Tuesday, 20 March 2012

My preliminary work is suggesting that the Vortex will hold DO levels in water for up to 8 days (which is when the experiment stopped, not when the DO levels dropped!).

FLOWFORM® OXYGENATION OF WATER Design for Life Company Limited, P O Box 25, Napier, New Zealand Phone + 64 6 833 7541 email info@flowform.net www.flowform.net www.healingwaterinstitute.org.nz Oxygenation, Organic content and pH The effectiveness of a system of wastewater treatment is frequently measured using the following parameters: - Dissolved oxygen: In water with high levels of organic compounds it is likely that dissolved oxygen will be depressed (Tebbut 1992). For biochemical oxidation to occur there must be sufficient aeration that can be measured by the concentration of dissolved oxygen present in the water. - Biochemical oxygen demand: (BOD) can be used as an indication of the concentration of organic compounds in water (Tebbut 1992). Therefore, by measuring the change in biochemical oxygen demand it is possible to determine if the amount of organic material is being reduced. - Faecal coliforms: are an indicator of bacterial and other pathogenic contamination. In ‘The Channon’ in New South Wales, Australia, four test runs in a Flowform system receiving communal laundry water showed the biochemical oxygen demand was reduced from an average of 424 to less than 20 mg/l over a 105 min period. Within this period, faecal coliform counts were reduced from an average of approximately 3100cfu/100ml to a level of 500cfu/100ml, and the amount of dissolved oxygen increased steadily from 0.1 to 3.9 ppm. (The dissolved oxygen (DO) concentration for 100% air saturated water at sea level is 8.6 mg O2/L (ppm) at 25°C and increases to 14.6 mg O2/L (ppm) at 0°C.) These results demonstrate the capacity of the Flowform system to break down organic matter and reduce bacterial contamination (Spencer 1995). In two sample tests conducted in New Zealand in the Fuglistaller farm by the Taranaki Regional Water Board (1989), over a 5 day period with the 50 litre p minute Flowform Järna series treating a 25 cubic metre dairy shed effluent pond at night time only the BOD levels dropped from 280 g/m3 to 88 g/m3. To be sprayed out onto paddocks as liquid fertiliser 30 g/m3 would be needed but as rain came along in day 6 we stopped the trial. It is likely that the BOD would have continued to drop. (Trousdell EDRI Report 1990) In Solborg, Norway, a system of ponds for wastewater treatment using Flowform vessels improved oxygen enrichment from 30% to 90% was detected between the inlet and outlet within the Flowform cascade (Mæhlum 1991, Schönberger and Liess 1995). The continuous rhythmical movements induced by the cascade also prevented freezing of the pond in winter. In the same installation, between the deposition pit and the 3rd pond, the content of chloride in the water was reduced by more than half (Mæhlum 1991, Schönberger and Liess 1995). Since chloride is hardly decomposed in nature, it was supposed that the chloride reduction was caused by intrusion of surrounding water and dilution. Measurements of the inflowing and out flowing water however showed that the reduction of chloride is stronger than would be possible through dilution (Mæhlum 1991). In trials in Holland the transmission coefficients for oxygen in a Flowform cascade were very similar to a meandering step cascade (Flowform Järna 0,39 / Flowform Malmö 0,45 / Flowform Olympia 0,49 / step cascade 0,46) (De Jonge 1982, Schönberger and Liess 1995). Flowform water had a pH-value that increased by 0.77 compared to untreated water, whereas the electrical conductivity decreased. (Brückmann et al. 1992). In New Zealand, oxygenation research was conducted in 1987 and 1988 to how different Flowform design types affected water. The Beehive, Järna and Taruna models were compared. The Hawkes Bay Regional Council water board scientist and Rob Dewdney carried out both field and laboratory tests using a dissolved oxygen meter and the Winkler test. Bore water at 13C with high levels of calcium was run once only through a Flowform cascade with 12 Beehive models, which are 4 and 5 chambered ‘lung’ designs with extra vortical chambers. This method was repeated 20 times to gain average readings. The oxygen readings taken at the start averaging as 1.4 parts per million (ppm) and the end as 7.0 