necessities of new created ecosystem. The metallic structure is facilitating the physical building of an ecosystem, directly, and helps the plants to grow fast. After planting and growth, inside a new created wetland, of 50% of herby aquatic flora biomass and 20% of ligneous biomass which just set the radicular mass giving signs of development, the water shall be set free percentually through the dams created by the junction area of the metal structures frameworks with the selected watercourse for environmental restoration. The metallic systems dimensioning is performed in proportion to the slope ≈ 1 ‰, structure of layer along the banks, granulometric structure of a layer, therefore biotope, the amount of biomass necessary to the proper functioning of the ecosystem, etc. Due to newly created wetlands (fig. 1.1.2) in the river sector where ecotechnical methods have been applied, the initial flow Q will be approximately the same as Q ', the flow of the particular sector. 13
  • 9. If the water level passes over newly created wetlands, the rate of flow in the selected layer sector is less than the rate of flow before the layer sector chosen for reconditioning because layers surfacing in order to build riparian areas. If the water level does not pass over newly created wetlands, the rate of flow in the selected layer is higher than the previous rate of flow when the layer sector was chosen for reconditioning. The newly created wetlands both functional and riparian can resist the drought on a relatively large period of time. 14 15
  • 10. 16 2. Method of layer drilling and terraces performance for riparian areas. In case of mountain rivers, which generally have a good ecological condition because of the lack of the anthropogenic item, the banks erosion and powerful floods destroy the habitat of many aquatic inhabitants and create great damages to the people. That is why I proposed to apply this method (fig.2.1) on water courses in Romania and beyond. 17
  • 11. 18 The method consists in carrying out circular drilling in the river layer in order to reduce the rate of flow into the layer of the river, to take the surplus of water from the wave of flood and create refuge platforms for many aquatic inhabitants. The circular drilling performed into the layer is done according to river flow: for a rate of flow of 4 m³/s the radius of drilling is about 1m, the thickness between 0.10 m and 0.20 m, for a rate of flow of 3 m³/s the resulting radius of drilling is about 0.80 m, the thickness between 0.10 meters and 0.20 meters, for a rate of flow of 2 m³/s the radius of drilling is approximately 0.50 m, the thickness is between 0.10 meters and 0.05 m. I gave some examples to better understand how these operations of drilling into the layer should be dimensioned. Given that the layers of watercourses in the mountain regions are so different morphologically, the size of these drillings will be finally set only depending on the local conditions. 19
  • 12. On the bank where the drillings into the layer have not been made, terraces will be built in order to create riparian areas. (Fig. 2.2). These terraces are effective in many cases: control the erosion by the means of sediments transport and distribution regularization, increase water quality, produce organic matter for aquatic habitats and ensure the wild habitat for flora and fauna, eliminate the excess of nutritional substances and other contaminated substances, shape the fluctuations of water temperature, maintain the flux of recharging and the base flux of groundwater towards water flowing, stabilize the banks and have control over the floods. So those three important issues the mountain rivers are facing with caused by strong floods and accidental pollution (damaged properties, devastation of habitats, water contamination) can largely be solved if we put into effect the following method: Method of layer drilling and terraces performance for riparian areas. The riparian people must understand that the method no 2 implies lower costs than the classic methods of diking that it has a greater efficacy against floods than the classic methods, it provides to the layer a natural touristic aspect, create and maintain a functional ecosystem, a real antipollution firewall for everyone. 20 3. Derivation method of the water flow through parallel channels and building the bridge over the selected sector, as support for increasing the hydrophilic vegetation The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. 21
  • 13. Before building the biotope bridge, which will support the land for the growth of hydrophilic massive vegetation, quantity of water must be directed through two rectangular channels which encompasses half-and-half around 10% of the river flow in the sector that will be restored (Fig. 3.1). The two channels with q1 and q2 rate flow are made for several reasons: - if there is no q1 and q 2 , the biotope bridge will restrict the flow Q, and in case of strong flood, it will be destroyed with all the ecosystem created. - being less than Q, the flow Q’ may be much cleaned of hydrophilic vegetation. - due to the lateral drilling inside of those two parallel channels, wetlands and riparian areas benefic for the watercourse are achieved, as it is known. After banks consolidation and leveling by the means of excavators and other equipment, and after fixing the bridge biotope which is a steel inoxidable structure of grating welded longitudinally and transversally forming rectangles of about 0.05 x0, 08m between them, on a metallic foundation, and after fixing the land on the bridge by the means of longitudinal profiles made of inoxidable metal welded on the metallic structure of the bridge, hydrophilic vegetation adaptable for that area shall be plant (fig.3.2). 