Water and waste water treatment systems of Vistino village - BASE Project - Implementation of the Baltic Sea Action Plan in Russia - helcom
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BASE Project - Implementation of the Baltic Sea Action Plan in Russia
Water and waste water treatment
systems of Vistino village
Photo: Harri Huhta/MTT
The report was prepared by the Marketing Agency MURKOT, St. Petersburg.
This report does not necessarily represent the views of HELCOM. HELCOM does not assume responsibility for
the content of the report.
Information included in this publication or extracts thereof are free for citation on the condition that the
complete reference of the publication is given as stated above.
Copyright 2014 Baltic Marine Environment Protection Commission HELCOM
1
Table of contents
1.DESCRIPTION OF THE TERRITORY ................................................................................................................ 5
1.1 Location of the territory on maps. ............................................................................................................ 5
1.2 Territory land tenure and condition of general plans ............................................................................... 7
1.3 Objects of natural and cultural heritage and protected areas.................................................................. 8
2. HYDROGRAPHY............................................................................................................................................ 9
2.1. Resources of underground waters ........................................................................................................... 9
2.2. Resources of surface waters .................................................................................................................. 10
3. DESCRIPTION OF EXISTING WATER SUPLLY AND SEWAGE SYSTEMS OF “VISTINO RURAL SETTLEMENT” 12
3.1. Main information about Vistino ............................................................................................................. 12
3.2. General characteristics of water supply and wastewater systems ........................................................ 13
3.2.1. Characteristics of the water supply network ...................................................................................... 14
3.2.2. Characteristics of the sewage network ............................................................................................... 14
3.2.3. Water consumption volume and wastewater volume ....................................................................... 16
3.2.4. Calculation of infiltration .................................................................................................................... 18
3.2.5. Balance of water supply and sewage systems .................................................................................... 20
3.2.6. Water intake and treatment facilities ................................................................................................. 21
3.2.7. Existing water supply and water treatment process ..................................................................... 22
3.2.8. Proposals for a water purification system ..................................................................................... 24
3.2.9. Waste water treatment facilities ........................................................................................................ 26
3.2.10. Suggestions for a waste treatment system. ...................................................................................... 33
4. FORECASTS OF DEVELOPMENT ............................................................................................................. 34
4.1 Forecast of development Vistino settlement.......................................................................................... 34
5. TECHNICAL SOLUTIONS AND PLANNING SCHEMES .............................................................................. 36
5.1. Drinking water sources ...................................................................................................................... 36
5.2 Suggestions for water supplay system .................................................................................................... 38
5.2.1. Technical description and basic parameters of the various options ............................................. 39
5.2.2. An assessment of the pipe network in need of refurbishment and recommended method of
reconstruction. .............................................................................................................................................. 39
5.2.3. Assessment of the risks and impacts of different options. ........................................................... 40
5.2.4. Comparison of different options in terms of cost and effect ........................................................ 41
6. GUIDELINES............................................................................................................................................ 44
7. CONCLUSIONS AND RECOMMENDATIONS ........................................................................................... 45
APPENDIX 1. Questionnaire .......................................................................................................................... 46
2
INTRODUCTION
This work was based on the technical specifications for the implementation of the survey of water supply
and water treatment, as well as wastewater and water treatment systems of Vistino village.
The objectives of this work is:
1. Rational providing consumers with water in sufficient quantity and quality solutions;
2. Ensure full diversion drains and cleaning them up to the standards of surface impoundment;
3. Conservation of natural water conditions and its protection from pollution and contamination.
PURPOSE OF WORK
1. The technical condition of the existing water treatment facilities and wastewater treatment .
1. Based on an assessment of the current situation ‐ how to find a technological solution to ensure the
quality of water treatment at household needs and domestic wastewater to achieve performance,
satisfying requirements Sanitary 2.1.4.1074‐01 "Drinking water hygiene requirements for water
quality of centralized drinking water supply. quality control " and SanPin 2.1.5.980‐00 " Hygienic
requirements for surface water " respectively.
2. Determining the possibility of using existing structures of buildings for accommodation and
operation of technological equipment. Consideration of possible options for the location of
treatment facilities.
3. Justification of the most appropriate choice of water treatment plants and their locations.
4. Determining the status of the existing water supply and sanitation, in order to identify areas
requiring full or partial replacement. Trace analysis of networks to determine whether the schema
change water and sewage networks and adding new sections of pipeline.
5. Justification most appropriate option trace networks and renovation sites.
SCOPE OF WORK
Water system. sewage Treatment Plants
1. Description of the current situation of water intake and water treatment systems ;
2. Assess the effectiveness of existing treatment facilities ;
3. Visual inspection of construction of the existing building WTP identifying and fixing defects;
4. A visual examination and documentation of existing engineering and manufacturing equipment to
the definition of suitability for use in the reconstruction of the WTP ;
5. Documentary examination of existing intake system and water purification ;
6. Selection of the optimal variant reconstruction WTP, with the selection of the main technological
equipment. Determining the cost of reconstruction of the enlarged by the proposed options;
7. Drawing conclusions on the results of the survey.
Water system. water supply network
1. Description of the current situation external water supply;
2. Analysis of the networks with the identification of sites for reconstruction;
3. Determine if it need to install new plumbing areas;
4. The final assessment of water supply networks in general proposals and selection of the optimal
variant of reconstruction and determination of the enlarged value;
5. Drawing conclusions on the results of the survey.
3
Drainage system . sewage Treatment Plants
1. Analysis of the current state of treatment facilities;
2. Identify sources of waste water , to determine the possibility of exclusion and localization effluent
analysis of chemical composition and quantity of waste generated;
3. Assess the effectiveness of existing treatment facilities on the following criteria: performance (
current and scheduled) , qualitative indicators of the chemical composition of the original and the
purified waste water , the state of operating units and assemblies , process technology necessary
compliance requirements;
4. Visual inspection of construction of the existing building WWTP identifying and fixing defects;
5. A visual examination and documentation of existing engineering and manufacturing equipment to
the definition of suitability for use in the reconstruction of WWTP;
6. Selection of the optimal variant reconstruction WWTP, with the selection of the main technological
equipment. Determining the cost of reconstruction of the enlarged by the proposed options;
7. Drawing conclusions on the results of the survey.
Drainage system. sewage network
1. Description of the current situation of external networks of wastewater;
2. Analysis of the networks with the identification of sites for reconstruction;
3. Determine if you need to install new drainage areas;
4. The final assessment in general water supply network proposals and selection of the optimal variant
of reconstruction and determination of the enlarged value;
5. Drawing conclusions on the results of the survey.
4
1.DESCRIPTION OF THE TERRITORY
1.1 Location of the territory on maps.
Vistino rural settlement is a municipality, a part of Kingiseppskiy district of Leningrad region of the Russian
Federation. Here we describe the village Vistino as part of Vistino rural settlement. Number of residents is
821 people. (Census of Population 2010. Rosstat).