ppm, showing an increase of 5.6 ppm over a distance of 4.8 metres. Each unit increased dissolved oxygen by an average of 0.465 ppm. Similar testing with the Flowform Järna model, which is a ‘kidney’ shape emphasising mixing and polishing, showed an average increase per unit of 0.2 ppm. This was repeated six months later in 1988, but with a cascade of 23 of the same Flowform Beehive models with the same bore water, giving a start reading of 0.7 ppm, a middle reading of 6.4 ppm and the end reading of 8.95 ppm. The water was run through this cascade once only, but again repeatedly with new water to gain average readings. Increase in the last 12 vessels was 0.163 ppm per unit. Oxygenation in water above 9 ppm becomes saturated and is supersaturated above 11 ppm. In order to find out more about Flowform capacity to oxygenate at the (super) saturated dissolved oxygen end range, we ran pre-oxygenated tap water and bore water through a ‘heart-lung’ Taruna cascade, at first just run through once to the 7th unit, and then reticulated repeatedly using a centrifugal pump. The start reading was 8.1 ppm and run once through to the 7th unit, the readings then showed 10.8 ppm. Running a total volume of 800 litres of water for six minutes (at 100 litres per minute) through the cascade gave a reading of 12 ppm, which is super saturated. After three minutes readings were 11.4 ppm. We tested natural oxygenation in the local Tukituki River, reading 12 ppm after 40 metres of gentle rapids, and 7.6 ppm before it. (I. Trousdell 1989) This indicates the need for more research into oxygenation, especially as there are some indications that oxygen which is introduced into water through Flowform activation may stay longer than through the method of spraying the water up into the air. (Chris Weeden, personal communication). This might be a more efficient and durable way of oxygen enrichment possibly because water that is polished through flow movement enriches and elaborates its internal microstructure. Oxygenation Trials at Laverstoke Farm (UK) 2009 Written by Joel Williams B. Agr. Sc (Hons) Agronomist at Laverstoke Park Produce “Thus far, I have primarily investigated the dissolved oxygen (DO) content of water treated with the FF and conventional air pump oxygenated water. Visually, a clear difference immediately arises between the subtle, passive, rhythmical movement through the Flowform® Vortex compared to the aggressive, forceful injection of bubbles of air pumped into water through diffusion tubes. Although both systems have satisfactory capability to aerate waters, once the pumps are turned off, it is the fascinating fact that the FF treated water has an ability to maintain its DO levels compared to the bubble diffuser method which immediately and rapidly declines within minutes. My preliminary work is suggesting that the Vortex will hold DO levels in water for up to 8 days (which is when the experiment stopped, not when the DO levels dropped!). Due to these exciting results, I intend to pursue further investigation and see how long DO levels can be maintained and also to perform a full chemical analysis (macro & micro elements, heavy metals, pH and EC) of treated waters prior to and after treatment through the FF over a period of time. What influence the FF will have over these chemical properties of water remains to be seen. Oxygen is an integral element to all life processes and I also have assessed the ability of the FF to sustain microbiological growth in liquid compost extracts and once again it performed equivalent to conventional aeration methods not only during the aeration process but also after dynamization ceased for the same period of up to 8 days. Microbial activity would normally significantly decline once conventional methods of aeration ceased. Again, I intend to do further work on elucidating the effect of FF treated water on soil microbiology. I can only speak positively about the Flowform™ and its use on our farm. I am more than happy to recommend its use to anyone as I have only had encouraging experiences with its use. Due to this, I have a keen interest in the future of water enhancement with this method and I look forward to contributing to the knowledge base with observational and quantitative data collection from my own experimental work.” Source ......... http://www.flowform.net/files/Oxygenation-Report.pdf