22 The sustaining support of the biotope bridge is clamped to the layer by the means of a dowels system and it is made of inoxidable metallic material as the bridge, built of perpendicular welded grating that form rectangles of about 0.05 x0, 08m, particularly made so as not to inhibit the growth of radicular mass of the planted hydrophilic vegetation. The biotope bridge will be provided with rectangular metallic windows. Throughout the length of the bridge support pillars must be established in order not to collapse because of the weight of soil and vegetation. This bridge is dimensioned regarding the water flow Q, layer’s depth H, rectangular layer’s width L and the selected sector’s length l, the supporting soil mass and environment conditions. The average slope of the watercourse must be of ≈ 1 ‰. The structural dimensioning of the biotope bridge is done by a static calculation, depending on the mass of soil that presses uniformly on the metal structure. For example, for 100m metallic bridge, with 4m opening and 1m height, some windows of about 0.05 x0, 5m shall be placed in the centre, symmetrically, regarding the bridge centre, any three meters at 1/3 of the sustaining support of the metallic structure. The windows will be designed related to the bridge size as well as the outside brightness. The hydrophilic vegetation, which is adaptable to the area in question, is taken from wetlands and riparian areas. This has ecosystemical functionality and is planted on the bridge of steel structure in order to create an aquatic miniecosystem like "the mangrove forest." 23
  • 14. In addition to protecting wildlife, soil sedimentation, protection against erosion, conservation of biological diversity, the mangrove forest, also, constitutes a natural filter, through its “aerial” roots, against pollution caused by organic substances, heavy metals, chemical fertilizers and particulate matter. In the newly formed ecosystem, the roots of hydrophilic trees, which are to be planted over 20% of their natural size, with time (several years), will enter through the grids of the metallic bridge into the selected sector of the river layer and into the banks of the layer sector. Inside this small forest, various species of obsolescent birds and animals may live and rest. Under the bridge, inside the water, a similar natural habitat like the one into the watercourses, benefic for the ihtiofauna shall be created, where species protected by law and properly developed hydrophilic vegetation can be found. Besides the fact that this method leads to the creation of an ecosystem as a natural filter against pollution of any kind, dissipater against floods, banks stabilizer, it also represents a way of biomass creation and protection which will belong to the river sector selected for the research but to all limitrophe areas of this river sector. The robustness of this work as well as the low costs in comparison with classical methods of environmental protection, in my opinion, makes this ecotechnical method became an effective support for the aquatic and riparian ecosystems. 24 25
  • 15. 4. The method of creating parallel channels with wetlands areas. The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. 26 The river flow must be directed through two rectangular channels, each of them having a capacity of 10% of the layer sector flow, which is going to be restored (fig.4.1). The two channels with flows q1 and q2 are built for several reasons: - water filtration within the three areas - creating a performing riparian area Within the channels, two pools which are shared by three or more biomass ecological lanes (wetlands) composed of hydrophilic plants (name of the plants) used as filter for water, are built. The method of creating parallel channels with wetlands lanes is a modern ecological method that, besides acting like an efficient filter regarding the contaminated water, it is also acting like a floods dissipater. The compact lanes consisted of vegetation facilitate the growth of aquatic flora and fauna because of the water quality: for example: the last basin is habitat for ihtiofauna which disappeared from the watercourse or is about disappearing. The method is effective, generally, for the 3rd quality of water. Many aquatic birds may live into these basins. A new functional ecosystem consisting of water, wetlands and riparian areas, extremely useful for the areas with less biomass, is to be created. 27