Figure 1, 1A. Location of Municipality “Vistino rural settlement” at Baltic sea and Gulf of Finland.
Leningrad region — subject of the Russian Federation, located on the North‐West of the European part of
the country, part of the North‐West Federal District and the North‐West Economic Region.
Territory is about 83,908 km², which is 0.49% of the territory of Russia. For this parameter, the region is
ranked on the 39th position in the country. From the west to the east region reaches for 500 km, and the
longest distance from the north to the south is 320 km.
5
Population is about 1 763 924 people. (in accordance with data of 2014 year).
Borders:
from the north — Republic of Karelia
from the east — Vologda region
from the south‐east – Novgorod region
from the south — Pskov region
with St. Petersburg (semi‐enclave)
with European Union: from the west— Estonia and from the north‐west — Finland
From the west the territory is bordering with the Gulf of Finland.
Figure 2. Location of Municipality “Vistino rural settlement” and Kingiseppskiy Municipal District at
map of Leningrad region
Kingiseppskiy municipal district is located in the western part of Leningrad region.
District borders:
from the north‐west and north boundary runs along the shore of the Gulf of Finland;
from the east ‐ along the administrative border with Lomonosovskiy and Volosovskiy districts;
from the south ‐ along the administrative border with Slantsevskiy district;
from the west ‐ along the state border of the Russian Federation and Estonia.
Geographical location defines a special position of the Kingiseppskiy district in Leningrad region.
Almost half of the administrative boundaries of Kingiseppskiy district coincides with the state border of the
Russian Federation. The District borders with two countries of the European Union ‐ Estonia and Finland. The
border with Finland is exclusively marine. Kingiseppskiy District has the largest water area of the Gulf of
Finland in comparison with the others districts of Leningrad region. The district also includes islands located
there in. The largest of them ‐ Hogland, Greater and Lesser Tuters, Powerful (Lavensaari), Seskar and Small
(Penisaari).
6
The coastline is about 126 km. It runs along the Gulf of Narva, Koporskaya Bay and Luga Bay. Luga Bay is
suitable for navigation of large ships. This part of the Gulf of Finland has a short period of freeze‐up and the
depth is suitable for navigation that allows constructing large‐scale modern seaport. Within the area there
are lower reaches of two navigable rivers ‐ Narva and Luga, those are connected with each other by another
navigable river ‐Rosson.
The district is a frontier area and important highways of federal importance (namely roads and railways)
cross the territory. Federal highway "St. Petersburg‐Tallinn" goes though Kingisepp town.
Total area of Kingiseppskiy municipal district is 290 800.00 hectares. Municipality "Kingiseppskiy municipal
district" includes the following settlements: Kingiseppskoe, Ivangorodskoe, Bolshelutskoe, Vistinskoe,
Kotelskoe, Opol’evskoe, Nezhnovskoe, Pustomerzhskoe, Ustlugskoe, Falileevskoe. The total population is
81 700 people (4.5% of the total population of the Leningrad region).
Geographical location of the district contributes to its social‐economic development. Economic condition of
the district is at a high level and is one of the main in the region. The district has a wide profile of industrial
orientation and is based on its own natural resources and has a high economic potential. Economic
development of the district is above the average of the region. There is well‐developed network of regional
roads, those connect almost all settlements with central roads. Great influence on the development of the
district has the construction of Ust‐Luga seaport.
1.2 Territory land tenure and condition of general plans
Vistino rural settlement is located on a peninsula along Sojkinskaja Luga Bay of the Gulf of Finland. The
northernmost point of the peninsula Soikinsky is cape Kolgomlya. In the central part of the territory there is
Sojkinskaja hill, maximum depth is about 136 meters above the sea level. About 60% of the land is covered
by forests, mostly coniferous.
7
1.3 Objects of natural and cultural heritage and protected areas
Table 1. Description of protected areas
Name of area Description
State natural complex The sanctuary is regional. Located in the vicinity of the Velkota village and in
sanctuary «Oakwood near blocks 89 and 115 of Kotelsky forest area of Kingiseppskiy forestry. The area
Velkota Village» of the sanctuary is 375 hectares.
State regional nature State nature complex sanctuary is located on the Kurgalskiy Peninsula. Area of
complex sanctuary the reserve is 59,950 hectares (area of the peninsula and the islands is 20 702
"Kurgalskiy" hectares, 848 hectares of water area of lakes and 38,400 hectares ‐ water
area of the Gulf of Finland).
Wetlands "The Kurgala Wetland "The Kurgala peninsula" have the international value and was
peninsula" created for purposes of compliance of Russia with obligations those are
following from the Convention on the Wetlands, having the international
value mainly as habitats of waterfowl, and recommendations of the Parties of
this Convention.
State integrated nature The wildlife sanctuary "Kotelsky" is organized on the basis of Lenoblispolkom's
wildlife sanctuary decision in 1976. The area is 10690 hectares, where the water area of lakes is
“Kotelsky” 3000 hectares.
Natural complex area The territory supposed to be a sanctuary is on a northwest extremity of the
“Soykinsky coast” Soykinsky peninsula.
Hydrological natural The territory supposed to be a sanctuary is the river Rosson connecting deltas
area “Rosson river valley” of the Luga river and Narva river. The area is unique on the hydrological
regime. Rosson connects Narva river with the Luga River that flows in 15 km
to the East.
Suggestions to organize of Ethnographic capacity of the Kingisepp municipal area is defined by
the ethno‐cultural reserve accommodation on its territories of the people of different cultures – the
in the area of the Luzhitsy Russians, the Vod, the Izhorians, Finns‐Ingermanlands
village
The Izhora ethnographic The ethnographic museum located on Tsentralnaya Street, in the village of
museum in Vistino village the Vistino of Kingisepp region of the Leningrad region, Izhora plays one of
leading and significant roles in the course of preservation of original cultural
values of the Finno‐Ugric people under the name of Izhor.
8
2. HYDROGRAPHY
The territory of the municipal area has the developed hydrographic network belonging to the basin of the
Baltic Sea, presented by the Luga and Koporsky Bays of Gulf of Finland of the Baltic Sea, the rivers and lakes.
Regarding nourishing conditions the hydrographic network of the territory belongs to the East European
type with the maximum spring snow high water and the small autumn rain. Seasonal distribution of a drain is
uneven and more than 40% happens in April‐May. In winter the nourishment of streams and lakes mainly
happens at the expense of underground waters that promoted by proximity of glint, delineating the
Ordovician plateau formed by karst limestone and dolomite.