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No chlorine is used in the pool, and the design indicator criterion was that frogs would live in the pool.

REPORT: October 2009 NATURAL SWIMMING POOL using Flowform™ eco-technology in Horowhenua, New Zealand Introduction The swimming pool is a small domestic pool, with a figure 8 shape about 9 m long and 6 m wide. It is about 50 sq m in area and 1.5 m deep. It has been designed to mimic a stream pool, with re-circulating water passing through a small wetland, a Flowform cascade and a holding margin pond. There is about 300 mm of river gravel on the bottom, and the Flowform cascade provides the stream sound effects, as well as their regenerative and energising functions. No chlorine is used in the pool, and the design indicator criterion was that frogs would live in the pool. The pool remains very pleasant and cool even during hot summer periods, and is really refreshing to swim in. We built it because our kids wanted a swimming pool at home, rather than having to drive to the local river — and we were interested in trying out a wetland-based pool, but one more like the pools of the fastflowing gravel bed rivers of New Zealand. Overview The plan and section of the pool shows its overall layout and the recirculation system. A small submersible dewatering pump takes the pool water, through perforated pipes in the gravel layer at the bottom of the pool, and delivers it to bottom-up flow filter ponds of gravel and reeds. From these wetland ponds, the water flows down a vortex-generating pipe, to the Flowform cascade, into the holding pond and back into the swimming pool. The pump flow rate was chosen to match the Flowform flowrate capacity, otherwise the design was based on an overall pattern approach. The system, thus, has the features of a stream environment, linked together in a specific arrangement. It includes: • an area of flow through a gravel matrix with water reeds on top (of the wetland filter ponds); • a still water holding pond of floating plants, like a stream backwater (of the lower pond); • a gravel bed in the main swimming pool; • and a pulsating ‘superstream’ Flowform cascade, like a stream riffle flow, upstream of a deep still water pool. The pond areas are quite small, compared to the main pool size, and the vitalising and energising action of the Flowform cascade is important in the maintenance of water clarity and purity of the whole system. The area around the pool has been planted with a range of species, from grasses, to shrubs, to small trees, to give rise to a complementing outdoor space. River stones have been used as a visual connecting form between the ponds and pool. The arch bridge over the centre of the figure 8, has been a platform for much fun — on and under the bridge — and the narrow connection under a bridge gives rise to two water spaces. The bridge is also the access to a shade gazebo, and a more sheltered area on one side.
Maintenance The swimming pool has been in use for many years, and throughout has provided a refreshing swim in a pleasant and restful environment. At the same time, it has provided an interesting place for our kids to swim and play in, and an especially exciting place for our dog. We have not tested the water for bacterial loads, but have never had any problems. Our younger daughter especially appreciated the lack of chlorine, as she was affected by the chlorine in public and school pools. The main maintenance issue is the build up of algae on the sides of the pool. Any build up on the Flowform units is easily controlled by turning off the water recirculation for a short time (when it is warm and dry). To manage the algae in the pool, we dose it with both alum and gypsum. This was based on research in Australia on how to make small water holes drinkable in droughts, and is very effective. Essentially, it starves the algae of phosphorus, and coagulates and settles the dead algae out onto the gravel bed. It is much cheaper than chlorine-based algaecides, and very much more effective — and unlike the chlorine products, does not affect the frogs. We do clean off some of the dead algae from the bottom, and occasionally add microbial preparations to break it down and allow it to be worked into the gravel matrix on the bottom of the pool. natural quality and feel. Flowform cascade Lower end, with the holding pool below
The Author: Gary Williams lives on a small permaculture farm in the Horowhenua, New Zealand, with his partner Emily. It has a diversity of garden, farm, forest and wilderness, and we use an organic management approach and the practices of biodynamics. He works from home as a consulting engineer on water and soil resource management, and provides advice, design and supervision services to a wide range of clients from individuals to councils and government departments. His latest book, "Out of the Helix", is a series of (word & picture) essays about cultural transformation, and how we can bring about the shift in world-view required to achieve a healthy, just and sustainable way of life. If you want to contact him please email us at info@flowform.net Source ............... http://www.flowform.net/files/Natural-Swimming-Pool-by-Gary-Williams.pdf



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So, a 5 metre long Flowform® cascade is about the same as a 50 metre active stream, in terms of water movement.