  • 16. 5. Creating wetlands into the minor layer by successive meandering. The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. 28 In the selected sector, two parallel side channels that will take over almost all rate of flow from the studied sector shall be created in order to perform the ecological restoration. After the lateral channels will have been developed and will have been in service, the old layer of the river sector where the water flows not longer, will be filled with earth having the same physical-chemical qualities in order to create a rectangular compact belt where mixed areas of riparian forests and wetlands shall be created (fig 5.1). Wetlands are an important habitat for fish and mollusks, water birds and a large number of animals, and for many plants, insects and other inhabitants contribute to maintaining the quality of water, filter the pollutants, retain the sedimentary material, oxygenate the water by a rich vegetation, absorb the nutrients (nitrogen, phosphorus, etc.), recycle them or, regulate the microclimate, contribute to preventing floods, erosion, aquifer reloading, water supplies. The riparian areas shape the fluctuations of water temperature, maintain the flux of recharging and the base flux of groundwater towards water flows, stabilize the banks and have control over the floods. Taking into account the functions of wetlands and riparian areas listed above I proposed this method which facilitates a direct collaboration between riparian areas and wetlands by creating a performing and auto-functional ecosystem. The main and secondary water supply channels which capture 20% of the maximum flow Q of a river sector, maintain the functionality of riparian-wetlands areas. (fig 5.1). 29
  • 17. The components of this method of ecological restoration are dimensioned regarding the water flow Q, layer’s depth H, rectangular layer’s width L and the selected sector’s length l. The hydrophilic vegetation (alders, sallow, bushes and semi-aquatic grass, etc.), that are to be used for creating riparian areas and wetlands, must be perfectly adaptable to the area. This newly created ecosystem will be a rest area for birds of passage; some of them are protected by law. Thus the wetlands and the riparian areas successfully replace the artificial structures built with high and non-functional expenses. After the recent big floods in Romania and not only, the big floods cannot be totally counter-balanced by the lake accumulation, dams, watercourses recalibration, check dams, watercourses concreting etc. The only solution can be an engineering project about environmental principles in order to strive towards an ecological arrangement of watercourses. Without having the necessary information about ecological principles, nobody will be able to perform a sustainable and efficient construction. The Nature’s reaction regarding the destructive offensive of people will find the necessary means to protect its ecosystems or to create new ones, affecting the ample hydrotechnical construction, so their existence and humans’ also. Those consequences are valid for all anthropogenic construction. 30 6. The method of layer’s ecologizing by the means of a metallic structure similar to the biotope bridge’s structure from extent no 3. The presented ecotechnical method may be applied on an anthropogenic or natural channel, concreted and unconcreted, with a varied form of layer, not necessarily rectangular or trapezoidal, which is located on a hill or plain from various parts of the Earth. This method is effective, also, for the concreted or paved water courses in North-West Europe which transit different cities. 31
  • 18. A metallic inoxidable structure of grating welded longitudinally and transversally forming rectangles of about 0.05 x0, 08m between them, is created. In case of unconcreted river sectors having a layer with an unadequate geometrical shape, then the shape of layer will be changed by the means of excavators of other mechanisms for drilling in order to create metallic structures easier (fig6.1). On this steel structure, a layer of aquatic soil shall be fixed by the means of an inoxidable wire system; the layer thickness will be set according to the layer’s opening and rate of flow, and various aquatic plants resistant to depollution but also to redress the zoobentos in the, shall be fixed, also will lead to creation of some fish species. These aquatic plants will act as a filter. The metallic structure having 1 to 3 cm thickness, will be introduced and fixed into the layer after the hydrophilic vegetation will have reached 50% of maturity. The 50% growth of the vegetation is valid only for nonligneous plants (aquatic grass, reeds, etc.). For hydrophilic ligneous plants (alders, sallow etc.) 20% of maturity is available, where the most important aspect is related to fixing and development of the radicular mass. Besides the inoxidable wire net, the radicular systems, also, includes the soil mass. The hydrophilic ligneous vegetation (alder, sallow etc.) will be planted by the end of the lower base of the cross-sectional wet perimeter and into the minor layer, too (fig 6.3). The ecological preparation of the layer sector which is to be renaturated (that means hydrophilic ligneous vegetation shall be plant into the soil surface), will be performed in a place fairly close to that sector. 32 Soil will be fixed on the inoxidable metal structure by an inoxidable net wire (fig 6.2). That upstream side of the net that encompasses soil will be protected against the water flow by an inoxidable metallic support welded together with the metal structure. After work completion, the water layer must be 0.01 to 0.02 m over ground level inside the metallic framework. The land dimensioning will be made depending on the average level of the water, slope, flow and rate of flow in the sector. This method is applied for the layer sectors with housing construction and patrimony, which are very close to the river banks and that can not be moved in case the water courses can not be changed. 33