2.1. Resources of underground waters
Figure 3. typical lithological section area near the Vistino
Within the Kingisepp area 6 water‐bearing complexes and formations are widespread. By results of
calculations of expected operational stocks of underground waters for the water‐bearing formations,
executed by PMA "Sevzapgeologiya", stocks for the Kingisepp area are the following:
• expected reserves of fresh waters of the Lomonosov water‐bearing formation within the lowland
are equal 4 thousand m3/d;
• expected reserves of fresh waters of the Lomonosov formation, Cambrian and ordovician
complexes are equal 460 thousand m3/d.
The existing water intake does not exceed 10% of perspective stocks. However nature of distribution of
resources of fresh underground waters and specifics of hydrogeologic conditions of certain territories of the
area does not allow counting on full on drinking water supply of the area with underground waters near
consumers. So, the northern part of the area, including the Vistino settlement, is not provided with fresh
underground waters which by quantity and quality could be a source of the centralized water supply.
The Lomonosov water‐bearing forming emerges under quaternary deposits in northern part of the area.
Underground waters are pressure head, pore‐deposit. Fresh waters with a mineralization 0,2‐0,6 g/dm3 are
widespread in places of exits of the formation under quaternary deposits. In process of immersion the
mineralization increases to 2, 5 g/dm3. The centralized water well‐field is not made; operation is conducted
by single wells.
Most surface waters that are relatively easy get, can have radioactive contamination.
92.2. Resources of surface waters
Belaya river is used as a source of drinking water for Vistino village. Belaya river belongs to the basin of
Habolovka river and refers to the 3rdclass of Division B in accordance with the classification of water
objects according to GOST 17.1.1.02‐77.
Belaya river flows from wetlands of coast Luga Bay, located five kilometers from the coastline of the Gulf
of Luga Bay.
Soils in the catchment area are boulder loam, sandy loam, sand with gravel and pebbles, underlained by
Silurian karst limestone.
Valley slopes are from medium steep to very steep. Their height increases downstream from 1.0‐1.5 m to
6.8 m.
In hydrological matter Belaya rivers an unexplored river. Characteristics of minimum flow is obtained by
estimated calculation. According to the certificate SU "St. Petersburg CGMS‐R" minimum estimated
natural 30‐day water consumption is 95% of Belaya river supply during the period of summer‐autumn
base flow is 0,020 m3/sec. During the winter base flow water consumption is close to the summer‐autumn
values.
Spring flood at Belayariver, by analogy with the small rivers of this region, usually begins in late March ‐
early April. The average duration of the flood is 15‐20 days. Flood peak is in the mid of the April. Water
raise level of average spring flood above the average winter base flow is 0.6‐0.7m. Spring flood recession
lasts about 45‐50 days. Usually the end of the flood starts in early June.
Water protection zone width is 50 m.
Riverside protection zone is set based on the slope of the shore of the water object and is 30 m for
reverse or zero bias, 40 m for slopes up to three degrees and 50 m for the slope of three or more degrees.
The strip of land along the shoreline of the water object for public usage (the riverside) is 5 m.
Table 2. Laboratory water test, Belaya river, 1st stage, WTP
Pos. number Ingredient name Measuring unit 16.12.2013 26.02.2014
1. Odor score 0 0
2. Color grad 126.6 130
3. Turbidity mg/dm3 by kaolin 0.85 0.8
4. РН 6.3 6
5. Oxidability 18.24 16.32
6. Rigidity 1.25 2.3
7. Dry sendiment mg/dm3 68 86
3
8. Anionic surfactant mg/dm 0.015 0.015
9. Oil products mg/dm3 0.05 0.05
10. Phenol (total and volatile) 0.0005 0.0005
10Lakes
Within the boundaries of the municipal area there are located 11 lakes. The largest of them are: Kopanskoe,
Glubokoe, Lipovskoe, White, Babinskoe, Habolovskoe. Kopanskoe and Glubokoe lakes are on border with MF
territory "Vistino joint venture". The Kopanskoelake has length of 7 km.
Water of lakes is low‐mineralized, of a hydrocarbonate class. The general mineralization of water is low and
in Babinskoe lakes it is 41.3 mg/l, Habolovo ‐40.8 mg/l, Sudachye ‐ 37.1 mg/l.
Table 3. Monitoring of water area of water object in 2013 year.
MPC of fish
September
Measuring
Parameter
to control
Position
October
number
August
pond
April
June
May
unit
July
1. рН ед. рН 8,12 8,18 8,18 7,7 8,01 7,72 7,68 8,5
2. Dissolved oxygen mg О2/dm3 14,3 16,6 15,24 11,54 9,6 11,11 10,41
3. Suspended solids mg/dm3 ≤3 ≤3 9,1 ≤3 4,8 11,2 ≤3 сф+0,25
4. BOD5 mg/dm3 0,85 ≤0,5 2,84 0,1 ≤0,5 0,92 ≤0,5 2
5. COD bichromate mg/dm3 50 60 54 31 20 17 19 15
6. Phenols mg/dm3 0,002 0,003 ≤0,0005 0,003 0,002 0,004 0,003 0,001
7. Sulfates mg/dm3 64 71 64 92 64 46 37 100
8. Chlorides mg/dm3 670 690 690 86 2300 2350 535 300
9. Phosphorustotal mg/dm3 ≤0,02 ≤0,02 ≤0,02 0,023 ≤0,02 0,026 0,025
10. Nitrites mg/dm3 ≤0,01 ≤0,01 ≤0,01 ≤0,01 ≤0,01 ≤0,01 ≤0,01 0,08
11. Nitrates mg/dm3 0,01 ≤0,01 ≤0,01 0,01 ≤0,01 0,04 0,04 40
12. Ammoniumnitrogen mg/dm3 0,12 0,12 0,067 0,064 0,057 0,021 ≤0,02 0,5
3
13. Nitrogen total mg/dm ≤1 ≤1 ≤1 0,38 0,63 0,446 0,39
14. Petroleum hydrocarbons mg/dm3 0,05 0,04 0,05 0,03 0,13 0,03 0,04 0,05
15. Iron mg/dm3 0,04 0,05 0,12 0,07 0,06 0,27 0,05 0,1
16. Copper mg/dm3 0,002 0,002 0,0023 0,001 0,011 0,0074 0,001 0,01
17. Manganese mg/dm3 0,017 0,015 0,004 0,015 0,008 0,04 0,07 0,01
18. Zinc mg/dm3 0,005 0,002 0,009 0,012 0,013 0,011 0,004 0,01
19. Nickel mg/dm3 0,005 0,003 0,005 ≤0,002 ≤0,002 0,0041 0,006 0,01
113. DESCRIPTION OF EXISTING WATER SUPPLY AND SEWAGE SYSTEMS OF “VISTINO
RURAL SETTLEMENT”
3.1. Main information about Vistino
Figure 5. Population dynamic
Table 4. Population of Vistino rural settlement
Distance from administrative Population,
Municipality Locality
center, km inhabitants
Vistino rural settlement Total ‐1901
Vistino village Administrative center 991
Valyanitsi village 1,5 51
Glinki village 4,5 55
Gorki village 3,5 113
Dubki village 4 17
Zalesie village 3 45
Koskolovo village 15 9
Koshkino village 7 3
Krasnaya Gorka village 5 10
Logi village 4,5 92
Logi community 6 14
Mishino village 7,5 20
Novoe Garkolovo village 16 5
Pahomovka village 2 40
Ruch’I village 2 319
Slobodka village 8 35
Smenkovo village 4,5 3
Staroe Garkolovo village 19 15
Yugantovo village 6,5 64
12Table 5. Characteristics of the housing.