POOLS and PONDS Every pond needs a stream to keep it fresh and oxygenated. Flowform® eco-technology is that mountain stream, and in fact it is a Superstream™, oxygenating and rejuvenating your pool or pond water most effectively. When we capture fresh water for our own use, we take it out of Nature, storing and transporting it in ways that reduce its capacity to support life. Flowform® eco-technology helps water support life, but using Nature's best methods of water rejuvenation. It has been effective in many many pools and ponds around the world, creating a refreshed water environment. What is the Superstream Effect™? It is where one forward Flowform® metre is similar to10 metres of natural stream flow with regard to water treatment. This is because the average drop of water flows repeatedly through a side to side, figure-eight in every Flowform® unit. Its like unraveling a figure8 ball of wool... lots of length all wrapped up in a small forward space. So, a 5 metre long Flowform® cascade is about the same as a 50 metre active stream, in terms of water movement. And it is water movement that Nature uses to activate water, to refresh fresh water Do take a look at the Flowform® video above to see this figure8 that is unique to our Flowform® technology. Garden Ponds: We have many instances of our cascades, even a single form, radically changing the quality of the water and the pond life. Fish become lively, the anaerobic algaes and sludges disappear and the water takes on a sparkling fresh look. Lifestyle Property Larger Ponds: many small farmers dig in ponds, collect rain or bore water and then become surprised that it becomes stagnant, supporting mosquito larvae and algaes. Our Flowform® returns the pond to a natural condition, as it would be in the mountains with a stream feeding it, when a cascade is installed. In addition the sculptures, the fascinating moving water and its relaxing splashing sounds add greatly to the landscape.. with greatly reduced or eliminated mosquito and algae infestations. Public Lakes: even small lakes over several acres can be improved using Flowform® cascades, as can be seen in the Lake te Ko Utu project in the Waikato, New Zealand. (see below) Once the water starts to travel through the middle of the still and stagnant body of water, the oxygen and the energetic frequency information spreads out through the whole water through internal currents and molecular passage of substance and frequencies. This can be done by introducing a small amount of artesian water, that is Superstreamed™ into something much more, or by recycling the water from the far side of the lake to the top of the Flowform® cascade down back into the main body of water. This then travels through the lake creating multiple internal streams. Conventional Swimming Pools: The addition of a Flowform® cascade adds greatly to the landscaping and social effect around your pool, while giving your pool what it wants... a mountain stream to treat the water! The water is simply routed from after the filtration system to the top of the cascade, to run directly into the pool through a lively, heart pulse waterfall. With the water no longer being semi-stagnant and in need of chlorine treatment to be safe and clean, you will find you need less chemicals and the water will feel softer and fresher with an extra sparkle to it. Natural Swimming Pools: we have various projects in Europe and New Zealand where home owners have created a natural pond for a family swimming pool, filtered by sand, reeds and rushes and run through a Flowform® cascade to oxygenate and refresh it prior to returning to the pool. Our Flowform® technology is experienced as an essential component of these living systems that needs no chemical treatment at all. Source.......... http://www.flowform.net/pools-and-ponds





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Wednesday, 14 March 2012

Making sense of water - Malvern Garden show 2012

New and very interesting design for this years Garden show at Malvern, 29th - 30th Sep 2012 'Making Sense of Water'























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Wednesday, 7 March 2012

This Saturday, Exploring flow, rhythm and the Flowform idea



Exploring flow, rhythm and
the Flowform idea
To register or for more information please contact Heather:
01453 837 619 heather.fields@ruskin-mill.org.uk
www.thefieldcentre.org.uk

‘Working with Water: Exploring flow, rhythm and the Flowform idea’ with Simon Charter


Join us for a Friday evening lecture and a full day Saturday as we explore the nature of water.
Rhythm is probably revealed in every manifestation of life on earth. It can also be seen as a fundamental aspect of water in movement.
In 1970 John Wilkes discovered how to bring this rhythmic water flow to expression in sculpted vessels which have since been called Flowforms. Many different designs have been made and installed worldwide, enlivening both places and processes. Specific biological benefits are always contextual however and not often reproducible.
This workshop will approach the nature of water in a qualitative way through observation of experimental water phenomena and videos of water in the environment. We will then model with clay and flowing water and see what happens in the conversation between the water and the modeller. Those who wish may try to create a vessel for rhythmic flow. Some work will be individual and some in groups.
There will be a presentation on water quality , its sensitivity and how this can be assessed in movement. This will focus on the work of the Institute of Flow Science in Germany started in 1961 by Theodor Schwenk.
The course will be led by Simon Charter who has been working with and designing Flowforms for 21 years.
Schedule:
Friday, 9 March
7pm – 9pm Evening lecture
Saturday, 10 March
9am – 5pm
Fee:
This workshop will be offered free of charge to anyone who participates in a guided reflection which will be completed during the course. Otherwise, the fee is £50.
Location:
Ruskin Mill Festival Room
Old Bristol Road
Nailsworth GL6 0LA
Meals:
Refreshments and lunches can be purchased on Saturday at The Organic Cafe at Ruskin Mill.
To register contact Heather: heather.fields@ruskin-mill.org.uk
+44(0)1453 837619 +44(0)7805 304 271








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