  • 19. 7. Performing passage areas between different flow sectors of watercourse and the old channels of the river. The presented ecotechnical method can be applied on an anthropogenic or natural channel, without concrete, situated on a hill or plane surface of different areas on the Planet. There are a variety of stagnant water channels and, also, of water flowing channels along water courses. Water quality of rivers can be improved through such channels by connecting them to water courses. This method shows a way to make the connection between the watercourse and the stagnant/running water channels, with the completion of operation of the new ecosystem created. The lentic channel has no direct connection with the new sector. This is supplied with water through underground springs and rain water (Fig 7.1). It is necessary to create a lotic system for water circulation in the lentic channel. This is achieved through a breach located downstream, where the bank separates the watercourse from the stagnant water channel. The connection between watercourse and lentic channel must be performed by means of durable plastic pipes which are to be fixed into the soil between river layer that needs restoration and the lentic channel.Before fixing the plastic pipes ot tubes into the ground which separates the the lentic channel with stagnant water, the ground is pulled so that the pipes are covered with 0.20 m and 0.50 m of soil. 34 The soil thickness should be taken into account the soil morphology and the possibility of maintaining water so as to create riparian areas and wetlands. The water will enter through channels’ batteries simultaneously with the penetration of water into the breach created on the bank. Riparian areas and the wetlands, that are to be formed after water flow goes over the top inside the sector layer selected for restoration, will function as real filters and stabilize the banks, both for the layer of the old channel and for the layer of the river chosen for study. The plastic pipes inside the connection channels, are designed according to the necessary quantity of water inside a stagnant water channel. Batteries of plastic pipes, according to the size and structure of the transited soil, are fitted with holes to create performing wetland, even a riparian area above them, consisted in grass and shrubs, water trees (examples for the temperate zone). Through plastic pipe holes the water will be extended across the entire mass of ground by leaking, infiltration and capillarity. One side of the pipes is put inside the layer, at the minimum level of river water and the other side is placed inside the stagnant water channel, throwing out the water captured from the river layer.(fig 7.2). The pipes’ holes are linearly disposed on eight directions in order to occupy a large of groundwater irrigation. A wetland for protection against communal and municipal discharges is created on the right side of stagnant water channel by leveling the banks. Through conducts or connecting pipes will flow almost the same rate of flow as through the breach. 35
  • 20. The water flow average should be of 1 ‰. Qb ≈ nq, where n is the number of connecting pipes between the sector selected for restoration and the stagnant water channel. The ecotechnical systems are dimensioned regarding the water flow Q, rate of flow V, layer’s depth H, rectangular layer’s width L and the selected sector’s length l, the size of stagnant water channel and the environmental conditions. 36 37
  • 21. 8. The method for changing the shape of a river sector banks in order to create new ecosystems. There are many situations where the banks of rivers doe not favor the growth of vegetation, do not protect people against floods and where the ihtiofauna can not move, laterally or longitudinally, in case of pollution. Therefore, by the means of ecotechniques, the banks of rivers will be shaped and transformed into environmental banks in order to be able to bear ecosystems created by wetlands and riparian areas. In this case, a study upon the layer sector where the banks are totally inefficient both ecologically and engineerically regarding the protection against floods is elaborated. 38 On the right bank of the river is a small quantity of hydrophilic and completely inefficient vegetation for the bank establishment in order to act as a filter for the polluted water and as habitat for various hydrophilic inhabitants. The left bank of the river has no vegetation, is gnawed and does not resist in case of major floods. In this situation, the right bank must be built in terraces of height h 'and length l' as shown in (fig.8.2) in order to form a wetland and a riparian area controlling soil erosion through the regularization of sediments transport and distribution, enhancing the quality of water, producing organic matter for aquatic habitats and providing wild habitat for flora and fauna, eliminating the excess of nutritional substances and other contaminated substances, modeling the fluctuations of water temperature, maintaining the recharging and basic flux of groundwater towards running water, stabilizing the banks and controlling the floods. After building the terraces on the bank, a plastic support for a strong sustaining of the banks and the planted hydrophilic vegetation, is fixed. The left bank has not so much place for remodeling, therefore, where is possible, we can extend it regarding the average level of water and the layer’s width, so we will do it vertically. Inside the layer, where the extension has been performed, some dissipaters shall be mounted for each meter and the newly created bank will be protected by wooden fascines. 39