Volume of the housing, thousand of m2 of total area
Municipality including
Total
Apartment building Individual houses
Vistino rural settlement 74.9 10.1 64.8
Table 6. demographic forecast
Settlement 1990 1997 2007 2010 2014 2020 2030
Vistino 897 907 991 821 995 2890 4356
In the villages there is the process of replacement of wooden houses for stone fundamental houses. Level of
engineering accomplishment in villages is very low.
Table 7. Engineering level of housing
Percentage of engineering equipment provision of the housing (%)
Municipality Water Central Hot water
Sewage Baths Gas Telephones
supply heating supply
Vistino 25 20 30 12 0 0 4
3.2. General characteristics of water supply and wastewater systems
Currently, the territory of the settlement, except village Vistino, has no central water supply and sewage
systems. History of construction of a centralized water supply and sewage systems at Vistino.
Table 8. Stages construction
Year Stage
1936 Construction of water intake, water treatment plant and water distribution networks
1982‐1989 Reconstruction of water intake and construction of sewage treatment plant, gravity flow
collector, treated water distribution networks and sewage system for water tower
(currently out of use), step up pumping stations
2008‐2012 Construction of networks to base "Efesk" and hotel "NOVOTEK". Compound of village
houses for water supply purposes have on their individual plots dug wells to a depth of 8
meters.
Main water supply for Vistino village is organized from surface water source – Belaya river. Water
purification is performed on water intake treatment plants (WTP) "Belaya Rechka". The capacity of plant is
400 m3/day. Structure of facilities and their technical condition will be indicted hereinafter.
Wastewater from consumers of Vistino village via gravity sewer collector flow to biological treatment plant
of project capacity 1670 m3/day and after treatment and disinfection is discharged into the Luga Bay of Gulf
of Finland of the Baltic sea. The sewage system is in very bad condition, which entails environmental
degradation and violate water protection zones of rivers and their tributaries.
Other localities of the settlement do not have a centralized pumping domestic sewage. Inhabitants enjoy
raking or outhouse toilets, which don’t have appropriate degree of waterproofing, that leads to pollution of
aquifers. In very rare cases, on the private plots bio toilets are installed.
Now days the water supply and sewage objects are of municipality property of the settlement and are
exploited by the "Sevzapkommunservis" company under the lease agreement.
133.2.1. Characteristics of the water supply network
The total length of the centralized water supply system networks in Vistino settlement is about 13.5 km. 1.8
km out of these is needed replacing.
Table 9. Sewage and Water supply network
Network segment Material Ø mm length
km
Sewage water network
From water intake and treatment facilities "Belaya rechka" to Vistino cast iron 350 9.6
village
To the water main pipe connected) that supply water to JSC "Novatek" PND pipe 200 3.6
Water supply network
Distribution networks cast iron 150 515
100 380
50 84
steel pipes 150 292
100 1993
50 719
32 24
At the same water pipe in the area of Smenkovo village there is intermediate concrete treated water tank
(TWT) of 500 m3 volume (CWT).
Due to significant changes in elevation 2 step up pumping stations were constructed in Vistino village. First
step up pumping station does not operate because there is no necessity as after TWT water comes to the
village with a pressure of 3.0 kg/cm2). At the second step up pumping station pump K 20/30 brand (1 pc.)
with frequency converter is installed. Installation of frequency converter provides energy saving. SPS number
2 delivers water to the upper part of the village to the three‐stored houses.
3.2.2. Characteristics of the sewage network
Sewer network length is about 5.5 km (1 mile ‐ collector Ø 250 mm; 4.5 km ‐ internal networks), a discharge
from WTP ‐ 600 m, Ø 250 mm, pipe material: cast iron, ceramics. 176 sewage wells are constructed on the
networks.
95% of the networks and their facilities have been built during the 1982‐1989 years. The networks are
pretty worn.
Below the route of water supply and sewage networks are shown.
14Figure 4. Water supply and sewage networks of Vistino village.
153.2.3. Water consumption volume and wastewater volume
Table 10. Physical indicators of water supply
Measuring Fact
Parameter Plan 2014 Comment
unit 2013
Total volume of water intake 1000 m3 57,6 72,1
Own needs 1000 m3 5,8 7,1 10%
Total volume to distribution network 1000 m3 51,8 65
Leakages 1000 m3 31% 25%
Total volume of water distributed
from water supply network , 1000 m3 46,7 55,5
including:
Population
1000 m3 15,7 19,9
Budget consumers
1000 m3 2,9 3,0
- Water supply companies 1000 m3
JSC «Novatek», 7
32,6
- Other consumers 1000 m3 28,1 months during
2013 year
Total consumption of power,
1000 kW h 152,4 167,5
including:
- Power consumption for
Frequency converter
technology needs 1000 kW h 125,5 140,5
is installed at SPS
- Specific energy consumption
kW h /m3 2,18 1,95
for technological needs
Characteristics of WWTP: start of construction of wastewater treatment plants (WWTP) ‐ 1982,
commissioning ‐ 1989. CBS p.Vistino built on the Model T‐1646 project (artist: TSNIIEP Engineering
equipment). CBS intended for cleaning households. domestic wastewater and sewage p.Vistino from fish
farm "Baltika". Design capacity of 1670 m3/day structures., actual ‐ 42.8 thousand m3/year, 118 m3/day. (in
fact in 2013.).
How they calculate water losses.
Metering of distributed water is organized by metering devices. Own (technology) needs and the volume of
leakages is within the limits. The growth of the leakage volume is caused by wear of the distribution pipes.
