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Total Water Management System
for Cgh Swa Swara, Gokarna

 
 
 
 
 

 

The Project
Primarily catering to the discerning international traveler who seeks to discover his ‘inner vibrations', Swa Swara, situated on Om Beach, 6km away from Gokarna, Karnataka accommodates Luxurious Courtyard Villas, Ayurvedic Spa, Restaurant, Library Bar, Music Room, Craft Centre, Swimming Pool, Art Gallery, Exhibition Hall, Yoga Space and related facilities.

The Site
The resort is located on a land of extent approx. 26 acres. Entering from the north, the land slopes down to the beach on the southern side. The upper stretch is relatively gently sloping with scrub vegetation. The middle stretch has a patch of dense vegetation and the lower stretch has a strip of paddy fields and coconut groves which open out into the pristine Om beach.

The southern boundary of site is stretch of Arabian Sea . The highest location at the site is approx. 30m above MSL.

The soil profile of the site is mainly lateritic, which is reddish brown in colour, having lateritic clay soil texture. The top layers are soft laterite with small boulders; but below depths of 3.0m, hard laterite rock formations prevail.

Climatic Conditions
Gokarna is located at 14deg N latitude and 74deg E longitude and has a hot and humid climate.

The average temperature ranges from 25 deg C to 29 deg C. The place has very high relative humidity ranges from 60% to 88%. The rainfall is mainly from the South West monsoons starting from mid June, continuing up to September. The annual rainfall received is about 3500 mm.

Sources of Water Supply
From the initial planning stage, it was obvious that one of the main constraints in the site was lack of availability of potable water.

As the site falls under Costal Regulation Zone I, according to the CRZ norms, 200m from the beach is to be a No Development Zone. There shall be no new constructions in this zone. Pumping of ground water is also prohibited in this zone. Almost 65% of the site falls under this zone. There were 3-4 existing shallow wells in the region but unable to yield the water to required quantity and Gokarna does not have any centralized water supply network.

The only other source is water supplied by private tanker lorries; but this, besides being extremely expensive, is also untreated water with uncertain quality.

After considering the various options, M/s ‘Inspiration' recommended that the best option would be to integrate the concept of Total on site water management for the project at the design stage itself: which would focus on

A reservoir with an impermeable lining to collect and store the bountiful rainwater for the dry months.
Gokarna does not have a centralized sewerage system and hence the need for a properly designed on the site treatment of sewage and waste water to prevent contamination of ground water in the few surface wells on the site.
Recycling of treated wastewater for non potable end uses such as flushing, gardening etc to conserve use of the harvested rain water.
Water Requirements
The water required for the project is as follows:
Cottages 24no.s at 2.5 occupants per unit 60 guests
Water required @300 lpcd for 60p 18000 lt.
     
Staff Quarters Residential accommodation for approx. 60 persons  
Water required @ 150 lpcd for 60p 9000 lt.
     
Miscellaneous   3000 lt
     
Total Water required per day 30000lt
     

Design of the Rain water harvesting system
Gokarna has an average annual rainfall of 3500 millimetres. The reservoir was needed to be planned for a capacity to address 180 totally dry days. The average annual evaporation loss in Gokarna is 1400 millimetres. Being a resort, the aesthetic appeal of the water body was of utmost priority; so there was a need to maintain a minimum level of water in the lake throughout the year.

Considering all the above factors, a consumption recharge profile was worked out to decide on the size of the lake required for rain water harvesting.

Month Volume of Water in lake at the beginning of month (m³) Usage (m³) per month Monthly Evaporaion rate ( in meter) Monthly Evaporation loss in m³ Average monthly rain fall(in meter) Recharge Volume (m³) Net volume at the end of month (m3) Depth of Water in Lake (in meter)
Jun 3687.12 675.00 0.08 344.00 1.03 14021.42 16689.54 3.30
Jul 14365.00 675.00 0.08 344.00 1.16 14231.87 14365.00 3.30
Aug 14365.00 1012.50 0.09 387.00 0.69 9384.97 14365.00 3.30
Sep 14365.00 1215.00 0.12 516.00 0.25 3400.35 14365.00 3.30
Oct 14365.00 1215.00 0.15 645.00 0.19 2584.27 14365.00 3.30
Nov 14365.00 1350.00 0.15 645.00 0.03 602.30 12972.30 3.01
Dec 12967.30 1350.00 0.15 626.40 0.02 401.53 11392.43 2.72
Jan 11392.43 1350.00 0.18 729.36 0.00 0.00 9313.07 2.30
Feb 9313.07 1350.00 0.20 761.40 0.00 0.00 7201.67 1.90
Mar 7201.67 1080.00 0.25 891.00 0.00 0.00 5230.67 1.47
Apr 5230.67 945.00 0.25 816.00 0.01 0.00 3469.67 1.06
May 3469.67 945.00 0.25 741.75 0.14 1904.20 3687.12 1.24

Consumption Recharge Profile of Lake
With such a large volume to be provided, the reservoir / lake had to be a major landscape feature on the site- its design and constructional detailing demanded an excellent aesthetic quality, besides structural soundness. A free flowing form was chosen based on the site levels, layout and master plan.