  • 22. After remodeling, the initial width L of the layer sector becomes width L '. Flow will be the same as Q but V will become smaller - V'- according to the flow functional parameters. 40 The above-mentioned methods are available because: - New functional and useful ecosystems are built for areas without many biocenotic values. - Confers an excellent habitat for various species of flora and fauna that have migrated or lived in newly created ecological areas. - After environmental restoration the groundwater quality will be improved and useful for riverain people and more. - The natural aesthetic aspect that encourages the organized tourism will have other values. 41
  • 23. - Beside the classical improvement of river water (cleaning, treatment), the methods listed above imply much lower costs. Very important to know: - The restored ecological zones must be immediately designated as areas SPA (avifaunistic protection areas) and SCI (areas of communitarian interest). - The development local fauna and flora must be carefully surveilled. - Drastic measures must be taken for those who fail to comply with environmental law. - In case of proper conditions, the ecological restoration of water course must be performed in order to recover and make operational the local ecobiomes. - The ecosystemic energy system should be maintained by creating new ecosystems. 42 Concluzii ConŃinutul acestei cărŃi arată prin exemple concrete, că râurile care reprezintă de fapt suportul vieŃii pot fi restaurate dând o undă de speranŃă florei si faunei acvatice si semiacvatice. DispariŃia niselor ecologice din cauza impactului antropic asupra ecosistemelor de orice fel, a dus la dispariŃia funcŃionalităŃii trofice deci la dispariŃia biocenozelor din cadrul ecosistemelor lăsând biotopurile nefuncŃionale. Cu ajutorul metodelor prezentate se crează miniecosisteme funcŃionale, adevărate generatoare ecologice, care vor duce la crearea funcŃionalităŃii locale si apoi globale a reŃelei ecobiomurilor din cadrul bazinelor hidrografice.Ceea ce am prezentat sunt doar cateva dintre metodele ce pot fi aplicate, dar în funcŃie de condiŃiile locale pot realiza si alte metode de restaurare ecologică a sectoarelor cursurilor de apă. łin să precizez, că în cărŃile mele, am încercat să scot in evidenŃă importanŃa gândirii ecologice prin crearea metodelor de restaurare ecologică a cursurilor de apă. Este necesar, acolo unde sunt condiŃii, ca sectorul de albie reconstruit, adică ecosistemul să nu fie izolat ci să stabilească legături si cu alte ecosisteme pe cursul râului, astfel încât acestea să formeze un ecobiom local progresiv funcŃional. Ecotehnia, bazându-se pe principii solide ecologice direcŃionează alte stiinte către perceperea si folosirea principilor naturale cu schimburi energetice funcŃionale benefice pentru mediul înconjurător, cu consumarea minimă a combustibililor fosili sau a altor resurse naturale. 43
  • 24. Închei, cu încrederea că, cititorii mei, unii mult mai profesionisti decât mine în domeniul ecotehniei, dar si alŃii din multe alte domenii stiinŃifice si nu numai, vor fi responsabili,vor înŃelege si vor veni cu soluŃii viabile în vederea păstrării măcar în condiŃiile actuale ale mediului înconjurător pentru generaŃiile viitoare. Conclusion The content of this book shows, by concrete examples, that the rivers which, actually represent the life support, can be restored by giving a hope for aquatic and semi-aquatic flora and fauna. Disappearance of ecological niches because of the anthropogenic impact upon ecosystems of any kind, led to the disappearance of trophic functionality , therefore, disappearance of biocenosis of the ecosystems leaving non-functional biotops. By the means of presented methods, it was possible to create functional miniecosystems, genuine ecological generators, which will lead to the creation of local and after global functionality of the ecobiomes network within the hydrographical basins. I have just presented some of the methods that can be applied, but, depending on local conditions, other methods of ecological restoration of watercourse sectors can be provided. 44 I would have to mention that, in my books, I tried to emphasis the importance of ecological thinking by creating ecological methods of watercourses restoration. It is necessary, where conditions are available, to rebuild the layer’s sector in order not to isolate the ecosystem but to maintain connections with other ecosystems along the river so that they form a local progressive functional ecobiome. Based on solid ecological principles, the ecotechniques is directing other sciences towards perception and use of natural principles along functional energetic exchanges beneficial to the environment, by a minimal consumption of fossil fuels and other natural resources. I conclude, having the confidence that my readers, some more professional in ecotechniques than me, but also others from many other scientific fields and not only, will be responsible, will understand and will come up with viable solutions in order to preserve at least the actual conditions of the environment for the future generations. Tipărit la: S.C. Nedea Print S.R.L., Bucuresti, Tel: 021-685.0514; Fax: 021-771.27.30 Mobil: 0744.384.598 E-mail: nedeaprint@hotmail.com All rights reserved 45