Every year the volume of water intake is growing, for example in 2010 water intake was 34.4 1000 m3 per
year, in 2013 ‐ 57,6 1000 m3 per year. Increase of water intake was due to the growth of water sold to the
needs of the population (labor inflows to build port facilities) and water use for construction enterprises.
Table 11. Forecast of water consumption Vistino
Water supply 2014 2020 2030
m3/year 63200 172800 357000
16A strong increase in water consumption due to the development of port infrastructure "Ust‐Luga"
Table 12. Calculation of consumption of water supply services by population in 2014 year
Position Consumption norm, Number of Year consumption,
Accomplishment type
number m3/people/month consumers, people 1000 m3
Vistino village
Full accomplishment
with installed metering
2,37 611 17,377
1 devices
without installed
5,47 14 0,919
metering devices
Houses with/without baths, with water supply and sewage
with installed metering
2,27 22 0,599
2 devices
without installed
3,95 19 0,901
metering devices
Houses with water supply and without sewage
with installed metering
1,18 11 0,156
3 devices
without installed
3,04 0,000
metering devices
Total for population 677 19,951
Table 13. Sewage indexes of Vistino village
Measuring
Index Fact 2013 Plan 2014 Comments
unit
1000 m3 42,8 46,8
Total volume of waste water, including:
Industrial discharge – total, 34,5 41,2
including:
- Population 1000 m3 15,7 19,9
- Budget consumers 1000 m3 2,9 3,0
- Other consumers 1000 m3 15,9 18,3
Infiltration 1000 m3 5,6 5,6
1000 m3 42,8 46,8
Total volume of treated waste water,
including:
For full biological treatment 1000 m3 42,8 46,8
140,8 148,5
Total consumption of power, including: 1000 kW h
- Power consumption for 82,6 90,3
1000 kW h
technology needs
- Specific energy consumption for 1000 kW 1,93 1,93
technological needs h/m3
17Table 14. Forecast of waste water consumption Vistino
WWater 2014 2020 2030
m3/day 120 320 650
3.2.4. Calculation of infiltration
Table 15. Calculation of weighted rate for the sewage warm season.
№ surface Area flows F, Runoff coefficient, F*W
hectare W
1 Area with a paved 2,8 0,6 1,68
2 lawns 49 0,1 4,9
in total 51,8 6,58
C. average.= 6,58/51,8 = 0,125
Calculation of the volume of surface runoff for the year.
According hydrometeorological station "OGMS Kingissepp" total amount of precipitation in the 12 months
2013. was ‐ 624.1 mm.
Table 16. Amount of precipitation
month amount of precipitation (mm)
January 42.1
February 28, 2
March 5.5
April 36.0
May 69.8
June 60.2
July 44.7
August‐ 51.7
September 60.2
October 54.9
November 63.8
December 44.8
Table 16. Calculation of weighted
№ Flow The layer of the precipitate, S ha Кu Кav V
h mm.
т.м3/year.
1 Rain 386,87 51,8 0,125 25,0
2 Thawed 157,23 51,8 0,6 0,65 31,4
Total 544,1 56,4
18Formulas for calculation:
Vд=10*h*S*kср.
Vт=10*h*S*ku*Kav., где
Ku factor as used in the case of snow removal from the territory
The average annual volume of infiltration of rainwater and meltwater Wk.inf cube. m entering the sewage
system of the village on the square S, ha determined by the formula
Wk.inf = k2 * V,
where k2 ‐ dimensionless coefficient accounting for infringement of tightness butt
compounds of sewer pipes, coupling pipes locations with wells and components wells received 0.1 to 0.5
depending on the sewer system.
Wk.inf = 0.1 * 56.4 = 5.64 t.m3/year
193.2.5. Balance of water supply and sewage systems
Water reservoir on the Belaya River Belaya River
WTP «Belaya River»
Q= 197,5 м3 /сут.
washing filters.
Q=19,7 м3/сут. ( 10%)
Served to the pumping station
of the 2nd ascent.
Q=197,5м3/сут.
Network losses
Total Filed in the city's network. Q= 177,8м3/сут
Q= 26,1 м3/сут. ( 14,7%)
d.Vistino OAO "Novatek"
Q= 62,5м3/сут (41,2 %) Q= 89,2м3/сут. (58,8 %)
Drains from Conceded by WWTP
inhabitants Q=128,2.м3/сут.
Q=112,9 м3/сут
Luga Bay Gulf
Baltic Sea
infiltrate
Q=15,3.м3/сут
Figure 5. Water Balance
203.2.6. Water intake and treatment facilities
Water intake and water treatment facilities at Vistino village have been constructed in accordance with
typical design project TP №3‐901‐80 in 1987‐1988.
Water source is Belaya river that is a small river of the 1st class. River feed is mainly ground‐snow. Flood
periods ‐ spring and autumn, although if there are a lot of rains during summer period the water level can go
up as well. Taking into account the low water level of the rivet at the water intake, a piled up dam have been
constructed with concrete culvert devices.
Figure 6. Dam WTP
Figure 7. Struya‐800
The volume of the water reservoir stable provides water intake treatment facilities "Struya‐800" at any time
during the year. Currently water source water is high colored, low turbidity, with low alkaline reserve, high
rigidity and pH. High color water of water source, requires a high raw water chemical treatment using a
coagulant and soda.
213.2.7. Existing water supply and water treatment process
Water from gabion via deepened pipes goes to 2 water intake wells, those are connected to the 1st stage
pumping station. Two pumps type ЭК‐9 (К‐45/90) pump raw water from the 1st stage pumping station via
pipes 250 mm diameter to с treatment facilities.
Figure 8. 1 stage pumping station
Inside the 1st stage pumping station in 2013 year piping of the pumping equipment was replaced for
polyethylene pipes and water metering unit was installed with metering device VSKHN‐150. The accuracy of
meter data are doubtful, as usually the metering device to be installed should be about 1‐2 caliber smaller
than the diameter of the main pipe. Today the metering device VSKHN‐150 is installed on the polyethylene
pipe with diameter of 160mm.
The 1st stage pumping station is equipped by workshop for preparation of soda solution that is dosed into
the suction pipe of the inlet well. The gap between dosing soda and coagulant is about 2 minutes. Coagulant
solution in the required doses, is being dosed into the pressure pipe connector assembly of 2 units before
the flocculation chamber. Disinfection reagent ‐ a solution of sodium hypochlorite ‐ is being dosed into the
filtered water. Before the flocculation camera there are sieve filters to trap big floating impurities.
Treatment facilities “Struya‐800” configured of two typical treatment units “Struya‐400” with total capacity
800 m3 per 24 hours.
This treatment unit consists of:
grid filter
flocculation chamber, совмещенная с трубчатым отстойником
sand pressure filter
equipment for coagulation, chlorination and water stabilization.