The free flowing form demanded a flexible material for lining. The lining had to be almost perfectly impermeable to prevent seepage losses, be resistant to ultra violet radiation and rodent attack, be non- toxic and be able to withstand any unforeseen uplift due to hydrostatic pressure.

Mr.V.N.Gore of Geoscience Services, Mumbai was the structural consultant for the lake. Based on the soil investigation reports and detailed site studies, Mr.Gore recommended that the critical criteria for the lining would be control of hydrostatic pressure in the lateritic soil from the vast catchment, impermeability of the membrane and last but not the least, the aesthetic appeal.

The detailed design encompassed the following
•  Depth of excavation of lake bed to be limited to the level of hitting hard laterite to optimize on costs.
Excavation to be done in a slope of 1 in 1.5 to naturally protect the sides of the reservoir.
Network of underdrainage below the lining of the lake to release hydrostatic pressure formation below the impermeable liner membrane and uplift.
Lining of lake with 2 layers of LDPE fabric liners – the main liner being 300 micron and top layer with 150 micron LDPE.
The floor of the lake was to be protected by a layer of 100mm of sand.
The sides were to be protected by pitching with random laterite masonry in a lean mortar.
Toe walls at the base of the lake would protect the pitching in position.
An overflow weir to divert the overflow from the lake in a controlled manner to the lower side of the`lake.
Collection of water from the underdrainage network.
A network of subsurface filter drains of various sections to drain the catchment within the site and bring filtered water to the lake.
A network of trench drains and filter tank to catch the water from the external catchment, filter it and let it into the lake as additional source.
Protective embankments on the sides of the lake to prevent unfiltered run offs into the lake.

Detailed cost estimates for each of the above items were taken. In comparison to a reservoir with ferrocement or RCC lining, the cost for the lake at Swa swara claims the following significant merits.

The cost was only about 1/3 rd that of a conventional r.c.c lining.
Being flexible materials – LDPE and laterite, it gave tremendous design and construction flexibility.
The construction required only semi-skilled/unskilled local labour and very little of mechanical equipment and tools.
The depth was fixed at 3 – 3.3 metres on an average since below this depth was hard lateritic rock which would be very difficult to excavate and blasting was to be avoided. There was also the concern that deeper storage may give rise to anaerobic conditions i.e oxygen starvation. Based on the consumption recharge profile, the corresponding area was fixed at 4200 square metres.


Construction of the Lake
The construction of the lake was started in April 2004. The bulk of the excavation was done with the help of four JCB excavators. The final leveling and shaping of the lake was done manually.

The entire excavation was completed in 45 days. This was followed by laying the underdrainage network on the northern side and base of the lake. The underdrainage consisted of perforated corrugated flexible HDPE pipes wrapped in non woven polypropylene filter fabric. After laying the under drainage network, a 50mm thick sand layer was provided on the sides and base of the lake.

This was followed by laying of the 1 st layer of liner fabric in Lake 1 – the 150 micron LDPE liner. By this time, we were overtaken by the monsoons which arrived almost two to three weeks ahead of normal. To protect the liner laid in Lake 1, it was covered with a layer of sacrificial fabric – slit tape HDPE. With this, we could harvest rain water during the monsoons in Lake 1 and use it for construction and other uses in the site. This helped us save almost two to three lakh liters of water used for construction.

After the monsoons, we resumed work on Lake 2. This involved reshaping of some of the sides which got damaged during monsoons. This was followed by laying of the two layers of liner fabrics. The 150 micron LDPE was given cold seal joints with bituminous sealants. The 300 micron fabric was given heat sealed joints. After the two layers of liners were laid, the base of the lake was given a layer of 100mm sand. Along the base, laterite masonry toe wall was built. The sides of the lake was then pitched with random laterite masonry in a lean cement mortar.

Subsurface filter drains
The rain water falling on the roofs as well as the surface run-off from the site is channelised to the lake for recharging it. The conventional storm water drains for surface drainage, besides being expensive; need recurring cleaning and maintenance for satisfactory performance.

To overcome this limitation, it was decided to opt for sub-surface drains. Subsurface drains, when properly designed and constructed need no maintenance and are also capable of draining the soil mass below ground in general. This would prevent water logging.

Considering the catchment area and quantity of water to be drained off, a network of filter drains of various sections have been provide as per drawings attached.