22Figure 9. Water intake and treatment facilities, equipment “Struya‐400”
After that water flows into the flocculation chamber where after the coagulant have been dosed flakes of
aluminum hydroxide form with the extraction from water of suspended and colloidal particulates.
The resulting flakes arrive into the chamber with drums consisting of filled tubes DN 40‐100 mm, arranged at
an angle of 60о. Intensive water clarification is achieved by sedimentation of particulates in the tubes of the
отстойника. Simultaneously there is a mixing of the part of the sludge in the flocculation chamber. Distilled
water with a bit of turbidity is being sent to sand filters for the final cleaning.
After that water flows to the treated water tank where pumps of the 2nd stage pump it to the distribution
pipe and then to the consumers via main pipeline (length 14 km).
Filters are filled with quartz sand of a certain fraction. In accordance with the technical regulations filters are
to be washed. As a result of filters washing there are rinsing waters those are to be discharged through
coastal discharge, which is a steel pipe DN 250 mm and a length of 100 m located on the right bank of the
Belaya river. The discharge is located at a distance of 10 m from the water, the place of discharge is fortified
by granite natural stone at a distance of 0.5 m up and downstream of the discharge.
Elements of the facilities:
sedimentation: pipes, diameter – 2 m, quantity – 2 pcs.
pressure filter: sand, diameter – 2 m, quantity – 2 pcs.
sieve filter– 2 pcs.
Dosing of coagulant and hypochlorite is organized by dosing pumps D‐VA‐98‐10, capacity 98 l/h, engine
power 0.25 kW.
Dosing of soda is used pump D‐VA 135/10, capacity 135 l/h, engine power 0.25 kW.
Chlorination. Elektrolitny unit EN‐25, 2 pcs, one is operating and the other one is standing by.
The unit consists of: solution tank– 1 pcs, electrolyzer – 1 pcs., operational tank – 1 pcs, rectifier – 1 pcs,
dosing pump GND‐25/25 – 1 pcs.
23Figure 10. Electrolysis room.
In the 2nd stage pumping station the following pumps are installed:
1. NM 50/20 B/B ‐ 3pcs., (Q=24‐78 m3/h, H=23‐48 m; N=9,2 kW);
2. Wash pump RB‐200, (Q=200 m3/h, H=20m, N=22 kW)
On the territory of the water intake and treatment plant there is a clean water reservoir‐1pcs.,Q‐50m3.
The 2nd stage pumping station via cast iron pipe of diameter 350 mm pumps water to Vistino village. On the
territory of water intake and treatment plant a diesel generator type A‐01ME is installed that is used when
there is no electric power supply. Technological process at the station is controlled by laboratory that is
located at the territory of the water intake and treatment plant "Belaya Rechka". Besides monthly water
quality monitoring is done by Center of Hygiene and Epidemiology in the Leningrad region in Kingiseppskiy
district.
Quality of drinking water purification needs improvement. Taking into account the forecast population
growth, increase water treatment plants providing capacity with 2 lines. Cleaning quality does not satisfy
residents. This is due to outdated equipment and a high degree of wear of water networks.
3.2.8. Proposals for a water purification system
As a purification of water supplied to habitants, a system based on the principles of microfiltration.
Estimated composition of water treatment plants:
‐ Block profiteered water.
Automatic mechanical filtration with crevice 200. At the heart of the filtering elements of the cartridge is
compressed polypropylene discs micro channels are in a compressed state to form a filter element. The
advantage of these elements is that the elements are little subject to wear. When pollution wheels pushes
the washed, completely restoring their filtering ability.
‐ Chemical dosing unit
Node proportional dosing ‐ is designed for input to correct reagent salt in water, to ensure efficiency
ultrafiltration system.
The metering unit with built‐in pH meter. Is used to adjust the pH.
‐ Block the main water purification from organic substances
24Ultrafiltration unit. The unit is designed for cleaning water from surface sources from mechanical impurities,
suspended solids, organic compounds and bacteria. The principle of operation of the plant: Source water is
treated by coagulation and then passes on the ultrafiltration membrane cleaning. Due to the fact that the
pore size of ultrafiltration membranes is very small , then the process of coagulation sufficient 30 ‐ 60
seconds of residence time , so the coagulant is dosed directly into the raw water supply pipe in an amount
much smaller than in a classical water treatment scheme . Purified water is collected into purified water
storage container. Minority (about 5‐15 %) is used for backwashing the membrane, and most of the served
user.
The choice of this water purification technology a number of reasons, first of all ‐ the poor quality of drinking
water in urban areas associated with disabilities of existing treatment facilities. Sandy granular filters that
are part of all water treatment plants, are often unable to hold very small particles (colloids) , bacteria and
viruses , usually developing in these filters . It is through ultrafiltration membranes can be cleaned with
water to European quality standards, because these membranes have a pore size of 0.002 ‐ 0.1 microns,
allowing delay bacteria and viruses. Also note the simplicity of installation of such systems, namely, each
such conduit system is connected to a source of water, the purified water pipe (for pure water storage
tanks), a conduit supplying the washing water from the clean water tanks and the sewer pipe.
System storage tanks with the automation system ‐ a prerequisite of ultrafiltration unit, is required to create
the volume of purified water for hydraulic and chemical cleaning ultrafiltration unit. The material from which
made storage tanks ‐ plastic, making them easier to transport and ensures the longevity of their service life.
The system is protected against tanks overflow and automation fill them.
‐ Block secondary water purification from residual organics
Rising pumping station based on low noise pumps Grundfos. In this pumping station consists of 3 pumps (2
working and 1 standby). System Automation station pumps work alternately switches , thereby achieving
uniform load on pump motors in the station . All pumps are equipped with a frequency converter station,
providing soft start equipment and lack of water hammer in the system. Also a complete pumping station
includes an accumulator 500 liters. to reduce the number of on / off pump motor and system protection
startup pump "dry ."
Water enters the system at a continuous carbon filters intended for cleaning water to the residual chlorine,
tastes, odors and organic compounds.
Loading filter ‐ activated carbon produced from special grades of bituminous coal, characterized by a narrow
particle size distribution, has a high activity. Activated carbon is characterized by a selective pore structure,
which provides a high degree of absorption and the ability to impregnate. Also, are sufficiently resistant to
abrasion, to resist the repeated regeneration. Mode of operation: Water is passed through the column at a
time. Process is controlled by an electronic control unit, according to testimony which the controller
determines the need for regeneration of a particular column. Controller independently carries regeneration
column , this time providing the consumer with purified water from other columns. Regeneration of the
filter automatically reverse current of water.
‐ Block water disinfection
The metering unit is in automatic mode. If necessary, one can easily change the dose of the reagent.
253.2.9. Waste water treatment facilities
Wastewater discharge of Vistino village is organized through sewage treatment plant’s discharge into the
Luga Bay of the Gulf of Finland.
Sewage network of Vistino village is separate. Civil sewage from the village and recreation via gravity
collector of total length 5493 linear meters and diameter 250 mm is going to the intake department of waste
water pumping station at Sewage treatment facilities (pipe material: cast iron and ceramics).
Start of construction of wastewater treatment plants (WWTP) ‐ 1982 year, commissioning – 1989 year.
WWPT of Vistino village are built in accordance with typical design project T‐1646 (contractor: “Engineering
equipment” company). WWTP have been built to treat civil sewage and intended for cleaning households.
domestic wastewater village Vistino and sewage from fish collective farm “Baltica”.
Designing capacity of the WWTP is 1670 m3 per day, fact – 42.8 1000 m3 per year, 118 m3 per day (fact, in
2013 year).
Structure of WWTP:
Administrative building
Waste water pumping station
Figure 11. Waste water pumping station.
Figure 12, 12A. Tank block aerotank‐clarifier – 3 pcs.
26Figure 13. Post precipitation.
Figure 14. Biological ponds – 2 pcs.
27Figure 15. UV disinfection unit.
Figure 16. Sludge field.
28Figure 17. Blowers.
Figure 18. Boiler building.
29Technological treatment scheme
Wastewater flows into the receiving chamber of the waste water pumping station (capacity 173 m3/h, depth
5.5 meters). For flow measuring of the sewage delivered into the receiving chamber there is a device for
proportional discharge.
From the receiving chamber sewage is delivered by pumps SM 125‐80‐315/4 (1pc.) and SD 50/56 (2 pcs.)
into the aero tank‐clarifier, which consists of two compartments separated by a shield. Dimensions of the
tank are 36x6 m (3 pcs). Aero tanks (two compartment) are used for biological wastewater treatment.
From aero tanks wastewater go to the secondary clarifiers, where suspended fine particles and activated
sludge sediment. In the secondary clarifier (dimensions 36x1,4 m) sludge mixture is sedimenting (runoff +
sludge). Biological treatment is performed in the extended aeration mode. Aeration in the aeration tanks is
pneumatic. Aerators are perforated pipes. Air is forced by blowers located in the separate building (blowers
station). Sedimentation zone is equipped by thin‐layer modules. Return of the circulating sludge in the
aeration zone is provided by of airlifts. Air for the airlifts is forced by gas blower 2AF51752 (2pcs.) and
1A24302a (2 pcs.), those are installed in the auxiliary building.
From the sedimentation zone water flows by gravity through the steel pipes (diameter 200 mm) to biological
ponds (2 pcs.). In biological ponds there is further treatment of biologically treated waste water by oxygen
saturation.
After biological ponds wastewater flow to disinfection by UV unit with lamps DB 15M and DB 30M.
Furthermore wastewater is discharged by gravity collector (DN 250mm, length 600m) through the scattering
of channel output into the Luga Bay of the Gulf of Finland. Discharge zone is 140 meters from the water's
edge.
Runoffs from fish farm “Baltica” (now the farm does not operate) come via separate sewer system into the
aeration tanks of the waste water treatment plant.
Today the situation at WWTP has worsened due to reduction of runoffs volume and pollution load that was
caused by the shutdown of the fish farm and the lack of industrial runoffs as a consequence. Besides all the
metal facilities have great physical deterioration.
Monitoring of the quality of treatment is done by Center of Hygiene and Epidemiology in the Leningrad
region in Kingiseppskiy area. Laboratory tests are performed quarterly. Below you can find the results of
laboratory examination of wastewater from WWTP of Vistino village.
30Table 17. The results of laboratory examination of incoming and treated wastewater at WWTP of Vistino
village.
Actual concentration rate, mg/l
Parameter name
Before treatment After treatment Treatment level, %
рН 7 7,7
Suspended solids 461 127 72,45
BOD total 83,5 45,6 45,39
COD 264 96 63,64
Nitrogen total 9,12 11,25
Ammonium nitrogen 10 14,1
Nitrogen nitrate (NO2) 4,9 4,5 8,16
Nitrite nitrogen (NO3) 0,08 0,1
Phosphorus total 1,53 2,61
Chloride 70 120
Iron total 1,34 1,52
Oil products 0,05 0,05
Dry sediment 237 397
Surfactants 0,107 0,068 36,45
Sulfate 25 24 4,00
Phosphate‐ion 4,1 7,4
Manganese 0,05 0,05
Phenol 0,0005 0,0005
Copper
Zinc
Wastewater from JSC "Novatek" is brought to existing WWTP at Vistino village by special transport. During
the construction period wastewater is being collected into the waterproof containers ‐ collectors.
Technical condition of WWTP of Vistino village is indicated in the following table.
31Table 18. Technical condition of WWTP of Vistino village.
Description of Necessary
Pos. Technical Necessary Resu
Name of facility building, facility, finance,
# condition repair lt
equipment 1000 rub.
1 2 3 4 5 6 7
One in
SМ 125‐80‐315/4 ‐1
Waste water operation, one
1 pcs.
pumps is standing by,
SD 50/56‐2 pcs.
one is in repair
One section of
Repair of metal
aeration tank
Size:20,8х5,9х4 construction
was prees out
Aeration tanks ‐ Rectangular and
2 by water. 100%
clarifiers ‐ 3 pcs. deepened facility (all reconstruction
deterioration of
out of metal). of
metal
impermeability
constructions
100%
Post‐precipitation deterioration of
3 Dimensions: 4х5,9х4
– 3 pcs. metal
constructions
Just one step
Deepened building, and just one
4 UV disinfection Replace lamps
self‐made. UV lamps lamp in
operation
It’s necessary to
warm up the
building and
Administrative make the inside
In limited
building with renewal, seal
5 operational
auxiliary the breaks and
condition
industrial building reinforce
supporting
constructions of
the building.
Necessary to
Rectangular
Biological ponds – In operational clean from
6 deepened facility.
2 pcs, condition biological
Size of each 24х35 m
incrustation
Sludge field– 6
7 13,5х37,8 m each Out of usage
pcs.
4 blowers (3 in
operation. + 1 is
In operational
8 Blowers station standing by)
condition
2АF51752 ‐2 pcs. and
1А24302а‐2pcs.