A typical sub surface filter drain consists of a trench lined with non woven polypropylene fabric, filled with graded filter media having a perforated drainage pipe inside. After wrapping the media with PP fabric, the top part of the trench is filled with coarse sand and random laterite. The top surface is finished with a layer of rounded pebbles and where the drains cross vehicular roads, dry open jointed laterite pitching is provided.

To tap rain water from the` larger catchment outside the site, which has the natural drainage through the site, drainage trenches were dug along the compound wall to guide the drainage, then chanelised through a rain water filter and diverted to the lake. The rain water filter has an overflow system which ensures that during very heavy rains, the excess flows out of the site causing no unplanned scouring/ erosions.

The lake ecosystem
The lake has been developed as close to a natural ecosystem as is possible. There is very restricted activity in the lake. While swimming is totally avoided, passive recreation like boating on small coracles can be tried.

Controlled aquaculture with grass carp takes care of the algae control; to ensure that the fish feed on the algae, feeding of fishes by guests / staff is to be totally discouraged.

Purification of water from the lake
The purification system for the harvested rain water consists of a simple pressure sand filtration, activated carbon filtration and chlorination for disinfection.

Treatment and disposal of sewage
In order to optimise the usage of water, the black and grey water (sewage and sullage water from kitchens and bathrooms) is treated and reused for gardening and other non-potable end uses.

Since there is open land available on the site, the main criteria for selection of the system for treatment and recycling of waste water were

requirement of minimum maintenance,
minimum dependence on mechanical systems,
adaptability to varying loads,
adaptability to varying climatic conditions (especially heavy rainfall),
aesthetic appeal and above all
possibility of recycling and safe reuse of water


The system adopted is known as the DEWATS approach (Decentralised Waste water Treatment System). The black water and grey water from the cottages and various blocks are collected in settler tanks. The primary treatment takes place in these settlers.

Within the settler, two main treatment processes take place. First, a mechanical treatment retains contaminants by sedimentation/ floatation and the waste water from the clarified layer flows through the outlet. Second, through biological treatment, the remaining organic pollutants are partly decomposed by micro-organisms. Through the digestion process the accumulated sludge is stabilized. Storage volume for sludge is provided for 18 – 24 months desludging interval. Average reduction of BOD in the settler is expected to be between 20 and 25 %.

For the Kitchen and the Ayurveda Block, oil separators have been installed prior to the Settler to remove excess of oil from the waste water. The collected waste oil is mixed with other bio degradable solid wastes and fed to the bio gas plant installed.

From these settlers, the effluent is taken to the Anaerobic Baffled Reactor for secondary stage of treatment.
In secondary treatment, biological and natural chemical processes are used to digest and remove most of the organic matter.

Several up flow chambers are constructed in series to help digest difficult degradable substances. The sewage flow is directed from top to bottom and up again. During the process the fresh influent is mixed and inoculated for digestion with the active blanket deposit of suspended particles and microorganisms occurring naturally at the bottom (activated sludge) of each chamber in such conditions.

The BOD reduction rate of the baffled reactor is about 75 –85%. The pathogen reduction is in the range of 40 – 75%. The Baffled Reactor is resistant to shock load and variable inflow, the operation and maintenance is simple.

The Horizontal Planted Garvel Filter (also called Root Zone System) forms the tertiary treatment. The planted gravel filter acts through the combined working of the filter material, the plants and the roots in the device. The Horizontal gravel filter is made of reed planted filter bodies consisting of graded gravel. The normal depth is 60cm. The main removal mechanisms are biological conversion, physical filtration and chemical adsorption. Mechanisms of BOD removal are mainly aerobic and anoxic.

After the planted filter, the treated water with BOD less than 30 mg/l is ready for collection for recycling for gardening. The treated water is collected in the Polishing Pond where it becomes “living water again” by undergoing further biological treatment, through natural UV exposure and flowing through an open water body, with all the necessary natural elements such as fish, frogs, dragonflies and different aquatic plants. At this stage the recycled wastewater can be reused without posing any treat to human handling. It is valuable for irrigation; the water is high in nutrient contents and beneficial to plant growth.

Since any treatment system requires flow by gravity it was decided to pump the sullage to an elevated terrain and then let it flow down by gravity. For this an artificial mount has been created using the excavated soil got from excavation of the lake and sullage is pumped to the top of it.
Performance of the system
The significant achievements in this Project could said to be
It is probably among the best examples for total on site water management as one of its strong concepts from the design stage. This had definite advantages that we could treat the system to blend with the landscape, make the most of the levels in the site.
It has helped prove that with the right balance of sensitivity and technology, very high end tourism can be successfully promoted even in very fragile eco systems.
 

 

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