In operational
9 Boiler building Boiler with wood
condition
323.2.10. Suggestions for a waste water treatment system.
As the underlying technology accept purification scheme (without agents) and nonchemical sludge
treatment provided by fig
Figure 19. Scheme WWTP
To implement this scheme used container type modules completely prefabricated:
‐ SNS module , which houses the grille , sewage pumps and measuring unit wastewater flow ;
‐ BTF unit , wet compartment that hosts the primary clarifier ‐ seal , with in‐plane loading aeration ( biotenk )
, secondary clarifier , filter, and dry compartment ‐ all technological and auxiliary equipment (UV ‐
installation, blower , heating and ventilation systems , automated etc.) ;
Used modern equipment mechanical dewatering (excess sludge).
‐ All modules have a closed design, insulation, heating and ventilation.
, Grit chambers and assembly mechanical dewatering and pumping station sewage effluent flow control
assembly and the central ACS placed in a separate production and administrative building (PAZ) . As part of
PAZ provides space for staff on duty (there are water and local drainage).
Mechanical treatment in the primary settling tank, biological treatment system and after treatment filter ,
UV ‐ disinfection sewage and sludge treatment in MINERALIZER ‐ compactor is implemented as a part of
modular units of container , completely prefabricated . Modular units have local ACS, which receives signals
from the central control systems.
334. FORECASTS OF DEVELOPMENT
4.1 Forecast of development for Vistino settlement.
Vistino rural settlements have a special place in the structure of municipal districts and on their development
was mainly due to the construction and operation of port facilities and structures. Construction of a large
commercial seaport of Ust‐Luga (ICC), as international experience shows, accompanied by coherent
industrialization and urbanization neighborhood: are major transportation hubs, combines the capabilities of
maritime, rail, road, and in some cases air transport; formation of industrial zones to finalize and partial
processing port cargo, as well as other enterprises and residential structures.
Vistino village becomes "growth point" territory Vistino rural development in the village, where it is planned
placement of production and transportation facilities associated with ICC
Calculated spatial planning stages taken in the master plan Vistino rural settlement:
the first stage of the Master Plan ‐ 2025 (the same as the design life "schemes of territorial planning
Kingiseppsky Municipal District");
the expected life of the Master Plan ‐ 2035;
perspective, beyond the design life of the project master plan for which to formulate the main
directions of urban development.
344.2 Predicted values of the main indicators
Table 19. Main indicators infrastructure Vistino rs.
№ Indicator Unit of measure Сurrent state 2025 2035
1. Territory settlement of all hectare 20299,2 20299,2 20299,2
2. population
2.1. The permanent population ths. 1,9 4,0 17,3
3. The total volume of housing 74,9 175,0 647,6
4. Objects of cultural and of public services
4.1. Objects training and educational purpose
Kindergarden th seats 0,2 0,3 1,0
Teaching Institutions th seats 0,4 0,8 1,9
Ambulance visits per shift 30 80 284
Hospitals beds 3 ‐ 233
Sport clubs th sq.m. 0,1 ‐ 6
Planar structures th.sq.m 0,2 34
Swimming Pools sq.m. water
‐ 130
surface
Club facilities seats 400 ‐ 1384
Movie Theaters seats 0 ‐ 606
Establishment of youth policy sq.m. 0 ‐ 433
Museums facility 1 1 2
5. Engineering infrastructure and landscaping
5.1. water infrastructure
water consumption
‐ Total, including: Th.m3/day 0,12 1,4 5,6
‐ For household needs Th.m3/day 0,05 1,1 4,2
‐ For industrial purposes (except for the Th.m3/day
cost of water from their own water 0,01 0,02 0,03
intakes of industrial enterprises)
Water recycling % ‐ 15 20
The average daily water consumption for l. / day per
63 280 323,7
one person person.
including
‐on the household needs l. / day per
26 220 242,8
person.
length of network km 17,0 14,2 31,1
5.2. Wastewater
Total received wastewater
‐ Total, including: Th.m3/day 0,23 1,1 4,4
‐ Domestic wastewater Th.m3/day 0,05 1,0 4,1
‐ Industrial waste water Th.m3/day 0,15 0,15 0,25
Performance of sewage treatment Th.m3/day
1,67 1,67 4,4
facilities
length of network km 5,5 9,2 18,9
5.3. Construction of rainwater drains closed km ‐ 1,87 1,48
5.4. Construction of open drains rainwater km ‐ 0,89 16,97
Construction of water treatment facility
5.5. ‐ ‐ 2
rainwater
355. TECHNICAL SOLUTIONS AND PLANNING SCHEMES
5.1. Drinking water sources
Within this territory provision groundwater is uneven, due to the peculiarities of geological structure and
hydrological conditions.
The source of water may be used groundwater Ordovician aquifer Izhorskogo plateau. Fresh water,
bicarbonate, are widely used for water supply in Kingiseppsky, Volosovsky and Lomonosov district of
Leningrad region of. Water intake may be placed on sites or Karstolovo Hrevitsa.
Also as an option you can consider the construction of a new water intake and structures‐tions of water
treatment on the right bank. Luga outside surges waves of intense action and anthropogenic pollution
sources (upper stream village. Mezhniki and Kuzemkino). Regulation of water intake must be specified
during engineering surveys.
In the village. Logs and pos. Old and New Garkolovo not provide centralized water supply. Sources of
water supply in these localities can be underground borehole.
Comparison of water supply options for investment shows a significant advantage of the organization of
a series of water. Meadows, which can be recommended for further implementation.
findings
Peak demand costs for municipal water potable plumbing defined to be:
The first phase of the project ‐ 1.1 th.m3/ day.,
Full capacity‐ 4.2 th.m3 / day.
Cover these costs is provided by the projected intake of the Luga River.
water supply scheme
The project envisages the further development of the centralized water supply system Vistino rural
settlement. The project envisages the closure of surface water intake on the river. White on primarily
due to the increase in population in the territory of Vistino rural settlement increases the need for
water. Increasing the capacity of water diversion on. White is not possible, since p. White aridity.
Water Vistino rural settlement at first planned to be on the surface of the source p. Meadows near the
village of Bol. Kuzemkino capacity of 75 th cubic meters. / Day, to be built for the city of Ust‐Luga. The
planned scheme provides for the supply of water to the needs of domestic water, fire and water
production and th. The future is possible for domestic water supply use the groundwater Ordovician
aquifer Izhorskogo plateau.
Water supply scheme Vistino rural settlement as follows:
Water from the river Luga will be supplied a pumping station on the first lift intake treatment facilities.
Coming cleaning cycle of clean water reservoirs, water will be the second lift pumping station in the
network diluting Vistino rural settlement. Water supply for the industrial zone is planned to construct a
separate water main.
Water supply network on the territory of the settlement is traced in a ring configuration, equipped with
armature and fire hydrants.
Water recreation, transportation, recreational, agricultural areas is planned to carry out the nearby
centralized water supply systems, in the case of the absence of those ‐ from underground water sources
from the activities on the preparation of hydrogen.
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